A | B | C | |
---|---|---|---|
1 | |||
2 | CSRM | ||
3 | Warning Letter with Opportunity to Correct Response Tracking Sheet | ||
5 | Item | Correction Action | Response |
6 | 1 | 1.Submit to DEQ a revised Inventory (AQ520 form), along with all supporting calculations in Excel format, as well as all information as required under OAR 340-245-0040(4), including the following updates: | Today's submittal includes a revised AQ520 form and this workbook provides the supporting calculations. |
7 | 2 | a.Roof monitor (TEU EU-3) and billet cutting (TEUs EU-10 and EU-12): use the data set“Filter Only no Blank Subtraction” instead of the “Filter Only Reagent BlankSubtraction” from the 2019 Emissions Testing report for the “Roof Monitor” and“Billet Cutting” TAC emission factors as the information provided was insufficient to support the validity of the blank corrections. | The "Filter Only no Blank Substraction" dataset has been used to estimate emissions from TEUs EU-3, EU-10, and EU-12 |
8 | 3 | b.Billet cutting (TEUs EU-10 and EU-12): update emissions to reflect existing conditions and emission points for TEU EU-10, as it is currently configured. | The emissions have been update to reflect the current configuration of the caster billet cutting TEU EU-10. |
9 | 4 | c.Melt shop (TEU EU-1): | The "Attachment A" emission factors have been used to update emissions from TEU EU-1, Melt Shop Baghouses. Emissions through the Melt Shop Baghouses (BH-1, BH-1A, BH-2) were alllocated using the same methodology proposed by DEQ for Organic TACs. |
10 | i.Include emission estimates for the following TACs, including any expected fugitive emissions, using emission factors listed in | ||
11 | “Attachment A. Emission Factors for Persistent Organic Pollutants and Polycyclic AromaticHydrocarbons”: | ||
12 | 1.Polychlorinated dibenzo-p-dioxins (PCDDs) & dibenzofurans (PCDFs)TEQ (DEQ SEQ ID 646); | ||
13 | 2.PCBs TEQ (DEQ SEQ ID 645); | ||
14 | 3.Polycyclic aromatic hydrocarbons (PAHs; DEQ SEQ ID 401)2; | ||
15 | 4.Benzo[a]pyrene (CASRN 50-32-8); | ||
16 | 5.Naphthalene (CASRN 91-20-3); | ||
17 | 6.Hexachlorobenzene (CASRN 118-74-1); and | ||
18 | 7.Polybrominated diphenyl ethers (PBDEs; DEQ SEQ ID 401); | ||
19 | 5 | d.Melt shop baghouses (TEU EU-1, baghouse BH-1): | Phosphorous emissions have been included in the TEU EU-1, baghouse BH-1 emission estimate. |
20 | i.Include emissions for phosphorus (DEQ ID 504), for consistency with detections in the 2013 Filter Testing data. | ||
21 | Phosphorus was detected in BH-1A,sample Run #3 at 50 mg/kg; | ||
22 | 6 | e.Melt shop baghouses (TEU EU-1, baghouses BH-1, BH-1A, and BH-2): | CSRM discontinued the practice of disposing of baghouse bags in the EAF in November of 2020. Fluoride emissions from baghouse bag burning has been removed from the emissions inventory. |
23 | i.Update fluoride (DEQ SEQ ID 239) emissions as follows: | ||
24 | 1.Update the daily fluoride emissions calculation for the burning ofbaghouse bags in BH-1 to use throughput in number of baghouse bagsburned instead of tons of steel produced; and | ||
25 | 2. Apportion fluoride emissions from TEU EU-1 to baghouses BH-1, BH-1A, and BH-2, as appropriate. | ||
26 | 7 | ii. Update organic TAC emissions estimates to: | The method used in 1.ii.e.3 was used to update organic TAC emissions from TEU EU-1 baghouses BH-1, BH-1A and BH-2. |
27 | 1. Include all TACs which have emissions information available in the “Electric Arc Furnace Baghouse Gases Emissions Test Report” (dated March 3, 1995, and provided as Attachment C); | ||
28 | 2. Include emissions from BH-2, accounting for additional emissions expected due to the increased collection efficiency achieved with the installation of BH-2; | ||
29 | 3. To satisfy requirements 1 and 2 above, emissions for BH-1, BH-1A, and BH-2 may be calculated as shown in Attachment D, using source test data for BH-1, documented baghouse flow rates, and the VOC calculation methodology used in the Title V Permit Review Report (page 27). Alternatively, justification may be provided for a different estimate. | ||
30 | 8 | iii. Update emission factors for the 7 MMBtu/hr Electric Arc Furnace burner (TEU EU-16_ng) to match the emission factors in the “Oregon DEQ 2020 Air Toxic Emissions Inventory Combustion Emission Factor Tool” for the “Natural Gas External Combustion, emission units < 10 MMBTU/hr”. | The emission factors have been updated. |
31 | 9 | f. Melt shop fugitive emissions (TEU EU-1, emission point MELTFUG): | The emission factors provided in Table B-4 for scrap billet cutting have been updated to reflect uncontrolled emissions. Associated baghouse and fugitive emissions are calculated based on the capture and removal efficiencies shown in Table B-4. It is noted that scrap billet cutting has been designated TEU EU-12. |
32 | i. In the supporting calculations, update the fugitive portion of the scrap billet cutting emissions (TEU EU-1, emission point MELTFUG) to use the uncontrolled emission factor rather than the controlled emission factor; alternatively fugitive emissions may be calculated separately for EU-1, EU-10, and EU-12 in both supporting calculations and the AQ520. | ||
33 | 10 | ii. In the supporting calculations, update the fugitive portion of the scrap billet cutting emissions (TEU EU-1, emission point MELTFUG) to correctly sum emissions from scrap billet cutting and the melt shop using consistent units (for example, pounds per tons of steel processed); alternatively fugitive emissions may be calculated separately for EU-1, EU-10, and EU-12 in both supporting calculations and the AQ520; and | The 10/10/22 version of the supporting calculations contained a cell reference error when summing the emissions at the MELTFUG emission point and this has been corrected. |
34 | 11 | iii. Update the daily Fluoride (DEQ SEQ ID 239) emissions calculation to use throughput in number of baghouse bags burned instead of tons of steel produced. | See comment to corrective action item 1.e above. |
35 | 12 | g. Roof monitor (TEU EU-3): | The daily emission calculations have been updated to use the daily emission factor instead of the annual emission factor |
36 | i. Update the daily emission calculations to use the daily emission factor instead of the annual emission factor; and | ||
37 | 13 | ii. Include emissions for mercury (CASRN 7439-97-6) as 0.00043 percent of particulate matter, as listed in CSRM’s Permit Review Report (36-5034-TV-01, Page 59). | Emissions of mercury (CASRN 7439-97-6) as 0.00043 percent of particulate matter, as listed in CSRM’s Permit Review Report (36-5034-TV-01, Page 59) has been included in conjunction with the PM10 emission factor in CSRM's Permit Review Report (36-5034-TV-01, Page 29). |
38 | 14 | h. Slag handling (TEU EU-5): | Zinc emission factor updated. |
39 | i. Update zinc (CASRN 7440-66-6) emission factors to reflect the analytical result of 160 mg/kg listed in the slag analytical report (currently the analytical result is listed as 16 mg/kg); | ||
40 | 15 | ii. Update the “Max Daily – Acute” emission factor to use a representative maximum daily average wind speed for unenclosed drop points; and | The Max Daily Acute emission factor has been updated using a 5-yr maxium daily average wind speed. |
41 | 16 | iii. Include emission estimates for the following TAC species, using concentrations listed in Attachment A: | Emission estimates for these species has been included based on the Appendix A information provided by DEQ. |
42 | 1. PCDDs & PCDFs TEQ (DEQ SEQ ID 646); and | ||
43 | 2. PCBs TEQ (DEQ SEQ ID 645); | ||
44 | 17 | i. Gasoline Dispensing Facility (TEU EU-15): |
VOC emissions from the GDF horizontal tank have been calculated
based on AP-42, Section 7.1.3 and these calculations are provided. The TCEQ guidance has been used to calcuate daily VOC working losses as requested. TAC emissions have been updated based on the speciation data provided by DEQ as requested. |
45 | i. Calculate VOC emissions from tank filling, breathing, and emptying using the methodology presented in AP-42, Section 7.1.3; | ||
46 | ii. Calculate daily VOC working losses using the attached methodology from the TCEQ (provided with DEQ’s August 26, 2022 letter) - assume maximum daily emissions are equal to maximum hourly emissions multiplied by the maximum hours of tank filling. Provide justification for the worst-case liquid temperature used, or assume the TCEQ default of 95 degrees F; and | ||
47 | iii. Include a complete set of TACs emitted from the gasoline dispensing facility - in the absence of site-specific gasoline composition data, the TAC speciation provided with DEQ’s August 26, 2022 letter may be used. | ||
48 | 18 | j. Include estimated emissions from scrap handling and unpaved roads: | CSRM submitted a dust sampling plan to DEQ on January 30, 2023. As described in that submission CSRM has proactively collected representative dust samples and we are including associated analytical results and TAC emissions estimates for scrap handling (EU-9) and unpaved roads (EU-11) with this emissions inventory for DEQ's consideration of the overall approach to estimating emissions from these sources. |
49 | i. Use established methodologies to determine PM emissions and site-specific dust sampling analysis to speciate TACs for the following TEUs: | ||
50 | 1. Scrap handling (permitted emission unit EU-9); and | ||
51 | 19 | 2. Fugitive dust from unpaved roads (permitted emission unit EU-11); and |
52 | ii. The dust sampling plan must be approved by DEQ prior to sampling and should include, at a minimum, heavy metal TACs, fluorides, PCDD/PCDFs, and PCBs. | ||
---|---|---|---|
53 | 20 | k. Revise the Inventory to include emissions from maintenance shops and routine maintenance activities (including incidental welding and miscellaneous chemical usage), or provide justification for exemption per OAR 340-245-0060(3)(a). |
The emissions inventory has been updated to include emissions
from electric arc welding. In November 2021 DEQ updated the CAO rules and revised the list of activities that could be considered Categorically Insignificant Activities (CIA) for the purposes of preparing a CAO emissions inventory (EI) and risk assessment. The rule changes resulted in fifteen different types of activities that under the original CAO rules were considered exempt TEUs and did not need to be included in a CAO assessment. Those fifteen activities were listed in the “Cleaner Air Oregon Exempt TEU Reporting” guidance document issued by DEQ on March 21, 2022. Attachment I provides an assessment of those activities and how they are addressed in this CAO EI. |
54 | 21 | l. Revise the AQ520 as follows: | An AQ520 Form is enclosed with this submission and it includes the updates requested in items 1.I.i and 1.I.ii. |
55 | i. Update the “Reference/Notes” column in Tab 3 to fully specify the source of the emission factor for each TEU and TAC (for example, AP-42, WebFire, specific source tests, etc.) and any related notes (for example, control efficiency references); and | ||
56 | ii. Update the “Control Efficiency” column in Tab 3 to specify the total combined control efficiency for each pollutant from the specificied TEU and TAC, when the control efficiency is known or estimated. | ||
57 | 22 | 2. Please provide the following additional documentation to support the emissions inventory: | Attachment J provides the raw material usage information requested. We note that Cascade does not use a "slag oxidizing agent" as a raw material but calcium carbide and silicon carbide are used as de-oxidizing agents and associated raw material usage information is also provided in Attachment J. |
58 | a. For all raw materials used, including but not limited to the slag oxidizing agent and molten metal additives: | ||
59 | i. Safety Data Sheets; and | ||
60 | ii. Estimated maximum annual and daily usage rates; | ||
61 | 23 | b. Substantiation for emissions of fluorides (DEQ SEQ ID 239), including testing data used in the development of permitted emission factors, as well as an explanation of why the emission factor listed in AP-42, Section 12.5.1, Table 5-9 (0.059 pounds F per ton steel produced) is not representative of emissions from the EAF and melt shop; | Please see Attachment H for a discussion of Fluoride emissions. |
62 | 24 | c. A detailed description of the wastewater system, including a process flow diagram, characterization of wastewater including available analytical data, and a description of each process unit and wastewater point of use; | Please see Attachment K for a response to this corrective action. |
63 | 25 | d. A detailed description of the slag wetting process, including: | See responses in red adjacent. |
64 | i. Location; (along a wall just northeast of the meltshop) | ||
65 | ii. Whether process is batch or continous (batch) | ||
66 | iii. Approximate temperature of slag; (~1800F) | ||
67 | iv. Source of water used and method of wetting; and (City water is used. The oxidizing agent is added via inline injection to a recirculating loop. A spray bar equipped with ~10 nozzles is used to wet the slag) | ||
68 | v. Amount of water applied, per ton slag handled; and (The spray bars apply about 120 gpm of water to the slag over a period of about 10 hours. At this flow rate and duration and assuming 370 tons of slag produced in a batch the amount of water applied would be about 195 gallons per ton of slag handled. | ||
69 | 26 | e. Description of process assumptions used to determine the 90% effectiveness factor for oxidation of hydrogen sulfide from the data reported in Rehmus et al, 1973. | Based on a review of the 1973 Rehmus paper and CSRM slag handling operations the effectiveness of the oxidizing agent has been reduced to 75% |
A | B | C | D | E | F | G | H | I | J | K | L | M | N | O | P | Q | R | S | T | U | V | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Attachment B - Emission Calculations | |||||||||||||||||||||
2 | Table B-1: Scrap Cutting and Handling Emissions | |||||||||||||||||||||
3 | ||||||||||||||||||||||
4 | Toxics Emission Unit ID: | EU-09sp | ||||||||||||||||||||
5 | Emission Point: | BH01 | ||||||||||||||||||||
6 | BH01A | |||||||||||||||||||||
7 | MELTFUG | |||||||||||||||||||||
8 | Description: | Metal TACs emissions from a torch cutting metal scrap (scrap preparation) | ||||||||||||||||||||
9 | ||||||||||||||||||||||
10 | Toxics Emission Unit ID: | EU-09ng | ||||||||||||||||||||
11 | Emission Point: | BH01 | ||||||||||||||||||||
12 | BH01A | |||||||||||||||||||||
13 | MELTFUG | |||||||||||||||||||||
14 | Description: | Natural gas combustion byproduct TAC emissions | ||||||||||||||||||||
15 | ||||||||||||||||||||||
16 | Toxics Emission Unit ID: | EU-09sh_Main | ||||||||||||||||||||
17 | Emission Point: | SH_Main | ||||||||||||||||||||
18 | Description: | Fugitive emissions of metal TACs from handling metal scrap (scrap handling main yard) | ||||||||||||||||||||
19 | ||||||||||||||||||||||
20 | Toxics Emission Unit ID: | EU-09sh_Sec | ||||||||||||||||||||
21 | Emission Point: | SH_Sec | ||||||||||||||||||||
22 | Description: | Fugitive emissions of metal TACs from handling metal scrap (scrap handling secondary pile) | ||||||||||||||||||||
23 | ||||||||||||||||||||||
24 | ||||||||||||||||||||||
25 | ||||||||||||||||||||||
26 | ||||||||||||||||||||||
27 | ||||||||||||||||||||||
28 | ||||||||||||||||||||||
29 | ||||||||||||||||||||||
30 | ||||||||||||||||||||||
31 | ||||||||||||||||||||||
32 | ||||||||||||||||||||||
33 | ||||||||||||||||||||||
34 | ||||||||||||||||||||||
35 | ||||||||||||||||||||||
36 | ||||||||||||||||||||||
37 | ||||||||||||||||||||||
38 | ||||||||||||||||||||||
39 | ||||||||||||||||||||||
40 | ||||||||||||||||||||||
41 | ||||||||||||||||||||||
42 | Operating Parameters & Input Assumptions: | |||||||||||||||||||||
43 | ||||||||||||||||||||||
44 | # torches | 1 | ||||||||||||||||||||
45 | Operating Hours | 8 | hrs/day | |||||||||||||||||||
46 | Operating Hours | 520 | hrs/yr | |||||||||||||||||||
47 | Gas Flow Rate | 30 | CFH per torch (see included cut sheet) | |||||||||||||||||||
48 | Annual Gas Usage | 15,600 | CF/yr | |||||||||||||||||||
49 | Daily Gas Usage | 240 | CF/day | |||||||||||||||||||
50 | PM Emission Rate | 0.06 | lb/hr (for torch cutting see included : Versar, "Title V Applicability Workbook", for Institute of Scrap Recycling Industries, 1996., Table D-5) |
51 | BH-1/1A Removal Eff. | 95% | ||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | BH-1/1A Capture Eff. | 95% | ||||||||||||||||||||
53 | ||||||||||||||||||||||
54 | Scrap Handling Rate (main) | 8,140 | tons/day (steel production rate + 10% X 2 for total quantity received and remove from area) | |||||||||||||||||||
55 | Scrap Handling Rate (main) | 1,584,000 | tons/yr (steel production rate + 10% X 2 for total quantity received and remove from area) | |||||||||||||||||||
56 | Scrap Handling Rate (secondary) | 2,011 | tons/day | |||||||||||||||||||
57 | Scrap Handling Rate (secondary) | 333,510 | tons/yr (maximum month in 2022 X 12 months * 2 for total quantity received and remove from the area) | |||||||||||||||||||
58 | ||||||||||||||||||||||
59 | EPA Drop Equation: AP-42 13.2.4 | |||||||||||||||||||||
60 | ||||||||||||||||||||||
61 | Wind Speed, daily | 20.85 | mph (meterological data - McMinnville WS - 5-yr max. daily average based on 2014-2018 data) | |||||||||||||||||||
62 | Wind Speed, annual | 6.66 | mph (meterological data - McMinnville WS - 5-yr average based on 2014-2018 data) | |||||||||||||||||||
63 | k factor | 0.35 | unitless (for PM10) | |||||||||||||||||||
64 | % moisture content, daily | 0.25 | % | |||||||||||||||||||
65 | % moisture content, annual | 0.25 | % | |||||||||||||||||||
66 | PM emission factor, daily (uncontrolled) | 0.1317 | lb/ton | |||||||||||||||||||
67 | PM emission factor, annual (uncontrolled) | 0.0299 | lb/ton | |||||||||||||||||||
68 | ||||||||||||||||||||||
69 | Water Spray Control Factor | 72% | ||||||||||||||||||||
70 | ||||||||||||||||||||||
71 | PM emission factor, daily | 0.0370 | lb/ton | |||||||||||||||||||
72 | PM emission factor, annual | 0.0084 | lb/ton | |||||||||||||||||||
73 | ||||||||||||||||||||||
74 | ||||||||||||||||||||||
75 | ||||||||||||||||||||||
76 | Scrap Cutting @ Melt Shop Charge Bay: EU-09sp Controlled by BH-1/1A (emission point BH01/BH01A) | |||||||||||||||||||||
77 | 83.3% | 16.7% | ||||||||||||||||||||
78 | BH01 | BH01A | ||||||||||||||||||||
79 | CAS or DEQ ID | TAC | wt.% | Annual & Daily EF (lb/hr) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Ref | |||||||||||
80 | 7439-96-5 | Manganese and Compounds | 1.13 | 0.000678 | 1.67E-02 | 2.58E-04 | 1.39E-02 | 2.15E-04 | 2.80E-03 | 4.30E-05 | Versar, "Title V Applicability Workbook", for Institute of Scrap Recycling Industries, 1996., Table D-5 & CSRM internal steel specification. Overall control efficiency estimate based on 95% control (EPA-452/F-03-025) and 95% capture (estimated). | |||||||||||
81 | 7440-50-8 | Copper and Compounds | 0.28 | 0.000168 | 4.15E-03 | 6.38E-05 | 3.46E-03 | 5.32E-05 | 6.93E-04 | 1.07E-05 | ||||||||||||
82 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.15 | 0.00009 | 2.22E-03 | 3.42E-05 | 1.85E-03 | 2.85E-05 | 3.71E-04 | 5.71E-06 | ||||||||||||
83 | 365 | Nickel Compounds, Insoluble | 0.08 | 0.000048 | 1.19E-03 | 1.82E-05 | 9.88E-04 | 1.52E-05 | 1.98E-04 | 3.05E-06 | ||||||||||||
84 | 7440-62-2 | Vanadium (fume or dust) | 0.005 | 0.000003 | 7.41E-05 | 1.14E-06 | 6.17E-05 | 9.50E-07 | 1.24E-05 | 1.90E-07 | ||||||||||||
85 | 7439-92-1 | Lead and Compounds | 0.004 | 0.0000024 | 5.93E-05 | 9.12E-07 | 4.94E-05 | 7.60E-07 | 9.90E-06 | 1.52E-07 | ||||||||||||
86 | ||||||||||||||||||||||
87 | ||||||||||||||||||||||
88 | Scrap Cutting @ Melt Shop Charge Bay: EU-09sp Fugitives (emission point MELTFUG) | |||||||||||||||||||||
89 | ||||||||||||||||||||||
90 | MELTFUG | |||||||||||||||||||||
91 | CAS or DEQ ID | TAC | wt.% | Annual & Daily EF (lb/hr) | Emission Rate (lb/yr) | Emission Rate (lb/day) | ||||||||||||||||
92 | 7439-96-5 | Manganese and Compounds | 1.13 | 0.000678 | 1.76E-02 | 2.71E-04 | Versar, "Title V Applicability Workbook", for Institute of Scrap Recycling Industries, 1996., Table D-5 & CSRM internal steel specification. Overall control efficiency estimate based on 95% control (EPA-452/F-03-025) and 95% capture (estimated). | |||||||||||||||
93 | 7440-50-8 | Copper and Compounds | 0.28 | 0.000168 | 4.37E-03 | 6.72E-05 | ||||||||||||||||
94 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.15 | 0.00009 | 2.34E-03 | 3.60E-05 | ||||||||||||||||
95 | 365 | Nickel Compounds, Insoluble | 0.08 | 0.000048 | 1.25E-03 | 1.92E-05 | ||||||||||||||||
96 | 7440-62-2 | Vanadium (fume or dust) | 0.005 | 0.000003 | 7.80E-05 | 1.20E-06 | ||||||||||||||||
97 | 7439-92-1 | Lead and Compounds | 0.004 | 0.0000024 | 6.24E-05 | 9.60E-07 | ||||||||||||||||
98 | ||||||||||||||||||||||
99 | ||||||||||||||||||||||
100 |
101 | ||||||||||||||||||||||
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102 | ||||||||||||||||||||||
103 | 83.3% | 16.7% | ||||||||||||||||||||
104 | Scrap Torch Cutting NG Emissions: EU-09ng Emissions at BH01/BH01A | BH01 | BH01A | |||||||||||||||||||
105 | CAS or DEQ ID | TAC | Annual & Daily EF (lb/MMSCF) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||||||||||||
106 | 71-43-2 | Benzene | 0.008 | 1.19E-04 | 1.82E-06 | 9.88E-05 | 1.52E-06 | 1.98E-05 | 3.05E-07 | Oregon DEQ 2020 ATEI Combustion EF Tool. 0% control assumed for natural gas combustion emissions | ||||||||||||
107 | 50-00-0 | Formaldehyde | 0.017 | 2.52E-04 | 3.88E-06 | 2.10E-04 | 3.23E-06 | 4.21E-05 | 6.47E-07 | |||||||||||||
108 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.0001 | 1.48E-06 | 2.28E-08 | 1.23E-06 | 1.90E-08 | 2.47E-07 | 3.81E-09 | |||||||||||||
109 | 50-32-8 | Benzo[a]pyrene | 0.0000012 | 1.78E-08 | 2.74E-10 | 1.48E-08 | 2.28E-10 | 2.97E-09 | 4.57E-11 | |||||||||||||
110 | 91-20-3 | Naphthalene | 0.0003 | 4.45E-06 | 6.84E-08 | 3.70E-06 | 5.70E-08 | 7.42E-07 | 1.14E-08 | |||||||||||||
111 | 75-07-0 | Acetaldehyde | 0.0043 | 6.37E-05 | 9.80E-07 | 5.31E-05 | 8.17E-07 | 1.06E-05 | 1.64E-07 | |||||||||||||
112 | 107-02-8 | Acrolein | 0.0027 | 4.00E-05 | 6.16E-07 | 3.33E-05 | 5.13E-07 | 6.68E-06 | 1.03E-07 | |||||||||||||
113 | 7664-41-7 | Ammonia | 18 | 2.67E-01 | 4.10E-03 | 2.22E-01 | 3.42E-03 | 4.45E-02 | 6.85E-04 | |||||||||||||
114 | 7440-38-2 | Arsenic and compounds | 0.0002 | 2.96E-06 | 4.56E-08 | 2.47E-06 | 3.80E-08 | 4.95E-07 | 7.62E-09 | |||||||||||||
115 | 7440-39-3 | Barium and compounds | 0.0044 | 6.52E-05 | 1.00E-06 | 5.43E-05 | 8.36E-07 | 1.09E-05 | 1.68E-07 | |||||||||||||
116 | 7440-41-7 | Beryllium and compounds | 0.000012 | 1.78E-07 | 2.74E-09 | 1.48E-07 | 2.28E-09 | 2.97E-08 | 4.57E-10 | |||||||||||||
117 | 7440-43-9 | Cadmium and compounds | 0.0011 | 1.63E-05 | 2.51E-07 | 1.36E-05 | 2.09E-07 | 2.72E-06 | 4.19E-08 | |||||||||||||
118 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.0014 | 2.07E-05 | 3.19E-07 | 1.73E-05 | 2.66E-07 | 3.46E-06 | 5.33E-08 | |||||||||||||
119 | 7440-48-4 | Cobalt and compounds | 0.000084 | 1.24E-06 | 1.92E-08 | 1.04E-06 | 1.60E-08 | 2.08E-07 | 3.20E-09 | |||||||||||||
120 | 7440-50-8 | Copper and compounds | 0.00085 | 1.26E-05 | 1.94E-07 | 1.05E-05 | 1.61E-07 | 2.10E-06 | 3.24E-08 | |||||||||||||
121 | 100-41-4 | Ethyl benzene | 0.0095 | 1.41E-04 | 2.17E-06 | 1.17E-04 | 1.80E-06 | 2.35E-05 | 3.62E-07 | |||||||||||||
122 | 110-54-3 | Hexane | 0.0063 | 9.34E-05 | 1.44E-06 | 7.78E-05 | 1.20E-06 | 1.56E-05 | 2.40E-07 | |||||||||||||
123 | 7439-92-1 | Lead and compounds | 0.0005 | 7.41E-06 | 1.14E-07 | 6.17E-06 | 9.50E-08 | 1.24E-06 | 1.90E-08 | |||||||||||||
124 | 7439-96-5 | Manganese and compounds | 0.00038 | 5.63E-06 | 8.66E-08 | 4.69E-06 | 7.22E-08 | 9.40E-07 | 1.45E-08 | |||||||||||||
125 | 7439-97-6 | Mercury and compounds | 0.00026 | 3.85E-06 | 5.93E-08 | 3.21E-06 | 4.94E-08 | 6.43E-07 | 9.90E-09 | |||||||||||||
126 | 1313-27-5 | Molybdenum trioxide | 0.00165 | 2.45E-05 | 3.76E-07 | 2.04E-05 | 3.13E-07 | 4.08E-06 | 6.28E-08 | |||||||||||||
127 | 365 | Nickel compounds, insoluble | 0.0021 | 3.11E-05 | 4.79E-07 | 2.59E-05 | 3.99E-07 | 5.20E-06 | 8.00E-08 | |||||||||||||
128 | 7782-49-2 | Selenium and compounds | 0.000024 | 3.56E-07 | 5.47E-09 | 2.96E-07 | 4.56E-09 | 5.94E-08 | 9.14E-10 | |||||||||||||
129 | 108-88-3 | Toluene | 0.0366 | 5.42E-04 | 8.34E-06 | 4.52E-04 | 6.95E-06 | 9.06E-05 | 1.39E-06 | |||||||||||||
130 | 7440-62-2 | Vanadium (fume or dust) | 0.0023 | 3.41E-05 | 5.24E-07 | 2.84E-05 | 4.37E-07 | 5.69E-06 | 8.76E-08 | |||||||||||||
131 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.0272 | 4.03E-04 | 6.20E-06 | 3.36E-04 | 5.17E-06 | 6.73E-05 | 1.04E-06 | |||||||||||||
132 | 7440-66-6 | Zinc and compounds | 0.029 | 4.30E-04 | 6.61E-06 | 3.58E-04 | 5.51E-06 | 7.18E-05 | 1.10E-06 | |||||||||||||
133 | ||||||||||||||||||||||
134 | ||||||||||||||||||||||
135 | Scrap Torch Cutting NG Emissions: EU-09ng Emissions at MELTFUG | |||||||||||||||||||||
136 | CAS or DEQ ID | TAC | Annual & Daily EF (lb/MMSCF) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||||||||||||||||
137 | 71-43-2 | Benzene | 0.008 | 6.24E-06 | 9.60E-08 | Oregon DEQ 2020 ATEI Combustion EF Tool. 0% control assumed for natural gas combustion emissions | ||||||||||||||||
138 | 50-00-0 | Formaldehyde | 0.017 | 1.33E-05 | 2.04E-07 | |||||||||||||||||
139 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.0001 | 7.80E-08 | 1.20E-09 | |||||||||||||||||
140 | 50-32-8 | Benzo[a]pyrene | 0.0000012 | 9.36E-10 | 1.44E-11 | |||||||||||||||||
141 | 91-20-3 | Naphthalene | 0.0003 | 2.34E-07 | 3.60E-09 | |||||||||||||||||
142 | 75-07-0 | Acetaldehyde | 0.0043 | 3.35E-06 | 5.16E-08 | |||||||||||||||||
143 | 107-02-8 | Acrolein | 0.0027 | 2.11E-06 | 3.24E-08 | |||||||||||||||||
144 | 7664-41-7 | Ammonia | 18 | 1.40E-02 | 2.16E-04 | |||||||||||||||||
145 | 7440-38-2 | Arsenic and compounds | 0.0002 | 1.56E-07 | 2.40E-09 | |||||||||||||||||
146 | 7440-39-3 | Barium and compounds | 0.0044 | 3.43E-06 | 5.28E-08 | |||||||||||||||||
147 | 7440-41-7 | Beryllium and compounds | 0.000012 | 9.36E-09 | 1.44E-10 | |||||||||||||||||
148 | 7440-43-9 | Cadmium and compounds | 0.0011 | 8.58E-07 | 1.32E-08 | |||||||||||||||||
149 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.0014 | 1.09E-06 | 1.68E-08 | |||||||||||||||||
150 | 7440-48-4 | Cobalt and compounds | 0.000084 | 6.55E-08 | 1.01E-09 |
151 | 7440-50-8 | Copper and compounds | 0.00085 | 6.63E-07 | 1.02E-08 | |||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
152 | 100-41-4 | Ethyl benzene | 0.0095 | 7.41E-06 | 1.14E-07 | |||||||||||||||||
153 | 110-54-3 | Hexane | 0.0063 | 4.91E-06 | 7.56E-08 | |||||||||||||||||
154 | 7439-92-1 | Lead and compounds | 0.0005 | 3.90E-07 | 6.00E-09 | |||||||||||||||||
155 | 7439-96-5 | Manganese and compounds | 0.00038 | 2.96E-07 | 4.56E-09 | |||||||||||||||||
156 | 7439-97-6 | Mercury and compounds | 0.00026 | 2.03E-07 | 3.12E-09 | |||||||||||||||||
157 | 1313-27-5 | Molybdenum trioxide | 0.00165 | 1.29E-06 | 1.98E-08 | |||||||||||||||||
158 | 365 | Nickel compounds, insoluble | 0.0021 | 1.64E-06 | 2.52E-08 | |||||||||||||||||
159 | 7782-49-2 | Selenium and compounds | 0.000024 | 1.87E-08 | 2.88E-10 | |||||||||||||||||
160 | 108-88-3 | Toluene | 0.0366 | 2.85E-05 | 4.39E-07 | |||||||||||||||||
161 | 7440-62-2 | Vanadium (fume or dust) | 0.0023 | 1.79E-06 | 2.76E-08 | |||||||||||||||||
162 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.0272 | 2.12E-05 | 3.26E-07 | |||||||||||||||||
163 | 7440-66-6 | Zinc and compounds | 0.029 | 2.26E-05 | 3.48E-07 | |||||||||||||||||
164 | ||||||||||||||||||||||
165 | ||||||||||||||||||||||
166 | ||||||||||||||||||||||
167 | ||||||||||||||||||||||
168 | ||||||||||||||||||||||
169 | ||||||||||||||||||||||
170 | ||||||||||||||||||||||
171 | ||||||||||||||||||||||
172 | Main Pile Scrap Handling Emissions: (Emission point SH_Main) | |||||||||||||||||||||
173 | ||||||||||||||||||||||
174 | CAS or DEQ ID | TAC | Mass Fraction (mg/kg) | Annual EF (lb/ton) | Daily EF (lb/ton) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||||||||||||||
175 | 7429-90-5 | Aluminum and Compounds | 14300 | 1.20E-04 | 5.29E-04 | 1.90E+02 | 4.30E+00 | Texas Commission on Environmental Quality (TCEQ) Guidance for Rock Crushing Plants, pgs 12-13 | ||||||||||||||
176 | 7440-36-0 | Antimony and Compounds | 17 | 1.43E-07 | 6.29E-07 | 2.26E-01 | 5.12E-03 | |||||||||||||||
177 | 7440-38-2 | Arsenic and Compounds | 21.9 | 1.84E-07 | 8.10E-07 | 2.91E-01 | 6.59E-03 | |||||||||||||||
178 | 7440-41-7 | Beryllium and Compounds | 0 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||
179 | 7440-43-9 | Cadmium and Compounds | 15 | 1.26E-07 | 5.55E-07 | 1.99E-01 | 4.52E-03 | |||||||||||||||
180 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 24.5 | 2.06E-07 | 9.06E-07 | 3.26E-01 | 7.38E-03 | |||||||||||||||
181 | 7440-48-4 | Cobalt and Compounds | 31.3 | 2.63E-07 | 1.16E-06 | 4.16E-01 | 9.42E-03 | |||||||||||||||
182 | 7440-50-8 | Copper and Compounds | 977 | 8.20E-06 | 3.61E-05 | 1.30E+01 | 2.94E-01 | |||||||||||||||
183 | 7439-92-1 | Lead and Compounds | 829 | 6.95E-06 | 3.07E-05 | 1.10E+01 | 2.50E-01 | |||||||||||||||
184 | 7439-96-5 | Manganese and Compounds | 3970 | 3.33E-05 | 1.47E-04 | 5.27E+01 | 1.20E+00 | |||||||||||||||
185 | 7439-97-6 | Mercury and Compounds | 1.03 | 8.64E-09 | 3.81E-08 | 1.37E-02 | 3.10E-04 | |||||||||||||||
186 | 365 | Nickel compounds, insoluble | 220 | 1.85E-06 | 8.14E-06 | 2.92E+00 | 6.62E-02 | |||||||||||||||
187 | 7782-49-2 | Selenium and Compounds | 0 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||
188 | 7440-22-4 | Silver and compounds | 2.93 | 2.46E-08 | 1.08E-07 | 3.89E-02 | 8.82E-04 | |||||||||||||||
189 | 7440-28-0 | Thallium and compounds | 0 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||
190 | 504 | Phosphorus and Compounds | 0 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||
191 | 7440-62-2 | Vanadium (fume or dust) | 84.8 | 7.11E-07 | 3.14E-06 | 1.13E+00 | 2.55E-02 | |||||||||||||||
192 | 7440-66-6 | Zinc and Compounds | 15300 | 1.28E-04 | 5.66E-04 | 2.03E+02 | 4.61E+00 | |||||||||||||||
193 | 7440-39-3 | Barium and compounds | 560 | 4.70E-06 | 2.07E-05 | 7.44E+00 | 1.69E-01 | |||||||||||||||
194 | ||||||||||||||||||||||
195 | ||||||||||||||||||||||
196 | Secondary Pile Scrap Handling Emissions (Emission point: SH_Sec) | |||||||||||||||||||||
197 | ||||||||||||||||||||||
198 | CAS or DEQ ID | TAC | Mass Fraction (mg/kg) | Annual EF (lb/ton) | Daily EF (lb/ton) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||||||||||||||
199 | 7429-90-5 | Aluminum and Compounds | 14300 | 1.20E-04 | 5.29E-04 | 4.00E+01 | 1.06E+00 | Texas Commission on Environmental Quality (TCEQ) Guidance for Rock Crushing Plants, pgs 12-13 | ||||||||||||||
200 | 7440-36-0 | Antimony and Compounds | 17 | 1.43E-07 | 6.29E-07 | 4.76E-02 | 1.26E-03 |
201 | 7440-38-2 | Arsenic and Compounds | 21.9 | 1.84E-07 | 8.10E-07 | 6.13E-02 | 1.63E-03 | |||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
202 | 7440-41-7 | Beryllium and Compounds | 0 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||
203 | 7440-43-9 | Cadmium and Compounds | 15 | 1.26E-07 | 5.55E-07 | 4.20E-02 | 1.12E-03 | |||||||||||||||
204 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 24.5 | 2.06E-07 | 9.06E-07 | 6.85E-02 | 1.82E-03 | |||||||||||||||
205 | 7440-48-4 | Cobalt and Compounds | 31.3 | 2.63E-07 | 1.16E-06 | 8.76E-02 | 2.33E-03 | |||||||||||||||
206 | 7440-50-8 | Copper and Compounds | 977 | 8.20E-06 | 3.61E-05 | 2.73E+00 | 7.27E-02 | |||||||||||||||
207 | 7439-92-1 | Lead and Compounds | 829 | 6.95E-06 | 3.07E-05 | 2.32E+00 | 6.17E-02 | |||||||||||||||
208 | 7439-96-5 | Manganese and Compounds | 3970 | 3.33E-05 | 1.47E-04 | 1.11E+01 | 2.95E-01 | |||||||||||||||
209 | 7439-97-6 | Mercury and Compounds | 1.03 | 8.64E-09 | 3.81E-08 | 2.88E-03 | 7.66E-05 | |||||||||||||||
210 | 365 | Nickel compounds, insoluble | 220 | 1.85E-06 | 8.14E-06 | 6.15E-01 | 1.64E-02 | |||||||||||||||
211 | 7782-49-2 | Selenium and Compounds | 0 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||
212 | 7440-22-4 | Silver and compounds | 2.93 | 2.46E-08 | 1.08E-07 | 8.20E-03 | 2.18E-04 | |||||||||||||||
213 | 7440-28-0 | Thallium and compounds | 0 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||
214 | 504 | Phosphorus and Compounds | 0 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||
215 | 7440-62-2 | Vanadium (fume or dust) | 84.8 | 7.11E-07 | 3.14E-06 | 2.37E-01 | 6.31E-03 | |||||||||||||||
216 | 7440-66-6 | Zinc and Compounds | 15300 | 1.28E-04 | 5.66E-04 | 4.28E+01 | 1.14E+00 | |||||||||||||||
217 | 7440-39-3 | Barium and compounds | 560 | 4.70E-06 | 2.07E-05 | 1.57E+00 | 4.16E-02 | |||||||||||||||
218 | ||||||||||||||||||||||
219 | ||||||||||||||||||||||
220 | ||||||||||||||||||||||
221 | ||||||||||||||||||||||
222 | ||||||||||||||||||||||
223 | ||||||||||||||||||||||
224 | ||||||||||||||||||||||
225 | ||||||||||||||||||||||
226 | ||||||||||||||||||||||
227 | AQ520 Info | |||||||||||||||||||||
228 | Row | CAS col | STER Col | LTER Col | CE | SLEF col | STEF col | Unit | Ref Col | |||||||||||||
229 | %SRC | EU-09sp-SC_BH01 | 80 | 1 | 8 | 7 | 96.04% | 4 | 4 | lb/hr | 20 | |||||||||||
230 | %SRC | EU-09sp-SC_BH01A | 80 | 1 | 10 | 9 | 99.21% | 4 | 4 | lb/hr | 20 | |||||||||||
231 | %SRC | EU-09sp-SC_MELTFUG | 92 | 1 | 6 | 5 | 95% | 4 | 4 | lb/hr | 20 | |||||||||||
232 | %SRC | EU-09ng-SC_BH01 | 106 | 1 | 7 | 6 | 20.87% | 3 | 3 | lb/MMSCF | 20 | |||||||||||
233 | %SRC | EU-09ng-SC_BH01A | 106 | 1 | 9 | 8 | 84.14% | 3 | 3 | lb/MMSCF | 20 | |||||||||||
234 | %SRC | EU-09ng-SC_MELTFUG | 137 | 1 | 5 | 4 | 95% | 3 | 3 | lb/MMSCF | 20 | |||||||||||
235 | %SRC | EU-09sh_Main | 175 | 1 | 7 | 6 | 4 | 5 | lb/acre | 20 | ||||||||||||
236 | %SRC | EU-09sh_Sec | 199 | 1 | 7 | 6 | 4 | 5 | lb/acre | 20 |
A | B | C | D | E | F | G | H | I | J | K | L | M | P | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Attachment B - Emission Calculations | |||||||||||||
2 | Table B-2: Emissions at the Melt Shop | |||||||||||||
3 | ||||||||||||||
4 | Toxics Emission Unit ID: | EU-1 | ||||||||||||
5 | Description: | Melt Shop EAF, Ladle Furnace metal and organic TAC emissions through baghouse stacks | ||||||||||||
6 | Emission Point: | BH01 | ||||||||||||
7 | BH01A | |||||||||||||
8 | BH02 | |||||||||||||
9 | ||||||||||||||
10 | Toxics Emission Unit ID: | EU-3_RM | ||||||||||||
11 | Description: | Roof monitor emissions | ||||||||||||
12 | Emission Point: | RMELT | ||||||||||||
13 | ||||||||||||||
14 | Toxics Emission Unit ID: | EU-3_MF | ||||||||||||
15 | Description: | Additional Melt Shop roof monitor emissions as building fugitives | ||||||||||||
16 | Emission Point: | MELTFUG | ||||||||||||
17 | ||||||||||||||
18 | Toxics Emission Unit ID: | EU-4 | ||||||||||||
19 | Description: | Melt Shop natural gas fired vertical preheater, emissions emitted through a stack | ||||||||||||
20 | Emission Point: | VERTP | ||||||||||||
21 | ||||||||||||||
22 | Toxics Emission Unit ID: | EU-16ng | ||||||||||||
23 | Description: | Melt Shop natural gas fired EAF preheaters, tundish heaters and horizontal heater emissions emitted through baghouse stacks and a roof monitor. | ||||||||||||
24 | Emission Point: | BH01 | ||||||||||||
25 | BH01A | |||||||||||||
26 | RMELT | |||||||||||||
27 | ||||||||||||||
28 | Toxics Emission Unit ID: | EU-16ng_MF | ||||||||||||
29 | Description: | Additional natural gas fired tundish heaters and horizontal heater emissions emitted through building fugitives. | ||||||||||||
30 | Emission Point: | MELTFUG | ||||||||||||
31 | ||||||||||||||
32 | ||||||||||||||
33 | ||||||||||||||
34 | ||||||||||||||
35 | ||||||||||||||
36 | ||||||||||||||
37 | ||||||||||||||
38 | ||||||||||||||
39 | Operating Parameters & Input Assumptions: | |||||||||||||
40 | ||||||||||||||
41 | Daily Steel Production | 3,700 | tons/day | |||||||||||
42 | Annual Steel Production | 720,000 | tons/year | |||||||||||
43 | Baghouse Capture Eff. | 95% | ||||||||||||
44 | Chromium VI Speciation Factor | 8.4% | ||||||||||||
45 | Stainless Steel Daily EF Multiplier | 64 | ||||||||||||
46 | Stainless Steel Annual EF Multiplier | 1.32 | 0.5% annual production rate | |||||||||||
47 | BH01 - Emissions Allocation | 83.3% | ||||||||||||
48 | BH01A - Emissions Allocation | 16.7% | ||||||||||||
49 | ||||||||||||||
50 |
51 | Emissions from Baghouse BH-1 (emission point BH01) | EU-1_BH01 | ||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | Melt Shop Activities | Scrap Billet Cutting (see Tabl B-4) | Total | |||||||||||
53 | CAS or DEQ ID | TAC | BH01 EF (lb/ton)(annual) | BH01 EF (lb/ton)(daily) | BH01 Emissions (lb/yr) | BH01 Emissions (lb/day) | BH01 Emissions (lb/yr) | BH01 Emissions (lb/day) | BH01 Emissions Total (lb/yr) | BH01 Emissions Total (lb/day) | ||||
54 | 7429-90-5 | Aluminum and Compounds | 5.22E-05 | 5.22E-05 | 3.76E+01 | 1.93E-01 | 1.72E-01 | 7.13E-04 | 37.7413 | 0.1931 | May 17-19, 2016 and May 21-22, 2013 BH1/BH1A/BH2 Horizon Engineering Source Tests for PM combined with June 20, 2013 Test America Filter analysis for speciation. Emission factor derived from outlet stack test and control efficiency does not apply. | |||
55 | 7440-36-0 | Antimony and Compounds | 5.61E-07 | 5.61E-07 | 4.04E-01 | 2.08E-03 | 9.92E-03 | 4.11E-05 | 0.4142 | 0.0021 | ||||
56 | 7440-38-2 | Arsenic and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 2.93E-02 | 1.21E-04 | 0.0293 | 0.0001 | ||||
57 | 7440-41-7 | Beryllium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.0000 | 0.0000 | ||||
58 | 7440-43-9 | Cadmium and Compounds | 2.02E-06 | 2.02E-06 | 1.46E+00 | 7.49E-03 | 0.00E+00 | 0.00E+00 | 1.4578 | 0.0075 | ||||
59 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 1.25E-06 | 6.04E-05 | 8.97E-01 | 2.23E-01 | 5.18E-03 | 2.14E-05 | 0.9017 | 0.2234 | ||||
60 | 7440-48-4 | Cobalt and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 1.40E-02 | 5.82E-05 | 0.0140 | 0.0001 | ||||
61 | 7440-50-8 | Copper and Compounds | 1.18E-05 | 1.18E-05 | 8.49E+00 | 4.36E-02 | 9.21E-01 | 3.81E-03 | 9.4148 | 0.0436 | ||||
62 | 7439-92-1 | Lead and Compounds | 6.01E-05 | 6.01E-05 | 4.33E+01 | 2.22E-01 | 3.35E-02 | 1.39E-04 | 43.3197 | 0.2224 | ||||
63 | 7439-96-5 | Manganese and Compounds | 1.07E-04 | 1.07E-04 | 7.72E+01 | 3.97E-01 | 6.16E-01 | 2.55E-03 | 77.7959 | 0.3966 | ||||
64 | 7439-97-6 | Mercury and compounds | 3.82E-07 | 3.82E-07 | 2.75E-01 | 1.41E-03 | 0.00E+00 | 0.00E+00 | 0.2752 | 0.0014 | ||||
65 | 365 | Nickel compounds, insoluble | 1.75E-06 | 1.75E-06 | 1.26E+00 | 6.46E-03 | 1.42E-01 | 5.87E-04 | 1.3996 | 0.0065 | ||||
66 | 504 | Phosphorus and Compounds | 5.67E-06 | 5.67E-06 | 4.08E+00 | 2.10E-02 | 4.97E-02 | 2.06E-04 | 4.1333 | 0.0210 | ||||
67 | 7782-49-2 | Selenium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.0000 | 0.0000 | ||||
68 | 7440-62-2 | Vanadium (fume or dust) | 5.90E-07 | 5.90E-07 | 4.25E-01 | 2.18E-03 | 1.12E-02 | 4.62E-05 | 0.4358 | 0.0022 | ||||
69 | 7440-66-6 | Zinc and Compounds | 1.14E-03 | 1.14E-03 | 8.21E+02 | 4.22E+00 | 1.62E-01 | 6.70E-04 | 820.9661 | 4.2180 | ||||
70 | 71-43-2 | Benzene | 9.68E-03 | 9.68E-03 | 6.97E+03 | 3.58E+01 | 0 | 0 | 6966.7200 | 35.8012 | Emissions Test Report for CSRM Electric Arc Furnace Baghouse (Horizon Engineering, March 3, 1995). Test result is at stack outlet and control efficiency does not apply to the emission factor. | |||
71 | 74-87-3 | Chloromethane (methyl chloride) | 5.14E-04 | 5.14E-04 | 3.70E+02 | 1.90E+00 | 0 | 0 | 370.3188 | 1.9030 | ||||
72 | 100-42-5 | Styrene | 9.97E-04 | 9.97E-04 | 7.18E+02 | 3.69E+00 | 0 | 0 | 717.6058 | 3.6877 | ||||
73 | 108-88-3 | Toluene | 1.37E-03 | 1.37E-03 | 9.84E+02 | 5.06E+00 | 0 | 0 | 983.8306 | 5.0558 | ||||
74 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 3.28E-04 | 3.28E-04 | 2.36E+02 | 1.21E+00 | 0 | 0 | 236.1196 | 1.2134 | ||||
75 | 108-90-7 | Chlorobenzene | 1.18E-04 | 1.18E-04 | 8.52E+01 | 4.38E-01 | 0 | 0 | 85.2346 | 0.4380 | ||||
76 | 100-41-4 | Ethyl benzene | 1.89E-04 | 1.89E-04 | 1.36E+02 | 7.00E-01 | 0 | 0 | 136.1317 | 0.6996 | ||||
77 | 75-01-4 | Vinyl chloride | 7.42E-05 | 7.42E-05 | 5.34E+01 | 2.74E-01 | 0 | 0 | 53.3955 | 0.2744 | ||||
78 | 74-83-9 | Bromomethane (methyl bromide) | 1.01E-04 | 1.01E-04 | 7.27E+01 | 3.74E-01 | 0 | 0 | 72.6986 | 0.3736 | ||||
79 | 75-69-4 | Trichlorofluoromethane (Freon 11) | 2.02E-04 | 2.02E-04 | 1.46E+02 | 7.49E-01 | 0 | 0 | 145.7648 | 0.7491 | ||||
80 | 75-09-2 | Dichloromethane (methylene chloride) | 9.05E-05 | 9.05E-05 | 6.51E+01 | 3.35E-01 | 0 | 0 | 65.1479 | 0.3348 | ||||
81 | 79-34-5 | 1,1,2,2-Tetrachloroethane | 2.00E-04 | 2.00E-04 | 1.44E+02 | 7.41E-01 | 0 | 0 | 144.2251 | 0.7412 | ||||
82 | 95-63-6 | 1,2,4-Trimethylbenzene | 1.24E-04 | 1.24E-04 | 8.96E+01 | 4.60E-01 | 0 | 0 | 89.5530 | 0.4602 | ||||
83 | 120-82-1 | 1,2,4-Trichlorobenzene | 2.14E-04 | 2.14E-04 | 1.54E+02 | 7.93E-01 | 0 | 0 | 154.2291 | 0.7926 | ||||
84 | 646 | PCDD/Fs TEQ | 8.64E-12 | 8.64E-12 | 6.22E-06 | 3.20E-08 | 0 | 0 | 0.0000062 | 0.0000000 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
85 | 645 | PCBs TEQ | 4.31E-13 | 4.31E-13 | 3.11E-07 | 1.60E-09 | 0 | 0 | 0.0000003 | 0.0000000 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
86 | 1336-36-3 | Total PCBs | 3.74E-10 | 3.74E-10 | 2.69E-04 | 1.38E-06 | 0 | 0 | 0.0002690 | 0.0000014 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
87 | 83-32-9 | Acenaphthene | 6.83E-11 | 6.83E-11 | 4.92E-05 | 2.53E-07 | 0 | 0 | 0.0000492 | 0.0000003 | 2023 Baghouse Dust Sampling | |||
88 | 208-96-8 | Acenaphthylene | 1.95E-10 | 1.95E-10 | 1.41E-04 | 7.22E-07 | 0 | 0 | 0.0001405 | 0.0000007 | ||||
89 | 120-12-7 | Anthracene | 6.83E-11 | 6.83E-11 | 4.92E-05 | 2.53E-07 | 0 | 0 | 0.0000492 | 0.0000003 | ||||
90 | 56-55-3 | Benz[a]anthracene | 1.18E-10 | 1.18E-10 | 8.53E-05 | 4.38E-07 | 0 | 0 | 0.0000853 | 0.0000004 | ||||
91 | 50-32-8 | Benzo[a]pyrene | 6.83E-11 | 6.83E-11 | 4.92E-05 | 2.53E-07 | 0 | 0 | 0.0000492 | 0.0000003 | ||||
92 | 205-99-2 | Benzo[b]fluoranthene | 3.76E-10 | 3.76E-10 | 2.71E-04 | 1.39E-06 | 0 | 0 | 0.0002710 | 0.0000014 | ||||
93 | 192-97-2 | Benzo[e]pyrene | 2.23E-10 | 2.23E-10 | 1.61E-04 | 8.25E-07 | 0 | 0 | 0.0001606 | 0.0000008 | ||||
94 | 191-24-2 | Benzo[g,h,i]perylene | 1.09E-10 | 1.09E-10 | 7.83E-05 | 4.02E-07 | 0 | 0 | 0.0000783 | 0.0000004 | ||||
95 | 207-08-9 | Benzo[k]fluoranthene | 9.06E-11 | 9.06E-11 | 6.52E-05 | 3.35E-07 | 0 | 0 | 0.0000652 | 0.0000003 | ||||
96 | 218-01-9 | Chrysene | 5.30E-10 | 5.30E-10 | 3.81E-04 | 1.96E-06 | 0 | 0 | 0.0003814 | 0.0000020 | ||||
97 | 53-70-3 | Dibenz[a,h]anthracene | 6.83E-11 | 6.83E-11 | 4.92E-05 | 2.53E-07 | 0 | 0 | 0.0000492 | 0.0000003 | ||||
98 | 206-44-0 | Fluoranthene | 1.81E-09 | 1.81E-09 | 1.30E-03 | 6.71E-06 | 0 | 0 | 0.0013048 | 0.0000067 | ||||
99 | 86-73-7 | Fluorene | 1.81E-10 | 1.81E-10 | 1.30E-04 | 6.71E-07 | 0 | 0 | 0.0001305 | 0.0000007 | ||||
100 | 193-39-5 | Indeno[1,2,3-cd]pyrene | 7.67E-11 | 7.67E-11 | 5.52E-05 | 2.84E-07 | 0 | 0 | 0.0000552 | 0.0000003 |
101 | 198-55-0 | Perylene | 6.83E-11 | 6.83E-11 | 4.92E-05 | 2.53E-07 | 0 | 0 | 0.0000492 | 0.0000003 | ||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
102 | 85-01-8 | Phenanthrene | 1.81E-09 | 1.81E-09 | 1.30E-03 | 6.71E-06 | 0 | 0 | 0.0013048 | 0.0000067 | ||||
103 | 129-00-0 | Pyrene | 1.00E-09 | 1.00E-09 | 7.23E-04 | 3.71E-06 | 0 | 0 | 0.0007227 | 0.0000037 | ||||
104 | 91-20-3 | Naphthalene | 2.26E-03 | 2.26E-03 | 1.63E+03 | 8.38E+00 | 0 | 0 | 1630.2556 | 8.3777 | Lee et al., 1999. Table 7. Emission factor is from stack outlet and control efficiency does not apply. | |||
105 | 118-74-1 | Hexachlorobenzene | 5.55E-06 | 5.55E-06 | 4.00E+00 | 2.05E-02 | 0 | 0 | 3.9964 | 0.0205 | UNEP, 2013. Table III.18.2. Emission factor is from stack outlet and control efficiency does not apply. | |||
106 | 447 | PBDEs | 6.16E-07 | 6.16E-07 | 4.44E-01 | 2.28E-03 | 0 | 0 | 0.4436 | 0.0023 | Wang et al. 2010, Table S10; Wu et al., Table 6. Average of emission factors. Emission factor is from stack outlet and control efficiency does not apply. | |||
107 | 239 | Fluorides | 3.50E-03 | 3.50E-03 | 2.10E+03 | 1.08E+01 | 0 | 0 | 2099.16 | 10.79 | Air Quality Permit, Nucor Steel Gallatin, Ghent, KY, Permit V-20-015 R1”, Kentucky Department of Environmental Protection, Division of Air Quality, April 19, 2021, pg14. Emission factor is from stack outlet and control efficiency does not apply. CE used to account for 01/01A split of emissions. | |||
108 | 7664-39-3 | Hydrogen Fluoride | 9.58E-04 | 9.58E-04 | 5.75E+02 | 2.95E+00 | 0 | 0 | 574.57 | 2.95 | Title V Operating Permit, Nucor Steel - Berkeley - Huger, South Carolina, Permit TV-0420-0060, South Carolina Department of Health and Environmental Control, Issue Date December 19, 2019, pgs 120-121. CE used at account for 01/01A split. | |||
109 | ||||||||||||||
110 | ||||||||||||||
111 | ||||||||||||||
112 | ||||||||||||||
113 | ||||||||||||||
114 | ||||||||||||||
115 | ||||||||||||||
116 | ||||||||||||||
117 | ||||||||||||||
118 | ||||||||||||||
119 | ||||||||||||||
120 | ||||||||||||||
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123 | ||||||||||||||
124 | ||||||||||||||
125 | ||||||||||||||
126 | Emissions from Baghouse BH-1A (emission point BH01A) | EU-1_BH01A | ||||||||||||
127 | Melt Shop Activities | Scrap Billet Cutting (see Tabl B-4) | Total | |||||||||||
128 | CAS or DEQ ID | TAC | BH01A EF (lb/ton)(annual) | BH01A EF (lb/ton)(daily) | BH01A Emissions (lb/yr) | BH01A Emissions (lb/day) | BH01A Emissions (lb/yr) | BH01A Emissions (lb/day) | BH01A Emissions Total (lb/yr) | BH01A Emissions Total (lb/day) | ||||
129 | 7429-90-5 | Aluminum and Compounds | 9.24E-05 | 9.24E-05 | 6.65E+01 | 3.42E-01 | 3.45E-02 | 1.43E-04 | 66.5445 | 0.3418 | May 17-19, 2016 and May 21-22, 2013 BH1/BH1A/BH2 Horizon Engineering Source Tests for PM combined with June 20, 2013 Test America Filter analysis for speciation. Emission factor derived from outlet stack test and control efficiency does not apply. | |||
130 | 7440-36-0 | Antimony and Compounds | 9.94E-07 | 9.94E-07 | 7.16E-01 | 3.68E-03 | 1.99E-03 | 8.24E-06 | 0.7177 | 0.0037 | ||||
131 | 7440-38-2 | Arsenic and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 5.87E-03 | 2.43E-05 | 0.0059 | 0.0000 | ||||
132 | 7440-41-7 | Beryllium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.0000 | 0.0000 | ||||
133 | 7440-43-9 | Cadmium and Compounds | 3.58E-06 | 3.58E-06 | 2.58E+00 | 1.33E-02 | 0.00E+00 | 0.00E+00 | 2.5809 | 0.0133 | ||||
134 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 2.20E-06 | 1.07E-04 | 1.59E+00 | 3.95E-01 | 1.04E-03 | 4.30E-06 | 1.5882 | 0.3955 | ||||
135 | 7440-48-4 | Cobalt and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 2.82E-03 | 1.17E-05 | 0.0028 | 0.0000 | ||||
136 | 7440-50-8 | Copper and Compounds | 2.09E-05 | 2.09E-05 | 1.50E+01 | 7.73E-02 | 1.85E-01 | 7.65E-04 | 15.2217 | 0.0773 | ||||
137 | 7439-92-1 | Lead and Compounds | 1.06E-04 | 1.06E-04 | 7.66E+01 | 3.94E-01 | 6.71E-03 | 2.78E-05 | 76.6378 | 0.3938 | ||||
138 | 7439-96-5 | Manganese and Compounds | 1.90E-04 | 1.90E-04 | 1.37E+02 | 7.02E-01 | 1.23E-01 | 5.11E-04 | 136.7581 | 0.7022 | ||||
139 | 7439-97-6 | Mercury and compounds | 6.77E-07 | 6.77E-07 | 4.87E-01 | 2.50E-03 | 0.00E+00 | 0.00E+00 | 0.4873 | 0.0025 | ||||
140 | 365 | Nickel compounds, insoluble | 3.09E-06 | 3.09E-06 | 2.23E+00 | 1.14E-02 | 2.84E-02 | 1.18E-04 | 2.2551 | 0.0114 | ||||
141 | 504 | Phosphorus and Compounds | 1.00E-05 | 1.00E-05 | 7.23E+00 | 3.72E-02 | 9.95E-03 | 4.12E-05 | 7.2393 | 0.0372 | ||||
142 | 7782-49-2 | Selenium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.0000 | 0.0000 | ||||
143 | 7440-62-2 | Vanadium (fume or dust) | 1.04E-06 | 1.04E-06 | 7.52E-01 | 3.86E-03 | 2.24E-03 | 9.26E-06 | 0.7541 | 0.0039 | ||||
144 | 7440-66-6 | Zinc and Compounds | 2.02E-03 | 2.02E-03 | 1.45E+03 | 7.47E+00 | 3.24E-02 | 1.34E-04 | 1453.1310 | 7.4673 | ||||
145 | 71-43-2 | Benzene | 1.94E-03 | 1.94E-03 | 1.40E+03 | 7.18E+00 | 0 | 0 | 1396.6894 | 7.1774 | Emissions Test Report for CSRM Electric Arc Furnace Baghouse (Horizon Engineering, March 3, 1995). Test result is at stack outlet and control efficiency does not apply to the emission factor. | |||
146 | 74-87-3 | Chloromethane (methyl chloride) | 1.03E-04 | 1.03E-04 | 7.42E+01 | 3.82E-01 | 0 | 0 | 74.2416 | 0.3815 | ||||
147 | 100-42-5 | Styrene | 2.00E-04 | 2.00E-04 | 1.44E+02 | 7.39E-01 | 0 | 0 | 143.8657 | 0.7393 | ||||
148 | 108-88-3 | Toluene | 2.74E-04 | 2.74E-04 | 1.97E+02 | 1.01E+00 | 0 | 0 | 197.2386 | 1.0136 | ||||
149 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 6.57E-05 | 6.57E-05 | 4.73E+01 | 2.43E-01 | 0 | 0 | 47.3373 | 0.2433 | ||||
150 | 108-90-7 | Chlorobenzene | 2.37E-05 | 2.37E-05 | 1.71E+01 | 8.78E-02 | 0 | 0 | 17.0878 | 0.0878 |
151 | 100-41-4 | Ethyl benzene | 3.79E-05 | 3.79E-05 | 2.73E+01 | 1.40E-01 | 0 | 0 | 27.2917 | 0.1402 | ||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
152 | 75-01-4 | Vinyl chloride | 1.49E-05 | 1.49E-05 | 1.07E+01 | 5.50E-02 | 0 | 0 | 10.7047 | 0.0550 | ||||
153 | 74-83-9 | Bromomethane (methyl bromide) | 2.02E-05 | 2.02E-05 | 1.46E+01 | 7.49E-02 | 0 | 0 | 14.5746 | 0.0749 | ||||
154 | 75-69-4 | Trichlorofluoromethane (Freon 11) | 4.06E-05 | 4.06E-05 | 2.92E+01 | 1.50E-01 | 0 | 0 | 29.2230 | 0.1502 | ||||
155 | 75-09-2 | Dichloromethane (methylene chloride) | 1.81E-05 | 1.81E-05 | 1.31E+01 | 6.71E-02 | 0 | 0 | 13.0609 | 0.0671 | ||||
156 | 79-34-5 | 1,1,2,2-Tetrachloroethane | 4.02E-05 | 4.02E-05 | 2.89E+01 | 1.49E-01 | 0 | 0 | 28.9143 | 0.1486 | ||||
157 | 95-63-6 | 1,2,4-Trimethylbenzene | 2.49E-05 | 2.49E-05 | 1.80E+01 | 9.23E-02 | 0 | 0 | 17.9536 | 0.0923 | ||||
158 | 120-82-1 | 1,2,4-Trichlorobenzene | 4.29E-05 | 4.29E-05 | 3.09E+01 | 1.59E-01 | 0 | 0 | 30.9199 | 0.1589 | ||||
159 | 646 | PCDD/Fs TEQ | 1.73E-12 | 1.73E-12 | 1.25E-06 | 6.41E-09 | 0 | 0 | 1.25E-06 | 6.41E-09 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
160 | 645 | PCBs TEQ | 8.65E-14 | 8.65E-14 | 6.23E-08 | 3.20E-10 | 0 | 0 | 6.23E-08 | 3.20E-10 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
161 | 1336-36-3 | Total PCBs | 7.49E-11 | 7.49E-11 | 5.39E-05 | 2.77E-07 | 0 | 0 | 5.39E-05 | 2.77E-07 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
162 | 83-32-9 | Acenaphthene | 1.37E-11 | 1.37E-11 | 9.86E-06 | 5.07E-08 | 0 | 0 | 9.86E-06 | 5.07E-08 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
163 | 208-96-8 | Acenaphthylene | 3.91E-11 | 3.91E-11 | 2.82E-05 | 1.45E-07 | 0 | 0 | 2.82E-05 | 1.45E-07 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
164 | 120-12-7 | Anthracene | 1.37E-11 | 1.37E-11 | 9.86E-06 | 5.07E-08 | 0 | 0 | 9.86E-06 | 5.07E-08 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
165 | 56-55-3 | Benz[a]anthracene | 2.38E-11 | 2.38E-11 | 1.71E-05 | 8.79E-08 | 0 | 0 | 1.71E-05 | 8.79E-08 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
166 | 50-32-8 | Benzo[a]pyrene | 1.37E-11 | 1.37E-11 | 9.86E-06 | 5.07E-08 | 0 | 0 | 9.86E-06 | 5.07E-08 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
167 | 205-99-2 | Benzo[b]fluoranthene | 7.55E-11 | 7.55E-11 | 5.43E-05 | 2.79E-07 | 0 | 0 | 5.43E-05 | 2.79E-07 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
168 | 192-97-2 | Benzo[e]pyrene | 4.47E-11 | 4.47E-11 | 3.22E-05 | 1.65E-07 | 0 | 0 | 3.22E-05 | 1.65E-07 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
169 | 191-24-2 | Benzo[g,h,i]perylene | 2.18E-11 | 2.18E-11 | 1.57E-05 | 8.07E-08 | 0 | 0 | 1.57E-05 | 8.07E-08 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
170 | 207-08-9 | Benzo[k]fluoranthene | 1.82E-11 | 1.82E-11 | 1.31E-05 | 6.72E-08 | 0 | 0 | 1.31E-05 | 6.72E-08 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
171 | 218-01-9 | Chrysene | 1.06E-10 | 1.06E-10 | 7.65E-05 | 3.93E-07 | 0 | 0 | 7.65E-05 | 3.93E-07 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
172 | 53-70-3 | Dibenz[a,h]anthracene | 1.37E-11 | 1.37E-11 | 9.86E-06 | 5.07E-08 | 0 | 0 | 9.86E-06 | 5.07E-08 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
173 | 206-44-0 | Fluoranthene | 3.63E-10 | 3.63E-10 | 2.62E-04 | 1.34E-06 | 0 | 0 | 2.62E-04 | 1.34E-06 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
174 | 86-73-7 | Fluorene | 3.63E-11 | 3.63E-11 | 2.62E-05 | 1.34E-07 | 0 | 0 | 2.62E-05 | 1.34E-07 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
175 | 193-39-5 | Indeno[1,2,3-cd]pyrene | 1.54E-11 | 1.54E-11 | 1.11E-05 | 5.69E-08 | 0 | 0 | 1.11E-05 | 5.69E-08 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
176 | 198-55-0 | Perylene | 1.37E-11 | 1.37E-11 | 9.86E-06 | 5.07E-08 | 0 | 0 | 9.86E-06 | 5.07E-08 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
177 | 85-01-8 | Phenanthrene | 3.63E-10 | 3.63E-10 | 2.62E-04 | 1.34E-06 | 0 | 0 | 2.62E-04 | 1.34E-06 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
178 | 129-00-0 | Pyrene | 2.01E-10 | 2.01E-10 | 1.45E-04 | 7.45E-07 | 0 | 0 | 1.45E-04 | 7.45E-07 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||
179 | 91-20-3 | Naphthalene | 4.54E-04 | 4.54E-04 | 3.27E+02 | 1.68E+00 | 0 | 0 | 326.8340 | 1.6796 | Lee et al., 1999. Table 7. Emission factor is from stack outlet and control efficiency does not apply. | |||
180 | 118-74-1 | Hexachlorobenzene | 1.11E-06 | 1.11E-06 | 8.01E-01 | 4.12E-03 | 0 | 0 | 0.8012 | 0.0041 | UNEP, 2013. Table III.18.2. Emission factor is from stack outlet and control efficiency does not apply. | |||
181 | 447 | PBDEs | 1.24E-07 | 1.24E-07 | 8.89E-02 | 4.57E-04 | 0 | 0 | 0.0889 | 0.0005 | Wang et al. 2010, Table S10; Wu et al., Table 6. Average of emission factors. Emission factor is from stack outlet and control efficiency does not apply. | |||
182 | 239 | Fluorides | 3.50E-03 | 3.50E-03 | 4.21E+02 | 2.16E+00 | 0 | 0 | 420.8400 | 2.1627 | Air Quality Permit, Nucor Steel Gallatin, Ghent, KY, Permit V-20-015 R1”, Kentucky Department of Environmental Protection, Division of Air Quality, April 19, 2021, pg14. Emission factor is from stack outlet and control efficiency does not apply. CE used to account for 01/01A split of emissions. | |||
183 | 7664-39-3 | Hydrogen Fluoride | 9.58E-04 | 9.58E-04 | 1.15E+02 | 5.92E-01 | 0 | 0 | 115.19 | 0.59 | Title V Operating Permit, Nucor Steel - Berkeley - Huger, South Carolina, Permit TV-0420-0060, South Carolina Department of Health and Environmental Control, Issue Date December 19, 2019, pgs 120-121. CE used at account for 01/01A split. | |||
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194 | ||||||||||||||
195 | Emissions from Baghouse BH-2 (emission point BH02) | |||||||||||||
196 | Melt Shop Activities | |||||||||||||
197 | CAS or DEQ ID | TAC | BH02 EF (lb/ton)(annual) | BH02 EF (lb/ton)(daily) | BH02 Emissions (lb/yr) | BH02 Emissions (lb/day) | ||||||||
198 | 7429-90-5 | Aluminum and Compounds | 7.13E-05 | 7.13E-05 | 5.13E+01 | 2.64E-01 | May 17-19, 2016 and May 21-22, 2013 BH1/BH1A/BH2 Horizon Engineering Source Tests for PM combined with June 20, 2013 Test America Filter analysis for speciation. Emission factor derived from outlet stack test and control efficiency does not apply. | |||||||
199 | 7440-36-0 | Antimony and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||
200 | 7440-38-2 | Arsenic and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 |
201 | 7440-41-7 | Beryllium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
202 | 7440-43-9 | Cadmium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||
203 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 9.91E-08 | 4.81E-06 | 7.14E-02 | 1.78E-02 | ||||||||
204 | 7440-48-4 | Cobalt and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||
205 | 7440-50-8 | Copper and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||
206 | 7439-92-1 | Lead and Compounds | 3.14E-06 | 3.14E-06 | 2.26E+00 | 1.16E-02 | ||||||||
207 | 7439-96-5 | Manganese and Compounds | 5.19E-06 | 5.19E-06 | 3.74E+00 | 1.92E-02 | ||||||||
208 | 7439-97-6 | Mercury and compounds | 5.40E-08 | 5.40E-08 | 3.89E-02 | 2.00E-04 | ||||||||
209 | 365 | Nickel compounds, insoluble | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||
210 | 504 | Phosphorus and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||
211 | 7782-49-2 | Selenium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||
212 | 7440-62-2 | Vanadium (fume or dust) | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||
213 | 7440-66-6 | Zinc and Compounds | 3.84E-05 | 3.84E-05 | 2.77E+01 | 1.42E-01 | ||||||||
214 | 71-43-2 | Benzene | 1.16E-03 | 1.16E-03 | 8.36E+02 | 4.30E+00 | Emissions Test Report for CSRM Electric Arc Furnace Baghouse (Horizon Engineering, March 3, 1995). Test result is at stack outlet and control efficiency does not apply to the emission factor. | |||||||
215 | 74-87-3 | Chloromethane (methyl chloride) | 6.17E-05 | 6.17E-05 | 4.45E+01 | 2.28E-01 | ||||||||
216 | 100-42-5 | Styrene | 1.20E-04 | 1.20E-04 | 8.61E+01 | 4.43E-01 | ||||||||
217 | 108-88-3 | Toluene | 1.64E-04 | 1.64E-04 | 1.18E+02 | 6.07E-01 | ||||||||
218 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 3.94E-05 | 3.94E-05 | 2.83E+01 | 1.46E-01 | ||||||||
219 | 108-90-7 | Chlorobenzene | 1.42E-05 | 1.42E-05 | 1.02E+01 | 5.26E-02 | ||||||||
220 | 100-41-4 | Ethyl benzene | 2.27E-05 | 2.27E-05 | 1.63E+01 | 8.40E-02 | ||||||||
221 | 75-01-4 | Vinyl chloride | 8.90E-06 | 8.90E-06 | 6.41E+00 | 3.29E-02 | ||||||||
222 | 74-83-9 | Bromomethane (methyl bromide) | 1.21E-05 | 1.21E-05 | 8.73E+00 | 4.48E-02 | ||||||||
223 | 75-69-4 | Trichlorofluoromethane (Freon 11) | 2.43E-05 | 2.43E-05 | 1.75E+01 | 8.99E-02 | ||||||||
224 | 75-09-2 | Dichloromethane (methylene chloride) | 1.09E-05 | 1.09E-05 | 7.82E+00 | 4.02E-02 | ||||||||
225 | 79-34-5 | 1,1,2,2-Tetrachloroethane | 2.40E-05 | 2.40E-05 | 1.73E+01 | 8.90E-02 | ||||||||
226 | 95-63-6 | 1,2,4-Trimethylbenzene | 1.49E-05 | 1.49E-05 | 1.08E+01 | 5.52E-02 | ||||||||
227 | 120-82-1 | 1,2,4-Trichlorobenzene | 2.57E-05 | 2.57E-05 | 1.85E+01 | 9.51E-02 | ||||||||
228 | 646 | PCDD/Fs TEQ | 1.07E-12 | 1.07E-12 | 7.69E-07 | 3.95E-09 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||||||
229 | 645 | PCBs TEQ | 9.07E-14 | 9.07E-14 | 6.53E-08 | 3.35E-10 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||||||
230 | 1336-36-3 | Total PCBs | 8.34E-10 | 8.34E-10 | 6.00E-04 | 3.09E-06 | 2006-2016 PM Source Testing and 2023 Baghouse Dust Sampling | |||||||
231 | 83-32-9 | Acenaphthene | 1.04E-10 | 1.04E-10 | 7.48E-05 | 3.84E-07 | ||||||||
232 | 208-96-8 | Acenaphthylene | 5.04E-10 | 5.04E-10 | 3.63E-04 | 1.86E-06 | ||||||||
233 | 120-12-7 | Anthracene | 9.87E-10 | 9.87E-10 | 7.11E-04 | 3.65E-06 | ||||||||
234 | 56-55-3 | Benz[a]anthracene | 8.31E-09 | 8.31E-09 | 5.99E-03 | 3.08E-05 | ||||||||
235 | 50-32-8 | Benzo[a]pyrene | 5.72E-09 | 5.72E-09 | 4.11E-03 | 2.11E-05 | ||||||||
236 | 205-99-2 | Benzo[b]fluoranthene | 2.29E-08 | 2.29E-08 | 1.65E-02 | 8.46E-05 | ||||||||
237 | 192-97-2 | Benzo[e]pyrene | 1.40E-08 | 1.40E-08 | 1.01E-02 | 5.19E-05 | ||||||||
238 | 191-24-2 | Benzo[g,h,i]perylene | 1.30E-08 | 1.30E-08 | 9.35E-03 | 4.81E-05 | ||||||||
239 | 207-08-9 | Benzo[k]fluoranthene | 5.20E-09 | 5.20E-09 | 3.74E-03 | 1.92E-05 | ||||||||
240 | 218-01-9 | Chrysene | 1.82E-08 | 1.82E-08 | 1.31E-02 | 6.73E-05 | ||||||||
241 | 53-70-3 | Dibenz[a,h]anthracene | 1.56E-09 | 1.56E-09 | 1.12E-03 | 5.77E-06 | ||||||||
242 | 206-44-0 | Fluoranthene | 2.86E-08 | 2.86E-08 | 2.06E-02 | 1.06E-04 | ||||||||
243 | 86-73-7 | Fluorene | 3.84E-10 | 3.84E-10 | 2.77E-04 | 1.42E-06 | ||||||||
244 | 193-39-5 | Indeno[1,2,3-cd]pyrene | 1.40E-08 | 1.40E-08 | 1.01E-02 | 5.19E-05 | ||||||||
245 | 198-55-0 | Perylene | 1.56E-09 | 1.56E-09 | 1.12E-03 | 5.77E-06 | ||||||||
246 | 85-01-8 | Phenanthrene | 7.79E-09 | 7.79E-09 | 5.61E-03 | 2.88E-05 | ||||||||
247 | 129-00-0 | Pyrene | 2.39E-08 | 2.39E-08 | 1.72E-02 | 8.84E-05 | ||||||||
248 | 91-20-3 | Naphthalene | 2.72E-04 | 2.72E-04 | 1.96E+02 | 1.01E+00 | Lee et al., 1999. Table 7. Emission factor is from stack outlet and control efficiency does not apply. | |||||||
249 | 118-74-1 | Hexachlorobenzene | 6.66E-07 | 6.66E-07 | 4.80E-01 | 2.47E-03 | UNEP, 2013. Table III.18.2. Emission factor is from stack outlet and control efficiency does not apply. | |||||||
250 | 447 | PBDEs | 7.40E-08 | 7.40E-08 | 5.33E-02 | 2.74E-04 | Wang et al. 2010, Table S10; Wu et al., Table 6. Average of emission factors. Emission factor is from stack outlet and control efficiency does not apply. |
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263 | Emissions from EU-3 Roof Monitor (emission point RMELT) | |||||||||||||
264 | ||||||||||||||
265 | CAS or DEQ ID | TAC | RMELT EF (lb/ton)(annual) | RMELT EF (lb/ton)(daily) | RMELT Emissions (lb/yr) | RMELT Emissions (lb/day) | ||||||||
266 | 7429-90-5 | Aluminum and Compounds | 1.25E-03 | 1.25E-03 | 899.6802 | 4.6234 | Particulate and Trace Metals Emissions Test Report Cascade Steel Rolling Mills McMinnville Facility Roof Monitor and Billet Cutting Exhausts McMinnville, OregonAugust 6 through 8, 2019 | |||||||
267 | 7440-36-0 | Antimony and Compounds | 3.30E-06 | 3.30E-06 | 2.3726 | 0.0122 | ||||||||
268 | 7440-38-2 | Arsenic and Compounds | 5.86E-06 | 5.86E-06 | 4.2202 | 0.0217 | ||||||||
269 | 7440-41-7 | Beryllium and Compounds | 0.00E+00 | 0.00E+00 | 0.0000 | 0.0000 | ||||||||
270 | 7440-43-9 | Cadmium and Compounds | 4.45E-07 | 4.45E-07 | 0.3203 | 0.0016 | ||||||||
271 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 2.99E-06 | 1.45E-04 | 2.1523 | 0.5363 | ||||||||
272 | 7440-48-4 | Cobalt and Compounds | 3.31E-06 | 3.31E-06 | 2.3855 | 0.0123 | ||||||||
273 | 7440-50-8 | Copper and Compounds | 1.42E-04 | 1.42E-04 | 101.9374 | 0.5238 | ||||||||
274 | 7439-92-1 | Lead and Compounds | 2.45E-04 | 2.45E-04 | 176.6452 | 0.9078 | ||||||||
275 | 7439-96-5 | Manganese and Compounds | 1.90E-03 | 1.90E-03 | 1370.4872 | 7.0428 | ||||||||
276 | 365 | Nickel compounds, insoluble | 1.89E-05 | 1.89E-05 | 13.5895 | 0.0698 | ||||||||
277 | 504 | Phosphorus and Compounds | 3.39E-05 | 3.39E-05 | 24.3850 | 0.1253 | ||||||||
278 | 7782-49-2 | Selenium and Compounds | 6.02E-06 | 6.02E-06 | 4.3357 | 0.0223 | ||||||||
279 | 7440-62-2 | Vanadium (fume or dust) | 5.67E-06 | 5.67E-06 | 4.0822 | 0.0210 | ||||||||
280 | 7440-66-6 | Zinc and Compounds | 1.54E-03 | 1.54E-03 | 1110.4715 | 5.7066 | ||||||||
281 | 7439-97-6 | Mercury and compounds | 2.57E-07 | 2.57E-07 | 0.1853 | 0.0010 | Title V Review Report 36-5034-TV-0l: page 59 (mercury), page 29 (PM10), and page 28 (PM) | |||||||
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294 | ||||||||||||||
295 | Melt Shop Process Emissions: EU-3 Fugitives MELTFUG | |||||||||||||
296 | Melt Shop Activities | Scrap Billet Cutting (see Tabl B-4) | Total | |||||||||||
297 | CAS or DEQ ID | TAC | MELTFUG EF (lb/ton)(annual) | MELTFUG EF (lb/ton)(daily) | MELTFUG Emissions (lb/yr) | MELTFUG Emissions (lb/day) | MELTFUG Emissions (lb/yr) | MELTFUG Emissions (lb/day) | MELTFUG Emissions Total (lb/yr) | MELTFUG Emissions Total (lb/day) | ||||
298 | 7429-90-5 | Aluminum and Compounds | 6.25E-05 | 6.25E-05 | 44.9840 | 0.2312 | 2.18E-01 | 9.01E-04 | 45.2016 | 0.2312 | 5% of uncontrolled Roof Monitor emissions as described in permit Review Report, pg 28 | |||
299 | 7440-36-0 | Antimony and Compounds | 1.65E-07 | 1.65E-07 | 0.1186 | 0.0006 | 1.25E-02 | 5.19E-05 | 0.1312 | 0.0006 | ||||
300 | 7440-38-2 | Arsenic and Compounds | 2.93E-07 | 2.93E-07 | 0.2110 | 0.0011 | 3.70E-02 | 1.53E-04 | 0.2480 | 0.0011 |
301 | 7440-41-7 | Beryllium and Compounds | 0.00E+00 | 0.00E+00 | 0.0000 | 0.0000 | 0.00E+00 | 0.00E+00 | 0.0000 | 0.0000 | ||||
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302 | 7440-43-9 | Cadmium and Compounds | 2.22E-08 | 2.22E-08 | 0.0160 | 0.0001 | 0.00E+00 | 0.00E+00 | 0.0160 | 0.0001 | ||||
303 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 1.49E-07 | 7.25E-06 | 0.1076 | 0.0268 | 6.54E-03 | 2.71E-05 | 0.1142 | 0.0268 | ||||
304 | 7440-48-4 | Cobalt and Compounds | 1.66E-07 | 1.66E-07 | 0.1193 | 0.0006 | 1.78E-02 | 7.35E-05 | 0.1370 | 0.0006 | ||||
305 | 7440-50-8 | Copper and Compounds | 7.08E-06 | 7.08E-06 | 5.0969 | 0.0262 | 1.16E+00 | 4.82E-03 | 6.2606 | 0.0262 | ||||
306 | 7439-92-1 | Lead and Compounds | 1.23E-05 | 1.23E-05 | 8.8323 | 0.0454 | 4.23E-02 | 1.75E-04 | 8.8746 | 0.0454 | ||||
307 | 7439-96-5 | Manganese and Compounds | 9.52E-05 | 9.52E-05 | 68.5244 | 0.3521 | 7.78E-01 | 3.22E-03 | 69.3025 | 0.3521 | ||||
308 | 365 | Nickel compounds, insoluble | 9.44E-07 | 9.44E-07 | 0.6795 | 0.0035 | 1.79E-01 | 7.42E-04 | 0.8587 | 0.0035 | ||||
309 | 504 | Phosphorus and Compounds | 1.69E-06 | 1.69E-06 | 1.2193 | 0.0063 | 6.27E-02 | 2.60E-04 | 1.2820 | 0.0063 | ||||
310 | 7782-49-2 | Selenium and Compounds | 3.01E-07 | 3.01E-07 | 0.2168 | 0.0011 | 0.00E+00 | 0.00E+00 | 0.2168 | 0.0011 | ||||
311 | 7440-62-2 | Vanadium (fume or dust) | 2.83E-07 | 2.83E-07 | 0.2041 | 0.0010 | 1.41E-02 | 5.84E-05 | 0.2182 | 0.0010 | ||||
312 | 7440-66-6 | Zinc and Compounds | 7.71E-05 | 7.71E-05 | 55.5236 | 0.2853 | 2.04E-01 | 8.47E-04 | 55.7280 | 0.2853 | ||||
313 | 7439-97-6 | Mercury and compounds | 1.29E-08 | 1.29E-08 | 0.0093 | 0.0000 | 0.00E+00 | 0.00E+00 | 0.0093 | 0.0000 | ||||
314 | 71-43-2 | Benzene | 6.72E-04 | 6.72E-04 | 484.1974 | 2.4882 | 0 | 0 | 484.1974 | 2.4882 | uncontrolled emissions backcalulated from baghouses | |||
315 | 74-87-3 | Chloromethane (methyl chloride) | 3.57E-05 | 3.57E-05 | 25.7377 | 0.1323 | 0 | 0 | 25.7377 | 0.1323 | ||||
316 | 100-42-5 | Styrene | 6.93E-05 | 6.93E-05 | 49.8747 | 0.2563 | 0 | 0 | 49.8747 | 0.2563 | ||||
317 | 108-88-3 | Toluene | 9.50E-05 | 9.50E-05 | 68.3777 | 0.3514 | 0 | 0 | 68.3777 | 0.3514 | ||||
318 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 2.28E-05 | 2.28E-05 | 16.4107 | 0.0843 | 0 | 0 | 16.4107 | 0.0843 | ||||
319 | 108-90-7 | Chlorobenzene | 8.23E-06 | 8.23E-06 | 5.9239 | 0.0304 | 0 | 0 | 5.9239 | 0.0304 | ||||
320 | 100-41-4 | Ethyl benzene | 1.31E-05 | 1.31E-05 | 9.4614 | 0.0486 | 0 | 0 | 9.4614 | 0.0486 | ||||
321 | 75-01-4 | Vinyl chloride | 5.15E-06 | 5.15E-06 | 3.7111 | 0.0191 | 0 | 0 | 3.7111 | 0.0191 | ||||
322 | 74-83-9 | Bromomethane (methyl bromide) | 7.02E-06 | 7.02E-06 | 5.0527 | 0.0260 | 0 | 0 | 5.0527 | 0.0260 | ||||
323 | 75-69-4 | Trichlorofluoromethane (Freon 11) | 1.41E-05 | 1.41E-05 | 10.1309 | 0.0521 | 0 | 0 | 10.1309 | 0.0521 | ||||
324 | 75-09-2 | Dichloromethane (methylene chloride) | 6.29E-06 | 6.29E-06 | 4.5279 | 0.0233 | 0 | 0 | 4.5279 | 0.0233 | ||||
325 | 79-34-5 | 1,1,2,2-Tetrachloroethane | 1.39E-05 | 1.39E-05 | 10.0239 | 0.0515 | 0 | 0 | 10.0239 | 0.0515 | ||||
326 | 95-63-6 | 1,2,4-Trimethylbenzene | 8.64E-06 | 8.64E-06 | 6.2241 | 0.0320 | 0 | 0 | 6.2241 | 0.0320 | ||||
327 | 120-82-1 | 1,2,4-Trichlorobenzene | 1.49E-05 | 1.49E-05 | 10.7192 | 0.0551 | 0 | 0 | 10.7192 | 0.0551 | ||||
328 | 646 | PCDD/Fs TEQ | 1.14E-11 | 1.14E-11 | 8.24E-06 | 4.23E-08 | 0 | 0 | 8.24E-06 | 4.23E-08 | ||||
329 | 645 | PCBs TEQ | 6.09E-13 | 6.09E-13 | 4.38E-07 | 2.25E-09 | 0 | 0 | 4.38E-07 | 2.25E-09 | ||||
330 | 1336-36-3 | Total PCBs | 1.28E-09 | 1.28E-09 | 9.23E-04 | 4.74E-06 | 0 | 0 | 9.23E-04 | 4.74E-06 | ||||
331 | 83-32-9 | Acenaphthene | 1.86E-10 | 1.86E-10 | 1.34E-04 | 6.88E-07 | 0 | 0 | 1.34E-04 | 6.88E-07 | ||||
332 | 208-96-8 | Acenaphthylene | 7.38E-10 | 7.38E-10 | 5.32E-04 | 2.73E-06 | 0 | 0 | 5.32E-04 | 2.73E-06 | ||||
333 | 120-12-7 | Anthracene | 1.07E-09 | 1.07E-09 | 7.70E-04 | 3.96E-06 | 0 | 0 | 7.70E-04 | 3.96E-06 | ||||
334 | 56-55-3 | Benz[a]anthracene | 8.46E-09 | 8.46E-09 | 6.09E-03 | 3.13E-05 | 0 | 0 | 6.09E-03 | 3.13E-05 | ||||
335 | 50-32-8 | Benzo[a]pyrene | 5.80E-09 | 5.80E-09 | 4.17E-03 | 2.14E-05 | 0 | 0 | 4.17E-03 | 2.14E-05 | ||||
336 | 205-99-2 | Benzo[b]fluoranthene | 2.33E-08 | 2.33E-08 | 1.68E-02 | 8.63E-05 | 0 | 0 | 1.68E-02 | 8.63E-05 | ||||
337 | 192-97-2 | Benzo[e]pyrene | 1.43E-08 | 1.43E-08 | 1.03E-02 | 5.29E-05 | 0 | 0 | 1.03E-02 | 5.29E-05 | ||||
338 | 191-24-2 | Benzo[g,h,i]perylene | 1.31E-08 | 1.31E-08 | 9.45E-03 | 4.85E-05 | 0 | 0 | 9.45E-03 | 4.85E-05 | ||||
339 | 207-08-9 | Benzo[k]fluoranthene | 5.30E-09 | 5.30E-09 | 3.82E-03 | 1.96E-05 | 0 | 0 | 3.82E-03 | 1.96E-05 | ||||
340 | 218-01-9 | Chrysene | 1.88E-08 | 1.88E-08 | 1.36E-02 | 6.96E-05 | 0 | 0 | 1.36E-02 | 6.96E-05 | ||||
341 | 53-70-3 | Dibenz[a,h]anthracene | 1.64E-09 | 1.64E-09 | 1.18E-03 | 6.07E-06 | 0 | 0 | 1.18E-03 | 6.07E-06 | ||||
342 | 206-44-0 | Fluoranthene | 3.08E-08 | 3.08E-08 | 2.21E-02 | 1.14E-04 | 0 | 0 | 2.21E-02 | 1.14E-04 | ||||
343 | 86-73-7 | Fluorene | 6.02E-10 | 6.02E-10 | 4.33E-04 | 2.23E-06 | 0 | 0 | 4.33E-04 | 2.23E-06 | ||||
344 | 193-39-5 | Indeno[1,2,3-cd]pyrene | 1.41E-08 | 1.41E-08 | 1.02E-02 | 5.22E-05 | 0 | 0 | 1.02E-02 | 5.22E-05 | ||||
345 | 198-55-0 | Perylene | 1.64E-09 | 1.64E-09 | 1.18E-03 | 6.07E-06 | 0 | 0 | 1.18E-03 | 6.07E-06 | ||||
346 | 85-01-8 | Phenanthrene | 9.97E-09 | 9.97E-09 | 7.18E-03 | 3.69E-05 | 0 | 0 | 7.18E-03 | 3.69E-05 | ||||
347 | 129-00-0 | Pyrene | 2.51E-08 | 2.51E-08 | 1.81E-02 | 9.29E-05 | 0 | 0 | 1.81E-02 | 9.29E-05 | ||||
348 | 91-20-3 | Naphthalene | 1.57E-04 | 1.57E-04 | 113.3052 | 0.5823 | 0 | 0 | 113.3052 | 0.5823 | ||||
349 | 118-74-1 | Hexachlorobenzene | 3.86E-07 | 3.86E-07 | 0.2778 | 0.0014 | 0 | 0 | 0.2778 | 0.0014 | ||||
350 | 447 | PBDEs | 4.28E-08 | 4.28E-08 | 0.0308 | 0.0002 | 0 | 0 | 0.0308 | 0.0002 |
351 | 239 | Fluorides | 3.50E-03 | 3.50E-03 | 2520.00 | 12.95 | 0 | 0 | 2520.00 | 12.95 | Backcalculated assuming overall capture and control of 95%, then 5% of total to MELTFUG | |||
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352 | 7664-39-3 | Hydrogen Fluoride | 5.04E-05 | 5.04E-05 | 36.30 | 0.19 | 0 | 0 | 36.30 | 0.19 | Backcalculated assuming 0% control, 95% capture, then 5% of total to MELTFUG | |||
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363 | Operating Parameters & Input Assumptions (Natural Gas Sources): | |||||||||||||
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370 | ||||||||||||||
371 | Natural Gas Source | # of units | Btu rating each unit (MMBtu/hr) | Emission Points | ||||||||||
372 | EAF Burners | 2 | 15 | BH01, BH01A | ||||||||||
373 | EAF Burner | 1 | 7 | BH01, BH01A | ||||||||||
374 | Tundish preheaters | 4 | 2 | RMELT, MELTFUG | ||||||||||
375 | Horizontal heaters | 2 | 7.5 | RMELT, MELTFUG | ||||||||||
376 | Vertical Preheater | 1 | 7.5 | EU4 VERTP | ||||||||||
377 | Tundish Dryer | 2 | 1.5 | RMELT, MELTFUG | ||||||||||
378 | ||||||||||||||
379 | Max. Daily Operating Hours | 24 | hrs/day | |||||||||||
380 | Max. Annual Operating Hours | 8760 | hrs/year | |||||||||||
381 | HHV Natural Gas | 1020 | btu/cf | |||||||||||
382 | ||||||||||||||
383 | Natural Gas Source | Annual Natural Gas Usage (MMCF/yr) | Daily Natural Gas Usage (MMCF/day) | |||||||||||
384 | Vertical Preheater | 64.4 | 0.18 | |||||||||||
385 | EAF Burners | 317.8 | 0.87 | |||||||||||
386 | Tundish Preheaters and dryers | 94.5 | 0.26 | |||||||||||
387 | Horizontal heaters | 128.8 | 0.35 | |||||||||||
388 | ||||||||||||||
389 | Vertical Preheater: EU-4 Emitted Through VERTP | EU-4 | ||||||||||||
390 | ||||||||||||||
391 | CAS or DEQ ID | TAC | EF (lb/MMSCF) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||||||||
392 | 71-43-2 | Benzene | 0.008 | 5.15E-01 | 1.41E-03 | Oregon DEQ 2020 ATEI Combustion EF Tool | ||||||||
393 | 50-00-0 | Formaldehyde | 0.017 | 1.10E+00 | 3.00E-03 | |||||||||
394 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.0001 | 6.44E-03 | 1.76E-05 | |||||||||
395 | 50-32-8 | Benzo[a]pyrene | 0.0000012 | 7.73E-05 | 2.12E-07 | |||||||||
396 | 91-20-3 | Naphthalene | 0.0003 | 1.93E-02 | 5.29E-05 | |||||||||
397 | 75-07-0 | Acetaldehyde | 0.0043 | 2.77E-01 | 7.59E-04 | |||||||||
398 | 107-02-8 | Acrolein | 0.0027 | 1.74E-01 | 4.76E-04 | |||||||||
399 | 7664-41-7 | Ammonia | 18 | 1.16E+03 | 3.18E+00 | |||||||||
400 | 7440-38-2 | Arsenic and compounds | 0.0002 | 1.29E-02 | 3.53E-05 |
401 | 7440-39-3 | Barium and compounds | 0.0044 | 2.83E-01 | 7.76E-04 | |||||||||
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402 | 7440-41-7 | Beryllium and compounds | 0.000012 | 7.73E-04 | 2.12E-06 | |||||||||
403 | 7440-43-9 | Cadmium and compounds | 0.0011 | 7.09E-02 | 1.94E-04 | |||||||||
404 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.0014 | 9.02E-02 | 2.47E-04 | |||||||||
405 | 7440-48-4 | Cobalt and compounds | 0.000084 | 5.41E-03 | 1.48E-05 | |||||||||
406 | 7440-50-8 | Copper and compounds | 0.00085 | 5.48E-02 | 1.50E-04 | |||||||||
407 | 100-41-4 | Ethyl benzene | 0.0095 | 6.12E-01 | 1.68E-03 | |||||||||
408 | 110-54-3 | Hexane | 0.0063 | 4.06E-01 | 1.11E-03 | |||||||||
409 | 7439-92-1 | Lead and compounds | 0.0005 | 3.22E-02 | 8.82E-05 | |||||||||
410 | 7439-96-5 | Manganese and compounds | 0.00038 | 2.45E-02 | 6.71E-05 | |||||||||
411 | 7439-97-6 | Mercury and compounds | 0.00026 | 1.67E-02 | 4.59E-05 | |||||||||
412 | 1313-27-5 | Molybdenum trioxide | 0.00165 | 1.06E-01 | 2.91E-04 | |||||||||
413 | 365 | Nickel compounds, insoluble | 0.0021 | 1.35E-01 | 3.71E-04 | |||||||||
414 | 7782-49-2 | Selenium and compounds | 0.000024 | 1.55E-03 | 4.24E-06 | |||||||||
415 | 108-88-3 | Toluene | 0.0366 | 2.36E+00 | 6.46E-03 | |||||||||
416 | 7440-62-2 | Vanadium (fume or dust) | 0.0023 | 1.48E-01 | 4.06E-04 | |||||||||
417 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.0272 | 1.75E+00 | 4.80E-03 | |||||||||
418 | 7440-66-6 | Zinc and compounds | 0.029 | 1.87E+00 | 5.12E-03 | |||||||||
419 | ||||||||||||||
420 | ||||||||||||||
421 | ||||||||||||||
422 | ||||||||||||||
423 | ||||||||||||||
424 | ||||||||||||||
425 | EAF Burners: EU-16ng Emitted Through BH01 and BH01A | |||||||||||||
426 | ||||||||||||||
427 | 83.3% | 16.7% | Totals Including EU-09ng & EU-12ng | |||||||||||
428 | BH01 | BH01A | BH01 | BH01A | ||||||||||
429 | CAS or DEQ ID | TAC | EF (lb/MMSCF) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |
430 | 71-43-2 | Benzene | 0.008 | 2.54E+00 | 6.96E-03 | 2.12E+00 | 5.80E-03 | 4.25E-01 | 1.16E-03 | 2.12E+00 | 5.80E-03 | 4.25E-01 | 1.16E-03 | Oregon DEQ 2020 ATEI Combustion EF Tool |
431 | 50-00-0 | Formaldehyde | 0.017 | 5.40E+00 | 1.48E-02 | 4.50E+00 | 1.23E-02 | 9.02E-01 | 2.47E-03 | 4.50E+00 | 1.23E-02 | 9.02E-01 | 2.47E-03 | |
432 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.0001 | 3.18E-02 | 8.71E-05 | 2.65E-02 | 7.25E-05 | 5.31E-03 | 1.45E-05 | 2.65E-02 | 7.25E-05 | 5.31E-03 | 1.45E-05 | |
433 | 50-32-8 | Benzo[a]pyrene | 0.0000012 | 3.81E-04 | 1.04E-06 | 3.18E-04 | 8.70E-07 | 6.37E-05 | 1.74E-07 | 3.18E-04 | 8.70E-07 | 6.37E-05 | 1.75E-07 | |
434 | 91-20-3 | Naphthalene | 0.0003 | 9.53E-02 | 2.61E-04 | 7.94E-02 | 2.18E-04 | 1.59E-02 | 4.36E-05 | 7.94E-02 | 2.18E-04 | 1.59E-02 | 4.36E-05 | |
435 | 75-07-0 | Acetaldehyde | 0.0043 | 1.37E+00 | 3.74E-03 | 1.14E+00 | 3.12E-03 | 2.28E-01 | 6.25E-04 | 1.14E+00 | 3.12E-03 | 2.28E-01 | 6.25E-04 | |
436 | 107-02-8 | Acrolein | 0.0027 | 8.58E-01 | 2.35E-03 | 7.15E-01 | 1.96E-03 | 1.43E-01 | 3.93E-04 | 7.15E-01 | 1.96E-03 | 1.43E-01 | 3.93E-04 | |
437 | 7664-41-7 | Ammonia | 18 | 5.72E+03 | 1.57E+01 | 4.76E+03 | 1.31E+01 | 9.55E+02 | 2.62E+00 | 4.77E+03 | 1.31E+01 | 9.55E+02 | 2.62E+00 | |
438 | 7440-38-2 | Arsenic and compounds | 0.0002 | 6.36E-02 | 1.74E-04 | 5.29E-02 | 1.45E-04 | 1.06E-02 | 2.91E-05 | 5.29E-02 | 1.45E-04 | 1.06E-02 | 2.91E-05 | |
439 | 7440-39-3 | Barium and compounds | 0.0044 | 1.40E+00 | 3.83E-03 | 1.16E+00 | 3.19E-03 | 2.33E-01 | 6.40E-04 | 1.16E+00 | 3.19E-03 | 2.34E-01 | 6.40E-04 | |
440 | 7440-41-7 | Beryllium and compounds | 0.000012 | 3.81E-03 | 1.04E-05 | 3.18E-03 | 8.70E-06 | 6.37E-04 | 1.74E-06 | 3.18E-03 | 8.70E-06 | 6.37E-04 | 1.74E-06 | |
441 | 7440-43-9 | Cadmium and compounds | 0.0011 | 3.50E-01 | 9.58E-04 | 2.91E-01 | 7.98E-04 | 5.84E-02 | 1.60E-04 | 2.91E-01 | 7.98E-04 | 5.84E-02 | 1.60E-04 | |
442 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.0014 | 4.45E-01 | 1.22E-03 | 3.71E-01 | 1.02E-03 | 7.43E-02 | 2.04E-04 | 3.71E-01 | 1.02E-03 | 7.43E-02 | 2.04E-04 | |
443 | 7440-48-4 | Cobalt and compounds | 0.000084 | 2.67E-02 | 7.31E-05 | 2.22E-02 | 6.09E-05 | 4.46E-03 | 1.22E-05 | 2.22E-02 | 6.09E-05 | 4.46E-03 | 1.22E-05 | |
444 | 7440-50-8 | Copper and compounds | 0.00085 | 2.70E-01 | 7.40E-04 | 2.25E-01 | 6.16E-04 | 4.51E-02 | 1.24E-04 | 2.25E-01 | 6.16E-04 | 4.51E-02 | 1.24E-04 | |
445 | 100-41-4 | Ethyl benzene | 0.0095 | 3.02E+00 | 8.27E-03 | 2.51E+00 | 6.89E-03 | 5.04E-01 | 1.38E-03 | 2.52E+00 | 6.89E-03 | 5.04E-01 | 1.38E-03 | |
446 | 110-54-3 | Hexane | 0.0063 | 2.00E+00 | 5.48E-03 | 1.67E+00 | 4.57E-03 | 3.34E-01 | 9.16E-04 | 1.67E+00 | 4.57E-03 | 3.34E-01 | 9.16E-04 | |
447 | 7439-92-1 | Lead and compounds | 0.0005 | 1.59E-01 | 4.35E-04 | 1.32E-01 | 3.63E-04 | 2.65E-02 | 7.27E-05 | 1.32E-01 | 3.63E-04 | 2.65E-02 | 7.27E-05 | |
448 | 7439-96-5 | Manganese and compounds | 0.00038 | 1.21E-01 | 3.31E-04 | 1.01E-01 | 2.76E-04 | 2.02E-02 | 5.52E-05 | 1.01E-01 | 2.76E-04 | 2.02E-02 | 5.52E-05 | |
449 | 7439-97-6 | Mercury and compounds | 0.00026 | 8.26E-02 | 2.26E-04 | 6.88E-02 | 1.89E-04 | 1.38E-02 | 3.78E-05 | 6.88E-02 | 1.89E-04 | 1.38E-02 | 3.78E-05 | |
450 | 1313-27-5 | Molybdenum trioxide | 0.00165 | 5.24E-01 | 1.44E-03 | 4.37E-01 | 1.20E-03 | 8.76E-02 | 2.40E-04 | 4.37E-01 | 1.20E-03 | 8.76E-02 | 2.40E-04 |
451 | 365 | Nickel compounds, insoluble | 0.0021 | 6.67E-01 | 1.83E-03 | 5.56E-01 | 1.52E-03 | 1.11E-01 | 3.05E-04 | 5.56E-01 | 1.52E-03 | 1.11E-01 | 3.05E-04 | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
452 | 7782-49-2 | Selenium and compounds | 0.000024 | 7.63E-03 | 2.09E-05 | 6.35E-03 | 1.74E-05 | 1.27E-03 | 3.49E-06 | 6.35E-03 | 1.74E-05 | 1.27E-03 | 3.49E-06 | |
453 | 108-88-3 | Toluene | 0.0366 | 1.16E+01 | 3.19E-02 | 9.69E+00 | 2.65E-02 | 1.94E+00 | 5.32E-03 | 9.69E+00 | 2.65E-02 | 1.94E+00 | 5.32E-03 | |
454 | 7440-62-2 | Vanadium (fume or dust) | 0.0023 | 7.31E-01 | 2.00E-03 | 6.09E-01 | 1.67E-03 | 1.22E-01 | 3.34E-04 | 6.09E-01 | 1.67E-03 | 1.22E-01 | 3.34E-04 | |
455 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.0272 | 8.64E+00 | 2.37E-02 | 7.20E+00 | 1.97E-02 | 1.44E+00 | 3.95E-03 | 7.20E+00 | 1.97E-02 | 1.44E+00 | 3.96E-03 | |
456 | 7440-66-6 | Zinc and compounds | 0.029 | 9.22E+00 | 2.52E-02 | 7.68E+00 | 2.10E-02 | 1.54E+00 | 4.22E-03 | 7.68E+00 | 2.10E-02 | 1.54E+00 | 4.22E-03 | |
457 | ||||||||||||||
458 | ||||||||||||||
459 | ||||||||||||||
460 | ||||||||||||||
461 | ||||||||||||||
462 | ||||||||||||||
463 | ||||||||||||||
464 | Tundish and Horizontal Heaters: EU-16ng Emitted Through RMELT | EU-16ng_RMELT | ||||||||||||
465 | ||||||||||||||
466 | CAS or DEQ ID | TAC | EF (lb/MMSCF) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||||||||
467 | 71-43-2 | Benzene | 0.008 | 1.79E+00 | 4.89E-03 | Oregon DEQ 2020 ATEI Combustion EF Tool | ||||||||
468 | 50-00-0 | Formaldehyde | 0.017 | 3.80E+00 | 1.04E-02 | |||||||||
469 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.0001 | 2.23E-02 | 6.12E-05 | |||||||||
470 | 50-32-8 | Benzo[a]pyrene | 0.0000012 | 2.68E-04 | 7.34E-07 | |||||||||
471 | 91-20-3 | Naphthalene | 0.0003 | 6.70E-02 | 1.84E-04 | |||||||||
472 | 75-07-0 | Acetaldehyde | 0.0043 | 9.60E-01 | 2.63E-03 | |||||||||
473 | 107-02-8 | Acrolein | 0.0027 | 6.03E-01 | 1.65E-03 | |||||||||
474 | 7664-41-7 | Ammonia | 18 | 4.02E+03 | 1.10E+01 | |||||||||
475 | 7440-38-2 | Arsenic and compounds | 0.0002 | 4.47E-02 | 1.22E-04 | |||||||||
476 | 7440-39-3 | Barium and compounds | 0.0044 | 9.82E-01 | 2.69E-03 | |||||||||
477 | 7440-41-7 | Beryllium and compounds | 0.000012 | 2.68E-03 | 7.34E-06 | |||||||||
478 | 7440-43-9 | Cadmium and compounds | 0.0011 | 2.46E-01 | 6.73E-04 | |||||||||
479 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.0014 | 3.13E-01 | 8.56E-04 | |||||||||
480 | 7440-48-4 | Cobalt and compounds | 0.000084 | 1.88E-02 | 5.14E-05 | |||||||||
481 | 7440-50-8 | Copper and compounds | 0.00085 | 1.90E-01 | 5.20E-04 | |||||||||
482 | 100-41-4 | Ethyl benzene | 0.0095 | 2.12E+00 | 5.81E-03 | |||||||||
483 | 110-54-3 | Hexane | 0.0063 | 1.41E+00 | 3.85E-03 | |||||||||
484 | 7439-92-1 | Lead and compounds | 0.0005 | 1.12E-01 | 3.06E-04 | |||||||||
485 | 7439-96-5 | Manganese and compounds | 0.00038 | 8.49E-02 | 2.32E-04 | |||||||||
486 | 7439-97-6 | Mercury and compounds | 0.00026 | 5.81E-02 | 1.59E-04 | |||||||||
487 | 1313-27-5 | Molybdenum trioxide | 0.00165 | 3.68E-01 | 1.01E-03 | |||||||||
488 | 365 | Nickel compounds, insoluble | 0.0021 | 4.69E-01 | 1.28E-03 | |||||||||
489 | 7782-49-2 | Selenium and compounds | 0.000024 | 5.36E-03 | 1.47E-05 | |||||||||
490 | 108-88-3 | Toluene | 0.0366 | 8.17E+00 | 2.24E-02 | |||||||||
491 | 7440-62-2 | Vanadium (fume or dust) | 0.0023 | 5.14E-01 | 1.41E-03 | |||||||||
492 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.0272 | 6.07E+00 | 1.66E-02 | |||||||||
493 | 7440-66-6 | Zinc and compounds | 0.029 | 6.48E+00 | 1.77E-02 | |||||||||
494 | ||||||||||||||
495 | ||||||||||||||
496 | ||||||||||||||
497 | ||||||||||||||
498 | ||||||||||||||
499 | ||||||||||||||
500 |
501 | ||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
502 | Tundish and Horizontal Heaters Fugitive Emissions: EU-16ng_mf Emitted Through MELTFUG | |||||||||||||
503 | ||||||||||||||
504 | EU-16ng_MELTFUG | Totals Including EU-09ng & EU-12ng | ||||||||||||
505 | CAS or DEQ ID | TAC | EF (lb/MMSCF) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||||||
506 | 71-43-2 | Benzene | 0.0004 | 8.9318E-01 | 2.45E-04 | 8.93E-02 | 2.45E-04 | Oregon DEQ 2020 ATEI Combustion EF Tool | ||||||
507 | 50-00-0 | Formaldehyde | 0.00085 | 1.90E-01 | 5.20E-04 | 1.90E-01 | 5.20E-04 | |||||||
508 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.000005 | 1.12E-03 | 3.06E-06 | 1.12E-03 | 3.06E-06 | |||||||
509 | 50-32-8 | Benzo[a]pyrene | 0.00000006 | 1.34E-05 | 3.67E-08 | 1.34E-05 | 3.67E-08 | |||||||
510 | 91-20-3 | Naphthalene | 0.000015 | 3.35E-03 | 9.18E-06 | 3.35E-03 | 9.18E-06 | |||||||
511 | 75-07-0 | Acetaldehyde | 0.000215 | 4.80E-02 | 1.32E-04 | 4.80E-02 | 1.32E-04 | |||||||
512 | 107-02-8 | Acrolein | 0.000135 | 3.01E-02 | 8.26E-05 | 3.02E-02 | 8.27E-05 | |||||||
513 | 7664-41-7 | Ammonia | 0.9 | 2.01E+02 | 5.51E-01 | 2.01E+02 | 5.51E-01 | |||||||
514 | 7440-38-2 | Arsenic and compounds | 0.00001 | 2.23E-03 | 6.12E-06 | 2.23E-03 | 6.12E-06 | |||||||
515 | 7440-39-3 | Barium and compounds | 0.00022 | 4.91E-02 | 1.35E-04 | 4.91E-02 | 1.35E-04 | |||||||
516 | 7440-41-7 | Beryllium and compounds | 0.0000006 | 1.34E-04 | 3.67E-07 | 1.34E-04 | 3.67E-07 | |||||||
517 | 7440-43-9 | Cadmium and compounds | 0.000055 | 1.23E-02 | 3.36E-05 | 1.23E-02 | 3.37E-05 | |||||||
518 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00007 | 1.56E-02 | 4.28E-05 | 1.56E-02 | 4.28E-05 | |||||||
519 | 7440-48-4 | Cobalt and compounds | 0.0000042 | 9.38E-04 | 2.57E-06 | 9.38E-04 | 2.57E-06 | |||||||
520 | 7440-50-8 | Copper and compounds | 0.0000425 | 9.49E-03 | 2.60E-05 | 9.49E-03 | 2.60E-05 | |||||||
521 | 100-41-4 | Ethyl benzene | 0.000475 | 1.06E-01 | 2.91E-04 | 1.06E-01 | 2.91E-04 | |||||||
522 | 110-54-3 | Hexane | 0.000315 | 7.03E-02 | 1.93E-04 | 7.04E-02 | 1.93E-04 | |||||||
523 | 7439-92-1 | Lead and compounds | 0.000025 | 5.58E-03 | 1.53E-05 | 5.58E-03 | 1.53E-05 | |||||||
524 | 7439-96-5 | Manganese and compounds | 0.000019 | 4.24E-03 | 1.16E-05 | 4.24E-03 | 1.16E-05 | |||||||
525 | 7439-97-6 | Mercury and compounds | 0.000013 | 2.90E-03 | 7.95E-06 | 2.90E-03 | 7.96E-06 | |||||||
526 | 1313-27-5 | Molybdenum trioxide | 0.0000825 | 1.84E-02 | 5.05E-05 | 1.84E-02 | 5.05E-05 | |||||||
527 | 365 | Nickel compounds, insoluble | 0.000105 | 2.34E-02 | 6.42E-05 | 2.34E-02 | 6.43E-05 | |||||||
528 | 7782-49-2 | Selenium and compounds | 0.0000012 | 2.68E-04 | 7.34E-07 | 2.68E-04 | 7.34E-07 | |||||||
529 | 108-88-3 | Toluene | 0.00183 | 4.09E-01 | 1.12E-03 | 4.09E-01 | 1.12E-03 | |||||||
530 | 7440-62-2 | Vanadium (fume or dust) | 0.000115 | 2.57E-02 | 7.04E-05 | 2.57E-02 | 7.04E-05 | |||||||
531 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.00136 | 3.04E-01 | 8.32E-04 | 3.04E-01 | 8.33E-04 | |||||||
532 | 7440-66-6 | Zinc and compounds | 0.00145 | 3.24E-01 | 8.87E-04 | 3.24E-01 | 8.87E-04 | |||||||
533 | ||||||||||||||
534 | ||||||||||||||
535 | ||||||||||||||
536 | ||||||||||||||
537 | ||||||||||||||
538 | ||||||||||||||
539 | ||||||||||||||
540 | ||||||||||||||
541 | ||||||||||||||
542 | AQ520 Info | |||||||||||||
543 | CE | SLEF col | STEF col | Unit | Ref Col | |||||||||
544 | %SRC | EU-1_BH01 | 54 | 1 | 6 | 5 | 3 | 4 | lb/ton | 16 | ||||
545 | %SRC | EU-1_BH01A | 129 | 1 | 6 | 5 | 3 | 4 | lb/ton | 16 | ||||
546 | %SRC | EU-1_BH02 | 198 | 1 | 6 | 5 | 3 | 4 | lb/ton | 16 | ||||
547 | %SRC | EU-3_RM | 266 | 1 | 6 | 5 | 3 | 4 | lb/ton | 16 | ||||
548 | %SRC | EU-3_MF | 298 | 1 | 6 | 5 | 3 | 4 | lb/ton | 16 | ||||
549 | %SRC | EU-4 | 392 | 1 | 5 | 4 | 3 | 3 | lb/MMSCF | 16 | ||||
550 | %SRC | EU-16ng_BH01 | 430 | 1 | 7 | 6 | 0.51077778 | 3 | 3 | lb/MMSCF | 16 | |||
551 | %SRC | EU-16ng_BH01A | 430 | 1 | 9 | 8 | 0.90192063 | 3 | 3 | lb/MMSCF | 16 | |||
552 | %SRC | EU-16ng_RMELT | 467 | 1 | 5 | 4 | 0.58730159 | 3 | 3 | lb/MMSCF | 16 | |||
553 | %SRC | EU-16ng_MF | 506 | 1 | 5 | 4 | 3 | 3 | lb/MMSCF | 16 |
A | B | C | D | E | F | G | H | I | J | K | P | |
---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Attachment B - Emission Calculations | |||||||||||
2 | Table B-3: Billet Cutting at Casting | |||||||||||
3 | ||||||||||||
4 | Toxics Emission Unit ID: | EU-10 | ||||||||||
5 | Description: | Metal TACs emissions from torch cutting of metal billets produced from casting | ||||||||||
6 | Emission Point(s): | BC01 | ||||||||||
7 | ||||||||||||
8 | ||||||||||||
9 | Toxics Emission Unit ID: | EU-10ng | ||||||||||
10 | Description: | Gas combustion emissions from torch cutting of metal billets produced from casting | ||||||||||
11 | Emission Point(s): | BC01 | ||||||||||
12 | ||||||||||||
13 | ||||||||||||
14 | ||||||||||||
15 | ||||||||||||
16 | ||||||||||||
17 | ||||||||||||
18 | ||||||||||||
19 | ||||||||||||
20 | ||||||||||||
21 | Operating Parameters & Input Assumptions: | |||||||||||
22 | ||||||||||||
23 | ||||||||||||
24 | Daily Steel Production | 3,700 | tons/day | |||||||||
25 | Annual Steel Production | 720,000 | tons/year | |||||||||
26 | Approx. Billet Weight | 2.5 | tons | |||||||||
27 | Daily Billet Cuts | 1480 | cuts/day | |||||||||
28 | Annual Billet Cuts | 288,000 | cuts/yr | |||||||||
29 | ||||||||||||
30 | # torches | 5 | ||||||||||
31 | Operating Hours | 24 | hrs/day | |||||||||
32 | Operating Hours | 8760 | hrs/yr | |||||||||
33 | Gas Flow Rate | 30 | CFH per torch (see included cut sheet in Tabl_B1 tab) | |||||||||
34 | Annual Gas Usage | 1314000 | CF/yr | |||||||||
35 | Daily Gas Usage | 3600 | CF/day | |||||||||
36 | Chromium VI Speciation Factor | 8.4% | ||||||||||
37 | Stainless Steel Daily EF Multiplier | 64 | ||||||||||
38 | Stainless Steel Annual EF Multiplier | 1.32 | 0.5% annual production rate | |||||||||
39 | ||||||||||||
40 | Billet Cutting @ Casting: EU-10 (emission point BC01) | |||||||||||
41 | ||||||||||||
42 | CAS or DEQ ID | TAC | EF (lb/cut)(annual) | EF (lb/cut)(daily) | Emission Rate (lb/yr) | Emission Rate (lb/day) | ||||||
43 | 7429-90-5 | Aluminum and Compounds | 9.01E-05 | 9.01E-05 | 25.953 | 0.13337 | Particulate and Trace Metals Emissions Test Report Cascade Steel Rolling Mills McMinnville Facility Roof Monitor and Billet Cutting Exhausts McMinnville, OregonAugust 6 through 8, 2019. Emissions testing is based on testing at an open vent and control efficiency does not apply to the emission factor. | |||||
44 | 7440-36-0 | Antimony and Compounds | 5.19E-06 | 5.19E-06 | 1.496 | 0.00769 | ||||||
45 | 7440-38-2 | Arsenic and Compounds | 1.53E-05 | 1.53E-05 | 4.411 | 0.02267 | ||||||
46 | 7440-41-7 | Beryllium and Compounds | 0.00E+00 | 0.00E+00 | 0.000 | 0.00000 | ||||||
47 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 3.58E-06 | 1.46E-05 | 1.030 | 0.02156 | ||||||
48 | 7440-48-4 | Cobalt and Compounds | 7.35E-06 | 7.35E-06 | 2.117 | 0.01088 | ||||||
49 | 7440-50-8 | Copper and Compounds | 4.82E-04 | 4.82E-04 | 138.807 | 0.71332 | ||||||
50 | 7439-92-1 | Lead and Compounds | 1.75E-05 | 1.75E-05 | 5.045 | 0.02593 |
51 | 7439-96-5 | Manganese and Compounds | 3.22E-04 | 3.22E-04 | 92.818 | 0.47698 | ||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | 365 | Nickel compounds, insoluble | 7.42E-05 | 7.42E-05 | 21.380 | 0.10987 | ||||||
53 | 504 | Phosphorus and Compounds | 2.60E-05 | 2.60E-05 | 7.484 | 0.03846 | ||||||
54 | 7782-49-2 | Selenium and Compounds | 0.00E+00 | 0.00E+00 | 0.000 | 0.00000 | ||||||
55 | 7440-66-6 | Zinc and Compounds | 8.47E-05 | 8.47E-05 | 24.383 | 0.12530 | ||||||
56 | 7440-43-9 | Cadmium and Compounds | 0.00E+00 | 0.00E+00 | 0.000 | 0.00000 | ||||||
57 | 7440-62-2 | Vanadium (fume or dust) | 5.84E-06 | 5.84E-06 | 1.681 | 0.00864 | ||||||
58 | ||||||||||||
59 | ||||||||||||
60 | ||||||||||||
61 | ||||||||||||
62 | ||||||||||||
63 | ||||||||||||
64 | ||||||||||||
65 | ||||||||||||
66 | ||||||||||||
67 | ||||||||||||
68 | ||||||||||||
69 | ||||||||||||
70 | ||||||||||||
71 | Billet Cutting @ Casting Torch Natural Gas: EU-10ng Emissions at BC01 | |||||||||||
72 | ||||||||||||
73 | ||||||||||||
74 | CAS or DEQ ID | TAC | EF (lb/MMSCF) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||||||
75 | 71-43-2 | Benzene | 0.008 | 1.05E-02 | 2.88E-05 | Oregon DEQ 2020 ATEI Combustion EF Tool | ||||||
76 | 50-00-0 | Formaldehyde | 0.017 | 2.23E-02 | 6.12E-05 | |||||||
77 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.0001 | 1.31E-04 | 3.60E-07 | |||||||
78 | 50-32-8 | Benzo[a]pyrene | 0.0000012 | 1.58E-06 | 4.32E-09 | |||||||
79 | 91-20-3 | Naphthalene | 0.0003 | 3.94E-04 | 1.08E-06 | |||||||
80 | 75-07-0 | Acetaldehyde | 0.0043 | 5.65E-03 | 1.55E-05 | |||||||
81 | 107-02-8 | Acrolein | 0.0027 | 3.55E-03 | 9.72E-06 | |||||||
82 | 7664-41-7 | Ammonia | 18 | 2.37E+01 | 6.48E-02 | |||||||
83 | 7440-39-3 | Barium and compounds | 0.0044 | 5.78E-03 | 1.58E-05 | |||||||
84 | 100-41-4 | Ethyl benzene | 0.0095 | 1.25E-02 | 3.42E-05 | |||||||
85 | 110-54-3 | Hexane | 0.0063 | 8.28E-03 | 2.27E-05 | |||||||
86 | 7439-97-6 | Mercury and compounds | 0.00026 | 3.42E-04 | 9.36E-07 | |||||||
87 | 1313-27-5 | Molybdenum trioxide | 0.00165 | 2.17E-03 | 5.94E-06 | |||||||
88 | 108-88-3 | Toluene | 0.0366 | 4.81E-02 | 1.32E-04 | |||||||
89 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.0272 | 3.57E-02 | 9.79E-05 | |||||||
90 | ||||||||||||
91 | ||||||||||||
92 | ||||||||||||
93 | ||||||||||||
94 | ||||||||||||
95 | ||||||||||||
96 | ||||||||||||
97 | ||||||||||||
98 | ||||||||||||
99 | AQ520 Info | |||||||||||
100 | Row | CAS col | STER Col | LTER Col | CE | SLEF col | STEF col | Unit | Ref Col | |||
101 | %SRC | EU-10 | 43 | 1 | 6 | 5 | 3 | 4 | lb/cut | 16 | ||
102 | %SRC | EU-10ng | 75 | 1 | 5 | 4 | 3 | 3 | lb/MMCSF | 16 |
A | B | C | D | E | F | G | H | I | J | K | P | |
---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Attachment B - Emission Calculations | |||||||||||
2 | Table B-4: Scrap Billet Cutting at Melt Shop Charge Bay | |||||||||||
3 | ||||||||||||
4 | Toxics Emission Unit ID: | EU-12 | ||||||||||
5 | Emission Point(s): | BH01 | ||||||||||
6 | BH01A | |||||||||||
7 | MELTFUG | |||||||||||
8 | Description: | Metal TACs emissions from torch cutting of scrap metal billets | ||||||||||
9 | ||||||||||||
10 | Toxics Emission Unit ID: | EU-12ng | ||||||||||
11 | Emission Point(s): | BH01 | ||||||||||
12 | BH01A | |||||||||||
13 | MELTFUG | |||||||||||
14 | Description: | Gas combustion emissions from torch cutting of scrap metal billets produced from casting | ||||||||||
15 | ||||||||||||
16 | ||||||||||||
17 | ||||||||||||
18 | ||||||||||||
19 | ||||||||||||
20 | ||||||||||||
21 | ||||||||||||
22 | Operating Parameters & Input Assumptions: | |||||||||||
23 | ||||||||||||
24 | ||||||||||||
25 | Daily Billet Cuts | 200 | cuts/day | |||||||||
26 | Annual Billet Cuts | 48,291 | cuts/yr | |||||||||
27 | BH-1/1A Removal Eff. | 95% | ||||||||||
28 | BH-1/1A Capture Eff. | 95% | ||||||||||
29 | Chromium VI Speciation Factor | 8.4% | ||||||||||
30 | ||||||||||||
31 | # torches | 1 | ||||||||||
32 | Operating Hours | 8 | hrs/day | |||||||||
33 | Operating Hours | 1932 | hrs/yr | |||||||||
34 | Gas Flow Rate | 30 | CFH per torch (see included cut sheet) | |||||||||
35 | Annual Gas Usage | 57949.2 | CF/yr | |||||||||
36 | Daily Gas Usage | 240 | CF/day | |||||||||
37 | ||||||||||||
38 | Scrap Billet Cutting @ Melt Shop Charge Bay: EU-12 Controlled by BH-1/1A (emission point BH01/BH01A) | |||||||||||
39 | ||||||||||||
40 | 83.3% | 16.7% | ||||||||||
41 | BH01 | BH01A | ||||||||||
42 | CAS or DEQ ID | TAC | EF (lb/cut) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||
43 | 7429-90-5 | Aluminum and Compounds | 9.01E-05 | 2.07E-01 | 8.56E-04 | 1.72E-01 | 7.13E-04 | 3.45E-02 | 1.43E-04 | Particulate and Trace Metals Emissions Test Report Cascade Steel Rolling Mills McMinnville Facility Roof Monitor and Billet Cutting Exhausts McMinnville, OregonAugust 6 through 8, 2019. Overall control efficiency estimate based on 95% control (EPA-452/F-03-025) and 95% capture (estimated). | ||
44 | 7440-36-0 | Antimony and Compounds | 5.19E-06 | 1.19E-02 | 4.93E-05 | 9.92E-03 | 4.11E-05 | 1.99E-03 | 8.24E-06 | |||
45 | 7440-38-2 | Arsenic and Compounds | 1.53E-05 | 3.51E-02 | 1.45E-04 | 2.93E-02 | 1.21E-04 | 5.87E-03 | 2.43E-05 | |||
46 | 7440-41-7 | Beryllium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||
47 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 2.71E-06 | 6.21E-03 | 2.57E-05 | 5.18E-03 | 2.14E-05 | 1.04E-03 | 4.30E-06 | |||
48 | 7440-48-4 | Cobalt and Compounds | 7.35E-06 | 1.69E-02 | 6.98E-05 | 1.40E-02 | 5.82E-05 | 2.82E-03 | 1.17E-05 | |||
49 | 7440-50-8 | Copper and Compounds | 4.82E-04 | 1.11E+00 | 4.58E-03 | 9.21E-01 | 3.81E-03 | 1.85E-01 | 7.65E-04 | |||
50 | 7439-92-1 | Lead and Compounds | 1.75E-05 | 4.02E-02 | 1.66E-04 | 3.35E-02 | 1.39E-04 | 6.71E-03 | 2.78E-05 |
51 | 7439-96-5 | Manganese and Compounds | 3.22E-04 | 7.39E-01 | 3.06E-03 | 6.16E-01 | 2.55E-03 | 1.23E-01 | 5.11E-04 | |||
---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | 365 | Nickel compounds, insoluble | 7.42E-05 | 1.70E-01 | 7.05E-04 | 1.42E-01 | 5.87E-04 | 2.84E-02 | 1.18E-04 | |||
53 | 504 | Phosphorus and Compounds | 2.60E-05 | 5.96E-02 | 2.47E-04 | 4.97E-02 | 2.06E-04 | 9.95E-03 | 4.12E-05 | |||
54 | 7782-49-2 | Selenium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||
55 | 7440-66-6 | Zinc and Compounds | 8.47E-05 | 1.94E-01 | 8.04E-04 | 1.62E-01 | 6.70E-04 | 3.24E-02 | 1.34E-04 | |||
56 | 7440-43-9 | Cadmium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||
57 | 7440-62-2 | Vanadium (fume or dust) | 5.84E-06 | 1.34E-02 | 5.54E-05 | 1.12E-02 | 4.62E-05 | 2.24E-03 | 9.26E-06 | |||
58 | ||||||||||||
59 | ||||||||||||
60 | ||||||||||||
61 | ||||||||||||
62 | ||||||||||||
63 | ||||||||||||
64 | Scrap Billet Cutting @ Melt Shop Charge Bay: EU-12 Fugitives (Emission Point MELTFUG) | |||||||||||
65 | EU-12_MELTFUG | |||||||||||
66 | CAS or DEQ ID | TAC | EF (lb/cut) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||||||
67 | 7429-90-5 | Aluminum and Compounds | 9.01E-05 | 0.218 | 0.00090 | Particulate and Trace Metals Emissions Test Report Cascade Steel Rolling Mills McMinnville Facility Roof Monitor and Billet Cutting Exhausts McMinnville, OregonAugust 6 through 8, 2019. Overall control efficiency estimate based on 95% control (EPA-452/F-03-025) and 95% capture (estimated). | ||||||
68 | 7440-36-0 | Antimony and Compounds | 5.19E-06 | 0.013 | 0.00005 | |||||||
69 | 7440-38-2 | Arsenic and Compounds | 1.53E-05 | 0.037 | 0.00015 | |||||||
70 | 7440-41-7 | Beryllium and Compounds | 0.00E+00 | 0.000 | 0.00000 | |||||||
71 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 2.71E-06 | 0.007 | 0.00003 | |||||||
72 | 7440-48-4 | Cobalt and Compounds | 7.35E-06 | 0.018 | 0.00007 | |||||||
73 | 7440-50-8 | Copper and Compounds | 4.82E-04 | 1.164 | 0.00482 | |||||||
74 | 7439-92-1 | Lead and Compounds | 1.75E-05 | 0.042 | 0.00018 | |||||||
75 | 7439-96-5 | Manganese and Compounds | 3.22E-04 | 0.778 | 0.00322 | |||||||
76 | 365 | Nickel compounds, insoluble | 7.42E-05 | 0.179 | 0.00074 | |||||||
77 | 504 | Phosphorus and Compounds | 2.60E-05 | 0.063 | 0.00026 | |||||||
78 | 7782-49-2 | Selenium and Compounds | 0.00E+00 | 0.000 | 0.00000 | |||||||
79 | 7440-66-6 | Zinc and Compounds | 8.47E-05 | 0.204 | 0.00085 | |||||||
80 | 7440-43-9 | Cadmium and Compounds | 0.00E+00 | 0.000 | 0.00000 | |||||||
81 | 7440-62-2 | Vanadium (fume or dust) | 5.84E-06 | 0.014 | 0.00006 | |||||||
82 | ||||||||||||
83 | ||||||||||||
84 | Scrap Billet Cutting @ Charge Bay Torch Natural Gas: EU-12ng Emissions at BH01/BH01A | |||||||||||
85 | 83.3% | 16.7% | ||||||||||
86 | BH01 | BH01A | ||||||||||
87 | CAS or DEQ ID | TAC | EF (lb/MMSCF) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||
88 | 71-43-2 | Benzene | 0.008 | 4.40E-04 | 1.82E-06 | 3.67E-04 | 1.52E-06 | 7.35E-05 | 3.05E-07 | Oregon DEQ 2020 ATEI Combustion EF Tool. Control efficiency assumed to be 0% for natural gas combustion emissions | ||
89 | 50-00-0 | Formaldehyde | 0.017 | 9.36E-04 | 3.88E-06 | 7.80E-04 | 3.23E-06 | 1.56E-04 | 6.47E-07 | |||
90 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.0001 | 5.51E-06 | 2.28E-08 | 4.59E-06 | 1.90E-08 | 9.19E-07 | 3.81E-09 | |||
91 | 50-32-8 | Benzo[a]pyrene | 0.0000012 | 6.61E-08 | 2.74E-10 | 5.50E-08 | 2.28E-10 | 1.10E-08 | 4.57E-11 | |||
92 | 91-20-3 | Naphthalene | 0.0003 | 1.65E-05 | 6.84E-08 | 1.38E-05 | 5.70E-08 | 2.76E-06 | 1.14E-08 | |||
93 | 75-07-0 | Acetaldehyde | 0.0043 | 2.37E-04 | 9.80E-07 | 1.97E-04 | 8.17E-07 | 3.95E-05 | 1.64E-07 | |||
94 | 107-02-8 | Acrolein | 0.0027 | 1.49E-04 | 6.16E-07 | 1.24E-04 | 5.13E-07 | 2.48E-05 | 1.03E-07 | |||
95 | 7664-41-7 | Ammonia | 18 | 9.91E-01 | 4.10E-03 | 8.25E-01 | 3.42E-03 | 1.65E-01 | 6.85E-04 | |||
96 | 7440-39-3 | Barium and compounds | 0.0044 | 2.42E-04 | 1.00E-06 | 2.02E-04 | 8.36E-07 | 4.05E-05 | 1.68E-07 | |||
97 | 100-41-4 | Ethyl benzene | 0.0095 | 5.23E-04 | 2.17E-06 | 4.36E-04 | 1.80E-06 | 8.73E-05 | 3.62E-07 | |||
98 | 110-54-3 | Hexane | 0.0063 | 3.47E-04 | 1.44E-06 | 2.89E-04 | 1.20E-06 | 5.79E-05 | 2.40E-07 | |||
99 | 7439-97-6 | Mercury and compounds | 0.00026 | 1.43E-05 | 5.93E-08 | 1.19E-05 | 4.94E-08 | 2.39E-06 | 9.90E-09 | |||
100 | 1313-27-5 | Molybdenum trioxide | 0.00165 | 9.08E-05 | 3.76E-07 | 7.57E-05 | 3.13E-07 | 1.52E-05 | 6.28E-08 |
101 | 108-88-3 | Toluene | 0.0366 | 2.01E-03 | 8.34E-06 | 1.68E-03 | 6.95E-06 | 3.36E-04 | 1.39E-06 | |||
---|---|---|---|---|---|---|---|---|---|---|---|---|
102 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.0272 | 1.50E-03 | 6.20E-06 | 1.25E-03 | 5.17E-06 | 2.50E-04 | 1.04E-06 | |||
103 | ||||||||||||
104 | ||||||||||||
105 | ||||||||||||
106 | ||||||||||||
107 | ||||||||||||
108 | ||||||||||||
109 | ||||||||||||
110 | ||||||||||||
111 | ||||||||||||
112 | Scrap Billet Cutting @ Charge Bay Torch Natural Gas: EU-12ng Emissions at MELTFUG | |||||||||||
113 | ||||||||||||
114 | EU-12ng_MELTFUG | |||||||||||
115 | CAS or DEQ ID | TAC | EF (lb/MMSCF) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||||||
116 | 71-43-2 | Benzene | 0.008 | 2.32E-05 | 9.60E-08 | Oregon DEQ 2020 ATEI Combustion EF Tool. Control efficiency assumed to be 0% for natural gas combustion emissions | ||||||
117 | 50-00-0 | Formaldehyde | 0.017 | 4.93E-05 | 2.04E-07 | |||||||
118 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.0001 | 2.90E-07 | 1.20E-09 | |||||||
119 | 50-32-8 | Benzo[a]pyrene | 0.0000012 | 3.48E-09 | 1.44E-11 | |||||||
120 | 91-20-3 | Naphthalene | 0.0003 | 8.69E-07 | 3.60E-09 | |||||||
121 | 75-07-0 | Acetaldehyde | 0.0043 | 1.25E-05 | 5.16E-08 | |||||||
122 | 107-02-8 | Acrolein | 0.0027 | 7.82E-06 | 3.24E-08 | |||||||
123 | 7664-41-7 | Ammonia | 18 | 5.22E-02 | 2.16E-04 | |||||||
124 | 7440-39-3 | Barium and compounds | 0.0044 | 1.27E-05 | 5.28E-08 | |||||||
125 | 100-41-4 | Ethyl benzene | 0.0095 | 2.75E-05 | 1.14E-07 | |||||||
126 | 110-54-3 | Hexane | 0.0063 | 1.83E-05 | 7.56E-08 | |||||||
127 | 7439-97-6 | Mercury and compounds | 0.00026 | 7.53E-07 | 3.12E-09 | |||||||
128 | 1313-27-5 | Molybdenum trioxide | 0.00165 | 4.78E-06 | 1.98E-08 | |||||||
129 | 108-88-3 | Toluene | 0.0366 | 1.06E-04 | 4.39E-07 | |||||||
130 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.0272 | 7.88E-05 | 3.26E-07 | |||||||
131 | ||||||||||||
132 | ||||||||||||
133 | ||||||||||||
134 | ||||||||||||
135 | ||||||||||||
136 | ||||||||||||
137 | ||||||||||||
138 | ||||||||||||
139 | ||||||||||||
140 | AQ520 Info | |||||||||||
141 | Row | CAS col | STER Col | LTER Col | CE | SLEF col | STEF col | Unit | Ref Col | |||
142 | %SRC | EU-12_BH01 | 43 | 1 | 7 | 6 | 96.0% | 3 | 3 | lb/cut | 16 | |
143 | %SRC | EU-12_BH01A | 43 | 1 | 9 | 8 | 99.2% | 3 | 3 | lb/cut | 16 | |
144 | %SRC | EU-12_MELTFUG | 67 | 1 | 5 | 4 | 95% | 3 | 3 | lb/cut | 16 | |
145 | %SRC | EU-12ng_BH01 | 88 | 1 | 7 | 6 | 20.9% | 3 | 3 | lb/MMSCF | 16 | |
146 | %SRC | EU-12ng_BH01A | 88 | 1 | 9 | 8 | 84.1% | 3 | 3 | lb/MMSCF | 16 | |
147 | %SRC | EU-12ng_MELTFUG | 116 | 1 | 5 | 4 | 95% | 3 | 3 | lb/MMSCF | 16 |
A | B | C | D | E | F | G | H | I | J | K | P | |
---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Attachment B - Emission Calculations | |||||||||||
2 | Table B-5: Slag Handling outside Melt Shop | |||||||||||
3 | ||||||||||||
4 | Toxics Emission Unit ID: | EU-5 | ||||||||||
5 | Emission Point(s): | SHF01 | ||||||||||
6 | Description: | Metal TAC and H2S emissions from unloading slag from the melt shop and loading slag into a truck | ||||||||||
7 | ||||||||||||
8 | ||||||||||||
9 | ||||||||||||
10 | ||||||||||||
11 | ||||||||||||
12 | ||||||||||||
13 | Operating Parameters & Input Assumptions: | |||||||||||
14 | ||||||||||||
15 | EPA Drop Equation: AP-42 13.2.4 (first dump - hot and dry) | |||||||||||
16 | ||||||||||||
17 | Wind Speed, daily | 20.85 | mph (meterological data - McMinnville WS - 5-yr max. daily average based on 2014-2018 data) | |||||||||
18 | Wind Speed, annual | 6.66 | mph (meterological data - McMinnville WS - 5-yr average based on 2014-2018 data) | |||||||||
19 | k factor | 0.35 | unitless (for PM10) | |||||||||
20 | % moisture content | 0.92 | % (AP-42: Table 13.2.4-1) | |||||||||
21 | PM emission factor, daily | 0.0213 | lb/ton | |||||||||
22 | PM emission factor, annual | 0.0048 | lb/ton | |||||||||
23 | Slag Handling Rate | 10% | by mass of steel production rate | |||||||||
24 | Daily Slag Handling Rate | 370 | ton/day | |||||||||
25 | Annual Slag Handling Rate | 72,000 | ton/yr | |||||||||
26 | ||||||||||||
27 | EPA Drop Equation: AP-42 13.2.4 (wet and cool) | |||||||||||
28 | ||||||||||||
29 | Wind Speed, daily | 20.85 | mph (meterological data - McMinnville WS - 5-yr max. daily average based on 2014-2018 data) | |||||||||
30 | Wind Speed, annual | 6.66 | mph (meterological data - McMinnville WS - 5-yr average based on 2014-2018 data) | |||||||||
31 | k factor | 0.35 | unitless (for PM10) | |||||||||
32 | % moisture content | 5.65 | % (provided by CSRM, avg. of three years) | |||||||||
33 | PM emission factor, daily | 0.0017 | lb/ton | |||||||||
34 | PM emission factor, annual | 0.0004 | lb/ton | |||||||||
35 | Slag Handling Rate | 10% | by mass of steel production rate | |||||||||
36 | Daily Slag Handling Rate | 370 | ton/day | |||||||||
37 | Annual Slag Handling Rate | 72,000 | ton/yr | |||||||||
38 | ||||||||||||
39 | Combined PM EF, daily | 0.0229 | lb/ton | |||||||||
40 | Combined PM EF, annual | 0.0052 | lb/ton | |||||||||
41 | ||||||||||||
42 | ||||||||||||
43 | Slag Hydrogen Sulfide (H2S) Emissions Estimate- Engineering Calculation | |||||||||||
44 | ||||||||||||
45 | Slag Production | 370 | T slag/day | |||||||||
46 | 72000 | T slag/yr | ||||||||||
47 | ||||||||||||
48 | Slag Density | 132 | lb/cf | |||||||||
49 | ||||||||||||
50 | Area of slag pile | 675 | sq ft | (estimate) |
51 | Crust Thickness | 0.25 | ft | (estimate) | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | ||||||||||||
53 | ||||||||||||
54 | Mass of Slag in Crust of Pile | 22,275 | lb slag | |||||||||
55 | ||||||||||||
56 | Fraction slag crust produced | 60.2 | lb slag in crust/ton slag produced | |||||||||
57 | ||||||||||||
58 | Effectiveness of oxidizing agent | 75% | (Ref: F.H Rehmus, D.P. Manka & E.A. Upton, "Control of H2S Emission During Slag Quenching", Journal of the Air Pollution Control Association, 23:10, 1973.) | |||||||||
59 | ||||||||||||
60 | Sulfur content | 0.28% | wt % | (provided by CSRM) | ||||||||
61 | ||||||||||||
62 | H2S Emission Factor | 0.045 | lb-H2S/ton-slag (assume all S in slag crust converted to H2S minus effectiveness of oxidizing agent) | |||||||||
63 | ||||||||||||
64 | Melt Shop Slag Handling: EU-5 Emission Point SHF01 | |||||||||||
65 | ||||||||||||
66 | CAS or DEQ ID | TAC | EF (lb/ton) (Annual) | EF (lb/ton) (Daily) | Emission Rate (lb/yr) | Emission Rate (lb/day) | ||||||
67 | 7429-90-5 | Aluminum and Compounds | 7.80E-05 | 3.44E-04 | 5.62E+00 | 1.27E-01 | EPA Drop Equation: AP-42 13.2.4, slag composition sample | |||||
68 | 7439-96-5 | Manganese and Compounds | 1.51E-04 | 6.65E-04 | 1.09E+01 | 2.46E-01 | ||||||
69 | 7440-22-4 | Silver and Compounds | 1.98E-09 | 8.71E-09 | 1.42E-04 | 3.22E-06 | ||||||
70 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 5.72E-10 | 2.52E-09 | 4.12E-05 | 9.33E-07 | ||||||
71 | 7440-36-0 | Antimony and Compounds | 4.11E-09 | 1.81E-08 | 2.96E-04 | 6.70E-06 | ||||||
72 | 7440-38-2 | Arsenic and Compounds | 1.72E-08 | 7.57E-08 | 1.24E-03 | 2.80E-05 | ||||||
73 | 7440-41-7 | Beryllium and Compounds | 1.61E-09 | 7.11E-09 | 1.16E-04 | 2.63E-06 | ||||||
74 | 7440-43-9 | Cadmium and Compounds | 8.32E-10 | 3.67E-09 | 5.99E-05 | 1.36E-06 | ||||||
75 | 7440-50-8 | Copper and Compounds | 7.80E-07 | 3.44E-06 | 5.62E-02 | 1.27E-03 | ||||||
76 | 7439-92-1 | Lead and Compounds | 2.44E-08 | 1.08E-07 | 1.76E-03 | 3.99E-05 | ||||||
77 | 7439-97-6 | Mercury and compounds | 3.38E-11 | 1.49E-10 | 2.43E-06 | 5.52E-08 | ||||||
78 | 365 | Nickel compounds, insoluble | 1.35E-07 | 5.96E-07 | 9.74E-03 | 2.21E-04 | ||||||
79 | 7782-49-2 | Selenium and Compounds | 1.82E-09 | 8.03E-09 | 1.31E-04 | 2.97E-06 | ||||||
80 | 7440-62-2 | Vanadium (fume or dust) | 3.38E-06 | 1.49E-05 | 2.43E-01 | 5.52E-03 | ||||||
81 | 7440-39-3 | Barium and Compounds | 2.18E-06 | 9.63E-06 | 1.57E-01 | 3.56E-03 | ||||||
82 | 1313-27-5 | Molybdenum trioxide | 8.58E-08 | 3.78E-07 | 6.18E-03 | 1.40E-04 | ||||||
83 | 504 | Phosphorus and Compounds | 1.82E-06 | 8.03E-06 | 1.31E-01 | 2.97E-03 | ||||||
84 | 7440-66-6 | Zinc and compounds | 8.32E-07 | 3.67E-06 | 5.99E-02 | 1.36E-03 | ||||||
85 | 7783-06-4 | Hydrogen sulfide | 4.49E-02 | 4.49E-02 | 3.23E+03 | 1.66E+01 | Engineering calculation (see supporting information) and effectiveness of oxidizing agent from F.H Rehmus, D.P. Manka & E.A. Upton, "Control of H2S Emission During Slag Quenching", Journal of the Air Pollution Control Association, 23:10, 1973. | |||||
86 | 646 | PCDD/Fs TEQ | 2.67E-14 | 1.18E-13 | 1.92E-09 | 4.35E-11 | EPA Drop Equation: AP-42 13.2.4, Remus, R., Aguado Monsonet, M.A., Roudier, S., Delgado Sancho, L. (2013). Best Available Techniques (BAT) Reference Document for Iron and Steel Production. European Commission Joint Research Committee Industrial Emissions Directive 2010/75/EU. | |||||
87 | 645 | PCBs TEQ | 2.67E-15 | 1.18E-14 | 1.92E-10 | 4.35E-12 | EPA Drop Equation: AP-42 13.2.4, Remus, R., Aguado Monsonet, M.A., Roudier, S., Delgado Sancho, L. (2013). Best Available Techniques (BAT) Reference Document for Iron and Steel Production. European Commission Joint Research Committee Industrial Emissions Directive 2010/75/EU. | |||||
88 | 239 | Fluorides | 1.73E-07 | 7.61E-07 | 1.24E-02 | 2.82E-04 | ||||||
89 | ||||||||||||
90 | ||||||||||||
91 | ||||||||||||
92 | ||||||||||||
93 | ||||||||||||
94 | AQ520 Info | |||||||||||
95 | Row | CAS col | STER Col | LTER Col | CE | SLEF col | STEF col | Unit | Ref Col | |||
96 | %SRC | EU-5 | 67 | 1 | 6 | 5 | 3 | 4 | lb/ton | 16 |
A | |
---|---|
1 | Attachment B - Emission Calculations |
2 | Table B-6: New Slag Handling Enclosure |
5 | (this table has been deleted from the EI Supporting Information documents) |
A | B | C | D | E | F | G | H | I | J | K | P | |
---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Attachment B - Emission Calculations | |||||||||||
2 | Table B-7: Gas Combustion Emissions @ Rod & Bar Mill Reheat Furnace | |||||||||||
3 | ||||||||||||
4 | Toxics Emission Unit ID: | EU-7 | ||||||||||
5 | Emission Point: | RFS2 | ||||||||||
6 | Description: | Stack natural gas combusion byproduct TAC emissions | ||||||||||
7 | ||||||||||||
8 | ||||||||||||
9 | Operating Parameters & Input Assumptions: | |||||||||||
10 | ||||||||||||
11 | Annual Gas Usage | 1,191,000 | MMBTU/yr (Permit Review Report Detail Sheets) | |||||||||
12 | Daily Gas Usage | 3263 | MMBTU/day | |||||||||
13 | HHV Natual Gas | 1020 | BTU/CF | |||||||||
14 | Annual Gas Usage | 1167.6 | MMCF/yr | |||||||||
15 | Daily Gas Usage | 3.2 | MMCF/day | |||||||||
16 | ||||||||||||
17 | ||||||||||||
18 | CAS or DEQ ID | TAC | EF (lb/MMSCF) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||||||
19 | 71-43-2 | Benzene | 0.0017 | 1.99E+00 | 5.44E-03 | Oregon DEQ 2020 ATEI Combustion EF Tool | ||||||
20 | 50-00-0 | Formaldehyde | 0.0036 | 4.20E+00 | 1.15E-02 | |||||||
21 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.0001 | 1.17E-01 | 3.20E-04 | |||||||
22 | 50-32-8 | Benzo[a]pyrene | 0.0000012 | 1.40E-03 | 3.84E-06 | |||||||
23 | 91-20-3 | Naphthalene | 0.0003 | 3.50E-01 | 9.60E-04 | |||||||
24 | 75-07-0 | Acetaldehyde | 0.0009 | 1.05E+00 | 2.88E-03 | |||||||
25 | 107-02-8 | Acrolein | 0.0008 | 9.34E-01 | 2.56E-03 | |||||||
26 | 7664-41-7 | Ammonia | 18 | 2.10E+04 | 5.76E+01 | |||||||
27 | 7440-38-2 | Arsenic and compounds | 0.0002 | 2.34E-01 | 6.40E-04 | |||||||
28 | 7440-39-3 | Barium and compounds | 0.0044 | 5.14E+00 | 1.41E-02 | |||||||
29 | 7440-41-7 | Beryllium and compounds | 0.000012 | 1.40E-02 | 3.84E-05 | |||||||
30 | 7440-43-9 | Cadmium and compounds | 0.0011 | 1.28E+00 | 3.52E-03 | |||||||
31 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.0014 | 1.63E+00 | 4.48E-03 | |||||||
32 | 7440-48-4 | Cobalt and compounds | 0.000084 | 9.81E-02 | 2.69E-04 | |||||||
33 | 7440-50-8 | Copper and compounds | 0.00085 | 9.93E-01 | 2.72E-03 | |||||||
34 | 100-41-4 | Ethyl benzene | 0.002 | 2.34E+00 | 6.40E-03 | |||||||
35 | 110-54-3 | Hexane | 0.0013 | 1.52E+00 | 4.16E-03 | |||||||
36 | 7439-92-1 | Lead and compounds | 0.0005 | 5.84E-01 | 1.60E-03 | |||||||
37 | 7439-96-5 | Manganese and compounds | 0.00038 | 4.44E-01 | 1.22E-03 | |||||||
38 | 7439-97-6 | Mercury and compounds | 0.00026 | 3.04E-01 | 8.32E-04 | |||||||
39 | 1313-27-5 | Molybdenum trioxide | 0.00165 | 1.93E+00 | 5.28E-03 | |||||||
40 | 365 | Nickel compounds, insoluble | 0.0021 | 2.45E+00 | 6.72E-03 | |||||||
41 | 7782-49-2 | Selenium and compounds | 0.000024 | 2.80E-02 | 7.68E-05 | |||||||
42 | 108-88-3 | Toluene | 0.0078 | 9.11E+00 | 2.50E-02 | |||||||
43 | 7440-62-2 | Vanadium (fume or dust) | 0.0023 | 2.69E+00 | 7.36E-03 | |||||||
44 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.0058 | 6.77E+00 | 1.86E-02 | |||||||
45 | 7440-66-6 | Zinc and compounds | 0.029 | 3.39E+01 | 9.28E-02 | |||||||
46 | ||||||||||||
47 | ||||||||||||
48 | ||||||||||||
49 | ||||||||||||
50 |
51 | ||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | AQ520 Info | |||||||||||
53 | Row | CAS col | STER Col | LTER Col | CE | SLEF col | STEF col | Unit | Ref Col | |||
54 | %SRC | EU-7 | 19 | 1 | 5 | 4 | 3 | 3 | lb/MMSCF | 16 |
A | B | C | D | E | F | G | H | I | J | K | P | |
---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Attachment B - Emission Calculations | |||||||||||
2 | Table B-8: Gas Combustion Emissions @ Thermal Treatment Oven | |||||||||||
3 | ||||||||||||
4 | Toxics Emission Unit ID: | EU-14 | ||||||||||
5 | Emission Point: | TTO | ||||||||||
6 | Description: | Stack natural gas combusion byproduct TAC emissions | ||||||||||
7 | ||||||||||||
8 | ||||||||||||
9 | Operating Parameters & Input Assumptions: | |||||||||||
10 | ||||||||||||
11 | Annual Gas Usage | 18,396 | MMBTU/yr (Permit Review Report Detail Sheets) | |||||||||
12 | Daily Gas Usage | 50 | MMBTU/day | |||||||||
13 | HHV Natual Gas | 1020 | BTU/CF | |||||||||
14 | Annual Gas Usage | 18.0 | MMCF/yr | |||||||||
15 | Daily Gas Usage | 0.049 | MMCF/day | |||||||||
16 | ||||||||||||
17 | ||||||||||||
18 | CAS or DEQ ID | TAC | EF (lb/MMSCF) | Emission Rate (lb/yr) | Emission Rate (lb/day) | |||||||
19 | 71-43-2 | Benzene | 0.008 | 1.44E-01 | 3.95E-04 | Oregon DEQ 2020 ATEI Combustion EF Tool | ||||||
20 | 50-00-0 | Formaldehyde | 0.017 | 3.07E-01 | 8.40E-04 | |||||||
21 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.0001 | 1.80E-03 | 4.94E-06 | |||||||
22 | 50-32-8 | Benzo[a]pyrene | 0.0000012 | 2.16E-05 | 5.93E-08 | |||||||
23 | 91-20-3 | Naphthalene | 0.0003 | 5.41E-03 | 1.48E-05 | |||||||
24 | 75-07-0 | Acetaldehyde | 0.0043 | 7.76E-02 | 2.12E-04 | |||||||
25 | 107-02-8 | Acrolein | 0.0027 | 4.87E-02 | 1.33E-04 | |||||||
26 | 7664-41-7 | Ammonia | 18 | 3.25E+02 | 8.89E-01 | |||||||
27 | 7440-38-2 | Arsenic and compounds | 0.0002 | 3.61E-03 | 9.88E-06 | |||||||
28 | 7440-39-3 | Barium and compounds | 0.0044 | 7.94E-02 | 2.17E-04 | |||||||
29 | 7440-41-7 | Beryllium and compounds | 0.000012 | 2.16E-04 | 5.93E-07 | |||||||
30 | 7440-43-9 | Cadmium and compounds | 0.0011 | 1.98E-02 | 5.44E-05 | |||||||
31 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.0014 | 2.52E-02 | 6.92E-05 | |||||||
32 | 7440-48-4 | Cobalt and compounds | 0.000084 | 1.51E-03 | 4.15E-06 | |||||||
33 | 7440-50-8 | Copper and compounds | 0.00085 | 1.53E-02 | 4.20E-05 | |||||||
34 | 100-41-4 | Ethyl benzene | 0.0095 | 1.71E-01 | 4.69E-04 | |||||||
35 | 110-54-3 | Hexane | 0.0063 | 1.14E-01 | 3.11E-04 | |||||||
36 | 7439-92-1 | Lead and compounds | 0.0005 | 9.02E-03 | 2.47E-05 | |||||||
37 | 7439-96-5 | Manganese and compounds | 0.00038 | 6.85E-03 | 1.88E-05 | |||||||
38 | 7439-97-6 | Mercury and compounds | 0.00026 | 4.69E-03 | 1.28E-05 | |||||||
39 | 1313-27-5 | Molybdenum trioxide | 0.00165 | 2.98E-02 | 8.15E-05 | |||||||
40 | 365 | Nickel compounds, insoluble | 0.0021 | 3.79E-02 | 1.04E-04 | |||||||
41 | 7782-49-2 | Selenium and compounds | 0.000024 | 4.33E-04 | 1.19E-06 | |||||||
42 | 108-88-3 | Toluene | 0.0366 | 6.60E-01 | 1.81E-03 | |||||||
43 | 7440-62-2 | Vanadium (fume or dust) | 0.0023 | 4.15E-02 | 1.14E-04 | |||||||
44 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.0272 | 4.91E-01 | 1.34E-03 | |||||||
45 | 7440-66-6 | Zinc and compounds | 0.029 | 5.23E-01 | 1.43E-03 | |||||||
46 | ||||||||||||
47 | ||||||||||||
48 | ||||||||||||
49 | ||||||||||||
50 |
51 | ||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | ||||||||||||
53 | ||||||||||||
54 | ||||||||||||
55 | ||||||||||||
56 | AQ520 Info | |||||||||||
57 | Row | CAS col | STER Col | LTER Col | CE | SLEF col | STEF col | Unit | Ref Col | |||
58 | %SRC | EU-14 | 19 | 1 | 5 | 4 | 3 | 3 | lb/MMSCF | 16 |
A | B | C | D | E | F | G | H | I | J | K | P | |
---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Attachment B - Emission Calculations | |||||||||||
2 | Table B-9: Emissions at Gasoline Dispensing Facility | |||||||||||
3 | ||||||||||||
4 | Toxics Emission Unit ID: | EU-15 | ||||||||||
5 | Emission Point: | GDF | ||||||||||
6 | Description: | Organic TAC emissions from filling a gasoline storage tank and dispensing fuel to vehicles. | ||||||||||
7 | ||||||||||||
8 | ||||||||||||
9 | ||||||||||||
10 | ||||||||||||
11 | ||||||||||||
12 | ||||||||||||
13 | ||||||||||||
14 | ||||||||||||
15 | ||||||||||||
16 | ||||||||||||
17 | ||||||||||||
18 | ||||||||||||
19 | ||||||||||||
20 | ||||||||||||
21 | Operating Parameters & Input Assumptions: | |||||||||||
22 | ||||||||||||
23 | Annual Gasoline Throughput | 10,000 | gal/yr (Permit Review Report, historical records) | |||||||||
24 | Daily Gasoline Vehicle Refilling Rate | 500 | gal/day (estimate) | |||||||||
25 | Tank Capacity | 6000 | gallons | |||||||||
26 | Maximum Tank Filling Rate, FRM | 6000 | gal/day | |||||||||
27 | Maximum Monthly Throughput | 6000 | gal/mo | |||||||||
28 | Tank Contents | Motor gasoline RVP 13 | (assumed worst case highest vapor pressure gasoline for AP-42 calculations) | |||||||||
29 | Vapor Molecular Weight, Mv | 62 | lb/lb-mole (AP-42 Table 7.1-2) | |||||||||
30 | Vapor Pressure Constant, A | 11.644 | dimensionless (AP-42 Table 7.1-2) | |||||||||
31 | Vapor Pressure Constant, B | 5043.6 | OR (AP-42 Table 7.1-2) | |||||||||
32 | Ideal Gas Constant, R | 80.273 | ((psia × gal)/(lbmol × oR)) (TCEQ) | |||||||||
33 | Worst Case Liquid Temperature, TLA | 554.67 | OR (TCEQ, 95F) | |||||||||
34 | VOC Emission Factor, Vehicle Refueling | 11 | lb/kgal (EPA AP-42, Table 5.2-7 ) | |||||||||
35 | VOC Emission Factor, Spillage | 0.7 | lb/kgal (EPA AP-42, Table 5.2-7 ) | |||||||||
36 | ||||||||||||
37 | ||||||||||||
38 | ||||||||||||
39 | Daily VOC Emissions | |||||||||||
40 | ||||||||||||
41 | Calculate true vapor pressure based on AP-42, Chapter 7, Eqn. 1-25. | |||||||||||
42 | ||||||||||||
43 | True Vapor Pressure, PVA | 12.82 | psia | |||||||||
44 | ||||||||||||
45 | Calculate daily VOC emission from filling tank based on TCEQ Equation 1 | |||||||||||
46 | ||||||||||||
47 | Maximum Daily Tank Emission Rate, LMAX | 107.1 | lb/day | |||||||||
48 | ||||||||||||
49 | Calculate daily VOC emissions from vehicle refueling based on AP-42, Table 5.2-7 | |||||||||||
50 |
51 | Maximum Daily Veh. Refuel Emission Rate, FMAX | 5.9 | lb/day | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | ||||||||||||
53 | Total Max. Daily VOC Emissions | 113.0 | lb/day | |||||||||
54 | ||||||||||||
55 | ||||||||||||
56 | Annual VOC Emissions | |||||||||||
57 | ||||||||||||
58 | Calculate annual VOC emissions from tank filling, breathing and emptying based on AP-42, Section 7.1.3 | |||||||||||
59 | See "Horizontal Tank" Tab | |||||||||||
60 | ||||||||||||
61 | Maximum Annual Tank Emission Rate | 3125.6 | lb/yr | |||||||||
62 | ||||||||||||
63 | Calculate VOC emissions from vehicle refueling based on AP-42, Table 5.2-7 | |||||||||||
64 | ||||||||||||
65 | Maximum Annual Veh. Refuel Emission Rate | 117.0 | lb/yr | |||||||||
66 | ||||||||||||
67 | Total Max. Annual VOC Emissions | 3242.6 | lb/yr | |||||||||
68 | ||||||||||||
69 | ||||||||||||
70 | Annual & Daily TAC Emissions | |||||||||||
71 | TAC Speciation Factors provided by DEQ | |||||||||||
72 | ||||||||||||
73 | ||||||||||||
74 | CAS or DEQ ID | TAC | TAC Speciation Factor (lb/lb-VOC) | Emissions (lb/yr) | Emissions (lb/day) | |||||||
75 | 526-73-8 | 1,2,3‐Trimethylbenzene | 0.00007058 | 0.23 | 0.0080 | AP-42, Section 7.1.3, AP-42, Table 5.2-7, TCEQ Guidance (Estimating Short Term Emission Rates from Fixed Roof Tanks, TCEQ - APDG 6250v3, revised 02/20, TAC Speciation for Gasoline (California Air Resources Board Speciation Profiles, highest weight fraction for each TAC from from Profile 691 ("Headspace vapors E10 summer gasoline fuel") and Profile 695 ("Headspace vapors E10 winter gasoline fuel") | ||||||
76 | 95‐63‐6 | 1,2,4‐Trimethylbenzene | 0.00039799 | 1.29 | 0.0450 | |||||||
77 | 108‐67‐8 | 1,3,5‐Trimethylbenzene | 0.00015565 | 0.50 | 0.0176 | |||||||
78 | 540‐84‐1 | 2,2,4‐Trimethylpentane | 0.01543471 | 50.05 | 1.7435 | |||||||
79 | 91‐57‐6 | 2‐Methyl naphthalene | 0.00000183 | 0.01 | 0.0002 | |||||||
80 | 71‐43‐2 | Benzene | 0.00549442 | 17.82 | 0.6207 | |||||||
81 | 110‐82‐7 | Cyclohexane | 0.00452826 | 14.68 | 0.5115 | |||||||
82 | 100‐41‐4 | Ethyl benzene | 0.00141423 | 4.59 | 0.1598 | |||||||
83 | 110‐54‐3 | Hexane | 0.02169322 | 70.34 | 2.4505 | |||||||
84 | 78‐79‐5 | Isoprene, except from vegetative emission sources | 0.00026761 | 0.87 | 0.0302 | |||||||
85 | 98‐82‐8 | Isopropylbenzene (cumene) | 0.00004279 | 0.14 | 0.0048 | |||||||
86 | 108‐38‐3 | m‐Xylene | 0.00267533 | 8.68 | 0.3022 | |||||||
87 | 91‐20‐3 | Naphthalene | 0.00000597 | 0.02 | 0.0007 | |||||||
88 | 95‐47‐6 | o‐Xylene | 0.00125055 | 4.06 | 0.1413 | |||||||
89 | 106‐42‐3 | p‐Xylene | 0.00116709 | 3.78 | 0.1318 | |||||||
90 | 108‐88‐3 | Toluene | 0.013467 | 43.67 | 1.5212 | |||||||
91 | ||||||||||||
92 | ||||||||||||
93 | ||||||||||||
94 | AQ520 Info | |||||||||||
95 | Row | CAS col | STER Col | LTER Col | CE | SLEF col | STEF col | Unit | Ref Col | |||
96 | %SRC | EU-15 | 75 | 1 | 5 | 4 | 3 | 3 | lb/lb-VOC | 16 |
A | B | C | D | E | F | G | H | I | J | K | L | M | N | O | P | Q | R | S | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Attachment B - Emission Calculations | ||||||||||||||||||
2 | Table B-10: Emissions from Unpaved Roads | ||||||||||||||||||
3 | |||||||||||||||||||
4 | Toxics Emission Unit ID: | EU-11 | |||||||||||||||||
5 | Emission Point: | SCRAP1 | |||||||||||||||||
6 | |||||||||||||||||||
7 | |||||||||||||||||||
8 | Description: | Dust from Vehicle Travel on Unpaved Roads | |||||||||||||||||
9 | |||||||||||||||||||
10 | |||||||||||||||||||
11 | |||||||||||||||||||
12 | |||||||||||||||||||
13 | |||||||||||||||||||
14 | |||||||||||||||||||
15 | |||||||||||||||||||
16 | |||||||||||||||||||
17 | |||||||||||||||||||
18 | |||||||||||||||||||
19 | Unpaved Roads - Constants and Eqn. 1a | ||||||||||||||||||
20 | |||||||||||||||||||
21 | |||||||||||||||||||
22 | |||||||||||||||||||
23 | |||||||||||||||||||
24 | E = Size-specific emission factor (lb/VMT) | ||||||||||||||||||
25 | |||||||||||||||||||
26 | Source | Constant | PM10 | Units | |||||||||||||||
27 | Table 13.2.2-2 | k, particle size factor | 1.5 | lb/VMT | |||||||||||||||
28 | Table 13.2.2-2 | a, empirical constant | 0.9 | none | |||||||||||||||
29 | Table 13.2.2-2 | b, empirical constant | 0.45 | none | |||||||||||||||
30 | Table 13.2.2-1 | s, silt content | 6 | % | |||||||||||||||
31 | Figure 13.2.2-1 | P, rainfall days > 0.01 in. | 150 | days | |||||||||||||||
32 | Review Report, pg. 29 | CE, control efficiency | 80% | % | |||||||||||||||
33 | |||||||||||||||||||
34 | |||||||||||||||||||
35 | Vehicle & Route Data | ||||||||||||||||||
36 | |||||||||||||||||||
37 | Vehicle/Truck Description | Route ID from Aerial | Mean Vehicle Wt., W (tons) | Trips/day | Trips/year | Segment Length, mi | VMT/day | VMT/yr | Daily E, lb/VMT | Annual E, lb/VMT | PM10 Emissions (lb/day) | PM10 Emissions (lb/yr) | |||||||
38 | Inbound Scrap Truck | Scrap1 | 50 | 20 | 4160 | 0.106 | 2.1 | 440.4 | 0.57 | 0.34 | 1.2 | 147.9 | |||||||
39 | |||||||||||||||||||
40 | Unpaved Roads EU-11 | ||||||||||||||||||
41 | Scrap1 | ||||||||||||||||||
42 | CAS or DEQ ID | TAC | Mass Fraction (mg/kg) | Annual EF (lb/VMT) | Daily EF (lb/VMT) | Emission Rate (lb/yr) | Emission Rate (lb/day) | ||||||||||||
43 | 7429-90-5 | Aluminum and Compounds | 14300 | 4.80E-03 | 8.15E-03 | 2.12E+00 | 1.73E-02 | AP-42 Section 13.2.2 empirical expressions, "Truck Sweep" TAC speciation as was used | |||||||||||
44 | 7440-36-0 | Antimony and Compounds | 17 | 5.71E-06 | 9.69E-06 | 2.51E-03 | 2.05E-05 | ||||||||||||
45 | 7440-38-2 | Arsenic and Compounds | 21.9 | 7.36E-06 | 1.25E-05 | 3.24E-03 | 2.64E-05 | ||||||||||||
46 | 7440-41-7 | Beryllium and Compounds | 0 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||||||
47 | 7440-43-9 | Cadmium and Compounds | 15 | 5.04E-06 | 8.55E-06 | 2.22E-03 | 1.81E-05 | ||||||||||||
48 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 24.5 | 8.23E-06 | 1.40E-05 | 3.62E-03 | 2.96E-05 | ||||||||||||
49 | 7440-48-4 | Cobalt and Compounds | 31.3 | 1.05E-05 | 1.78E-05 | 4.63E-03 | 3.78E-05 | ||||||||||||
50 | 7440-50-8 | Copper and Compounds | 977 | 3.28E-04 | 5.57E-04 | 1.45E-01 | 1.18E-03 |
51 | 7439-92-1 | Lead and Compounds | 829 | 2.78E-04 | 4.73E-04 | 1.23E-01 | 1.00E-03 | ||||||||||||
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52 | 7439-96-5 | Manganese and Compounds | 3970 | 1.33E-03 | 2.26E-03 | 5.87E-01 | 4.79E-03 | ||||||||||||
53 | 7439-97-6 | Mercury and Compounds | 1.03 | 3.46E-07 | 5.87E-07 | 1.52E-04 | 1.24E-06 | ||||||||||||
54 | 365 | Nickel compounds, insoluble | 220 | 7.39E-05 | 1.25E-04 | 3.25E-02 | 2.66E-04 | ||||||||||||
55 | 7782-49-2 | Selenium and Compounds | 0 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||||||
56 | 7440-22-4 | Silver and compounds | 2.93 | 9.84E-07 | 1.67E-06 | 4.33E-04 | 3.54E-06 | ||||||||||||
57 | 7440-28-0 | Thallium and compounds | 0 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||||||
58 | 504 | Phosphorus and Compounds | 0 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||||||
59 | 7440-62-2 | Vanadium (fume or dust) | 84.8 | 2.85E-05 | 4.84E-05 | 1.25E-02 | 1.02E-04 | ||||||||||||
60 | 7440-66-6 | Zinc and Compounds | 15300 | 5.14E-03 | 8.72E-03 | 2.26E+00 | 1.85E-02 | ||||||||||||
61 | 7440-39-3 | Barium and compounds | 560 | 1.88E-04 | 3.19E-04 | 8.28E-02 | 6.76E-04 | ||||||||||||
62 | |||||||||||||||||||
63 | |||||||||||||||||||
64 | |||||||||||||||||||
65 | |||||||||||||||||||
66 | AQ520 Info | ||||||||||||||||||
67 | Row | CAS col | STER Col | LTER Col | CE | SLEF col | STEF col | Unit | Ref Col | ||||||||||
68 | %SRC | EU-11 | 43 | 1 | 7 | 6 | 4 | 5 | lb/VMT | 16 |
A | B | C | D | E | F | G | H | I | J | K | L | M | N | O | P | Q | R | S | T | U | V | W | X | Y | Z | AA | AB | AC | AD | AE | AF | AG | AH | AI | AJ | AK | AL | AM | AN | AO | AP | AQ | AR | AS | AT | AU | AV | AW | AX | AY | AZ | BA | BC | BD | BH | |
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1 | Attachment B - Emission Calculations | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
2 | Table B-11: Emissions from Electric Arc Welding | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
3 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
4 | Toxics Emission Unit ID: | EU-17 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||
5 | Emission Point: | MaintFab | ||||||||||||||||||||||||||||||||||||||||||||||||||||||
6 | Description: | Metal TAC emissions from electric arc welding at maintenance shop | ||||||||||||||||||||||||||||||||||||||||||||||||||||||
7 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
8 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
9 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
10 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
11 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
12 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
13 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
14 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
15 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
16 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
17 | Electric Arc Welding EU-17 | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
18 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
19 | Welding Process/Rod Type | TACs Listed in AP-42 Table 12.19-2 | Other Trace TAC Metals or Inorganics per SDS ? | SDAPCD Method to Use | SDS Product Type/Name | |||||||||||||||||||||||||||||||||||||||||||||||||||
20 | FCAW E71T | Cr, Co, Mn, Ni | Y (Al, AlO, Sb, Ba, Cu, F) | Section 1.1.2 | Hobart Tubular Arc Welding Electrodes | |||||||||||||||||||||||||||||||||||||||||||||||||||
21 | SMAW E7018 | Cr, Co, Mn, Ni | Y (Al, F, Si) | Section 1.1.2 | Lincoln Electric Excalibur 7018 MR | |||||||||||||||||||||||||||||||||||||||||||||||||||
22 | SMAW E6010 | Cr, CrVI, Mn, Ni | N | Section 1.1.1 | Hobart 6010 Mild Steel Electrodes | |||||||||||||||||||||||||||||||||||||||||||||||||||
23 | SMAW E6011 | Cr, Co, Mn, Ni | N | Section 1.1.1 | Hobart 6011 Mild Steel Electrodes | |||||||||||||||||||||||||||||||||||||||||||||||||||
24 | SMAW C889 | NA | Y (Ni, F, Al) | Section 1.1.3 | Cronatron Certanium 889 | |||||||||||||||||||||||||||||||||||||||||||||||||||
25 | SMAW C707 | NA | Y (Cr, Ni,F, Al, Mn) | Section 1.1.3 | Cronatron Certanium 707 | |||||||||||||||||||||||||||||||||||||||||||||||||||
26 | GMAW E70S | Cr, Co, Mn, Ni | N | Section 1.1.1 | Radnor ER70S-6 | |||||||||||||||||||||||||||||||||||||||||||||||||||
27 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
28 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
29 | Fume Extractor overall DRE | 75% | ||||||||||||||||||||||||||||||||||||||||||||||||||||||
30 | Electrode Type | FCAW E71T | SMAW E7018 | SMAW E6010 | SMAW E6011 | SMAW Unk. (Certainium 889) | SMAW Unk. (Certainium 707) | GMAW E70S | Total EU-17 @ MaintFab | |||||||||||||||||||||||||||||||||||||||||||||||
31 | Annual Usage, lb/yr | 1000 | 150 | 50 | 50 | 10 | 30 | 150 | 1440 | |||||||||||||||||||||||||||||||||||||||||||||||
32 | Daily Usage, lb/day | 125 | 5 | 5 | 5 | 2 | 2 | 20 | 164 | |||||||||||||||||||||||||||||||||||||||||||||||
33 | CAS or DEQ ID | TAC | PM10 Emission Factor (lb/1000 lb rod) | Fume Correction Factor | Wt% per SDS | SDAPCD Calculated EF (lbs/1000 lbs) | AP-42 Table 12.19-2 EF (lbs/1000 lbs) | Emissions (lb/yr) | Emissions (lb/day) | PM10 Emission Factor (lb/1000 lb rod) | Fume Correction Factor | Wt% per SDS | SDAPCD Calculated EF (lbs/1000 lbs) | AP-42 Table 12.19-2 EF (lbs/1000 lbs) | Emissions (lb/yr) | Emissions (lb/day) | PM10 Emission Factor (lb/1000 lb rod) | Fume Correction Factor | Wt% per SDS | SDAPCD Calculated EF (lbs/1000 lbs) | AP-42 Table 12.19-2 EF (lbs/1000 lbs) | Emissions (lb/yr) | Emissions (lb/day) | PM10 Emission Factor (lb/1000 lb rod) | Fume Correction Factor | Wt% per SDS | SDAPCD Calculated EF (lbs/1000 lbs) | AP-42 Table 12.19-2 EF (lbs/1000 lbs) | Emissions (lb/yr) | Emissions (lb/day) | PM10 Emission Factor (lb/1000 lb rod) | Fume Correction Factor | Wt% per SDS | SDAPCD Calculated EF (lbs/1000 lbs) | AP-42 Table 12.19-2 EF (lbs/1000 lbs) | Emissions (lb/yr) | Emissions (lb/day) | PM10 Emission Factor (lb/1000 lb rod) | Fume Correction Factor | Wt% per SDS | SDAPCD Calculated EF (lbs/1000 lbs) | AP-42 Table 12.19-2 EF (lbs/1000 lbs) | Emissions (lb/yr) | Emissions (lb/day) | PM10 Emission Factor (lb/1000 lb rod) | Fume Correction Factor | Wt% per SDS | SDAPCD Calculated EF (lbs/1000 lbs) | AP-42 Table 12.19-2 EF (lbs/1000 lbs) | Emissions (lb/yr) | Emissions (lb/day) | Emissions (lb/yr) | Emissions (lb/day) | Composite EF (lb/1000 lbs) | Composite EF (lb/1000 lbs) | |
34 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.0002 | 5.00E-05 | 6.25E-06 | 0.0033 | 1.24E-04 | 4.13E-06 | 0.001 | 1.25E-05 | 1.25E-06 | 0.00275 | 3.44E-05 | 3.44E-06 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 15.1% | 0.87 | 6.50E-03 | 4.33E-04 | 0.00005 | 1.88E-06 | 2.50E-07 | 6.72E-03 | 4.49E-04 | 4.67E-03 | 2.74E-03 | San Diego Air Pollution Control District, Welding Operations, Revised July 11, 2022. The fume extractor will use a MERV 14 filter and based on this an overall capture and control efficiency of 75% is assumed. Control efficency incorporated in emission factor. | ||||||||||||||||||||||
35 | 7440-48-4 | Cobalt and Compounds | 0.001 | 2.50E-04 | 3.13E-05 | 0.001 | 3.75E-05 | 1.25E-06 | 0.00E+00 | 0.00E+00 | 0.001 | 1.25E-05 | 1.25E-06 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 0.001 | 3.75E-05 | 5.00E-06 | 3.38E-04 | 3.88E-05 | 2.34E-04 | 2.36E-04 | ||||||||||||||||||||||||
36 | 7439-96-5 | Manganese and Compounds | 0.662 | 1.66E-01 | 2.07E-02 | 1.03 | 3.86E-02 | 1.29E-03 | 0.991 | 1.24E-02 | 1.24E-03 | 0.998 | 1.25E-02 | 1.25E-03 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 3% | 0.17 | 1.29E-03 | 8.60E-05 | 0.318 | 1.19E-02 | 1.59E-03 | 2.42E-01 | 2.61E-02 | 1.68E-01 | 1.59E-01 | |||||||||||||||||||||||
37 | 365 | Nickel compounds, insoluble | 0.004 | 1.00E-03 | 1.25E-04 | 0.002 | 7.50E-05 | 2.50E-06 | 0.004 | 5.00E-05 | 5.00E-06 | 0.005 | 6.25E-05 | 6.25E-06 | 20 | 0.2865 | 45% | 2.58 | 6.45E-03 | 1.29E-03 | 20 | 0.2865 | 10% | 0.57 | 4.30E-03 | 2.87E-04 | 0.001 | 3.75E-05 | 5.00E-06 | 1.20E-02 | 1.72E-03 | 8.31E-03 | 1.05E-02 | |||||||||||||||||||||||
38 | 7429-90-5 | Aluminum and Compounds | 12.2 | 1 | 8% | 0.98 | 2.44E-01 | 3.05E-02 | 18.4 | 0.2865 | 0.55% | 0.03 | 1.09E-03 | 3.62E-05 | 25.6 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 38.4 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 3% | 0.17 | 4.30E-04 | 8.60E-05 | 20 | 0.2865 | 0.4% | 0.02 | 1.87E-04 | 1.25E-05 | 5.2 | 0.5464 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 2.46E-01 | 3.06E-02 | 1.71E-01 | 1.87E-01 | ||||||||
39 | 1309-64-4 | Antimony trioxide | 12.2 | 1 | 1% | 0.12 | 3.05E-02 | 3.81E-03 | 18.4 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 25.6 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 38.4 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 5.2 | 0.5464 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 3.05E-02 | 3.81E-03 | 2.12E-02 | 2.32E-02 | ||||||||
40 | 7440-39-3 | Barium and compounds | 12.2 | 1 | 11% | 1.39 | 3.48E-01 | 4.35E-02 | 18.4 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 25.6 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 38.4 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 5.2 | 0.5464 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 3.48E-01 | 4.35E-02 | 2.41E-01 | 2.65E-01 | ||||||||
41 | 239 | Fluorides | 12.2 | 1 | 10% | 1.16 | 2.91E-01 | 3.64E-02 | 18.4 | 0.2865 | 3.7% | 0.19 | 7.22E-03 | 2.41E-04 | 25.6 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 38.4 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 1.5% | 0.08 | 2.09E-04 | 4.18E-05 | 20 | 0.2865 | 1.5% | 0.08 | 6.28E-04 | 4.18E-05 | 5.2 | 0.5464 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 2.99E-01 | 3.67E-02 | 2.08E-01 | 2.24E-01 | ||||||||
42 | 7440-50-8 | Copper and compounds | 12.2 | 1 | 2% | 0.24 | 6.10E-02 | 7.63E-03 | 18.4 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 25.6 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 38.4 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 5.2 | 0.5464 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 6.10E-02 | 7.63E-03 | 4.24E-02 | 4.65E-02 | ||||||||
43 | 7631-86-9 | Silica, crystalline (respirable) | 12.2 | 1 | 2% | 0.244 | 6.10E-02 | 7.63E-03 | 18.4 | 0.2865 | 0.55% | 0.03 | 1.09E-03 | 3.62E-05 | 25.6 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 38.4 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 5.2 | 0.5464 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 6.21E-02 | 7.66E-03 | 4.31E-02 | 4.67E-02 | ||||||||
44 | 1313-27-5 | Molybdenum Trioxide | 12.2 | 1 | 3.0003% | 0.37 | 9.15E-02 | 1.14E-02 | 18.4 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 25.6 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 38.4 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 20 | 0.2865 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 5.2 | 0.5464 | 0% | 0.00 | 0.00E+00 | 0.00E+00 | 9.15E-02 | 1.14E-02 | 6.35E-02 | 6.97E-02 | ||||||||
45 | 1.31 | 0.16 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||
46 | 0.26 | 0.03 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||
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64 | AQ520 Info | |||||||||||||||||||||||||||||||||||||||||||||||||||||||
65 | Row | CAS col | STER Col | LTER Col | CE | SLEF col | STEF col | Unit | Ref Col | |||||||||||||||||||||||||||||||||||||||||||||||
66 | %SRC | EU-17 | 34 | 1 | 53 | 52 | 55 | 56 | lb/1000 lb wire | 60 |
A | B | C | D | E | F | G | H | I | J | K | P | |
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1 | Attachment B - Emission Calculations | |||||||||||
2 | Table B-12: Material Handling | |||||||||||
3 | ||||||||||||
4 | Toxics Emission Unit ID: | EU-18 | ||||||||||
5 | Emission Point(s): | ATDSiMn | TAC Emissions from truck dump of SiMn alloy to storage bunkers | |||||||||
6 | ATDFeMn | TAC Emissions from truck dump of FeMn alloy to storage bunkers | ||||||||||
7 | AULDSiMn | TAC Emissions from SiMn alloy unloading to feeder | ||||||||||
8 | AULDFeMn | TAC Emissions from FeMn alloy unloading to feeder | ||||||||||
9 | LIMEBCKT | TAC Emissions from lime addition to scrap charge bucket | ||||||||||
10 | ||||||||||||
11 | Description: | TAC Emissions from truck dump of alloys to storage bunkers, alloy unloading to feeder and lime addition to scrap charge bucket | ||||||||||
12 | ||||||||||||
13 | ||||||||||||
14 | ||||||||||||
15 | ||||||||||||
16 | ||||||||||||
17 | ||||||||||||
18 | ||||||||||||
19 | ||||||||||||
20 | ||||||||||||
21 | ||||||||||||
22 | ||||||||||||
23 | ||||||||||||
24 | ||||||||||||
25 | Operating Parameters & Input Assumptions: | |||||||||||
26 | ||||||||||||
27 | Emission Factors: | |||||||||||
28 | ||||||||||||
29 | Alloy Truck Dump to Bunker Pile - EPA Drop Equation: AP-42 13.2.4 | |||||||||||
30 | ||||||||||||
31 | Wind Speed, daily | 20.85 | mph (meterological data - McMinnville WS - 5-yr max. daily average based on 2014-2018 data) | |||||||||
32 | Wind Speed, annual | 6.66 | mph (meterological data - McMinnville WS - 5-yr average based on 2014-2018 data) | |||||||||
33 | k factor | 0.35 | unitless (for PM10) | |||||||||
34 | % moisture content | 0.25 | % (AP-42: Table 13.2.4-1, lowest in range) | |||||||||
35 | Control Factor | 89.6% | Alloys are dumped into a three sided enclosure with a roof and water sprays | See the "Water_Spray" tab for the derivation of this control efficiency | ||||||||
36 | PM emission factor, daily | 0.0137 | lb/ton | |||||||||
37 | PM emission factor, annual | 0.0031 | lb/ton | |||||||||
38 | ||||||||||||
39 | Alloy Unload to Feeder | 0.000016 | lb/ton (AP-42 Table 11.19.2-2 Truck Unloading to Feeder) | |||||||||
40 | ||||||||||||
41 | Lime to Charge Buckets | 0.61 | lb/ton (AP-42 Table 11.17-4 Product Loading Enclosed Truck*) | |||||||||
42 | *This factor is used instead of the open truck factor because the lime is transferred by putting the entire super sack into the charge bucket and the material transfer activity is essentially "enclosed". | |||||||||||
43 | ||||||||||||
44 | Material Handling Rates: | |||||||||||
45 | ||||||||||||
46 | Material | Max. Annual (tons) | Max Daily (tons) | |||||||||
47 | Silicon Manganese - SiMn | 9,956 | 31.5 | (one 63,000 pound per load truck dumps per day) | ||||||||
48 | Ferro Manganese - FeMn | 348 | 31.5 | (one 63,000 pound per load truck dumps per day) | ||||||||
49 | Dolomitic Lime | 18,095 | 78 | |||||||||
50 | Quicklime | 8,355 | 39 |
51 | ||||||||||||
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52 | ||||||||||||
53 | ||||||||||||
54 | Material Handling: EU-18 Emission Point ATDSiMn | |||||||||||
55 | ||||||||||||
56 | Alloy Truck Dump | CAS or DEQ ID | TAC | Wt.% | EF (lb/ton) (Annual) | EF (lb/ton) (Daily) | Emission Rate (lb/yr) | Emission Rate (lb/day) | ||||
57 | SiMn | 7439-96-5 | Manganese and Compounds | 75.5% | 2.34E-03 | 1.03E-02 | 23.33 | 0.33 | EPA Drop Equation: AP-42 13.2.4 , 63% PM10 control for 3-sided enclosure, 72% control for water spray. Control efficency incorporated in emission factor | |||
58 | 504 | Phosphorus and Compounds | 0.3% | 9.31E-06 | 4.10E-05 | 0.093 | 0.001 | |||||
59 | ||||||||||||
60 | ||||||||||||
61 | Material Handling: EU-18 Emission Point ATDFeMn | |||||||||||
62 | ||||||||||||
63 | FeMn | 7439-96-5 | Manganese and Compounds | 89% | 2.76E-03 | 1.22E-02 | 0.96 | 0.38 | EPA Drop Equation: AP-42 13.2.4 , 63% PM10 control for 3-sided enclosure, 72% control for water spray. Control efficency incorporated in emission factor | |||
64 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.5% | 1.55E-05 | 6.84E-05 | 0.005 | 0.0022 | |||||
65 | 365 | Nickel compounds, insoluble | 0.5% | 1.55E-05 | 6.84E-05 | 0.005 | 0.0022 | |||||
66 | ||||||||||||
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70 | ||||||||||||
71 | ||||||||||||
72 | ||||||||||||
73 | Material Handling: EU-18 Emission Point AULD_SiMn | |||||||||||
74 | ||||||||||||
75 | Alloy Unload to Feeder | CAS or DEQ ID | TAC | Wt.% | EF (lb/ton) (Annual) | EF (lb/ton) (Daily) | Emission Rate (lb/yr) | Emission Rate (lb/day) | ||||
76 | SiMn | 7439-96-5 | Manganese and Compounds | 75.5% | 1.21E-05 | 1.21E-05 | 0.12 | 0.00038 | AP-42 Table 11.19.2-2 Truck Unloading to Feeder | |||
77 | 504 | Phosphorus and Compounds | 0.3% | 4.80E-08 | 4.80E-08 | 0.00048 | 0.0000015 | |||||
78 | ||||||||||||
79 | Material Handling: EU-18 Emission Point AULD_FeMn | |||||||||||
80 | ||||||||||||
81 | FeMn | 7439-96-5 | Manganese and Compounds | 89% | 1.42E-05 | 1.42E-05 | 0.0049 | 0.000449 | AP-42 Table 11.19.2-2 Truck Unloading to Feeder | |||
82 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.5% | 8.00E-08 | 8.00E-08 | 0.000028 | 0.00000252 | |||||
83 | 365 | Nickel compounds, insoluble | 0.5% | 8.00E-08 | 8.00E-08 | 0.000028 | 0.00000252 | |||||
84 | ||||||||||||
85 | ||||||||||||
86 | ||||||||||||
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88 | ||||||||||||
89 | ||||||||||||
90 | Material Handling: EU-18 Emission Point LIMEBCKT | |||||||||||
91 | ||||||||||||
92 | Lime in Super Sack to Charge Bucket | CAS or DEQ ID | TAC | Wt.% | EF (lb/ton) (Annual) | EF (lb/ton) (Daily) | Emission Rate (lb/yr) | Emission Rate (lb/day) | NOTE: CAS number on SDS is 14808-60-7 | |||
93 | Dolomitic Lime and Quick Lime | 7631-86-9 | Crystalline Silica | 0.50005% | 3.05E-03 | 3.05E-03 | 80.68 | 0.35 | Changing to 7631-86-9 to treat as HAP | AP-42 Table 11.17-4 Product Loading Enclosed Truck | ||
94 | ||||||||||||
95 | ||||||||||||
96 | ||||||||||||
97 | ||||||||||||
98 | AQ520 Info | |||||||||||
99 | Row | CAS col | STER Col | LTER Col | CE | SLEF col | STEF col | Unit | Ref Col | |||
100 | %SRC | EU-18_ATDSiMn | 57 | 2 | 8 | 7 | 5 | 6 | lb/ton | 16 |
101 | %SRC | EU-18_ATDFeMn | 63 | 2 | 8 | 7 | 5 | 6 | lb/ton | 16 | ||
---|---|---|---|---|---|---|---|---|---|---|---|---|
102 | %SRC | EU-18_AULDSiMn | 76 | 2 | 8 | 7 | 5 | 6 | lb/ton | 16 | ||
103 | %SRC | EU-18_AULDFeMn | 81 | 2 | 8 | 7 | 5 | 6 | lb/ton | 16 | ||
104 | %SRC | EU-18_LIMEBCKT | 93 | 2 | 8 | 7 | 5 | 6 | lb/ton | 16 |
A | B | C | E | |
---|---|---|---|---|
1 | Attachment B - Emission Calculations | |||
2 | Table B-13: Exempt TEUs | |||
4 | Toxics Emission Unit ID: | EU-Chem | ||
5 | Emission Point(s): | CHEM | maintenance shop chemical usage | |
6 | Description: | maintenance shop chemical usage | ||
9 | Toxics Emission Unit ID: | EU-CT | ||
10 | Emission Point(s): | CT | ||
11 | Description: | Cooling towers |
A | B | C | D | E | F | G | |
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A | B | C | D | E | G | H | I | J | K | L | M | N | O | P | Q | R | S | T | U | V | W | X | Y | Z | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Cascade Steel Rolling Mills CAO ATEI | ||||||||||||||||||||||||
2 | Supporting Data Reduction - Slag Composition Analytical | ||||||||||||||||||||||||
3 | |||||||||||||||||||||||||
4 | |||||||||||||||||||||||||
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6 | CAS or DEQ ID | TAC | Analytical Result (mg/kg) | Mass Fraction | Notes | ||||||||||||||||||||
7 | 7429-90-5 | Aluminum and Compounds | 15000 | 1.50E-02 | |||||||||||||||||||||
8 | 7439-96-5 | Manganese and Compounds | 29000 | 2.90E-02 | |||||||||||||||||||||
9 | 7440-22-4 | Silver and Compounds | 0.38 | 3.80E-07 | |||||||||||||||||||||
10 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.11 | 1.10E-07 | Analytical Result was ND. Value shown is 1/2 MDL | ||||||||||||||||||||
11 | 7440-36-0 | Antimony and Compounds | 0.79 | 7.90E-07 | |||||||||||||||||||||
12 | 7440-38-2 | Arsenic and Compounds | 3.3 | 3.30E-06 | |||||||||||||||||||||
13 | 7440-41-7 | Beryllium and Compounds | 0.31 | 3.10E-07 | |||||||||||||||||||||
14 | 7440-43-9 | Cadmium and Compounds | 0.16 | 1.60E-07 | |||||||||||||||||||||
15 | 7440-50-8 | Copper and Compounds | 150 | 1.50E-04 | |||||||||||||||||||||
16 | 7439-92-1 | Lead and Compounds | 4.7 | 4.70E-06 | |||||||||||||||||||||
17 | 7439-97-6 | Mercury and compounds | 0.0065 | 6.50E-09 | Analytical Result was ND. Value shown is 1/2 MDL | ||||||||||||||||||||
18 | 365 | Nickel compounds, insoluble | 26 | 2.60E-05 | |||||||||||||||||||||
19 | 7782-49-2 | Selenium and Compounds | 0.35 | 3.50E-07 | |||||||||||||||||||||
20 | 7440-62-2 | Vanadium (fume or dust) | 650 | 6.50E-04 | |||||||||||||||||||||
21 | 7440-39-3 | Barium and Compounds | 420 | 4.20E-04 | |||||||||||||||||||||
22 | 504 | Phosphorus and Compounds | 350 | 3.50E-04 | |||||||||||||||||||||
23 | 1313-27-5 | Molybdenum trioxide | 16.5 | 1.65E-05 | Analytical Result was for total Molybdenum. Value shown as Molybdenum Trioxide | ||||||||||||||||||||
24 | 7440-66-6 | Zinc and compounds | 160 | 1.60E-04 | |||||||||||||||||||||
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26 | 239 | Fluorides | 33.2 | 3.32E-05 | |||||||||||||||||||||
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A | B | C | D | E | F | G | H | I | J | K | L | |
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1 | Cascade Steel Rolling Mills CAO ATEI | |||||||||||
2 | Supporting Data Reduction - Baghouse Dust Filter Analysis | |||||||||||
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15 | BH1/BH1A (using BH1A filter analysis data because BH1 had negative mass (filter weighed less than tare after drying)) | |||||||||||
16 | ||||||||||||
17 | CAS or DEQ ID | TAC | Analysis of Filter Sample1 (mg/kg) | Total Mass of Filter Sample2 (kg) | Total Mass of Metal Caught on Filter (mg) | Total Mass of PM Caught on Filter3 (mg) | Mass Fraction of Metal in PM | Ave. of 2013/2016 ST PM Emission Factor BH1A (lb/ton) | BH1A Filter Analysis Derived Emission Factor (lb/ton) | Ave. of 2013/2016 ST PM Emission Factor BH1 (lb/ton) | BH1 Filter Analysis Derived Emission Factor (lb/ton) | |
18 | 7429-90-5 | Aluminum and Compounds | 307 | 0.0047159 | 1.45 | 144.8 | 0.010 | 0.00925 | 9.24E-05 | 0.005225 | 5.22E-05 | |
19 | 7440-48-4 | Cobalt and Compounds | 0.0 | 0.0047159 | 0.00 | 144.8 | 0.000000 | 0.00925 | 0.00E+00 | 0.005225 | 0.00E+00 | Co was ND on three sample filters |
20 | 7440-50-8 | Copper and Compounds | 69 | 0.0047159 | 0.33 | 144.8 | 0.0023 | 0.00925 | 2.09E-05 | 0.005225 | 1.18E-05 | |
21 | 7440-66-6 | Zinc and Compounds | 6700 | 0.0047159 | 31.60 | 144.8 | 0.218 | 0.00925 | 2.02E-03 | 0.005225 | 1.14E-03 | |
22 | 7440-62-2 | Vanadium (fume or dust) | 3.5 | 0.0047159 | 0.02 | 144.8 | 0.00011 | 0.00925 | 1.04E-06 | 0.005225 | 5.90E-07 | |
23 | 7439-97-6 | Mercury and Compounds | 2.2 | 0.0047159 | 0.01 | 144.8 | 0.00007 | 0.00925 | 6.77E-07 | 0.005225 | 3.82E-07 | |
24 | 7440-38-2 | Arsenic and Compounds | 0.0 | 0.0047159 | 0.00 | 144.8 | 0.00000 | 0.00925 | 0.00E+00 | 0.005225 | 0.00E+00 | As was ND on three sample filters |
25 | 7440-43-9 | Cadmium and Compounds | 11.9 | 0.0047159 | 0.06 | 144.8 | 0.00039 | 0.00925 | 3.58E-06 | 0.005225 | 2.02E-06 | |
26 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 66.0 | 0.0047159 | 0.31 | 144.8 | 0.00215 | 0.00925 | 1.99E-05 | 0.005225 | 1.12E-05 | (As total Chromium) |
27 | 7439-92-1 | Lead and Compounds | 353.3 | 0.0047159 | 1.67 | 144.8 | 0.01151 | 0.00925 | 1.06E-04 | 0.005225 | 6.01E-05 | |
28 | 7439-96-5 | Manganese and Compounds | 630.0 | 0.0047159 | 2.97 | 144.8 | 0.02052 | 0.00925 | 1.90E-04 | 0.005225 | 1.07E-04 | |
29 | 365 | Nickel compounds, insoluble | 10.3 | 0.0047159 | 0.05 | 144.8 | 0.00033 | 0.00925 | 3.09E-06 | 0.005225 | 1.75E-06 | |
30 | 7440-36-0 | Antimony and Compounds | 3.3 | 0.0047159 | 0.02 | 144.8 | 0.00011 | 0.00925 | 9.94E-07 | 0.005225 | 5.61E-07 | |
31 | 504 | Phosphorus and Compounds | 33.3 | 0.0047159 | 0.16 | 144.8 | 0.00109 | 0.00925 | 1.00E-05 | 0.005225 | 5.67E-06 | |
32 | ||||||||||||
33 | ||||||||||||
34 | 1Average of three runs. Units in mg of metal per kg of total sample inclusive of collected material and filter media. 6/20/2013 Test America Report. See "Filter Data" tab. | |||||||||||
35 | 2Average of three runs. Page 59 of 2013 Horizon Report. Total weight of sample inclusive of collected materials and filter media after drying. | |||||||||||
36 | 3Average of three runs. Page 59 of 2013 Horizon Report with blank correction (pg 53) | |||||||||||
37 | ||||||||||||
38 | ||||||||||||
39 | ||||||||||||
40 | BH2 | |||||||||||
41 | ||||||||||||
42 | CAS or DEQ ID | TAC | Analysis of Filter Sample1 (mg/kg) | Total Mass of Filter Sample2 (kg) | Total Mass of Metal Caught on Filter (mg) | Total Mass of PM Caught on Filter3 (mg) | Mass Fraction of Metal in PM | 2013 ST PM Emission Factor (lb/ton) | BH2 Filter Analysis Derived Emission Factor (lb/ton) | |||
43 | 7429-90-5 | Aluminum and Compounds | 197 | 0.0045512 | 0.895 | 3.517 | 0.255 | 0.00028 | 7.13E-05 | |||
44 | 7440-48-4 | Cobalt and Compounds | 0.0 | 0.0045512 | 0.000 | 3.517 | 0.000000 | 0.00028 | 0.00E+00 | Co was ND in three sample filters | ||
45 | 7440-50-8 | Copper and Compounds | 0.0 | 0.0045512 | 0.000 | 3.517 | 0.0000 | 0.00028 | 0.00E+00 | Cu was ND in three sample filters | ||
46 | 7440-66-6 | Zinc and Compounds | 106 | 0.0045512 | 0.482 | 3.517 | 0.137 | 0.00028 | 3.84E-05 | |||
47 | 7440-62-2 | Vanadium (fume or dust) | 0.0 | 0.0045512 | 0.000 | 3.517 | 0.00000 | 0.00028 | 0.00E+00 | V was ND in three sample filters | ||
48 | 7439-97-6 | Mercury and Compounds | 0.1 | 0.0045512 | 0.001 | 3.517 | 0.00019 | 0.00028 | 5.40E-08 | |||
49 | 7440-38-2 | Arsenic and Compounds | 0.0 | 0.0045512 | 0.000 | 3.517 | 0.00000 | 0.00028 | 0.00E+00 | As was ND on three sample filters | ||
50 | 7440-43-9 | Cadmium and Compounds | 0.0 | 0.0045512 | 0.000 | 3.517 | 0.00000 | 0.00028 | 0.00E+00 | Cd was ND on three sample filters |
51 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 2.5 | 0.0045512 | 0.011 | 3.517 | 0.00319 | 0.00028 | 8.94E-07 | (As total Chromium) | ||
---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | 7439-92-1 | Lead and Compounds | 8.7 | 0.0045512 | 0.039 | 3.517 | 0.01122 | 0.00028 | 3.14E-06 | |||
53 | 7439-96-5 | Manganese and Compounds | 14.3 | 0.0045512 | 0.065 | 3.517 | 0.01855 | 0.00028 | 5.19E-06 | |||
54 | 365 | Nickel compounds, insoluble | 0.0 | 0.0045512 | 0.000 | 3.517 | 0.00000 | 0.00028 | 0.00E+00 | Ni was ND on three sample filters | ||
55 | ||||||||||||
56 | ||||||||||||
57 | 1Average of three runs. Units in mg of metal per kg of total sample inclusive of collected material and filter media. 6/20/2013 Test America Report. See "Filter Data" tab. | |||||||||||
58 | 2Average of three runs. Page 60 of 2013 Horizon Report. Total weight of sample inclusive of collected materials and filter media after drying (negative mass shown w/o blank correction). | |||||||||||
59 | 3Average of three runs. Page 60 of 2013 Horizon Report with blank correction (pg 53) |
J | K | L | M | N | O | P | Q | R | S | T | U | V | W | X | Y | Z | AA | AB | AC | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Cascade Steel Rolling Mills CAO ATEI | |||||||||||||||||||
2 | Supporting Data Reduction - Baghouse Dust Filter Raw Data | |||||||||||||||||||
3 | ||||||||||||||||||||
4 | 2013 Filter Sample Analysis (mg/kg Filter), italicized were ND at the value listed | Filter Weights and Total PM from 2013 Horizon Report | ||||||||||||||||||
5 | Aluminum | Cadmium | Chromium | Copper | Lead | Manganese | Nickel | Vanadium | Zinc | Antimony | Arsenic | Cobalt | Phophorus | Mercury | Tare (g) | Average post (g) | Net (g) | Blank Correction (g) | Total PM, incl blank (g) | |
6 | BH-1 | 230 | 2 | 3.4 | 2.7 | 11 | 21 | 4.9 | 2 | 180 | 4.9 | 4.9 | 2 | 49 | 0.24 | 4.5301 | 4.5105 | -0.0196 | -0.01125 | -0.00835 |
7 | 230 | 2 | 2.9 | 1 | 6.7 | 15 | 4.9 | 2 | 120 | 4.9 | 4.9 | 2 | 49 | 0.1 | 4.5671 | 4.5438 | -0.0233 | -0.01125 | -0.01205 | |
8 | 290 | 1.9 | 2.6 | 0.95 | 6.9 | 10 | 4.8 | 1.9 | 110 | 4.8 | 4.8 | 1.9 | 48 | 0.27 | 4.5578 | 4.5369 | -0.0209 | -0.01125 | -0.00965 | |
9 | Avg | 250 | 0 | 3.0 | 1.6 | 8.2 | 15 | 0 | 0 | 137 | 0 | 0 | 0 | 0 | 0.2 | 4.5517 | 4.5304 | -0.0213 | -0.0100 | |
10 | BH-1A | 330 | 8.1 | 50 | 50 | 260 | 500 | 8.3 | 3.1 | 5000 | 5 | 5 | 2 | 50 | 0.9 | 4.5895 | 4.6824 | 0.0929 | -0.01125 | 0.10415 |
11 | 250 | 6.6 | 28 | 28 | 190 | 290 | 2.5 | 1 | 3100 | 5 | 5 | 2 | 50 | 0.37 | 4.6215 | 4.6609 | 0.0394 | -0.01125 | 0.05065 | |
12 | 340 | 21 | 120 | 130 | 610 | 1100 | 20 | 6.3 | 12000 | 4.9 | 4.8 | 1.9 | 50 | 2.1 | 4.536 | 4.8044 | 0.2684 | -0.01125 | 0.27965 | |
13 | Avg | 307 | 11.9 | 66 | 69 | 353 | 630 | 10.3 | 3.5 | 6700 | 3.3 | 0 | 0 | 33 | 1.1 | 4.5823 | 4.7159 | 0.1336 | 0.1448 | |
14 | BH-2 | 210 | 2 | 2.7 | 2 | 5.9 | 15 | 5 | 2 | 78 | 5 | 5 | 2 | 50 | 0.089 | 4.5734 | 4.5675 | -0.0059 | -0.01125 | 0.00535 |
15 | 200 | 2 | 2.4 | 2 | 9.1 | 14 | 4.9 | 2 | 110 | 4.9 | 4.9 | 2 | 49 | 0.0485 | 4.5464 | 4.5368 | -0.0096 | -0.01125 | 0.00165 | |
16 | 180 | 2 | 2.3 | 2 | 11 | 14 | 4.9 | 2 | 130 | 4.9 | 4.9 | 2 | 49 | 0.086 | 4.5569 | 4.5492 | -0.0077 | -0.01125 | 0.00355 | |
17 | Avg | 197 | 0 | 2.5 | 0 | 8.7 | 14.3 | 0 | 0 | 106 | 0 | 0 | 0 | 0 | 0.075 | 4.5589 | 4.5512 | -0.0077 | 0.0035 | |
18 | ||||||||||||||||||||
19 | = ND | |||||||||||||||||||
20 | If all samples are ND, then average is zero per DEQ HRA draft guidance | |||||||||||||||||||
21 | If one or two samples are above detection limit, remaining are at 1/2 the detection limit | |||||||||||||||||||
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A | B | C | D | E | F | G | H | I | J | K | L | M | O | P | Q | R | S | T | U | V | W | X | Y | Z | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | CSRM Metals Data | Cascade Steel Rolling Mills CAO ATEI | |||||||||||||||||||||||
2 | Client: | Cascade Steel Rolling Mills | Supporting Data Reduction - Billet Cutting @ Casting Vent Source Test Data | ||||||||||||||||||||||
3 | Facility: | McMinnville Facility | |||||||||||||||||||||||
4 | Test Location: | Billet Cutting | |||||||||||||||||||||||
5 | Test Method: | Oregon Method 8 | |||||||||||||||||||||||
6 | |||||||||||||||||||||||||
7 | Source Condition | Acetone Wash Only no Blank Subtraction | |||||||||||||||||||||||
8 | Date | 8/7/19 | 8/7/19 | 8/7/19 | 8/8/19 | ||||||||||||||||||||
9 | Start Time | 10:07 | 12:27 | 15:05 | 8:55 | ||||||||||||||||||||
10 | End Time | 11:07 | 13:07 | 16:05 | 9:55 | ||||||||||||||||||||
11 | Run 1 | Run 3 | Run 5 | Run 7 | Average | ||||||||||||||||||||
12 | Stack Conditions | ||||||||||||||||||||||||
13 | Average Gas Temperature, °F | 114.0 | 117.0 | 136.0 | 140.0 | 126.8 | |||||||||||||||||||
14 | Flue Gas Moisture, percent by volume | 1.4% | 1.4% | 1.4% | 1.4% | 1.4% | |||||||||||||||||||
15 | Average Flue Pressure, in. Hg | 29.83 | 29.83 | 29.83 | 29.83 | 29.83 | |||||||||||||||||||
16 | Gas Sample Volume, dscf | 1,265.764 | 949.324 | 662.194 | 712.541 | 897.456 | |||||||||||||||||||
17 | Average Gas Velocity, ft/sec | 9.395 | 10.413 | 11.281 | 11.090 | 10.545 | |||||||||||||||||||
18 | Gas Volumetric Flow Rate, acfm | 84,587 | 93,757 | 101,574 | 99,849 | 94,942 | |||||||||||||||||||
19 | Gas Volumetric Flow Rate, dscfm | 76,464 | 84,323 | 88,456 | 86,403 | 83,912 | |||||||||||||||||||
20 | Gas Volumetric Flow Rate, scfm | 77,574 | 85,536 | 89,714 | 87,602 | 85,107 | |||||||||||||||||||
21 | Average %CO2 by volume, dry basis | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 | |||||||||||||||||||
22 | Average %O2 by volume, dry basis | 20.9 | 20.9 | 20.9 | 20.9 | 20.9 | |||||||||||||||||||
23 | Isokinetic Variance | 89.8 | 91.6 | 85.9 | 94.6 | 90.5 | |||||||||||||||||||
24 | Metal Production Rate, ton/hr | 89.0 | 121.0 | 120.0 | 140.0 | 117.5 | |||||||||||||||||||
25 | |||||||||||||||||||||||||
26 | |||||||||||||||||||||||||
27 | |||||||||||||||||||||||||
28 | |||||||||||||||||||||||||
29 | |||||||||||||||||||||||||
30 | |||||||||||||||||||||||||
31 | Aluminum (Al) Emissions | ||||||||||||||||||||||||
32 | ug of sample collected | 239.00 | 223.00 | ≤ | 60.00 | ≤ | 140.00 | ≤ | 165.50 | ||||||||||||||||
33 | ppb | 5.94 | 7.39 | ≤ | 2.85 | ≤ | 6.18 | ≤ | 5.59 | ||||||||||||||||
34 | ug/dscm | 6.67 | 8.30 | ≤ | 3.20 | ≤ | 6.94 | ≤ | 6.28 | ||||||||||||||||
35 | lb/hr | 1.91E-03 | 1.78E-03 | ≤ | 1.06E-03 | ≤ | 2.25E-03 | ≤ | 1.75E-03 | ||||||||||||||||
36 | lb/ton | 2.15E-05 | 1.47E-05 | ≤ | 8.83E-06 | ≤ | 1.60E-05 | ≤ | 1.53E-05 | ||||||||||||||||
37 | lb/ton ND Adjusted | 2.15E-05 | 1.47E-05 | 4.42E-06 | 8.02E-06 | 1.22E-05 | |||||||||||||||||||
38 | Antimony (Sb) Emissions | ||||||||||||||||||||||||
39 | ug of sample collected | ≤ | 3.00 | ≤ | 3.00 | ≤ | 3.00 | ≤ | 3.00 | ≤ | 3.00 | ||||||||||||||
40 | ppb | ≤ | 0.02 | ≤ | 0.02 | ≤ | 0.03 | ≤ | 0.03 | ≤ | 0.03 | ||||||||||||||
41 | ug/dscm | ≤ | 0.08 | ≤ | 0.11 | ≤ | 0.16 | ≤ | 0.15 | ≤ | 0.13 | ||||||||||||||
42 | lb/hr | ≤ | 2.40E-05 | ≤ | 2.40E-05 | ≤ | 5.30E-05 | ≤ | 4.80E-05 | ≤ | 3.73E-05 | ||||||||||||||
43 | lb/ton | ≤ | 2.70E-07 | ≤ | 1.98E-07 | ≤ | 4.42E-07 | ≤ | 3.43E-07 | ≤ | 3.13E-07 | ||||||||||||||
44 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||||||
45 | Arsenic (As) Emissions | ||||||||||||||||||||||||
46 | ug of sample collected | ≤ | 0.80 | 0.90 | ≤ | 0.80 | ≤ | 0.80 | ≤ | 0.83 | |||||||||||||||
47 | ppb | ≤ | 0.01 | 0.01 | ≤ | 0.01 | ≤ | 0.01 | ≤ | 0.01 | |||||||||||||||
48 | ug/dscm | ≤ | 0.02 | 0.03 | ≤ | 0.04 | ≤ | 0.04 | ≤ | 0.03 | |||||||||||||||
49 | lb/hr | ≤ | 6.00E-06 | 7.00E-06 | ≤ | 1.40E-05 | ≤ | 1.30E-05 | ≤ | 1.00E-05 | |||||||||||||||
50 | lb/ton | ≤ | 6.74E-08 | 5.79E-08 | ≤ | 1.17E-07 | ≤ | 9.29E-08 | ≤ | 8.37E-08 |
51 | lb/ton ND Adjusted | 3.37E-08 | 5.79E-08 | 5.83E-08 | 4.64E-08 | 4.91E-08 | |||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | Beryllium (Be) Emissions | ||||||||||||||||||||||||
53 | ug of sample collected | ≤ | 0.18 | ≤ | 0.18 | ≤ | 0.18 | ≤ | 0.18 | ≤ | 0.18 | ||||||||||||||
54 | ppb | ≤ | 0.01 | ≤ | 0.02 | ≤ | 0.03 | ≤ | 0.02 | ≤ | 0.02 | ||||||||||||||
55 | ug/dscm | ≤ | 0.01 | ≤ | 0.01 | ≤ | 0.01 | ≤ | 0.01 | ≤ | 0.01 | ||||||||||||||
56 | lb/hr | ≤ | 1.00E-06 | ≤ | 1.00E-06 | ≤ | 3.00E-06 | ≤ | 3.00E-06 | ≤ | 2.00E-06 | ||||||||||||||
57 | lb/ton | ≤ | 1.12E-08 | ≤ | 8.26E-09 | ≤ | 2.50E-08 | ≤ | 2.14E-08 | ≤ | 1.65E-08 | ||||||||||||||
58 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||||||
59 | Chromium (Cr) Emissions | ||||||||||||||||||||||||
60 | ug of sample collected | 29.40 | 53.10 | 5.00 | 78.50 | 41.50 | |||||||||||||||||||
61 | ppb | 0.38 | 0.91 | 0.12 | 1.80 | 0.80 | |||||||||||||||||||
62 | ug/dscm | 0.82 | 1.98 | 0.27 | 3.89 | 1.74 | |||||||||||||||||||
63 | lb/hr | 2.35E-04 | 4.24E-04 | 8.80E-05 | 1.26E-03 | 5.02E-04 | |||||||||||||||||||
64 | lb/ton | 2.64E-06 | 3.50E-06 | 7.33E-07 | 8.99E-06 | 3.97E-06 | |||||||||||||||||||
65 | lb/ton ND Adjusted | 2.64E-06 | 3.50E-06 | 7.33E-07 | 8.99E-06 | 3.97E-06 | |||||||||||||||||||
66 | Cobalt (Co) Emissions | ||||||||||||||||||||||||
67 | ug of sample collected | 3.10 | 5.27 | 0.56 | 4.51 | 3.36 | |||||||||||||||||||
68 | ppb | 0.04 | 0.08 | 0.01 | 0.09 | 0.05 | |||||||||||||||||||
69 | ug/dscm | 0.09 | 0.20 | 0.03 | 0.22 | 0.14 | |||||||||||||||||||
70 | lb/hr | 2.48E-05 | 4.21E-05 | 9.89E-06 | 1.00E-04 | 4.42E-05 | |||||||||||||||||||
71 | lb/ton | 2.78E-07 | 3.48E-07 | 8.24E-08 | 7.14E-07 | 3.56E-07 | |||||||||||||||||||
72 | lb/ton ND Adjusted | 2.78E-07 | 3.48E-07 | 8.24E-08 | 7.14E-07 | 3.56E-07 | |||||||||||||||||||
73 | Copper (Cu) Emissions | ||||||||||||||||||||||||
74 | ug of sample collected | 20.70 | 37.50 | 7.40 | 40.30 | 26.48 | |||||||||||||||||||
75 | ppb | 0.22 | 0.53 | 0.15 | 0.76 | 0.41 | |||||||||||||||||||
76 | ug/dscm | 0.58 | 1.39 | 0.39 | 2.00 | 1.09 | |||||||||||||||||||
77 | lb/hr | 2.00E-04 | 3.00E-04 | 1.00E-04 | 6.00E-04 | 3.00E-04 | |||||||||||||||||||
78 | lb/ton | 2.25E-06 | 2.48E-06 | 8.33E-07 | 4.29E-06 | 2.46E-06 | |||||||||||||||||||
79 | lb/ton ND Adjusted | 2.25E-06 | 2.48E-06 | 8.33E-07 | 4.29E-06 | 2.46E-06 | |||||||||||||||||||
80 | Lead (Pb) Emissions | ||||||||||||||||||||||||
81 | ug of sample collected | 2.59 | 2.23 | ≤ | 0.60 | 1.89 | ≤ | 1.83 | |||||||||||||||||
82 | ppb | 0.01 | 0.01 | ≤ | 0.00 | 0.01 | ≤ | 0.01 | |||||||||||||||||
83 | ug/dscm | 0.07 | 0.08 | ≤ | 0.03 | 0.09 | ≤ | 0.07 | |||||||||||||||||
84 | lb/hr | 2.07E-05 | 1.78E-05 | ≤ | 1.06E-05 | 3.03E-05 | ≤ | 1.99E-05 | |||||||||||||||||
85 | lb/ton | 2.33E-07 | 1.47E-07 | ≤ | 8.83E-08 | 2.17E-07 | ≤ | 1.71E-07 | |||||||||||||||||
86 | lb/ton ND Adjusted | 2.33E-07 | 1.47E-07 | 4.42E-08 | 2.17E-07 | 1.60E-07 | |||||||||||||||||||
87 | Manganese (Mn) Emissions | ||||||||||||||||||||||||
88 | ug of sample collected | 325.00 | 420.00 | 48.10 | 467.00 | 315.03 | |||||||||||||||||||
89 | ppb | 3.97 | 6.84 | 1.12 | 10.13 | 5.51 | |||||||||||||||||||
90 | ug/dscm | 9.07 | 15.62 | 2.57 | 23.15 | 12.60 | |||||||||||||||||||
91 | lb/hr | 2.60E-03 | 3.40E-03 | 8.00E-04 | 7.50E-03 | 3.58E-03 | |||||||||||||||||||
92 | lb/ton | 2.92E-05 | 2.81E-05 | 6.67E-06 | 5.36E-05 | 2.94E-05 | |||||||||||||||||||
93 | lb/ton ND Adjusted | 2.92E-05 | 2.81E-05 | 6.67E-06 | 5.36E-05 | 2.94E-05 | |||||||||||||||||||
94 | Nickel (Ni) Emissions | ||||||||||||||||||||||||
95 | ug of sample collected | 18.30 | 36.80 | 4.40 | 37.90 | 24.35 | |||||||||||||||||||
96 | ppb | 0.21 | 0.56 | 0.10 | 0.77 | 0.41 | |||||||||||||||||||
97 | ug/dscm | 0.51 | 1.37 | 0.23 | 1.88 | 1.00 | |||||||||||||||||||
98 | lb/hr | 1.00E-04 | 3.00E-04 | 1.00E-04 | 6.00E-04 | 2.75E-04 | |||||||||||||||||||
99 | lb/ton | 1.12E-06 | 2.48E-06 | 8.33E-07 | 4.29E-06 | 2.18E-06 | 1.12E-06 | 2.48E-06 | 8.33E-07 | 4.29E-06 | |||||||||||||||
100 | lb/ton ND Adjusted | 1.12E-06 | 2.48E-06 | 8.33E-07 | 4.29E-06 | 2.18E-06 |
101 | Phosphorus (P) Emissions | ||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
102 | ug of sample collected | ≤ | 90.00 | ≤ | 90.00 | ≤ | 90.00 | ≤ | 90.00 | ≤ | 90.00 | ||||||||||||||
103 | ppb | ≤ | 1.95 | ≤ | 2.60 | ≤ | 3.73 | ≤ | 3.46 | ≤ | 2.93 | ||||||||||||||
104 | ug/dscm | ≤ | 2.51 | ≤ | 3.35 | ≤ | 4.80 | ≤ | 4.46 | ≤ | 3.78 | ||||||||||||||
105 | lb/hr | ≤ | 7.00E-04 | ≤ | 7.00E-04 | ≤ | 1.60E-03 | ≤ | 1.40E-03 | ≤ | 1.10E-03 | ||||||||||||||
106 | lb/ton | ≤ | 7.87E-06 | ≤ | 5.79E-06 | ≤ | 1.33E-05 | ≤ | 1.00E-05 | ≤ | 9.25E-06 | ||||||||||||||
107 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||||||
108 | Selenium (Se) Emissions | ||||||||||||||||||||||||
109 | ug of sample collected | ≤ | 2.00 | ≤ | 2.00 | ≤ | 2.00 | ≤ | 2.00 | ≤ | 2.00 | ||||||||||||||
110 | ppb | ≤ | 0.02 | ≤ | 0.02 | ≤ | 0.03 | ≤ | 0.03 | ≤ | 0.03 | ||||||||||||||
111 | ug/dscm | ≤ | 0.06 | ≤ | 0.07 | ≤ | 0.11 | ≤ | 0.10 | ≤ | 0.09 | ||||||||||||||
112 | lb/hr | ≤ | 1.60E-05 | ≤ | 1.60E-05 | ≤ | 3.53E-05 | ≤ | 3.21E-05 | ≤ | 2.48E-05 | ||||||||||||||
113 | lb/ton | ≤ | 1.80E-07 | ≤ | 1.32E-07 | ≤ | 2.95E-07 | ≤ | 2.29E-07 | ≤ | 2.09E-07 | ||||||||||||||
114 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||||||
115 | Zinc (Zn) Emissions | ||||||||||||||||||||||||
116 | ug of sample collected | 46.00 | 37.00 | ≤ | 10.00 | 21.00 | ≤ | 28.50 | |||||||||||||||||
117 | ppb | 0.47 | 0.51 | ≤ | 0.20 | 0.38 | ≤ | 0.39 | |||||||||||||||||
118 | ug/dscm | 1.28 | 1.38 | ≤ | 0.53 | 1.04 | ≤ | 1.06 | |||||||||||||||||
119 | lb/hr | 4.00E-04 | 3.00E-04 | ≤ | 2.00E-04 | 3.00E-04 | ≤ | 3.00E-04 | |||||||||||||||||
120 | lb/ton | 4.49E-06 | 2.48E-06 | ≤ | 1.67E-06 | 2.14E-06 | ≤ | 2.70E-06 | |||||||||||||||||
121 | lb/ton ND Adjusted | 4.49E-06 | 2.48E-06 | 8.33E-07 | 2.14E-06 | 2.49E-06 | |||||||||||||||||||
122 | Cadmium (Cd) Emissions | ||||||||||||||||||||||||
123 | ug of sample collected | ≤ | 0.18 | ≤ | 0.18 | ≤ | 0.18 | ≤ | 0.18 | ≤ | 0.18 | ||||||||||||||
124 | ppb | ≤ | 0.001 | ≤ | 0.001 | ≤ | 0.002 | ≤ | 0.002 | ≤ | 0.002 | ||||||||||||||
125 | ug/dscm | ≤ | 0.01 | ≤ | 0.01 | ≤ | 0.01 | ≤ | 0.01 | ≤ | 0.01 | ||||||||||||||
126 | lb/hr | ≤ | 1.44E-06 | ≤ | 2.11E-06 | ≤ | 3.18E-06 | ≤ | 2.89E-06 | ≤ | 2.41E-06 | ||||||||||||||
127 | lb/ton | ≤ | 1.62E-08 | ≤ | 1.74E-08 | ≤ | 2.65E-08 | ≤ | 2.06E-08 | ≤ | 2.02E-08 | ||||||||||||||
128 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||||||
129 | Vanadium Emissions | ||||||||||||||||||||||||
130 | ug of sample collected | 10.90 | 12.20 | ≤ | 0.60 | 7.39 | ≤ | 7.77 | |||||||||||||||||
131 | ppb | 0.14 | 0.21 | ≤ | 0.02 | 0.17 | ≤ | 0.136 | |||||||||||||||||
132 | ug/dscm | 0.30 | 0.45 | ≤ | 0.03 | 0.37 | ≤ | 0.29 | |||||||||||||||||
133 | lb/hr | 1.00E-04 | 1.00E-04 | ≤ | 1.06E-05 | 1.00E-04 | ≤ | 7.77E-05 | |||||||||||||||||
134 | lb/ton | 1.12E-06 | 8.26E-07 | ≤ | 8.26E-07 | 8.26E-07 | ≤ | 9.01E-07 | 1.12E-06 | 8.26E-07 | 8.83E-08 | 7.14E-07 | |||||||||||||
135 | lb/ton ND Adjusted | 1.12E-06 | 8.26E-07 | 4.13E-07 | 8.26E-07 | 7.97E-07 |
A | B | C | D | E | F | G | H | I | J | K | L | M | N | O | P | Q | R | S | T | U | V | W | X | Y | Z | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | CSRM Metals Data | Cascade Steel Rolling Mills CAO ATEI | ||||||||||||||||||||||||
2 | Client: | Cascade Steel Rolling Mills | Supporting Data Reduction - Billet Cutting @ Casting Vent Source Test Data | |||||||||||||||||||||||
3 | Facility: | McMinnville Facility | Not Used. DEQ Requests "Filter Only no Blank Subtraction" be used in 12/13/22 letter. | |||||||||||||||||||||||
4 | Test Location: | Billet Cutting | ||||||||||||||||||||||||
5 | Test Method: | Oregon Method 8 | ||||||||||||||||||||||||
6 | ||||||||||||||||||||||||||
7 | Source Condition | Filter Only Reagent Blank Subtraction | ||||||||||||||||||||||||
8 | Date | 8/7/19 | 8/7/19 | 8/7/19 | 8/8/19 | |||||||||||||||||||||
9 | Start Time | 10:07 | 12:27 | 15:05 | 8:55 | |||||||||||||||||||||
10 | End Time | 11:07 | 13:07 | 16:05 | 9:55 | |||||||||||||||||||||
11 | Run 1 | Run 3 | Run 5 | Run 7 | Average | |||||||||||||||||||||
12 | Stack Conditions | |||||||||||||||||||||||||
13 | Average Gas Temperature, °F | 114.0 | 117.0 | 136.0 | 140.0 | 126.8 | ||||||||||||||||||||
14 | Flue Gas Moisture, percent by volume | 1.4% | 1.4% | 1.4% | 1.4% | 1.4% | ||||||||||||||||||||
15 | Average Flue Pressure, in. Hg | 29.83 | 29.83 | 29.83 | 29.83 | 29.83 | ||||||||||||||||||||
16 | Gas Sample Volume, dscf | 1,265.764 | 949.324 | 662.194 | 712.541 | 897.456 | ||||||||||||||||||||
17 | Average Gas Velocity, ft/sec | 9.395 | 10.413 | 11.281 | 11.090 | 10.545 | ||||||||||||||||||||
18 | Gas Volumetric Flow Rate, acfm | 84,587 | 93,757 | 101,574 | 99,849 | 94,942 | ||||||||||||||||||||
19 | Gas Volumetric Flow Rate, dscfm | 76,464 | 84,323 | 88,456 | 86,403 | 83,912 | ||||||||||||||||||||
20 | Gas Volumetric Flow Rate, scfm | 77,574 | 85,536 | 89,714 | 87,602 | 85,107 | ||||||||||||||||||||
21 | Average %CO2 by volume, dry basis | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 | ||||||||||||||||||||
22 | Average %O2 by volume, dry basis | 20.9 | 20.9 | 20.9 | 20.9 | 20.9 | ||||||||||||||||||||
23 | Isokinetic Variance | 89.8 | 91.6 | 85.9 | 94.6 | 90.5 | ||||||||||||||||||||
24 | Metal Production Rate, ton/hr | 89.0 | 121.0 | 120.0 | 140.0 | 117.5 | ||||||||||||||||||||
25 | ||||||||||||||||||||||||||
26 | ||||||||||||||||||||||||||
27 | ||||||||||||||||||||||||||
28 | ||||||||||||||||||||||||||
29 | ||||||||||||||||||||||||||
30 | ||||||||||||||||||||||||||
31 | Aluminum (Al) Emissions | |||||||||||||||||||||||||
32 | ug of sample collected | 210.00 | 200.00 | 320.00 | ≤ | 180.00 | ≤ | 227.50 | ||||||||||||||||||
33 | ppb | 5.22 | 6.63 | 15.20 | ≤ | 7.95 | ≤ | 8.75 | ||||||||||||||||||
34 | ug/dscm | 5.86 | 7.44 | 17.07 | ≤ | 8.92 | ≤ | 9.82 | ||||||||||||||||||
35 | lb/hr | 1.68E-03 | 1.60E-03 | 5.65E-03 | ≤ | 2.89E-03 | ≤ | 2.95E-03 | ||||||||||||||||||
36 | lb/ton | 1.89E-05 | 1.32E-05 | 4.71E-05 | ≤ | 2.06E-05 | ≤ | 2.49E-05 | ||||||||||||||||||
37 | lb/ton ND Adjusted | 1.89E-05 | 1.32E-05 | 4.71E-05 | 1.03E-05 | 2.24E-05 | ||||||||||||||||||||
38 | Antimony (Sb) Emissions | |||||||||||||||||||||||||
39 | ug of sample collected | 8.10 | 23.00 | 31.00 | 13.00 | 18.78 | ||||||||||||||||||||
40 | ppb | 0.05 | 0.17 | 0.33 | 0.13 | 0.17 | ||||||||||||||||||||
41 | ug/dscm | 0.23 | 0.86 | 1.65 | 0.64 | 0.85 | ||||||||||||||||||||
42 | lb/hr | 6.50E-05 | 1.84E-04 | 5.48E-04 | 2.09E-04 | 2.52E-04 | ||||||||||||||||||||
43 | lb/ton | 7.30E-07 | 1.52E-06 | 4.57E-06 | 1.49E-06 | 2.08E-06 | ||||||||||||||||||||
44 | lb/ton ND Adjusted | 7.30E-07 | 1.52E-06 | 4.57E-06 | 1.49E-06 | 2.08E-06 | ||||||||||||||||||||
45 | Arsenic (As) Emissions | |||||||||||||||||||||||||
46 | ug of sample collected | 52.00 | 84.00 | 70.00 | 33.00 | 59.75 | ||||||||||||||||||||
47 | ppb | 0.47 | 1.00 | 1.20 | 0.53 | 0.80 | ||||||||||||||||||||
48 | ug/dscm | 1.45 | 3.12 | 3.73 | 1.64 | 2.49 | ||||||||||||||||||||
49 | lb/hr | 4.16E-04 | 6.71E-04 | 1.24E-03 | 5.29E-04 | 7.13E-04 | ||||||||||||||||||||
50 | lb/ton | 4.67E-06 | 5.55E-06 | 1.03E-05 | 3.78E-06 | 6.08E-06 |
51 | lb/ton ND Adjusted | 4.67E-06 | 5.55E-06 | 1.03E-05 | 3.78E-06 | 6.08E-06 | ||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | Beryllium (Be) Emissions | |||||||||||||||||||||||||
53 | ug of sample collected | ≤ | 2.70 | ≤ | 2.70 | ≤ | 2.70 | ≤ | 2.70 | ≤ | 2.70 | |||||||||||||||
54 | ppb | ≤ | 0.20 | ≤ | 0.27 | ≤ | 0.38 | ≤ | 0.36 | ≤ | 0.30 | |||||||||||||||
55 | ug/dscm | ≤ | 0.08 | ≤ | 0.10 | ≤ | 0.14 | ≤ | 0.13 | ≤ | 0.11 | |||||||||||||||
56 | lb/hr | ≤ | 2.20E-05 | ≤ | 2.20E-05 | ≤ | 4.80E-05 | ≤ | 4.30E-05 | ≤ | 3.38E-05 | |||||||||||||||
57 | lb/ton | ≤ | 2.47E-07 | ≤ | 1.82E-07 | ≤ | 4.00E-07 | ≤ | 3.07E-07 | ≤ | 2.84E-07 | |||||||||||||||
58 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||||||||||||||
59 | Chromium (Cr) Emissions | |||||||||||||||||||||||||
60 | ug of sample collected | 51.60 | 117.60 | 107.60 | 56.60 | 83.35 | ||||||||||||||||||||
61 | ppb | 0.67 | 2.02 | 2.65 | 1.30 | 1.66 | ||||||||||||||||||||
62 | ug/dscm | 1.44 | 4.37 | 5.74 | 2.81 | 3.59 | ||||||||||||||||||||
63 | lb/hr | 4.12E-04 | 9.40E-04 | 1.90E-03 | 9.08E-04 | 1.04E-03 | ||||||||||||||||||||
64 | lb/ton | 4.63E-06 | 7.77E-06 | 1.58E-05 | 6.49E-06 | 8.68E-06 | ||||||||||||||||||||
65 | lb/ton ND Adjusted | 4.63E-06 | 7.77E-06 | 1.58E-05 | 6.49E-06 | 8.68E-06 | ||||||||||||||||||||
66 | Cobalt (Co) Emissions | |||||||||||||||||||||||||
67 | ug of sample collected | 23.00 | 39.00 | 29.00 | 13.00 | 26.00 | ||||||||||||||||||||
68 | ppb | 0.26 | 0.59 | 0.63 | 0.26 | 0.44 | ||||||||||||||||||||
69 | ug/dscm | 0.64 | 1.45 | 1.55 | 0.64 | 1.07 | ||||||||||||||||||||
70 | lb/hr | 1.84E-04 | 3.12E-04 | 5.12E-04 | 2.00E-04 | 3.02E-04 | ||||||||||||||||||||
71 | lb/ton | 2.07E-06 | 2.58E-06 | 4.27E-06 | 1.43E-06 | 2.58E-06 | ||||||||||||||||||||
72 | lb/ton ND Adjusted | 2.07E-06 | 2.58E-06 | 4.27E-06 | 1.43E-06 | 2.58E-06 | ||||||||||||||||||||
73 | Copper (Cu) Emissions | |||||||||||||||||||||||||
74 | ug of sample collected | 810.00 | 2,100.00 | 2,800.00 | 1,200.00 | 1,727.50 | ||||||||||||||||||||
75 | ppb | 8.55 | 29.55 | 56.47 | 22.49 | 29.26 | ||||||||||||||||||||
76 | ug/dscm | 22.60 | 78.12 | 149.32 | 59.47 | 77.38 | ||||||||||||||||||||
77 | lb/hr | 6.50E-03 | 1.68E-02 | 4.95E-02 | 1.92E-02 | 2.30E-02 | ||||||||||||||||||||
78 | lb/ton | 7.30E-05 | 1.39E-04 | 4.12E-04 | 1.37E-04 | 1.90E-04 | ||||||||||||||||||||
79 | lb/ton ND Adjusted | 7.30E-05 | 1.39E-04 | 4.12E-04 | 1.37E-04 | 1.90E-04 | ||||||||||||||||||||
80 | Lead (Pb) Emissions | |||||||||||||||||||||||||
81 | ug of sample collected | 8.10 | 10.00 | 91.00 | 110.00 | 54.78 | ||||||||||||||||||||
82 | ppb | 0.03 | 0.04 | 0.56 | 0.63 | 0.32 | ||||||||||||||||||||
83 | ug/dscm | 0.23 | 0.37 | 4.85 | 5.45 | 2.73 | ||||||||||||||||||||
84 | lb/hr | 6.47E-05 | 7.99E-05 | 1.61E-03 | 1.76E-03 | 8.79E-04 | ||||||||||||||||||||
85 | lb/ton | 7.27E-07 | 6.60E-07 | 1.34E-05 | 1.26E-05 | 6.85E-06 | ||||||||||||||||||||
86 | lb/ton ND Adjusted | 7.27E-07 | 6.60E-07 | 1.34E-05 | 1.26E-05 | 6.85E-06 | ||||||||||||||||||||
87 | Manganese (Mn) Emissions | |||||||||||||||||||||||||
88 | ug of sample collected | 570.00 | 1,100.00 | 1,400.00 | 590.00 | 915.00 | ||||||||||||||||||||
89 | ppb | 6.96 | 17.90 | 32.66 | 12.79 | 17.58 | ||||||||||||||||||||
90 | ug/dscm | 15.90 | 40.92 | 74.66 | 29.24 | 40.18 | ||||||||||||||||||||
91 | lb/hr | 4.60E-03 | 8.80E-03 | 2.47E-02 | 9.50E-03 | 1.19E-02 | ||||||||||||||||||||
92 | lb/ton | 5.17E-05 | 7.27E-05 | 2.06E-04 | 6.79E-05 | 9.95E-05 | ||||||||||||||||||||
93 | lb/ton ND Adjusted | 5.17E-05 | 7.27E-05 | 2.06E-04 | 6.79E-05 | 9.95E-05 | ||||||||||||||||||||
94 | Nickel (Ni) Emissions | |||||||||||||||||||||||||
95 | ug of sample collected | 179.32 | 399.32 | 329.32 | 169.32 | 269.32 | ||||||||||||||||||||
96 | ppb | 2.05 | 6.08 | 7.19 | 3.44 | 4.69 | ||||||||||||||||||||
97 | ug/dscm | 5.00 | 14.85 | 17.56 | 8.39 | 11.45 | ||||||||||||||||||||
98 | lb/hr | 1.40E-03 | 3.20E-03 | 5.82E-03 | 2.70E-03 | 3.28E-03 | ||||||||||||||||||||
99 | lb/ton | 1.57E-05 | 2.64E-05 | 4.85E-05 | 1.93E-05 | 2.75E-05 | ||||||||||||||||||||
100 | lb/ton ND Adjusted | 1.57E-05 | 2.64E-05 | 4.85E-05 | 1.93E-05 | 2.75E-05 |
101 | Phosphorus (P) Emissions | |||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
102 | ug of sample collected | 54.00 | 111.00 | 152.00 | 65.00 | 95.50 | ||||||||||||||||||||
103 | ppb | 1.17 | 3.20 | 6.29 | 2.50 | 3.29 | ||||||||||||||||||||
104 | ug/dscm | 1.51 | 4.13 | 8.11 | 3.22 | 4.24 | ||||||||||||||||||||
105 | lb/hr | 4.00E-04 | 9.00E-04 | 2.70E-03 | 1.00E-03 | 1.25E-03 | ||||||||||||||||||||
106 | lb/ton | 4.49E-06 | 7.44E-06 | 2.25E-05 | 7.14E-06 | 1.04E-05 | ||||||||||||||||||||
107 | lb/ton ND Adjusted | 4.49E-06 | 7.44E-06 | 2.25E-05 | 7.14E-06 | 1.04E-05 | ||||||||||||||||||||
108 | Selenium (Se) Emissions | |||||||||||||||||||||||||
109 | ug of sample collected | ≤ | 9.00 | ≤ | 9.00 | ≤ | 9.00 | ≤ | 9.00 | ≤ | 9.00 | |||||||||||||||
110 | ppb | ≤ | 0.08 | ≤ | 0.10 | ≤ | 0.15 | ≤ | 0.14 | ≤ | 0.12 | |||||||||||||||
111 | ug/dscm | ≤ | 0.25 | ≤ | 0.33 | ≤ | 0.48 | ≤ | 0.45 | ≤ | 0.38 | |||||||||||||||
112 | lb/hr | ≤ | 7.19E-05 | ≤ | 7.19E-05 | ≤ | 1.59E-04 | ≤ | 1.44E-04 | ≤ | 1.12E-04 | |||||||||||||||
113 | lb/ton | ≤ | 8.08E-07 | ≤ | 5.94E-07 | ≤ | 1.33E-06 | ≤ | 1.03E-06 | ≤ | 9.40E-07 | |||||||||||||||
114 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||||||||||||||
115 | Zinc (Zn) Emissions | |||||||||||||||||||||||||
116 | ug of sample collected | 160.00 | 84.00 | 550.00 | 210.00 | 251.00 | ||||||||||||||||||||
117 | ppb | 1.64 | 1.15 | 10.78 | 3.83 | 4.35 | ||||||||||||||||||||
118 | ug/dscm | 4.46 | 3.12 | 29.33 | 10.41 | 11.83 | ||||||||||||||||||||
119 | lb/hr | 1.30E-03 | 7.00E-04 | 9.70E-03 | 3.40E-03 | 3.78E-03 | ||||||||||||||||||||
120 | lb/ton | 1.46E-05 | 5.79E-06 | 8.08E-05 | 2.43E-05 | 3.14E-05 | ||||||||||||||||||||
121 | lb/ton ND Adjusted | 1.46E-05 | 5.79E-06 | 8.08E-05 | 2.43E-05 | 3.14E-05 | ||||||||||||||||||||
122 | Cadmium (Cd) Emissions | |||||||||||||||||||||||||
123 | ug of sample collected | ≤ | 0.90 | ≤ | 0.90 | ≤ | 0.90 | ≤ | 0.90 | ≤ | 0.90 | |||||||||||||||
124 | ppb | ≤ | 0.005 | ≤ | 0.007 | ≤ | 0.010 | ≤ | 0.010 | ≤ | 0.008 | |||||||||||||||
125 | ug/dscm | ≤ | 0.03 | ≤ | 0.03 | ≤ | 0.05 | ≤ | 0.04 | ≤ | 0.04 | |||||||||||||||
126 | lb/hr | ≤ | 7.19E-06 | ≤ | 1.06E-05 | ≤ | 1.59E-05 | ≤ | 1.44E-05 | ≤ | 1.20E-05 | |||||||||||||||
127 | lb/ton | ≤ | 8.08E-08 | ≤ | 8.74E-08 | ≤ | 1.33E-07 | ≤ | 1.03E-07 | ≤ | 1.01E-07 | |||||||||||||||
128 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||||||||||||||
129 | Vanadium Emissions | |||||||||||||||||||||||||
130 | ug of sample collected | 23.00 | 24.00 | 4.80 | 5.70 | 14.38 | ||||||||||||||||||||
131 | ppb | 0.30 | 0.42 | 0.12 | 0.13 | 0.245 | ||||||||||||||||||||
132 | ug/dscm | 0.64 | 0.89 | 0.26 | 0.28 | 0.52 | ||||||||||||||||||||
133 | lb/hr | 2.00E-04 | 3.00E-04 | 8.48E-05 | 1.00E-04 | 1.71E-04 | ||||||||||||||||||||
134 | lb/ton | 2.25E-06 | 2.48E-06 | 7.07E-07 | 7.14E-07 | 1.54E-06 | ||||||||||||||||||||
135 | lb/ton ND Adjusted | 2.25E-06 | 2.48E-06 | 7.07E-07 | 7.14E-07 | 1.54E-06 |
A | B | C | D | E | F | G | H | I | J | K | L | M | P | Q | R | S | T | U | V | W | X | Y | Z | AA | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | CSRM Metals Data | Cascade Steel Rolling Mills CAO ATEI | |||||||||||||||||||||||
2 | Client: | Cascade Steel Rolling Mills | Supporting Data Reduction - Billet Cutting @ Casting Vent Source Test Data | ||||||||||||||||||||||
3 | Facility: | McMinnville Facility | |||||||||||||||||||||||
4 | Test Location: | Billet Cutting | |||||||||||||||||||||||
5 | Test Method: | Oregon Method 8 | |||||||||||||||||||||||
6 | |||||||||||||||||||||||||
7 | Source Condition | Filter Only no Blank Subtraction | |||||||||||||||||||||||
8 | Date | 8/7/19 | 8/7/19 | 8/7/19 | 8/8/19 | ||||||||||||||||||||
9 | Start Time | 10:07 | 12:27 | 15:05 | 8:55 | ||||||||||||||||||||
10 | End Time | 11:07 | 13:07 | 16:05 | 9:55 | ||||||||||||||||||||
11 | Run 1 | Run 3 | Run 5 | Run 7 | Average | ||||||||||||||||||||
12 | Stack Conditions | ||||||||||||||||||||||||
13 | Average Gas Temperature, °F | 114.0 | 117.0 | 136.0 | 140.0 | 126.8 | |||||||||||||||||||
14 | Flue Gas Moisture, percent by volume | 1.4% | 1.4% | 1.4% | 1.4% | 1.4% | |||||||||||||||||||
15 | Average Flue Pressure, in. Hg | 29.83 | 29.83 | 29.83 | 29.83 | 29.83 | |||||||||||||||||||
16 | Gas Sample Volume, dscf | 1,265.764 | 949.324 | 662.194 | 712.541 | 897.456 | |||||||||||||||||||
17 | Average Gas Velocity, ft/sec | 9.395 | 10.413 | 11.281 | 11.090 | 10.545 | |||||||||||||||||||
18 | Gas Volumetric Flow Rate, acfm | 84,587 | 93,757 | 101,574 | 99,849 | 94,942 | |||||||||||||||||||
19 | Gas Volumetric Flow Rate, dscfm | 76,464 | 84,323 | 88,456 | 86,403 | 83,912 | |||||||||||||||||||
20 | Gas Volumetric Flow Rate, scfm | 77,574 | 85,536 | 89,714 | 87,602 | 85,107 | |||||||||||||||||||
21 | Average %CO2 by volume, dry basis | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 | |||||||||||||||||||
22 | Average %O2 by volume, dry basis | 20.9 | 20.9 | 20.9 | 20.9 | 20.9 | |||||||||||||||||||
23 | Isokinetic Variance | 89.8 | 91.6 | 85.9 | 94.6 | 90.5 | |||||||||||||||||||
24 | Metal Production Rate, ton/hr | 89.0 | 121.0 | 120.0 | 140.0 | 117.5 | |||||||||||||||||||
25 | |||||||||||||||||||||||||
26 | |||||||||||||||||||||||||
27 | |||||||||||||||||||||||||
28 | |||||||||||||||||||||||||
29 | |||||||||||||||||||||||||
30 | |||||||||||||||||||||||||
31 | Aluminum (Al) Emissions | ||||||||||||||||||||||||
32 | ug of sample collected | 230.00 | 220.00 | 340.00 | ≤ | 180.00 | ≤ | 242.50 | |||||||||||||||||
33 | ppb | 5.72 | 7.29 | 16.15 | ≤ | 7.95 | ≤ | 9.28 | |||||||||||||||||
34 | ug/dscm | 6.42 | 8.18 | 18.13 | ≤ | 8.92 | ≤ | 10.41 | |||||||||||||||||
35 | lb/hr | 1.84E-03 | 1.76E-03 | 6.01E-03 | ≤ | 2.89E-03 | ≤ | 3.12E-03 | |||||||||||||||||
36 | lb/ton | 2.07E-05 | 1.45E-05 | 5.01E-05 | ≤ | 2.06E-05 | ≤ | 2.65E-05 | |||||||||||||||||
37 | lb/ton ND Adjusted | 2.07E-05 | 1.45E-05 | 5.01E-05 | 1.03E-05 | 2.39E-05 | |||||||||||||||||||
38 | Antimony (Sb) Emissions | ||||||||||||||||||||||||
39 | ug of sample collected | 8.10 | 23.00 | 31.00 | 13.00 | 18.78 | |||||||||||||||||||
40 | ppb | 0.05 | 0.17 | 0.33 | 0.13 | 0.17 | |||||||||||||||||||
41 | ug/dscm | 0.23 | 0.86 | 1.65 | 0.64 | 0.85 | |||||||||||||||||||
42 | lb/hr | 6.50E-05 | 1.84E-04 | 5.48E-04 | 2.09E-04 | 2.52E-04 | |||||||||||||||||||
43 | lb/ton | 7.30E-07 | 1.52E-06 | 4.57E-06 | 1.49E-06 | 2.08E-06 | |||||||||||||||||||
44 | lb/ton ND Adjusted | 7.30E-07 | 1.52E-06 | 4.57E-06 | 1.49E-06 | 2.08E-06 | |||||||||||||||||||
45 | Arsenic (As) Emissions | ||||||||||||||||||||||||
46 | ug of sample collected | 52.00 | 84.00 | 70.00 | 33.00 | 59.75 | |||||||||||||||||||
47 | ppb | 0.47 | 1.00 | 1.20 | 0.53 | 0.80 | |||||||||||||||||||
48 | ug/dscm | 1.45 | 3.12 | 3.73 | 1.64 | 2.49 | |||||||||||||||||||
49 | lb/hr | 4.16E-04 | 6.71E-04 | 1.24E-03 | 5.29E-04 | 7.13E-04 | |||||||||||||||||||
50 | lb/ton | 4.67E-06 | 5.55E-06 | 1.03E-05 | 3.78E-06 | 6.08E-06 |
51 | lb/ton ND Adjusted | 4.67E-06 | 5.55E-06 | 1.03E-05 | 3.78E-06 | 6.08E-06 | |||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | Beryllium (Be) Emissions | ||||||||||||||||||||||||
53 | ug of sample collected | ≤ | 2.70 | ≤ | 2.70 | ≤ | 2.70 | ≤ | 2.70 | ≤ | 2.70 | ||||||||||||||
54 | ppb | ≤ | 0.20 | ≤ | 0.27 | ≤ | 0.38 | ≤ | 0.36 | ≤ | 0.30 | ||||||||||||||
55 | ug/dscm | ≤ | 0.08 | ≤ | 0.10 | ≤ | 0.14 | ≤ | 0.13 | ≤ | 0.11 | ||||||||||||||
56 | lb/hr | ≤ | 2.20E-05 | ≤ | 2.20E-05 | ≤ | 4.80E-05 | ≤ | 4.30E-05 | ≤ | 3.38E-05 | ||||||||||||||
57 | lb/ton | ≤ | 2.47E-07 | ≤ | 1.82E-07 | ≤ | 4.00E-07 | ≤ | 3.07E-07 | ≤ | 2.84E-07 | ||||||||||||||
58 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||||||
59 | Chromium (Cr) Emissions | ||||||||||||||||||||||||
60 | ug of sample collected | 54.00 | 120.00 | 110.00 | 59.00 | 85.75 | |||||||||||||||||||
61 | ppb | 0.70 | 2.06 | 2.71 | 1.35 | 1.71 | |||||||||||||||||||
62 | ug/dscm | 1.51 | 4.46 | 5.87 | 2.92 | 3.69 | |||||||||||||||||||
63 | lb/hr | 4.32E-04 | 9.59E-04 | 1.94E-03 | 9.46E-04 | 1.07E-03 | |||||||||||||||||||
64 | lb/ton | 4.85E-06 | 7.93E-06 | 1.62E-05 | 6.76E-06 | 8.93E-06 | |||||||||||||||||||
65 | lb/ton ND Adjusted | 4.85E-06 | 7.93E-06 | 1.62E-05 | 6.76E-06 | 8.93E-06 | |||||||||||||||||||
66 | Cobalt (Co) Emissions | ||||||||||||||||||||||||
67 | ug of sample collected | 23.00 | 39.00 | 29.00 | 13.00 | 26.00 | |||||||||||||||||||
68 | ppb | 0.26 | 0.59 | 0.63 | 0.26 | 0.44 | |||||||||||||||||||
69 | ug/dscm | 0.64 | 1.45 | 1.55 | 0.64 | 1.07 | |||||||||||||||||||
70 | lb/hr | 1.84E-04 | 3.12E-04 | 5.12E-04 | 2.00E-04 | 3.02E-04 | |||||||||||||||||||
71 | lb/ton | 2.07E-06 | 2.58E-06 | 4.27E-06 | 1.43E-06 | 2.58E-06 | |||||||||||||||||||
72 | lb/ton ND Adjusted | 2.07E-06 | 2.58E-06 | 4.27E-06 | 1.43E-06 | 2.58E-06 | |||||||||||||||||||
73 | Copper (Cu) Emissions | ||||||||||||||||||||||||
74 | ug of sample collected | 810.00 | 2,100.00 | 2,800.00 | 1,200.00 | 1,727.50 | |||||||||||||||||||
75 | ppb | 8.55 | 29.55 | 56.47 | 22.49 | 29.26 | |||||||||||||||||||
76 | ug/dscm | 22.60 | 78.12 | 149.32 | 59.47 | 77.38 | |||||||||||||||||||
77 | lb/hr | 6.50E-03 | 1.68E-02 | 4.95E-02 | 1.92E-02 | 2.30E-02 | |||||||||||||||||||
78 | lb/ton | 7.30E-05 | 1.39E-04 | 4.12E-04 | 1.37E-04 | 1.90E-04 | |||||||||||||||||||
79 | lb/ton ND Adjusted | 7.30E-05 | 1.39E-04 | 4.12E-04 | 1.37E-04 | 1.90E-04 | |||||||||||||||||||
80 | Lead (Pb) Emissions | ||||||||||||||||||||||||
81 | ug of sample collected | 8.10 | 10.00 | 91.00 | 110.00 | 54.78 | |||||||||||||||||||
82 | ppb | 0.03 | 0.04 | 0.56 | 0.63 | 0.32 | |||||||||||||||||||
83 | ug/dscm | 0.23 | 0.37 | 4.85 | 5.45 | 2.73 | |||||||||||||||||||
84 | lb/hr | 6.47E-05 | 7.99E-05 | 1.61E-03 | 1.76E-03 | 8.79E-04 | |||||||||||||||||||
85 | lb/ton | 7.27E-07 | 6.60E-07 | 1.34E-05 | 1.26E-05 | 6.85E-06 | |||||||||||||||||||
86 | lb/ton ND Adjusted | 7.27E-07 | 6.60E-07 | 1.34E-05 | 1.26E-05 | 6.85E-06 | |||||||||||||||||||
87 | Manganese (Mn) Emissions | ||||||||||||||||||||||||
88 | ug of sample collected | 570.00 | 1,100.00 | 1,400.00 | 590.00 | 915.00 | |||||||||||||||||||
89 | ppb | 6.96 | 17.90 | 32.66 | 12.79 | 17.58 | |||||||||||||||||||
90 | ug/dscm | 15.90 | 40.92 | 74.66 | 29.24 | 40.18 | |||||||||||||||||||
91 | lb/hr | 4.60E-03 | 8.80E-03 | 2.47E-02 | 9.50E-03 | 1.19E-02 | |||||||||||||||||||
92 | lb/ton | 5.17E-05 | 7.27E-05 | 2.06E-04 | 6.79E-05 | 9.95E-05 | |||||||||||||||||||
93 | lb/ton ND Adjusted | 5.17E-05 | 7.27E-05 | 2.06E-04 | 6.79E-05 | 9.95E-05 | |||||||||||||||||||
94 | Nickel (Ni) Emissions | ||||||||||||||||||||||||
95 | ug of sample collected | 180.00 | 400.00 | 330.00 | 170.00 | 270.00 | |||||||||||||||||||
96 | ppb | 2.06 | 6.09 | 7.21 | 3.45 | 4.70 | |||||||||||||||||||
97 | ug/dscm | 5.02 | 14.88 | 17.60 | 8.43 | 11.48 | |||||||||||||||||||
98 | lb/hr | 1.40E-03 | 3.20E-03 | 5.83E-03 | 2.70E-03 | 3.28E-03 | |||||||||||||||||||
99 | lb/ton | 1.57E-05 | 2.64E-05 | 4.86E-05 | 1.93E-05 | 2.75E-05 | |||||||||||||||||||
100 | lb/ton ND Adjusted | 1.57E-05 | 2.64E-05 | 4.86E-05 | 1.93E-05 | 2.75E-05 |
101 | Phosphorus (P) Emissions | ||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
102 | ug of sample collected | 54.00 | 111.00 | 152.00 | 65.00 | 95.50 | |||||||||||||||||||
103 | ppb | 1.17 | 3.20 | 6.29 | 2.50 | 3.29 | |||||||||||||||||||
104 | ug/dscm | 1.51 | 4.13 | 8.11 | 3.22 | 4.24 | |||||||||||||||||||
105 | lb/hr | 4.00E-04 | 9.00E-04 | 2.70E-03 | 1.00E-03 | 1.25E-03 | |||||||||||||||||||
106 | lb/ton | 4.49E-06 | 7.44E-06 | 2.25E-05 | 7.14E-06 | 1.04E-05 | |||||||||||||||||||
107 | lb/ton ND Adjusted | 4.49E-06 | 7.44E-06 | 2.25E-05 | 7.14E-06 | 1.04E-05 | |||||||||||||||||||
108 | Selenium (Se) Emissions | ||||||||||||||||||||||||
109 | ug of sample collected | ≤ | 9.00 | ≤ | 9.00 | ≤ | 9.00 | ≤ | 9.00 | ≤ | 9.00 | ||||||||||||||
110 | ppb | ≤ | 0.08 | ≤ | 0.10 | ≤ | 0.15 | ≤ | 0.14 | ≤ | 0.12 | ||||||||||||||
111 | ug/dscm | ≤ | 0.25 | ≤ | 0.33 | ≤ | 0.48 | ≤ | 0.45 | ≤ | 0.38 | ||||||||||||||
112 | lb/hr | ≤ | 7.19E-05 | ≤ | 7.19E-05 | ≤ | 1.59E-04 | ≤ | 1.44E-04 | ≤ | 1.12E-04 | ||||||||||||||
113 | lb/ton | ≤ | 8.08E-07 | ≤ | 5.94E-07 | ≤ | 1.33E-06 | ≤ | 1.03E-06 | ≤ | 9.40E-07 | ||||||||||||||
114 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||||||
115 | Zinc (Zn) Emissions | ||||||||||||||||||||||||
116 | ug of sample collected | 160.00 | 84.00 | 550.00 | 210.00 | 251.00 | |||||||||||||||||||
117 | ppb | 1.64 | 1.15 | 10.78 | 3.83 | 4.35 | |||||||||||||||||||
118 | ug/dscm | 4.46 | 3.12 | 29.33 | 10.41 | 11.83 | |||||||||||||||||||
119 | lb/hr | 1.30E-03 | 7.00E-04 | 9.70E-03 | 3.40E-03 | 3.78E-03 | |||||||||||||||||||
120 | lb/ton | 1.46E-05 | 5.79E-06 | 8.08E-05 | 2.43E-05 | 3.14E-05 | |||||||||||||||||||
121 | lb/ton ND Adjusted | 1.46E-05 | 5.79E-06 | 8.08E-05 | 2.43E-05 | 3.14E-05 | |||||||||||||||||||
122 | Cadmium (Cd) Emissions | ||||||||||||||||||||||||
123 | ug of sample collected | ≤ | 0.90 | ≤ | 0.90 | ≤ | 0.90 | ≤ | 0.90 | ≤ | 0.90 | ||||||||||||||
124 | ppb | ≤ | 0.005 | ≤ | 0.007 | ≤ | 0.010 | ≤ | 0.010 | ≤ | 0.008 | ||||||||||||||
125 | ug/dscm | ≤ | 0.03 | ≤ | 0.03 | ≤ | 0.05 | ≤ | 0.04 | ≤ | 0.04 | ||||||||||||||
126 | lb/hr | ≤ | 7.19E-06 | ≤ | 1.06E-05 | ≤ | 1.59E-05 | ≤ | 1.44E-05 | ≤ | 1.20E-05 | ||||||||||||||
127 | lb/ton | ≤ | 8.08E-08 | ≤ | 8.74E-08 | ≤ | 1.33E-07 | ≤ | 1.03E-07 | ≤ | 1.01E-07 | ||||||||||||||
128 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||||||||||||
129 | Vanadium Emissions | ||||||||||||||||||||||||
130 | ug of sample collected | 23.00 | 24.00 | 4.80 | 5.70 | 14.38 | |||||||||||||||||||
131 | ppb | 0.30 | 0.42 | 0.12 | 0.13 | 0.245 | |||||||||||||||||||
132 | ug/dscm | 0.64 | 0.89 | 0.26 | 0.28 | 0.52 | |||||||||||||||||||
133 | lb/hr | 2.00E-04 | 3.00E-04 | 8.48E-05 | 1.00E-04 | 1.71E-04 | |||||||||||||||||||
134 | lb/ton | 2.25E-06 | 2.48E-06 | 7.07E-07 | 7.14E-07 | 1.54E-06 | |||||||||||||||||||
135 | lb/ton ND Adjusted | 2.25E-06 | 2.48E-06 | 7.07E-07 | 7.14E-07 | 1.54E-06 |
A | B | C | D | E | F | G | I | J | K | L | M | N | O | P | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Billet Cutting Vent | Cascade Steel Rolling Mills CAO ATEI | |||||||||||||
2 | CAS or DEQ ID | TAC | Acetone Rinse (lb/ton) | Filter Only no Blank Subtraction (lb/ton) | Total (lb/ton) | Total (lb/billet cut) | Supporting Data Reduction - Billet Cutting @ Casting Vent Source Test Data | ||||||||
3 | 7429-90-5 | Aluminum and Compounds | 1.22E-05 | 2.39E-05 | 3.60E-05 | 9.01E-05 | 4.51E-06 | ||||||||
4 | 7440-36-0 | Antimony and Compounds | 0.00E+00 | 2.08E-06 | 2.08E-06 | 5.19E-06 | |||||||||
5 | 7440-38-2 | Arsenic and Compounds | 4.91E-08 | 6.08E-06 | 6.13E-06 | 1.53E-05 | |||||||||
6 | 7440-41-7 | Beryllium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||
7 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 3.97E-06 | 8.93E-06 | 1.29E-05 | 3.23E-05 | |||||||||
8 | 7440-48-4 | Cobalt and Compounds | 3.56E-07 | 2.58E-06 | 2.94E-06 | 7.35E-06 | |||||||||
9 | 7440-50-8 | Copper and Compounds | 2.46E-06 | 1.90E-04 | 1.93E-04 | 4.82E-04 | |||||||||
10 | 7439-92-1 | Lead and Compounds | 1.60E-07 | 6.85E-06 | 7.01E-06 | 1.75E-05 | |||||||||
11 | 7439-96-5 | Manganese and Compounds | 2.94E-05 | 9.95E-05 | 1.29E-04 | 3.22E-04 | |||||||||
12 | 365 | Nickel compounds, insoluble | 2.18E-06 | 2.75E-05 | 2.97E-05 | 7.42E-05 | |||||||||
13 | 504 | Phosphorus and Compounds | 0.00E+00 | 1.04E-05 | 1.04E-05 | 2.60E-05 | |||||||||
14 | 7782-49-2 | Selenium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||
15 | 7440-66-6 | Zinc and Compounds | 2.49E-06 | 3.14E-05 | 3.39E-05 | 8.47E-05 | |||||||||
16 | 7440-43-9 | Cadmium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | |||||||||
17 | 7440-62-2 | Vanadium (fume or dust) | 7.97E-07 | 1.54E-06 | 2.33E-06 | 5.84E-06 | |||||||||
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A | B | C | D | E | F | G | H | I | J | K | L | M | O | P | Q | R | S | T | U | V | W | X | Y | AA | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | CSRM Metals Data | Cascade Steel Rolling Mills CAO ATEI | |||||||||||||||||||||||
2 | Client: | Cascade Steel Rolling Mills | Supporting Data Reduction - Melt Shop Roof Monitor Source Test Data | ||||||||||||||||||||||
3 | Facility: | McMinnville Facility | |||||||||||||||||||||||
4 | Test Location: | Roof Monitor | |||||||||||||||||||||||
5 | Test Method: | Oregon Method 8 | |||||||||||||||||||||||
6 | |||||||||||||||||||||||||
7 | Source Condition | Acetone Only no Blank Subtraction | |||||||||||||||||||||||
8 | Date | 8/6/19 | 8/6/19 | 8/6/19 | |||||||||||||||||||||
9 | Start Time | 9:35 | 12:18 | 13:35 | |||||||||||||||||||||
10 | End Time | 10:45 | 13:24 | 14:47 | |||||||||||||||||||||
11 | Run 1 | Run 3 | Run 5 | Average | |||||||||||||||||||||
12 | Stack Conditions | ||||||||||||||||||||||||
13 | Average Gas Temperature, °F | 94.0 | 103.9 | 105.3 | 101.1 | ||||||||||||||||||||
14 | Flue Gas Moisture, percent by volume | 1.4% | 1.4% | 1.4% | 1.4% | ||||||||||||||||||||
15 | Average Flue Pressure, in. Hg | 29.80 | 29.80 | 29.80 | 29.80 | ||||||||||||||||||||
16 | Gas Sample Volume, dscf | 1,357.794 | 1,409.673 | 1,094.646 | 1,287.371 | ||||||||||||||||||||
17 | Average Gas Velocity, ft/sec | 8.630 | 9.611 | 7.090 | 8.444 | ||||||||||||||||||||
18 | Gas Volumetric Flow Rate, acfm | 402,862 | 448,642 | 330,958 | 394,154 | ||||||||||||||||||||
19 | Gas Volumetric Flow Rate, dscfm | 377,051 | 412,758 | 303,468 | 364,426 | ||||||||||||||||||||
20 | Gas Volumetric Flow Rate, scfm | 382,414 | 418,413 | 307,907 | 369,578 | ||||||||||||||||||||
21 | Average %CO2 by volume, dry basis | 0.0 | 0.0 | 0.0 | 0.0 | ||||||||||||||||||||
22 | Average %O2 by volume, dry basis | 20.9 | 20.9 | 20.9 | 20.9 | ||||||||||||||||||||
23 | Isokinetic Variance | 101.2 | 96.0 | 101.4 | 99.5 | ||||||||||||||||||||
24 | Metal Production Rate, ton/hr | 132.0 | 116.0 | 131.0 | 126.3 | ||||||||||||||||||||
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31 | Aluminum (Al) Emissions | ||||||||||||||||||||||||
32 | ug of sample collected | 5,440.00 | 884.00 | 941.00 | 2,421.67 | ||||||||||||||||||||
33 | ppb | 126.04 | 19.73 | 27.04 | 57.60 | ||||||||||||||||||||
34 | ug/dscm | 141.49 | 22.15 | 30.36 | 64.67 | ||||||||||||||||||||
35 | lb/hr | 2.00E-01 | 3.42E-02 | 3.46E-02 | 8.96E-02 | ||||||||||||||||||||
36 | lb/ton | 1.51E-03 | 2.95E-04 | 2.64E-04 | 6.91E-04 | ||||||||||||||||||||
37 | lb/ton ND Adjusted | 1.51E-03 | 2.95E-04 | 2.64E-04 | 6.91E-04 | ||||||||||||||||||||
38 | Antimony (Sb) Emissions | ||||||||||||||||||||||||
39 | ug of sample collected | ≤ | 3.00 | ≤ | 3.00 | ≤ | 3.00 | ≤ | 3.00 | ||||||||||||||||
40 | ppb | ≤ | 0.02 | ≤ | 0.02 | ≤ | 0.02 | ≤ | 0.02 | ||||||||||||||||
41 | ug/dscm | ≤ | 0.08 | ≤ | 0.08 | ≤ | 0.10 | ≤ | 0.09 | ||||||||||||||||
42 | lb/hr | ≤ | 1.10E-04 | ≤ | 1.16E-04 | ≤ | 1.10E-04 | ≤ | 1.12E-04 | ||||||||||||||||
43 | lb/ton | ≤ | 8.33E-07 | ≤ | 1.00E-06 | ≤ | 8.40E-07 | ≤ | 8.91E-07 | ||||||||||||||||
44 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||||||||||||||
45 | Arsenic (As) Emissions | ||||||||||||||||||||||||
46 | ug of sample collected | 3.59 | ≤ | 0.80 | ≤ | 0.80 | ≤ | 1.73 | |||||||||||||||||
47 | ppb | 0.03 | ≤ | 0.01 | ≤ | 0.01 | ≤ | 0.01 | |||||||||||||||||
48 | ug/dscm | 0.09 | ≤ | 0.02 | ≤ | 0.03 | ≤ | 0.05 | |||||||||||||||||
49 | lb/hr | 1.32E-04 | ≤ | 3.10E-05 | ≤ | 2.90E-05 | ≤ | 6.40E-05 | |||||||||||||||||
50 | lb/ton | 1.00E-06 | ≤ | 2.67E-07 | ≤ | 2.21E-07 | ≤ | 4.96E-07 |
51 | lb/ton ND Adjusted | 1.00E-06 | 1.34E-07 | 1.11E-07 | 4.15E-07 | ||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | Beryllium (Be) Emissions | ||||||||||||||||||||||||
53 | ug of sample collected | ≤ | 0.18 | ≤ | 0.18 | ≤ | 0.18 | ≤ | 0.18 | ||||||||||||||||
54 | ppb | ≤ | 0.01 | ≤ | 0.01 | ≤ | 0.02 | ≤ | 0.01 | ||||||||||||||||
55 | ug/dscm | ≤ | 0.01 | ≤ | 0.01 | ≤ | 0.01 | ≤ | 0.01 | ||||||||||||||||
56 | lb/hr | ≤ | 7.00E-06 | ≤ | 7.00E-06 | ≤ | 7.00E-06 | ≤ | 7.00E-06 | ||||||||||||||||
57 | lb/ton | ≤ | 5.30E-08 | ≤ | 6.03E-08 | ≤ | 5.34E-08 | ≤ | 5.56E-08 | ||||||||||||||||
58 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||||||||||||||
59 | Chromium (Cr) Emissions | ||||||||||||||||||||||||
60 | ug of sample collected | 68.50 | 15.40 | 19.60 | 34.50 | ||||||||||||||||||||
61 | ppb | 0.82 | 0.18 | 0.29 | 0.43 | ||||||||||||||||||||
62 | ug/dscm | 1.78 | 0.39 | 0.63 | 0.93 | ||||||||||||||||||||
63 | lb/hr | 2.52E-03 | 5.96E-04 | 7.21E-04 | 1.28E-03 | ||||||||||||||||||||
64 | lb/ton | 1.91E-05 | 5.14E-06 | 5.50E-06 | 9.90E-06 | ||||||||||||||||||||
65 | lb/ton ND Adjusted | 1.91E-05 | 5.14E-06 | 5.50E-06 | 9.90E-06 | ||||||||||||||||||||
66 | Cobalt (Co) Emissions | ||||||||||||||||||||||||
67 | ug of sample collected | 8.32 | 1.20 | 1.74 | 3.75 | ||||||||||||||||||||
68 | ppb | 0.09 | 0.01 | 0.02 | 0.04 | ||||||||||||||||||||
69 | ug/dscm | 0.22 | 0.03 | 0.06 | 0.10 | ||||||||||||||||||||
70 | lb/hr | 3.00E-04 | 4.41E-05 | 1.00E-04 | 1.48E-04 | ||||||||||||||||||||
71 | lb/ton | 2.27E-06 | 3.80E-07 | 7.63E-07 | 1.14E-06 | ||||||||||||||||||||
72 | lb/ton ND Adjusted | 2.27E-06 | 3.80E-07 | 7.63E-07 | 1.14E-06 | ||||||||||||||||||||
73 | Copper (Cu) Emissions | ||||||||||||||||||||||||
74 | ug of sample collected | 49.50 | 11.30 | 15.50 | 25.43 | ||||||||||||||||||||
75 | ppb | 0.49 | 0.11 | 0.19 | 0.26 | ||||||||||||||||||||
76 | ug/dscm | 1.29 | 0.28 | 0.50 | 0.69 | ||||||||||||||||||||
77 | lb/hr | 1.80E-03 | 4.00E-04 | 6.00E-04 | 9.33E-04 | ||||||||||||||||||||
78 | lb/ton | 1.36E-05 | 3.45E-06 | 4.58E-06 | 7.22E-06 | ||||||||||||||||||||
79 | lb/ton ND Adjusted | 1.36E-05 | 3.45E-06 | 4.58E-06 | 7.22E-06 | ||||||||||||||||||||
80 | Lead (Pb) Emissions | ||||||||||||||||||||||||
81 | ug of sample collected | 43.20 | 7.13 | 9.99 | 20.11 | ||||||||||||||||||||
82 | ppb | 0.13 | 0.02 | 0.04 | 0.06 | ||||||||||||||||||||
83 | ug/dscm | 1.12 | 0.18 | 0.32 | 0.54 | ||||||||||||||||||||
84 | lb/hr | 1.60E-03 | 3.00E-04 | 4.00E-04 | 7.67E-04 | ||||||||||||||||||||
85 | lb/ton | 1.21E-05 | 2.59E-06 | 3.05E-06 | 5.92E-06 | ||||||||||||||||||||
86 | lb/ton ND Adjusted | 1.21E-05 | 2.59E-06 | 3.05E-06 | 5.92E-06 | ||||||||||||||||||||
87 | Manganese (Mn) Emissions | ||||||||||||||||||||||||
88 | ug of sample collected | 4,540.00 | 519.00 | 672.00 | 1,910.33 | ||||||||||||||||||||
89 | ppb | 51.66 | 5.69 | 9.48 | 22.28 | ||||||||||||||||||||
90 | ug/dscm | 118.08 | 13.00 | 21.68 | 50.92 | ||||||||||||||||||||
91 | lb/hr | 1.67E-01 | 2.01E-02 | 2.47E-02 | 7.05E-02 | ||||||||||||||||||||
92 | lb/ton | 1.26E-03 | 1.73E-04 | 1.89E-04 | 5.42E-04 | ||||||||||||||||||||
93 | lb/ton ND Adjusted | 1.26E-03 | 1.73E-04 | 1.89E-04 | 5.42E-04 | ||||||||||||||||||||
94 | Nickel (Ni) Emissions | ||||||||||||||||||||||||
95 | ug of sample collected | 19.70 | 6.60 | 8.80 | 11.70 | ||||||||||||||||||||
96 | ppb | 0.21 | 0.07 | 0.12 | 0.13 | ||||||||||||||||||||
97 | ug/dscm | 0.51 | 0.17 | 0.28 | 0.32 | ||||||||||||||||||||
98 | lb/hr | 7.00E-04 | 3.00E-04 | 3.00E-04 | 4.33E-04 | ||||||||||||||||||||
99 | lb/ton | 5.30E-06 | 2.59E-06 | 2.29E-06 | 3.39E-06 | #REF! | 2.59E-06 | 2.29E-06 | 3.43E-06 | ||||||||||||||||
100 | lb/ton ND Adjusted | 5.30E-06 | 2.59E-06 | 2.29E-06 | 3.39E-06 |
101 | Phosphorus (P) Emissions | ||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
102 | ug of sample collected | 103.00 | ≤ | 90.00 | ≤ | 90.00 | ≤ | 94.33 | |||||||||||||||||
103 | ppb | 2.08 | ≤ | 1.75 | ≤ | 2.25 | ≤ | 2.03 | |||||||||||||||||
104 | ug/dscm | 2.68 | ≤ | 2.25 | ≤ | 2.90 | ≤ | 2.61 | |||||||||||||||||
105 | lb/hr | 3.80E-03 | ≤ | 3.50E-03 | ≤ | 3.30E-03 | ≤ | 3.53E-03 | |||||||||||||||||
106 | lb/ton | 2.88E-05 | ≤ | 3.02E-05 | ≤ | 2.52E-05 | ≤ | 2.81E-05 | 2.88E-05 | 3.02E-05 | 2.52E-05 | ||||||||||||||
107 | lb/ton ND Adjusted | 2.88E-05 | 1.51E-05 | 1.26E-05 | 1.88E-05 | ||||||||||||||||||||
108 | Selenium (Se) Emissions | ||||||||||||||||||||||||
109 | ug of sample collected | 2.70 | ≤ | 2.00 | ≤ | 2.00 | ≤ | 2.23 | |||||||||||||||||
110 | ppb | 0.02 | ≤ | 0.02 | ≤ | 0.02 | ≤ | 0.02 | |||||||||||||||||
111 | ug/dscm | 0.07 | ≤ | 0.05 | ≤ | 0.06 | ≤ | 0.06 | |||||||||||||||||
112 | lb/hr | 1.00E-04 | ≤ | 1.00E-04 | ≤ | 1.00E-04 | ≤ | 1.00E-04 | |||||||||||||||||
113 | lb/ton | 7.58E-07 | ≤ | 8.62E-07 | ≤ | 7.63E-07 | ≤ | 7.94E-07 | |||||||||||||||||
114 | lb/ton ND Adjusted | 7.58E-07 | 4.31E-07 | 3.82E-07 | 5.23E-07 | ||||||||||||||||||||
115 | Zinc (Zn) Emissions | ||||||||||||||||||||||||
116 | ug of sample collected | 449.00 | 97.00 | 119.00 | 221.67 | ||||||||||||||||||||
117 | ppb | 4.29 | 0.89 | 1.41 | 2.20 | ||||||||||||||||||||
118 | ug/dscm | 11.68 | 2.43 | 3.84 | 5.98 | ||||||||||||||||||||
119 | lb/hr | 1.65E-02 | 3.80E-03 | 4.40E-03 | 8.23E-03 | ||||||||||||||||||||
120 | lb/ton | 1.25E-04 | 3.28E-05 | 3.36E-05 | 6.38E-05 | ||||||||||||||||||||
121 | lb/ton ND Adjusted | 1.25E-04 | 3.28E-05 | 3.36E-05 | 6.38E-05 | ||||||||||||||||||||
122 | Cadmium (Cd) Emissions | ||||||||||||||||||||||||
123 | ug of sample collected | 0.72 | ≤ | 0.18 | 0.20 | 0.37 | Cd and V Results corrected per R1 | ||||||||||||||||||
124 | ppb | 0.00 | ≤ | 0.00 | 0.00 | 0.00 | |||||||||||||||||||
125 | ug/dscm | 0.02 | ≤ | 0.01 | 0.01 | 0.01 | |||||||||||||||||||
126 | lb/hr | 2.65E-05 | ≤ | 6.97E-06 | 7.33E-06 | 1.36E-05 | |||||||||||||||||||
127 | lb/ton | 2.00E-07 | ≤ | 6.01E-08 | 5.60E-08 | 1.05E-07 | 2.00E-07 | 6.01E-08 | 5.60E-08 | ||||||||||||||||
128 | lb/ton ND Adjusted | 2.00E-07 | 3.00E-08 | 5.60E-08 | 9.55E-08 | ||||||||||||||||||||
129 | Vanadium Emissions | ||||||||||||||||||||||||
130 | ug of sample collected | 20.70 | 3.40 | 3.96 | 9.35 | ||||||||||||||||||||
131 | ppb | 0.25 | 0.04 | 0.06 | 0.12 | ||||||||||||||||||||
132 | ug/dscm | 0.54 | 0.09 | 0.13 | 0.25 | ||||||||||||||||||||
133 | lb/hr | 8.00E-04 | 1.00E-04 | 1.00E-04 | 3.33E-04 | ||||||||||||||||||||
134 | lb/ton | 6.06E-06 | 8.62E-07 | 7.63E-07 | 2.56E-06 | 6.06E-06 | #REF! | 8.62E-07 | 7.63E-07 | 2.64E-06 | 8.62E-07 | 7.63E-07 | |||||||||||||
135 | lb/ton ND Adjusted | 6.06E-06 | 8.62E-07 | 7.63E-07 | 2.56E-06 |
A | B | C | D | E | F | G | H | I | J | K | L | M | |
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1 | CSRM Metals Data | ||||||||||||
2 | Client: | Cascade Steel Rolling Mills | |||||||||||
3 | Facility: | McMinnville Facility | |||||||||||
4 | Test Location: | Roof Monitor | |||||||||||
5 | Test Method: | Oregon Method 8 | |||||||||||
7 | Source Condition | Filter Only no Blank Subtraction | |||||||||||
8 | Date | 8/6/19 | 8/6/19 | 8/6/19 | |||||||||
9 | Start Time | 9:35 | 12:18 | 13:35 | |||||||||
10 | End Time | 10:45 | 13:24 | 14:47 | |||||||||
11 | Run 1 | Run 3 | Run 5 | Average | |||||||||
12 | Stack Conditions | ||||||||||||
13 | Average Gas Temperature, °F | 94.0 | 103.9 | 105.3 | 101.1 | ||||||||
14 | Flue Gas Moisture, percent by volume | 1.4% | 1.4% | 1.4% | 1.4% | ||||||||
15 | Average Flue Pressure, in. Hg | 29.80 | 29.80 | 29.80 | 29.80 | ||||||||
16 | Gas Sample Volume, dscf | 1,357.794 | 1,409.673 | 1,094.646 | 1,287.371 | ||||||||
17 | Average Gas Velocity, ft/sec | 8.630 | 9.611 | 7.090 | 8.444 | ||||||||
18 | Gas Volumetric Flow Rate, acfm | 402,862 | 448,642 | 330,958 | 394,154 | ||||||||
19 | Gas Volumetric Flow Rate, dscfm | 377,051 | 412,758 | 303,468 | 364,426 | ||||||||
20 | Gas Volumetric Flow Rate, scfm | 382,414 | 418,413 | 307,907 | 369,578 | ||||||||
21 | Average %CO2 by volume, dry basis | 0.0 | 0.0 | 0.0 | 0.0 | ||||||||
22 | Average %O2 by volume, dry basis | 20.9 | 20.9 | 20.9 | 20.9 | ||||||||
23 | Isokinetic Variance | 101.2 | 96.0 | 101.4 | 99.5 | ||||||||
24 | Metal Production Rate, ton/hr | 132.0 | 116.0 | 131.0 | 126.3 | ||||||||
31 | Aluminum (Al) Emissions | ||||||||||||
32 | ug of sample collected | 3,100.00 | 920.00 | 1,800.00 | 1,940.00 | ||||||||
33 | ppb | 71.83 | 20.53 | 51.73 | 48.03 | ||||||||
34 | ug/dscm | 80.63 | 23.05 | 58.07 | 53.92 | ||||||||
35 | lb/hr | 1.14E-01 | 3.56E-02 | 6.62E-02 | 7.19E-02 | ||||||||
36 | lb/ton | 8.63E-04 | 3.07E-04 | 5.06E-04 | 5.58E-04 | ||||||||
37 | lb/ton ND Adjusted | 8.63E-04 | 3.07E-04 | 5.06E-04 | 5.58E-04 | ||||||||
38 | Antimony (Sb) Emissions | ||||||||||||
39 | ug of sample collected | 7.40 | 6.60 | 20.00 | 11.33 | ||||||||
40 | ppb | 0.04 | 0.03 | 0.13 | 0.07 | ||||||||
41 | ug/dscm | 0.19 | 0.17 | 0.65 | 0.34 | ||||||||
42 | lb/hr | 2.72E-04 | 2.56E-04 | 7.36E-04 | 4.21E-04 | ||||||||
43 | lb/ton | 2.06E-06 | 2.21E-06 | 5.62E-06 | 3.30E-06 | ||||||||
44 | lb/ton ND Adjusted | 2.06E-06 | 2.21E-06 | 5.62E-06 | 3.30E-06 | ||||||||
45 | Arsenic (As) Emissions | ||||||||||||
46 | ug of sample collected | 13.00 | 12.00 | 31.00 | 18.67 | ||||||||
47 | ppb | 0.11 | 0.10 | 0.32 | 0.18 | ||||||||
48 | ug/dscm | 0.34 | 0.30 | 1.00 | 0.55 | ||||||||
49 | lb/hr | 4.78E-04 | 4.65E-04 | 1.14E-03 | 6.95E-04 | ||||||||
50 | lb/ton | 3.62E-06 | 4.01E-06 | 8.71E-06 | 5.45E-06 | ||||||||
51 | lb/ton ND Adjusted | 3.62E-06 | 4.01E-06 | 8.71E-06 | 5.45E-06 | ||||||||
52 | Beryllium (Be) Emissions | ||||||||||||
53 | ug of sample collected | ≤ | 2.70 | ≤ | 0.27 | ≤ | 2.70 | ≤ | 1.89 | ||||
54 | ppb | ≤ | 0.19 | ≤ | 0.02 | ≤ | 0.23 | ≤ | 0.15 | ||||
55 | ug/dscm | ≤ | 0.07 | ≤ | 0.01 | ≤ | 0.09 | ≤ | 0.06 | ||||
56 | lb/hr | ≤ | 9.90E-05 | ≤ | 1.00E-05 | ≤ | 9.90E-05 | ≤ | 6.93E-05 | ||||
57 | lb/ton | ≤ | 7.50E-07 | ≤ | 8.62E-08 | ≤ | 7.56E-07 | ≤ | 5.31E-07 |
58 | lb/ton ND Adjusted | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
59 | Chromium (Cr) Emissions | ||||||||||||
60 | ug of sample collected | 43.00 | 35.00 | 98.00 | 58.67 | ||||||||
61 | ppb | 0.52 | 0.41 | 1.46 | 0.79 | ||||||||
62 | ug/dscm | 1.12 | 0.88 | 3.16 | 1.72 | ||||||||
63 | lb/hr | 1.58E-03 | 1.36E-03 | 3.61E-03 | 2.18E-03 | ||||||||
64 | lb/ton | 1.20E-05 | 1.17E-05 | 2.75E-05 | 1.71E-05 | ||||||||
65 | lb/ton ND Adjusted | 1.20E-05 | 1.17E-05 | 2.75E-05 | 1.71E-05 | ||||||||
66 | Cobalt (Co) Emissions | ||||||||||||
67 | ug of sample collected | 9.90 | 3.80 | 8.20 | 7.30 | ||||||||
68 | ppb | 0.11 | 0.04 | 0.11 | 0.08 | ||||||||
69 | ug/dscm | 0.26 | 0.10 | 0.26 | 0.21 | ||||||||
70 | lb/hr | 4.00E-04 | 1.40E-04 | 3.00E-04 | 2.80E-04 | ||||||||
71 | lb/ton | 3.03E-06 | 1.20E-06 | 2.29E-06 | 2.17E-06 | ||||||||
72 | lb/ton ND Adjusted | 3.03E-06 | 1.20E-06 | 2.29E-06 | 2.17E-06 | ||||||||
73 | Copper (Cu) Emissions | ||||||||||||
74 | ug of sample collected | 340.00 | 360.00 | 670.00 | 456.67 | ||||||||
75 | ppb | 3.34 | 3.41 | 8.18 | 4.98 | ||||||||
76 | ug/dscm | 8.84 | 9.02 | 21.62 | 13.16 | ||||||||
77 | lb/hr | 1.25E-02 | 1.39E-02 | 2.47E-02 | 1.70E-02 | ||||||||
78 | lb/ton | 9.47E-05 | 1.20E-04 | 1.89E-04 | 1.34E-04 | ||||||||
79 | lb/ton ND Adjusted | 9.47E-05 | 1.20E-04 | 1.89E-04 | 1.34E-04 | ||||||||
80 | Lead (Pb) Emissions | ||||||||||||
81 | ug of sample collected | 1,300.00 | 250.00 | 970.00 | 840.00 | ||||||||
82 | ppb | 3.92 | 0.73 | 3.63 | 2.76 | ||||||||
83 | ug/dscm | 33.81 | 6.26 | 31.29 | 23.79 | ||||||||
84 | lb/hr | 4.78E-02 | 9.70E-03 | 3.57E-02 | 3.11E-02 | ||||||||
85 | lb/ton | 3.62E-04 | 8.36E-05 | 2.73E-04 | 2.39E-04 | ||||||||
86 | lb/ton ND Adjusted | 3.62E-04 | 8.36E-05 | 2.73E-04 | 2.39E-04 | ||||||||
87 | Manganese (Mn) Emissions | ||||||||||||
88 | ug of sample collected | 7,200.00 | 2,700.00 | 4,200.00 | 4,700.00 | ||||||||
89 | ppb | 81.92 | 29.59 | 59.28 | 56.93 | ||||||||
90 | ug/dscm | 187.26 | 67.64 | 135.50 | 130.13 | ||||||||
91 | lb/hr | 2.65E-01 | 1.05E-01 | 1.55E-01 | 1.75E-01 | ||||||||
92 | lb/ton | 2.00E-03 | 9.02E-04 | 1.18E-03 | 1.36E-03 | ||||||||
93 | lb/ton ND Adjusted | 2.00E-03 | 9.02E-04 | 1.18E-03 | 1.36E-03 | ||||||||
94 | Nickel (Ni) Emissions | ||||||||||||
95 | ug of sample collected | 35.00 | 39.00 | 85.00 | 53.00 | ||||||||
96 | ppb | 0.37 | 0.40 | 1.12 | 0.63 | ||||||||
97 | ug/dscm | 0.91 | 0.98 | 2.74 | 1.54 | ||||||||
98 | lb/hr | 1.30E-03 | 1.50E-03 | 3.10E-03 | 1.97E-03 | ||||||||
99 | lb/ton | 9.85E-06 | 1.29E-05 | 2.37E-05 | 1.55E-05 | ||||||||
100 | lb/ton ND Adjusted | 9.85E-06 | 1.29E-05 | 2.37E-05 | 1.55E-05 | ||||||||
101 | Phosphorus (P) Emissions | ||||||||||||
102 | ug of sample collected | 61.00 | 27.00 | 72.00 | 53.33 | ||||||||
103 | ppb | 1.23 | 0.53 | 1.80 | 1.19 | ||||||||
104 | ug/dscm | 1.59 | 0.68 | 2.32 | 1.53 | ||||||||
105 | lb/hr | 2.20E-03 | 1.00E-03 | 2.60E-03 | 1.93E-03 | ||||||||
106 | lb/ton | 1.67E-05 | 8.62E-06 | 1.98E-05 | 1.50E-05 | ||||||||
107 | lb/ton ND Adjusted | 1.67E-05 | 8.62E-06 | 1.98E-05 | 1.50E-05 |
108 | Selenium (Se) Emissions | ||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
109 | ug of sample collected | 13.00 | 13.00 | 29.00 | 18.33 | ||||||||
110 | ppb | 0.10 | 0.10 | 0.29 | 0.16 | ||||||||
111 | ug/dscm | 0.34 | 0.33 | 0.94 | 0.54 | ||||||||
112 | lb/hr | 5.00E-04 | 5.00E-04 | 1.10E-03 | 7.00E-04 | ||||||||
113 | lb/ton | 3.79E-06 | 4.31E-06 | 8.40E-06 | 5.50E-06 | ||||||||
114 | lb/ton ND Adjusted | 3.79E-06 | 4.31E-06 | 8.40E-06 | 5.50E-06 | ||||||||
115 | Zinc (Zn) Emissions | ||||||||||||
116 | ug of sample collected | 5,200.00 | 1,800.00 | 8,500.00 | 5,166.67 | ||||||||
117 | ppb | 49.73 | 16.58 | 100.82 | 55.71 | ||||||||
118 | ug/dscm | 135.25 | 45.09 | 274.22 | 151.52 | ||||||||
119 | lb/hr | 1.91E-01 | 6.97E-02 | 3.13E-01 | 1.91E-01 | ||||||||
120 | lb/ton | 1.45E-03 | 6.01E-04 | 2.39E-03 | 1.48E-03 | ||||||||
121 | lb/ton ND Adjusted | 1.45E-03 | 6.01E-04 | 2.39E-03 | 1.48E-03 | ||||||||
122 | Cadmium (Cd) Emissions | ||||||||||||
123 | ug of sample collected | 1.00 | 1.30 | 1.20 | 1.17 | ||||||||
124 | ppb | 0.01 | 0.01 | 0.01 | 0.01 | ||||||||
125 | ug/dscm | 0.03 | 0.03 | 0.04 | 0.03 | ||||||||
126 | lb/hr | 3.67E-05 | 5.04E-05 | 4.40E-05 | 4.37E-05 | ||||||||
127 | lb/ton | 2.78E-07 | 4.34E-07 | 3.36E-07 | 3.49E-07 | ||||||||
128 | lb/ton ND Adjusted | 2.78E-07 | 4.34E-07 | 3.36E-07 | 3.49E-07 | ||||||||
129 | Vanadium Emissions | ||||||||||||
130 | ug of sample collected | 15.00 | 4.60 | 9.70 | 9.77 | ||||||||
131 | ppb | 0.18 | 0.05 | 0.15 | 0.13 | ||||||||
132 | ug/dscm | 0.39 | 0.12 | 0.31 | 0.27 | ||||||||
133 | lb/hr | 6.00E-04 | 2.00E-04 | 4.00E-04 | 4.00E-04 | ||||||||
134 | lb/ton | 4.55E-06 | 1.72E-06 | 3.05E-06 | 3.11E-06 | ||||||||
135 | lb/ton ND Adjusted | 4.55E-06 | 1.72E-06 | 3.05E-06 | 3.11E-06 |
A | B | C | D | E | F | H | I | J | K | L | M | N | O | P | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Roof Monitor | Cascade Steel Rolling Mills CAO ATEI | |||||||||||||
2 | Metal | Acetone Rinse No Blank Correction (lb/ton) | Filter Only No Blank Correction (lb/ton) | Total (lb/ton) | Supporting Data Reduction - Melt Shop Roof Monitor Source Test Data | ||||||||||
3 | 7429-90-5 | Aluminum and Compounds | 6.91E-04 | 5.58E-04 | 1.25E-03 | ||||||||||
4 | 7440-36-0 | Antimony and Compounds | 0.00E+00 | 3.30E-06 | 3.30E-06 | ||||||||||
5 | 7440-38-2 | Arsenic and Compounds | 4.15E-07 | 5.45E-06 | 5.86E-06 | ||||||||||
6 | 7440-41-7 | Beryllium and Compounds | 0.00E+00 | 0.00E+00 | 0.00E+00 | ||||||||||
7 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 9.90E-06 | 1.71E-05 | 2.70E-05 | (As total Chromium) | |||||||||
8 | 7440-48-4 | Cobalt and Compounds | 1.14E-06 | 2.17E-06 | 3.31E-06 | ||||||||||
9 | 7440-50-8 | Copper and Compounds | 7.22E-06 | 1.34E-04 | 1.42E-04 | ||||||||||
10 | 7439-92-1 | Lead and Compounds | 5.92E-06 | 2.39E-04 | 2.45E-04 | ||||||||||
11 | 7439-96-5 | Manganese and Compounds | 5.42E-04 | 1.36E-03 | 1.90E-03 | ||||||||||
12 | 365 | Nickel compounds, insoluble | 3.39E-06 | 1.55E-05 | 1.89E-05 | ||||||||||
13 | 504 | Phosphorus and Compounds | 1.88E-05 | 1.50E-05 | 3.39E-05 | ||||||||||
14 | 7782-49-2 | Selenium and Compounds | 5.23E-07 | 5.50E-06 | 6.02E-06 | ||||||||||
15 | 7440-66-6 | Zinc and Compounds | 6.38E-05 | 1.48E-03 | 1.54E-03 | ||||||||||
16 | 7440-43-9 | Cadmium and Compounds | 9.55E-08 | 3.49E-07 | 4.45E-07 | ||||||||||
17 | 7440-62-2 | Vanadium (fume or dust) | 2.56E-06 | 3.11E-06 | 5.67E-06 | ||||||||||
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A | B | C | D | E | F | G | H | I | J | K | L | |
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1 | Attachment D. Recommended Organic TAC Emission Factors for EU-1. | |||||||||||
3 | Emission Factors | |||||||||||
4 | CAO Name | CASRN | Run 1a | Run 2a | Run 3a | Source Test Average | BH-1b (lb/ton) | BH-1Ac (lb/ton) | BH-2d (lb/ton) | Total Emissions (lb/ton) | ||
10 | Benzene (lb/ton) | Benzene | 71-43-2 | 0.013 | 0.0030 | 0.013 | 9.68E-03 | 9.68E-03 | 1.94E-03 | 1.16E-03 | 1.28E-02 | x |
13 | Chloromethane (lb/ton) | Chloromethane (methyl chloride) | 74-87-3 | 5.81E-04 | 2.83E-04 | 6.79E-04 | 5.14E-04 | 5.14E-04 | 1.03E-04 | 6.17E-05 | 6.79E-04 | x |
16 | Styrene (lb/ton) | Styrene | 100-42-5 | 1.40E-03 | 3.00E-04 | 1.29E-03 | 9.97E-04 | 9.97E-04 | 2.00E-04 | 1.20E-04 | 1.32E-03 | x |
19 | Toluene (lb/ton) | Toluene | 108-88-3 | 2.15E-03 | 5.65E-04 | 1.38E-03 | 1.37E-03 | 1.37E-03 | 2.74E-04 | 1.64E-04 | 1.80E-03 | x |
22 | Xylene (mixture) (lb/ton) | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 1330-20-7 | 4.95E-04 | 1.94E-04 | 2.94E-04 | 3.28E-04 | 3.28E-04 | 6.57E-05 | 3.94E-05 | 4.33E-04 | x |
26 | Chlorobenzene (lb/ton) | Chlorobenzene | 108-90-7 | 1.34E-04 | 9.72E-05 | 1.24E-04 | 1.18E-04 | 1.18E-04 | 2.37E-05 | 1.42E-05 | 1.56E-04 | x |
30 | Ethyl benzene (lb/ton) | Ethyl benzene | 100-41-4 | 2.80E-04 | 9.72E-05 | 1.90E-04 | 1.89E-04 | 1.89E-04 | 3.79E-05 | 2.27E-05 | 2.50E-04 | x |
34 | Vinyl Chloride (lb/ton) | Vinyl chloride | 75-01-4 | 8.40E-05 | 5.48E-05 | 8.37E-05 | 7.42E-05 | 7.42E-05 | 1.49E-05 | 8.90E-06 | 9.79E-05 | x |
38 | Bromomethane (lb/ton) | Bromomethane (methyl bromide) | 74-83-9 | 9.91E-05 | 8.39E-05 | 1.20E-04 | 1.01E-04 | 1.01E-04 | 2.02E-05 | 1.21E-05 | 1.33E-04 | x |
42 | Trichlorofluoromethane (lb/ton) | Trichlorofluoromethane (Freon 11) | 75-69-4 | 1.90E-04 | 1.24E-04 | 2.94E-04 | 2.02E-04 | 2.02E-04 | 4.06E-05 | 2.43E-05 | 2.67E-04 | x |
46 | Methylene chloride (lb/ton) | Dichloromethane (methylene chloride) | 75-09-2 | 9.91E-05 | 7.51E-05 | 9.73E-05 | 9.05E-05 | 9.05E-05 | 1.81E-05 | 1.09E-05 | 1.19E-04 | x |
50 | 1,1,2,2-Tetrachloroethane (lb/ton) | 1,1,2,2-Tetrachloroethane | 79-34-5 | 2.58E-04 | 1.50E-04 | 1.92E-04 | 2.00E-04 | 2.00E-04 | 4.02E-05 | 2.40E-05 | 2.65E-04 | x |
54 | 1,2,4-Trimethylbenzene (lb/ton) | 1,2,4-Trimethylbenzene | 95-63-6 | 1.31E-04 | 1.06E-04 | 1.36E-04 | 1.24E-04 | 1.24E-04 | 2.49E-05 | 1.49E-05 | 1.64E-04 | x |
58 | 1,2,4-Trichlorobenzene (lb/ton) | 1,2,4-Trichlorobenzene | 120-82-1 | 2.80E-04 | 1.59E-04 | 2.04E-04 | 2.14E-04 | 2.14E-04 | 4.29E-05 | 2.57E-05 | 2.83E-04 | x |
60 | a Data is for BH-1, from the Emissions Test Report for CSRM Electric Arc Furnace Baghouse (Horizon Engineering, March 3, 1995). | |||||||||||
61 | b Average of Emissions Test results | |||||||||||
62 | c Additional BH-1A emissions are estimated based on the baghouse flow rate allocation estimates in the May 2013 source test report: 83.3 percent to BH-1 and 16.7 percent to BH-1A. | |||||||||||
63 | d Additional BH-2 emissions are estimated assuming 10 percent of the combined BH-1 and BH-1A emissions, following the VOC calculation methodology used in CSRM's Title V Permit Review Report (page 27). | |||||||||||
65 | Notes | |||||||||||
66 | BH = Baghouse | |||||||||||
67 | CASRN = Chemical Abstracts Services Registry Number | |||||||||||
68 | CSRM = Cascade Steel Rolling Mills |
A | B | C | D | E | F | G | H | |
---|---|---|---|---|---|---|---|---|
1 | Attachment B. Emission Factor Details: Dioxins/Furans | |||||||
3 | Emission Unit | Pollutant | Emission Factor Source | Notes | Emission Factor | Converted Emission Factor | ||
4 | Value | Units | Value | Units | ||||
5 | EAF | PCDD/Fs | Amended AB2588 Health Risk Assessment - TAMCO. January 2015. See Appendix B-1a & -1b. | Based on stack testing from a similar mini mill that melts scrap and makes rebar. | 1.58E-09 | lb TEQ/ton steel produced | ||
6 | Slag Concentration | PCDD/Fs | Remus et al., 2013. Table 8-9. | Average values in slag from Swedish steel plants melting scrap in EAF. | 0.005125 | μg TEQ/kg | 1.03E-08 | lb TEQ/ton slag |
8 | Notes: | |||||||
9 | EAF = electric arc furnace | |||||||
10 | kg = kilogram | |||||||
11 | lb = pounds | |||||||
12 | PCDD/Fs = Polychlorinated dibenzo-p-dioxins (PCDDs) & dibenzofurans (PCDFs) | |||||||
13 | TEQ = toxic equivalency | |||||||
14 | ton = US ton | |||||||
15 | μg = micrograms |
A | B | C | D | E | F | G | H | |
---|---|---|---|---|---|---|---|---|
1 | Attachment B. Emission Factor Details: PCBs | |||||||
3 | Emission Unit | Pollutant | Emission Factor Source | Notes | Emission Factor | Converted Emission Factor | ||
4 | Name | Value | Units | Value | Units | |||
5 | EAF | TEQ | Wu et al. 2014. Table 6. | EAF melting scrap (104 tonne/hr), alloying agents (1.1 t/hr), flux (2.1 t/hr), and coke (1.8 t/hr). Producing carbon steel at rate of 100 t/hr. Baghouse control devices. | 0.0232 | μg TEQ/metric ton feedstock | 4.64E-11 | lb TEQ/ton metal melted |
6 | EAF | TEQ | Remus et al., 2013. Table 8-4. | Swedish EAF Steel Plant A | 0.22 | μg TEQ/metric ton LS | 4.40E-10 | lb TEQ/ton metal melted |
7 | EAF | TEQ | Remus et al., 2013. Table 8-4. | Swedish EAF Steel Plant B | 0.04 | μg TEQ/metric ton LS | 7.99E-11 | lb TEQ/ton metal melted |
8 | EAF | TEQ | Remus et al., 2013. Table 8-4. | Swedish EAF Steel Plant C | 0.015 | μg TEQ/metric ton LS | 3.00E-11 | lb TEQ/ton metal melted |
9 | EAF | TEQ | Remus et al., 2013. Table 8-4. | Swedish EAF Steel Plant D | 0.02 | μg TEQ/metric ton LS | 4.00E-11 | lb TEQ/ton metal melted |
10 | EAF | TEQ | Remus et al., 2013. Table 8-4. | Swedish EAF Steel Plant E | 0.42 | μg TEQ/metric ton LS | 8.39E-10 | lb TEQ/ton metal melted |
11 | EAF | TEQ | Remus et al., 2013. Table 8-4. | Swedish EAF Steel Plant F | 0.012 | μg TEQ/metric ton LS | 2.40E-11 | lb TEQ/ton metal melted |
12 | EAF | TEQ | Remus et al., 2013. Table 8-4. | Swedish EAF Steel Plant G | 0.28 | μg TEQ/metric ton LS | 5.59E-10 | lb TEQ/ton metal melted |
13 | EAF | TEQ | Remus et al., 2013. Table 8-4. | Swedish EAF Steel Plant H | 0.56 | μg TEQ/metric ton LS | 1.12E-09 | lb TEQ/ton metal melted |
14 | EAF | TEQ | Remus et al., 2013. Table 8-4. | Average of eight Swedish EAFs sampled, all with fabric filter controls. | 0.20 | μg TEQ/metric ton LS | 3.91E-10 | lb TEQ/ton metal melted |
15 | EAF | TEQ | Wu et al., 2014; Remus et al., 2013. | Average of 9 EAFs with filter controls. | 0.18 | μg TEQ/metric ton | 3.57E-10 | lb TEQ/ton metal melted |
16 | Slag Concentration | TEQ | Remus et al., 2013. Table 8-9. | Average values in slag from Swedish steel plants melting scrap in EAF. | 0.0005125 | μg TEQ/kg | 1.03E-09 | lb TEQ/ton slag |
18 | Notes: | |||||||
19 | LS = liquid steel | |||||||
20 | TEF = Toxicity equivalency factor | |||||||
21 | PCB = Polychlorinated biphenyls | |||||||
22 | t = metric ton |
A | B | C | D | E | F | G | H | I | |
---|---|---|---|---|---|---|---|---|---|
1 | Attachment B. Emission Factor Details: PAHs | ||||||||
3 | Emission Unit | Pollutant | Emission Factor Source | Notes | Emission Factor | Converted Emission Factor | |||
4 | Name | TEF | Value | Units | Value | Units | |||
5 | EAF | Naphthalene | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 1020 | μg/kg feedstock | 2.04E-03 | lb/ton metal melted | |
6 | EAF | Acenaphthylene | NA | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 39.6 | μg/kg feedstock | ||
7 | EAF | Acenaphthene | NA | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 10.2 | μg/kg feedstock | ||
8 | EAF | Fluorene | NA | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 9.75 | μg/kg feedstock | ||
9 | EAF | Phenanthrene | 0 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 2.67 | μg/kg feedstock | ||
10 | EAF | Anthracene | 0 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 45.1 | μg/kg feedstock | ||
11 | EAF | Fluoranthene | 0.08 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 25.4 | μg/kg feedstock | ||
12 | EAF | Pyrene | 0 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 18.2 | μg/kg feedstock | ||
13 | EAF | Cyclopenta[c,d]pyrene | 0.4 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 1.9 | μg/kg feedstock | ||
14 | EAF | Benz[a]anthracene | 0.2 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 1.9 | μg/kg feedstock | ||
15 | EAF | Chrysene | 0.1 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 0.961 | μg/kg feedstock | ||
16 | EAF | Benzo[b]fluoranthene | 0.8 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 2.9 | μg/kg feedstock | ||
17 | EAF | Benzo[k]fluoranthene | 0.03 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 0.343 | μg/kg feedstock | ||
18 | EAF | Benzo[e]pyrene | NA | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 1.51 | μg/kg feedstock | ||
19 | EAF | Benzo[a]pyrene | 1 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 0.692 | μg/kg feedstock | 1.38E-06 | lb/ton metal melted |
20 | EAF | Perylene | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 0.288 | μg/kg feedstock | |||
21 | EAF | Indeno[1,2,3-cd]pyrene | 0.07 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 1.25 | μg/kg feedstock | ||
22 | EAF | Dibenz[a,h]anthracene | 10 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 0.34 | μg/kg feedstock | ||
23 | EAF | Benzo [b]chrysene | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 0.358 | μg/kg feedstock | |||
24 | EAF | Benzo[g,h,i]perylene | 0.009 | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 1.68 | μg/kg feedstock | ||
25 | EAF | Coronene | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs | 0.381 | μg/kg feedstock | |||
26 | EAF | BaP Eq | Lee et al., 1999, Table 7 | Group III, Average of 4 steel plant EAFs, calculated BaP TEQ | 9.79 | μg/kg feedstock | 1.96E-05 | lb BaPeq/ton metal melted |
A | B | C | D | E | F | G | H | |
---|---|---|---|---|---|---|---|---|
1 | Attachment B. Emission Factor Details: Hexachlorobenzene | |||||||
3 | Emission Unit | Pollutant | Emission Factor Source | Notes | Emission Factor | Converted Emission Factor | ||
4 | Name | Value | Units | Value | Units | |||
5 | EAF | Hexachlorobenzene | UNEP, 2013. Table III.18.2 (p. 231). | Dirty scrap (cutting oils, general contamination), scrap preheating, limited controls. *Medium level of confidence indicated* | 2500 | μg/metric ton LS | 5.00E-06 | lb/ton metal melted |
6 | EAF | Hexachlorobenzene | UNEP, 2013. Table III.18.2 (p. 231). | Clean scrap/virgin iron or dirty scrap, afterburner and fabric filter. *Medium level of confidence indicated* | 2500 | μg/metric ton LS | 5.00E-06 | lb/ton metal melted |
A | B | C | D | E | F | G | H | |
---|---|---|---|---|---|---|---|---|
1 | Attachment B. Emission Factor Details: PBDEs | |||||||
3 | Emission Unit | Pollutant | Emission Factor Source | Notes | Emission Factor | Converted Emission Factor | ||
4 | Name | Value | Units | Value | Units | |||
5 | EAF | PBDEs | Wang et al. 2010. Table S10. | Average of 6 EAFs with bag filter control. | 531 | μg/metric ton feedstock | 1.06E-06 | lb/ton metal melted |
6 | EAF | PBDEs | Wu et al. 2014. Table 6. | EAF melting scrap (104 tonne/hr), alloying agents (1.1 t/hr), flux (2.1 t/hr), and coke (1.8 t/hr). Producing carbon steel at rate of 100 t/hr. Baghouse control devices. | 24 | μg/metric ton feedstock | 4.80E-08 | lb/ton metal melted |
7 | EAF | PBDEs | Wang et al., 2010; Wu et al., 2014. | Average of emission factors. | 277.5 | μg/metric ton feedstock | 5.55E-07 | lb/ton metal melted |
A | B | C | D | E | F | G | H | I | J | K | L | |
---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Attachment A. Emission Factors for Persistent Organic Pollutants and Polycyclic Aromatic Hydrocarbons | |||||||||||
3 | TAC | CASRN or DEQ SEQ ID | Basis | Value | Units | Reference | BH-1 (lb/ton) | BH-1A (lb/ton) | BH-2 (lb/ton) | BH-1 (lb/ton) | BH-1A (lb/ton) | BH-2 (lb/ton) |
4 | Melt Shop - Electric Arc Furnace (EAF) | Allocation1 | in tons steel produced | |||||||||
5 | ||||||||||||
6 | ||||||||||||
7 | ||||||||||||
8 | Naphthalene | 91-20-3 | Total Mass | 2.04E-03 | lb/ton metal melted | Lee et al., 1999. Table 7. | 2.04E-03 | 4.09E-04 | 2.45E-04 | 2.26E-03 | 4.54E-04 | 2.72E-04 |
9 | ||||||||||||
10 | Hexachlorobenzene | 118-74-1 | Total Mass | 5.00E-06 | lb/ton metal melted | UNEP, 2013. Table III.18.2. | 5.00E-06 | 1.00E-06 | 6.00E-07 | 5.55E-06 | 1.11E-06 | 6.66E-07 |
11 | PBDEs | 447 | Total Mass | 5.55E-07 | lb/ton metal melted | Wang et al. 2010, Table S10; Wu et al., Table 6. Average of emission factors. | 5.55E-07 | 1.11E-07 | 6.66E-08 | 6.16E-07 | 1.24E-07 | 7.40E-08 |
12 | Slag Concentrations | |||||||||||
13 | PCDD/Fs TEQ | 646 | TEQ | 1.03E-08 | lb TEQ/ton slag | Remus et al., 2013. Table 8-9. | 1Allocation method same as DEQ suggested approach for other organic TACs | |||||
14 | PCBs TEQ | 645 | TEQ | 1.03E-09 | lb TEQ/ton slag | Remus et al., 2013. Table 8-9. | See "Organic TAC Efs" tab. | |||||
16 | Notes: | |||||||||||
17 | BaPeq = Benzo[a]pyrene-equivalent | |||||||||||
18 | PAH = Polycyclic aromatic hydrocarbons | |||||||||||
19 | PBDE = Polybrominated diphenyl ether | |||||||||||
20 | PCDD/Fs = Polychlorinated dibenzo-p-dioxins (PCDDs) & dibenzofurans (PCDFs) | |||||||||||
21 | PCB = Polychlorinated biphenyls | |||||||||||
22 | TAC = Toxic Air Contaminant | |||||||||||
23 | TEQ = Toxic Equivalency | |||||||||||
24 | Strikethough data is not used in the emission calculations. Site specific data has been obtained an will be used. | |||||||||||
26 | References: | |||||||||||
27 | Lee, W. J., Lai, S. O., Chen, S. J., & Hsueh, H. J. (1999). PAH emission from the steel and iron industries. WIT Transactions on Ecology and the Environment, 37. | |||||||||||
29 | Remus, R., Aguado Monsonet, M.A., Roudier, S., Delgado Sancho, L. (2013). Best Available Techniques (BAT) Reference Document for Iron and Steel Production. European Commission Joint Research Committee Industrial Emissions Directive 2010/75/EU. | |||||||||||
30 | https://publications.jrc.ec.europa.eu/repository/bitstream/JRC69967/lfna25521enn.pdf | |||||||||||
32 | TAMCO Amended AB2588 Health Risk Assessment, Prepared by Environ International Corporation, Los Angeles, CA, January 2015. | |||||||||||
33 | https://www.aqmd.gov/docs/default-source/planning/risk-assessment/gerdau/final-approved-hra-(jan-2015).pdf?sfvrsn=2 | |||||||||||
35 | UN Environment Programme (UNEP). (2013). Toolkit for identification and quantification of releases of dioxins, furans and other unintentional POPs. | |||||||||||
36 | http://toolkit.pops.int/publish/Downloads/01-UNEP-POPS-TOOLKIT-2012-En.pdf | |||||||||||
38 | Wang, L. C., Lee, W. J., Lee, W. S., & Chang-Chien, G. P. (2010). Emission estimation and congener-specific characterization of polybrominated diphenyl ethers from various stationary and mobile sources. Environmental Pollution, 158(10), 3108-3115. | |||||||||||
40 | Wu, E. M. Y., Wang, L. C., Lin, S. L., & Chang-Chien, G. P. (2014). Validation and characterization of persistent organic pollutant emissions from stack flue gases of an electric arc furnace by using a long-term sampling system (AMESA®). Aerosol and Air Quality Research, 14(1), 185-196. | |||||||||||
43 | TAC | CASRN or DEQ SEQ ID | Basis | Value | Units | Reference | BH-1 (lb/ton) | BH-1A (lb/ton) | BH-2 (lb/ton) | BH-1 (lb/ton) | BH-1A (lb/ton) | BH-2 (lb/ton) |
44 | Melt Shop - Electric Arc Furnace (EAF) | Allocation1 | in tons steel produced | |||||||||
45 | PCDD/Fs TEQ | 646 | TEQ | 1.58E-09 | lb TEQ/ton steel produced | TAMCO Amended AB2588 Health Risk Assessment, January 2015. Appendix B-1a & -1b. | 1.58E-09 | 3.17E-10 | 1.90E-10 | 1.58E-09 | 3.17E-10 | 1.90E-10 |
46 | PCBs TEQ | 645 | TEQ | 3.57E-10 | lb TEQ/ton metal melted | Wu et al., 2014, Table 6; Remus et al., 2013, Table 8.4. Average of emission factors. | 3.57E-10 | 7.16E-11 | 4.28E-11 | 3.97E-10 | 7.95E-11 | 4.76E-11 |
47 | PAHs | 401 | BaPeq | 1.96E-05 | lb BaPeq/ton metal melted | Lee et al., 1999. Table 7. | 1.96E-05 | 3.92E-06 | 2.35E-06 | 2.17E-05 | 4.36E-06 | 2.61E-06 |
48 | Naphthalene | 91-20-3 | Total Mass | 2.04E-03 | lb/ton metal melted | Lee et al., 1999. Table 7. | 2.04E-03 | 4.09E-04 | 2.45E-04 | 2.26E-03 | 4.54E-04 | 2.72E-04 |
49 | Benzo[a]pyrene | 50-32-8 | Total Mass | 1.38E-06 | lb/ton metal melted | Lee et al., 1999. Table 7. | 1.38E-06 | 2.77E-07 | 1.66E-07 | 1.54E-06 | 3.08E-07 | 1.84E-07 |
50 | Hexachlorobenzene | 118-74-1 | Total Mass | 5.00E-06 | lb/ton metal melted | UNEP, 2013. Table III.18.2. | 5.00E-06 | 1.00E-06 | 6.00E-07 | 5.55E-06 | 1.11E-06 | 6.66E-07 |
51 | PBDEs | 447 | Total Mass | 5.55E-07 | lb/ton metal melted | Wang et al. 2010, Table S10; Wu et al., Table 6. Average of emission factors. | 5.55E-07 | 1.11E-07 | 6.66E-08 | 6.16E-07 | 1.24E-07 | 7.40E-08 |
52 | Slag Concentrations | |||||||||||
53 | PCDD/Fs TEQ | 646 | TEQ | 1.03E-08 | lb TEQ/ton slag | Remus et al., 2013. Table 8-9. | 1Allocation method same as DEQ suggested approach for other organic TACs | |||||
54 | PCBs TEQ | 645 | TEQ | 1.03E-09 | lb TEQ/ton slag | Remus et al., 2013. Table 8-9. | See "Organic TAC Efs" tab. |
A | B | C | D | E | F | G | H | |
---|---|---|---|---|---|---|---|---|
1 | Cascade Steel Rolling Mills CAO ATEI | |||||||
2 | Supporting Data Reduction - Baghouse PM Source Test Data Summary | |||||||
3 | ||||||||
4 | ||||||||
5 | Baghouse 1/1A | Baghouse 2 | ||||||
6 | Date of Source Test | lb/hour | lb/ton | kg/ton | Date | lb/hour | lb/ton | kg/ton |
7 | 6/8/2006 | 2.2 | 0.02 | 0.0091 | 6/6/2006 | 0.098 | 0.009 | 0.0041 |
8 | 6/6/2007 | 0.56 | 0.0048 | 0.0022 | 6/8/2007 | 0.068 | 0.0005 | 0.0002 |
9 | 5/6/2008 | 4.89 | 0.035 | 0.0159 | 5/5/2008 | 2.6 | 0.0218 | 0.0099 |
10 | 4/14/2009 | 2.1 | 0.017 | 0.0077 | 4/14/2009 | 0.12 | 0.0011 | 0.0005 |
11 | 5/11/2010 | 1.72 | 0.015 | 0.0068 | 5/11/2010 | 0.16 | 0.0016 | 0.0007 |
12 | 5/9/2011 | 0.17 | 0.0017 | 0.0008 | 5/9/2011 | 0.72 | 0.0072 | 0.0033 |
13 | 5/29/2012 | 0.3 | 0.0026 | 0.0012 | 5/30/2012 | 0.58 | 0.0049 | 0.0022 |
14 | 5/21/2013 | 1.06 | 0.0081 | 0.0037 | 5/22/2013 | 0.0317 | 0.00025 | 0.0001 |
15 | 5/19/2016 | 2.3 | 0.021 | 0.0095 | 5/17/2001 | 0.035 | 0.00031 | 0.0001 |
16 | Average | 1.70 | 0.014 | 0.0063 | Average | 0.490 | 0.005 | 0.0024 |
17 | ||||||||
18 | ||||||||
19 | ||||||||
20 | ||||||||
21 | ||||||||
22 | ||||||||
23 | ||||||||
24 |
A | B | C | D | E | |
---|---|---|---|---|---|
1 | Cascade Steel Rolling Mills CAO ATEI | ||||
2 | Supporting Data Reduction - Summary of Baghouse Dust D/F and PCB Analytical Results | ||||
3 | |||||
4 | |||||
5 | |||||
6 | |||||
7 | |||||
8 | |||||
9 | Location | Date | PCDD/PCDF TEQ (pg/g) | PCB TEQ (pg/g) | Total PCB (pg/g) |
10 | Baghouse 1/1A | 5/10/2023 | 502 | 25.5 | 26400 |
11 | 4/13/2023 | 738 | 36.4 | 27200 | |
12 | Average | 620 | 31.0 | 26800 | |
13 | Baghouse 2 | 5/10/2023 | 196 | 15.6 | 161000 |
14 | 4/13/2023 | 215 | 19.3 | 160000 | |
15 | Average | 206 | 17.45 | 160500 | |
16 | |||||
17 | Abbreviations | ||||
18 | PCDD/Fs = Polychlorinated dibenzo-p-dioxins (PCDDs) & dibenzofurans (PCDFs) | ||||
19 | PCB = Polychlorinated biphenyls | ||||
20 | TEQ = Toxic Equivalency |
A | B | C | D | E | F | G | H | I | J | K | L | M | N | O | P | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Cascade Steel Rolling Mills CAO ATEI | |||||||||||||||
2 | Supporting Data Reduction - Summary of Baghouse Dust PAH Analytical Results | |||||||||||||||
3 | ||||||||||||||||
4 | ||||||||||||||||
5 | ||||||||||||||||
6 | ||||||||||||||||
7 | ||||||||||||||||
8 | Individual EFs for 11/14/23 Submittal | |||||||||||||||
9 | Polycyclic Aromatic Hydrocarbon | Toxic Equivalency Factor (TEF) | Bahgouse 1 5/10/23 (ug/kg) | Baghouse Dust 1 4/13/23 (ug/kg) | Baghouse 1 Average (ug/kg) | Baghouse 1 Average BAPe (ug/kg) | Baghouse 2 5/10/23 (ug/kg) | Baghouse Dust 2 4/13/23 (ug/kg) | Baghouse 2 Average (ug/kg) | Baghouse 2 Average BAPe (ug/kg) | Baghouse 1/1A BAPe (ug/kg) | Baghouse 2 BAPe (ug/kg) | Baghouse 1 (lb/ton) | Baghouse 1A (lb/ton) | Baghouse 2 (lb/ton) | Remark |
10 | Acenaphthene | -- | <4.9 | <4.9 | <4.9 | -- | 20 | 23 | 21.5 | -- | -- | -- | 6.83E-11 | 1.37E-11 | 1.04E-10 | * |
11 | Acenaphthylene | -- | 14 | 9.1 | 11.55 | -- | 97 | 93 | 95 | -- | -- | -- | 1.95E-10 | 3.91E-11 | 5.04E-10 | * |
12 | Anthracene | 0 | <4.9 | <4.9 | <4.9 | 0 | 190 | 210 | 200 | 0 | 0 | 0 | 6.83E-11 | 1.37E-11 | 9.87E-10 | |
13 | Benz[a]anthracene | 0.2 | 8.5 | 9.1 | 8.8 | 1.76 | 1600 | 1800 | 1700 | 340 | 1.7 | 320 | 1.18E-10 | 2.38E-11 | 8.31E-09 | |
14 | Benzo[a]pyrene | 1 | <4.9 | 5.3 | 5.1 | 5.1 | 1100 | 1200 | 1150 | 1150 | 4.9 | 1100 | 6.83E-11 | 1.37E-11 | 5.72E-09 | |
15 | Benzo[b]fluoranthene | 0.8 | 27 | 39 | 33 | 26.4 | 4400 | 4800 | 4600 | 3680 | 21.6 | 3520 | 3.76E-10 | 7.55E-11 | 2.29E-08 | |
16 | Benzo[e]pyrene | -- | 16 | 21 | 18.5 | -- | 2700 | 2900 | 2800 | -- | -- | -- | 2.23E-10 | 4.47E-11 | 1.40E-08 | * |
17 | Benzo[g,h,i]perylene | 0.009 | 7.8 | 12 | 9.9 | 0.0891 | 2500 | 2700 | 2600 | 23.4 | 0.0702 | 22.5 | 1.09E-10 | 2.18E-11 | 1.30E-08 | |
18 | Benzo[k]fluoranthene | 0.03 | 6.5 | 8.4 | 7.45 | 0.2235 | 1000 | 1200 | 1100 | 33 | 0.195 | 30 | 9.06E-11 | 1.82E-11 | 5.20E-09 | |
19 | Chrysene | 0.1 | 38 | 43 | 40.5 | 4.05 | 3500 | 3800 | 3650 | 365 | 3.8 | 350 | 5.30E-10 | 1.06E-10 | 1.82E-08 | |
20 | Dibenz[a,h]anthracene | 10 | <4.9 | <4.9 | <4.9 | 49 | 300 | 350 | 325 | 3250 | 49 | 3000 | 6.83E-11 | 1.37E-11 | 1.56E-09 | |
21 | Fluoranthene | 0.08 | 130 | 120 | 125 | 10 | 5500 | 6100 | 5800 | 464 | 10.4 | 440 | 1.81E-09 | 3.63E-10 | 2.86E-08 | |
22 | Fluorene | -- | 13 | 8.5 | 10.75 | -- | 74 | 83 | 78.5 | -- | -- | -- | 1.81E-10 | 3.63E-11 | 3.84E-10 | * |
23 | Indeno[1,2,3-cd]pyrene | 0.07 | 5.5 | 11 | 8.25 | 0.5775 | 2700 | 2900 | 2800 | 196 | 0.385 | 189 | 7.67E-11 | 1.54E-11 | 1.40E-08 | |
24 | Naphthalene | -- | 21 | 18 | 19.5 | -- | 140 | 160 | 150 | -- | -- | -- | 2.93E-10 | 5.87E-11 | 7.27E-10 | ** |
25 | Perylene | -- | <4.9 | <4.9 | <4.9 | -- | 300 | 340 | 320 | -- | -- | -- | 6.83E-11 | 1.37E-11 | 1.56E-09 | * |
26 | Phenanthrene | 0 | 130 | 92 | 111 | 0 | 1500 | 1600 | 1550 | 0 | 0 | 0 | 1.81E-09 | 3.63E-10 | 7.79E-09 | * |
27 | Pyrene | 0 | 72 | 51 | 61.5 | 0 | 4600 | 4800 | 4700 | 0 | 0 | 0 | 1.00E-09 | 2.01E-10 | 2.39E-08 | * |
28 | TOTAL | 97.2 | 9501 | 92.1 | 8972 | |||||||||||
29 | ||||||||||||||||
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41 |
A | B | C | D | E | F | G | H | I | J | K | |
---|---|---|---|---|---|---|---|---|---|---|---|
1 | Cascade Steel Rolling Mills CAO ATEI | ||||||||||
2 | Supporting Data Reduction - Derivation of DF, PCB, PAH Emission Factors | ||||||||||
3 | |||||||||||
4 | |||||||||||
5 | |||||||||||
6 | |||||||||||
7 | |||||||||||
8 | |||||||||||
9 | |||||||||||
10 | |||||||||||
11 | |||||||||||
12 | Baghouse 1/1A Combined | ||||||||||
13 | |||||||||||
14 | Baghouse Dust Analytical Results | Emission Factors | |||||||||
15 | PM EF (kg/ton) | PCDD/PCDF TEQ (pg/g) | PCB TEQ (pg/g) | Total PCB (pg/g) |
PAH (ug/kg) |
Benzo(a)pyrene (ug/kg) |
PCDD/PCDF TEQ (lb/ton) | PCB TEQ (lb/ton) | Total PCB (lb/ton) |
PAH (lb/ton) |
Benzo(a)pyrene (lb/ton) |
16 | 0.0063 | 620 | 31.0 | 26800 | 92.1 | 4.9 | 8.64E-12 | 4.31E-13 | 3.74E-10 | 1.28E-09 | 6.83E-11 |
17 | |||||||||||
18 | BH1 Emission Factors | ||||||||||
19 | PCDD/PCDF TEQ (lb/ton) | PCB TEQ (lb/ton) | Total PCB (lb/ton) |
PAH (lb/ton) |
Benzo(a)pyrene (lb/ton) |
||||||
20 | 8.64E-12 | 4.31E-13 | 3.74E-10 | 1.28E-09 | 6.83E-11 | ||||||
21 | |||||||||||
22 | BH1A Emission Factors | ||||||||||
23 | PCDD/PCDF TEQ (lb/ton) | PCB TEQ (lb/ton) | Total PCB (lb/ton) |
PAH (lb/ton) |
Benzo(a)pyrene (lb/ton) |
||||||
24 | 1.73E-12 | 8.65E-14 | 7.49E-11 | 2.57E-10 | 1.37E-11 | ||||||
25 | |||||||||||
26 | |||||||||||
27 | Baghouse 2 | ||||||||||
28 | |||||||||||
29 | Baghouse Dust Analytical Results | Baghouse 2 Emission Factors | |||||||||
30 | PM EF (kg/ton) | PCDD/PCDF TEQ (pg/g) | PCB TEQ (pg/g) | Total PCB (pg/g) |
PAH (ug/kg) |
Benzo(a)pyrene (ug/kg) |
PCDD/PCDF TEQ (lb/ton) | PCB TEQ (lb/ton) | Total PCB (lb/ton) |
PAH (lb/ton) |
Benzo(a)pyrene (lb/ton) |
31 | 0.0024 | 206 | 17 | 160500 | 8972 | 1100 | 1.07E-12 | 9.07E-14 | 8.34E-10 | 4.66E-08 | 5.72E-09 |
B | C | D | E | F | G | H | I | J | K | L | M | N | O | P | Q | R | S | T | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | |||||||||||||||||||
2 | Estimating Emissions from Horizontal Tank | ||||||||||||||||||
3 | Enter tank specific information in all blue cells. | ||||||||||||||||||
4 | |||||||||||||||||||
5 | Tank information | ||||||||||||||||||
6 | Tank identification | TEU EU-15 | |||||||||||||||||
7 | Description | 6,000 Gallon Unleaded Gasoline Storage Tank | |||||||||||||||||
8 | Facility Name | CSRM | |||||||||||||||||
9 | |||||||||||||||||||
10 | Property | Value | Units | Description | About the value | ||||||||||||||
11 | Product Stored | A. Motor gasoline RVP 13 | select one | Type of fuel stored in the tank. | Choose "Gasoline" or "Diesel" from the drop-down box. | ||||||||||||||
12 | Chemical Stored | ||||||||||||||||||
13 | Storage tank position | Above | select one | Fixed roof structure. | Choose "Above" or "Under" from the drop-down box. | ||||||||||||||
14 | Annual throughput | 10,000 | gal/yr | Gallons stored in his tank over the period of 12 consecutive months. | |||||||||||||||
15 | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec | |||||||
16 | Or Monthly throughput | 6,000 | 6,000 | 6,000 | 6,000 | 6,000 | 6,000 | 6,000 | 6,000 | 6,000 | 6,000 | 6,000 | 6,000 | ||||||
17 | Maximum annual throughput is less than 10,000 gal/yr. Maximum monthly throughput is less than 3,000 gal./mo. with zero gallons added to the tank 5-7 months of the year. | ||||||||||||||||||
18 | |||||||||||||||||||
19 | Physical properties of the tank | ||||||||||||||||||
20 | Property | Value | Units | Description | About the value | ||||||||||||||
21 | Shell length | HS | 17 | feet | This is actual length of the tank. | Use the outside height of the tank. | |||||||||||||
22 | Shell diameter | D | 9.17 | feet | This is the actual width of the cylindrical shell. | Use the outside diameter of the tank. | |||||||||||||
23 | Shell effective height | HE | 7.20 | feet | Calculated effective height of the tank. | ||||||||||||||
24 | Shell effective diameter | DE | 14.09 | feet | Calculated effective diameter of the cylindrical shell. | ||||||||||||||
25 | Shell radius | RS | 4.585 | feet | Calculated radius | The shell diameter divided by 2. | |||||||||||||
26 | Working volume | 8398.1 | gallons | Calculated volume | Area = ∏*(DE/2)2 * shell effective height (SE). Conversion factor: 7.48 gallon/ft3. | ||||||||||||||
27 | Turnovers per year (actual) | N | 1.2 | dimensionless | Calculated number the tank is emptied and refilled, annually. | Actual throughput and working volume. Value = "0" if liquid is stored for an entire year. | |||||||||||||
28 | Shell color/shade | J. Red - primer | select one | Tank shell color and shade are used to identify paint solar absorptance. | Default value is "White/NA". Go to Table 7.1-6. | A. New | 3 | 4 | (determines column in | ||||||||||
29 | Shell condition | B. Average | select one | Tank condition is used to identify paint solar absorptance. Only aboveground. | Default value is "Average" Go to Table 7.1-6. | B. Average | 4 | Table 7.1-6) | |||||||||||
30 | Paint solar absorptance | α | 0.90 | dimensionless | Paint effectiveness in absorbing radiant energy. | Default value for "White/NA", "Average" condition tank is: 0.25. Go to Table 7.1-6. | C. Aged | 5 | |||||||||||
31 | Vacuum setting | PBV | -0.03 | psig | Vacuum setting is a value set for the tank at the facility. | Must be between 0 and -1 psig. Default value is -0.03 psig. | |||||||||||||
32 | Pressure setting | PBP | 0.03 | psig | Breather vent pressure is a reading from the tank monitoring system. | Must be between 0 and 1 psig. Default value is 0.03 psig. | |||||||||||||
33 | |||||||||||||||||||
34 | |||||||||||||||||||
35 | Weather data | ||||||||||||||||||
36 | Property | Value | Units | Description | About the value | ||||||||||||||
37 | Nearest major city | Salem, OR | Select one | Nearest major city to the tank location. | Go to Table 7.1-7. | ||||||||||||||
38 | Average annual maximum temperature | TAX | 63.0 | °F | Average over a calendar year. | Go to Table 7.1-7. | |||||||||||||
39 | Average annual minimum temperature | TAN | 43.8 | °F | Average over a calendar year. | Go to Table 7.1-7. | |||||||||||||
40 | Atmospheric pressure | PA | 14.6 | psia | Average for the location. | Barometric pressure of 29.9 inches of mercury is approximately 14.7 psia. | |||||||||||||
41 | Solar insolation | I | 1145.3 | Btu/(ft2·day) | Total for a horizontal surface. | Go to Table 7.1-7. | |||||||||||||
42 | |||||||||||||||||||
43 | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec | |||||||
44 | estimated daily maximum ambient temperature, °F | TAX | 47.4 | 51.6 | 55.6 | 59.9 | 67.1 | 72.6 | 81.8 | 81.3 | 76.3 | 63.4 | 52.2 | 46.6 | |||||
45 | estimated daily minimum ambient temperature, °F | TAN | 36.0 | 35.9 | 38.3 | 40.9 | 46.1 | 50.3 | 54.9 | 54.3 | 50.2 | 43.7 | 39.4 | 35.7 | |||||
46 | Average atmospheric pressure, psia | PA | 14.6 | 14.6 | 14.6 | 14.6 | 14.6 | 14.6 | 14.6 | 14.6 | 14.6 | 14.6 | 14.6 | 14.6 | |||||
47 | average daily total insolation factor, Btu/(ft2*day) | I | 370.0 | 638.0 | 951.0 | 1355.0 | 1703.0 | 1859.0 | 2099.0 | 1846.0 | 1392.0 | 807.0 | 416.0 | 307.0 | |||||
48 | |||||||||||||||||||
49 | |||||||||||||||||||
50 | Calculation of VOC Emission = Total Losses (LT) | Calculated value |
51 | Variable | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec | Notes (equations are from AP-42, Chapter 7) | |||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | Total losses (VOC actual emissions) | LT | 264.05 | 244.72 | 264.30 | 257.77 | 264.30 | 257.77 | 264.30 | 264.30 | 257.77 | 264.30 | 257.77 | 264.30 | 3,125.64 | lb/yr | Equation 1-1 | ||
53 | Standing storage losses | LS | 202.26 | 182.69 | 202.26 | 195.74 | 202.26 | 195.74 | 202.26 | 202.26 | 195.74 | 202.26 | 195.74 | 202.26 | 2,381.48 | lb/yr | Equation 1-2 | ||
54 | Working losses (actual) | LW | 61.79 | 62.03 | 62.03 | 62.03 | 62.03 | 62.03 | 62.03 | 62.03 | 62.03 | 62.03 | 62.03 | 62.03 | 744.16 | lb/yr | Equation 1-35 | ||
55 | Annual net throughput (actual) | Q | 142.86 | 142.86 | 142.86 | 142.86 | 142.86 | 142.86 | 142.86 | 142.86 | 142.86 | 142.86 | 142.86 | 142.86 | bbl/yr | Based on actual throughput entered by user (gal/year) / 42 bbl/gal | |||
56 | Working loss turnover factor (actual) | KN | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | dimensionless | Saturation; turnovers >36 = (180 + N) / 6N; turnovers at 36 or lower = 1 | |||
57 | Stock vapor density | WV | 0.08 | 0.08 | 0.08 | 0.08 | 0.08 | 0.08 | 0.08 | 0.08 | 0.08 | 0.08 | 0.08 | 0.08 | lb/ft3 | Equation 1-22 | |||
58 | Vapor Molecular Weight at 60 °F | MV | 62.0 | 62.0 | 62.0 | 62.0 | 62.0 | 62.0 | 62.0 | 62.0 | 62.0 | 62.0 | 62.0 | 62.0 | lb/lb-mole | Table 7.1-2 | |||
59 | Vapor pressure | PVA | 7.00569 | 7.00569 | 7.00569 | 7.00569 | 7.00569 | 7.00569 | 7.00569 | 7.00569 | 7.00569 | 7.00569 | 7.00569 | 7.00569 | psia | Equation 1-25, PVA based on TLA | |||
60 | Vapor space volume | VV | 561.37 | 561.37 | 561.37 | 561.37 | 561.37 | 561.37 | 561.37 | 561.37 | 561.37 | 561.37 | 561.37 | 561.37 | ft3 | Equation 1-3 | |||
61 | Vapor space tank outage | HVO | 3.60 | 3.60 | 3.60 | 3.60 | 3.60 | 3.60 | 3.60 | 3.60 | 3.60 | 3.60 | 3.60 | 3.60 | feet | Equation 1-16, note for HVO horizontal | |||
62 | Vapor space expansion factor | KE | 0.351 | 0.351 | 0.351 | 0.351 | 0.351 | 0.351 | 0.351 | 0.351 | 0.351 | 0.351 | 0.351 | 0.351 | dimensionless | Equation 1-5 | |||
63 | Vented vapor saturation factor | KS | 0.43 | 0.43 | 0.43 | 0.43 | 0.43 | 0.43 | 0.43 | 0.43 | 0.43 | 0.43 | 0.43 | 0.43 | dimensionless | Equation 1-21 | |||
64 | Vent setting correction factor | KB | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | 1.00 | dimensionless | Equation 1-41, breather vent setting greater than 0.3 psig | |||
65 | Working loss product factor | KP | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | dimensionless | Assume value of 1 for gasoline or diesel. | |||
66 | Ideal gas constant | R | 10.731 | 10.731 | 10.731 | 10.731 | 10.731 | 10.731 | 10.731 | 10.731 | 10.731 | 10.731 | 10.731 | 10.731 | psia*ft3/lb-mole*°R | Constant, Equation 1-22 | |||
67 | Average vapor temperature | TV | 523.30 | 523.30 | 523.30 | 523.30 | 523.30 | 523.30 | 523.30 | 523.30 | 523.30 | 523.30 | 523.30 | 523.30 | °R | Equation 1-33 | |||
68 | Daily average liquid surface temperature | TLA | 520.10 | 520.10 | 520.10 | 520.10 | 520.10 | 520.10 | 520.10 | 520.10 | 520.10 | 520.10 | 520.10 | 520.10 | °R | Equation 1-28 | |||
69 | Daily vapor temperature range | ΔTV | 34.04 | 34.04 | 34.04 | 34.04 | 34.04 | 34.04 | 34.04 | 34.04 | 34.04 | 34.04 | 34.04 | 34.04 | °R | Equation 1-7 | |||
70 | Daily ambient temperature range | ΔTA | 19.18 | 19.18 | 19.18 | 19.18 | 19.18 | 19.18 | 19.18 | 19.18 | 19.18 | 19.18 | 19.18 | 19.18 | °R | Equation 1-11 | |||
71 | Daily maximum ambient temperature | TAX | 522.68 | 522.68 | 522.68 | 522.68 | 522.68 | 522.68 | 522.68 | 522.68 | 522.68 | 522.68 | 522.68 | 522.68 | °R | Table 7-1-7. Conversion factor: Rankine = Fahrenheit + 459.7 | |||
72 | Daily minimum ambient temperature | TAN | 503.51 | 503.51 | 503.51 | 503.51 | 503.51 | 503.51 | 503.51 | 503.51 | 503.51 | 503.51 | 503.51 | 503.51 | °R | Table 7-1-7. Conversion factor: Rankine = Fahrenheit + 459.7 | |||
73 | Daily average ambient temperature | TAA | 513.10 | 513.10 | 513.10 | 513.10 | 513.10 | 513.10 | 513.10 | 513.10 | 513.10 | 513.10 | 513.10 | 513.10 | °R | Equation 1-30 | |||
74 | Liquid bulk temperature | TB | 516.19 | 516.19 | 516.19 | 516.19 | 516.19 | 516.19 | 516.19 | 516.19 | 516.19 | 516.19 | 516.19 | 516.19 | °R | Equation 1-31 | |||
75 | Daily vapor pressure range | ΔPV | 2.23 | 2.23 | 2.23 | 2.23 | 2.23 | 2.23 | 2.23 | 2.23 | 2.23 | 2.23 | 2.23 | 2.23 | psia | Equation 1-9 | |||
76 | Breather vent pressure setting range | ΔPB | 0.06 | 0.06 | 0.06 | 0.06 | 0.06 | 0.06 | 0.06 | 0.06 | 0.06 | 0.06 | 0.06 | 0.06 | psi | Equation 1-10 | |||
77 | Vapor pressure equation constant | A | 11.6 | 11.6 | 11.6 | 11.6 | 11.6 | 11.6 | 11.6 | 11.6 | 11.6 | 11.6 | 11.6 | 11.6 | dimensionless | Table 7.1-2 | |||
78 | Vapor pressure equation constant | B | 5043.6 | 5043.6 | 5043.6 | 5043.6 | 5043.6 | 5043.6 | 5043.6 | 5043.6 | 5043.6 | 5043.6 | 5043.6 | 5043.6 | °R | Table 7.1-2 | |||
79 | Antoine's Eq Constant | A | dimensionless | ||||||||||||||||
80 | Antoine's Eq Constant | B | °C | ||||||||||||||||
81 | Antoine's Eq Constant | C | °C | ||||||||||||||||
82 | Partial Pressure of chemical selected | pi | mm Hg | ||||||||||||||||
83 | Vapor Mole Fraction of chemical selected | yi | assumes chemical stored is sole product and not a mixture | ||||||||||||||||
84 | Vapor pressure at TLX | PVX | 8.1893 | 8.1893 | 8.1893 | 8.1893 | 8.1893 | 8.1893 | 8.1893 | 8.1893 | 8.1893 | 8.1893 | 8.1893 | 8.1893 | psia | Equation 1-9, note 5 | |||
85 | Vapor pressure at TLN | PVN | 5.9621 | 5.9621 | 5.9621 | 5.9621 | 5.9621 | 5.9621 | 5.9621 | 5.9621 | 5.9621 | 5.9621 | 5.9621 | 5.9621 | psia | Equation 1-9, note 5 | |||
86 | Maximum TLA | TLX | 528.61 | 528.61 | 528.61 | 528.61 | 528.61 | 528.61 | 528.61 | 528.61 | 528.61 | 528.61 | 528.61 | 528.61 | °R | Equation 1-9, note to Figure 7.1-17 | |||
87 | Minimum TLA | TLN | 511.60 | 511.60 | 511.60 | 511.60 | 511.60 | 511.60 | 511.60 | 511.60 | 511.60 | 511.60 | 511.60 | 511.60 | °R | Equation 1-9, note to Figure 7.1-17 |
B | C | D | E | F | G | H | I | J | K | L | M | N | O | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | ||||||||||||||
2 | Reference tables from AP-42, chapter 7 | |||||||||||||
3 | AP-42, Chapter 7 (updated June 2020) | https://www3.epa.gov/ttn/chief/ap42/ch07/final/ch07s01.pdf | ||||||||||||
5 | Table 7.1-2 Properties of selected petroleum liquids at 60°F | |||||||||||||
7 | Petroleum liquid | Vapor molecular weight | Liquid molecular weight b | Liquid density | Vapor pressure equation constant | Vapor pressure equation constant | True vapor pressure | |||||||
8 | ||||||||||||||
9 | MV | ML | WL | A | B | PVA | ||||||||
10 | (lb/lb-mole) | lb/lb-mole | (lb/gal) | (dimensionless) | (°R) | (psi) | ||||||||
11 | A. Motor gasoline RVP 13 | 62 | 92 | 5.6 | 11.644 | 5043.6 | 7.0 | |||||||
12 | B. Motor gasoline RVP 10 | 66 | 92 | 5.6 | 11.724 | 5237.3 | 5.2 | |||||||
13 | C. Motor gasoline RVP 7 | 68 | 92 | 5.6 | 11.833 | 5500.6 | 3.5 | |||||||
14 | D. Jet naphtha (JP-4) | 80 | 120 | 6.4 | 11.368 | 5784.3 | 1.3 | |||||||
15 | E. Jet kerosene (Jet A) | 130 | 162 | 7.0 | 12.390 | 8933.0 | 0.008 | |||||||
16 | F. No. 2 fuel oil (diesel) | 130 | 188 | 7.1 | 12.101 | 8907.0 | 0.006 | |||||||
17 | G. No. 6 fuel oil | 130 | 387 | 7.9 | 10.781 | 8933.0 | 0.002 | |||||||
18 | H. Vacuum residual oil | 190 | 387 | 7.9 | 10.104 | 10475.5 | 0.0004 | |||||||
19 | I. Other. Next Question | |||||||||||||
23 | Table 7.1-6 Paint solar absorption for fixed roof tanks | |||||||||||||
24 | Paint Color | Paint shade or type | Reflective condition (α)1 | |||||||||||
25 | ||||||||||||||
26 | New | Average | Aged | Select one | ||||||||||
27 | A. White | 0.17 | 0.25 | 0.34 | Aluminum paint/Specular shade | |||||||||
28 | B. Aluminum - specular | 0.39 | 0.44 | 0.49 | Aluminum paint/Diffuse shade | |||||||||
29 | C. Aluminum - diffuse | 0.60 | 0.64 | 0.68 | Aluminum metal/unpainted | |||||||||
30 | D. Beige/cream | 0.35 | 0.42 | 0.49 | Beige/Cream/no shade | |||||||||
31 | E. Black | 0.97 | 0.97 | 0.97 | Black/no shade | |||||||||
32 | F. Brown | 0.58 | 0.62 | 0.67 | Brown/no shade | |||||||||
33 | G. Gray - light | 0.54 | 0.58 | 0.63 | Gray/Light shade | |||||||||
34 | H. Gray - medium | 0.68 | 0.71 | 0.74 | Gray/Medium shade | |||||||||
35 | I. Green - dark | 0.89 | 0.90 | 0.91 | Green/Dark shade | |||||||||
36 | J. Red - primer | 0.89 | 0.90 | 0.91 | Red/Primer shade | |||||||||
37 | K. Rust - red iron oxide | 0.38 | 0.44 | 0.50 | Rust/Red iron oxide shade | |||||||||
38 | L. Tan | 0.43 | 0.49 | 0.55 | Tan/no shade | |||||||||
39 | M. Aluminum - mill finish, unpainted | 0.10 | 0.12 | 0.15 | White/NA | |||||||||
40 | 1Reflective condition definitions | |||||||||||||
41 | New: For paint, paint still retains the fresh shine of having been recently applied; for mill-finished aluminum, surface is shiny. | |||||||||||||
42 | Average: For paint, paint is in good condition, but the initial shine has faded; for mill-finished aluminum, surface is oxidized but still bright. | |||||||||||||
43 | Aged: For paint, paint is noticeably faded and dull; for mill-finish aluminum, surface is dull. | |||||||||||||
44 | 2Refers to aluminum as the base metal, rather than aluminum colored paint. | |||||||||||||
47 | Table 7.1-3 Physical properties of selected petrochemicals a | |||||||||||||
48 | Chemical name | CAS registry no. | Molecular weight | Liquid densityd (lb/gal) | True vapor pressure at 60 °F (psia) | Antoine's equationb | Normal boiling point (°F) | |||||||
49 | Constants | Temperature range c | ||||||||||||
50 | A dimensionless | B (°C) | C (°C) | Minimum (°F) | Maximum (°F) | |||||||||
51 | Acetaldehyde | 00075-07-0 | 44.05 | 6.54 | 64 | 12.19 | 8.063 | 1,637.1 | 295.47 | 32 | 94 | 69 | ||
52 | Acetic acid | 00064-19-7 | 60.05 | 8.72 | 77 | 0.176 | 7.557 | 1,642.5 | 233.39 | 63 | 244 | 244 | ||
53 | Acetic anhydride {acetic acid anhydride} | 00108-24-7 | 102.09 | 9.03 | 0.053 | 7.122 | 1,427.8 | 198.04 | 145 | 283 | 282 | |||
54 | Acetone | 00067-64-1 | 58.08 | 6.55 | 77 | 2.921 | 7.300 | 1,312.3 | 240.71 | 7 | 454 | 133 | ||
55 | Acetonitrile | 00075-05-8 | 41.05 | 6.56 | 1.09 | 7.154 | 1,355.4 | 235.30 | 59 | 192 | 179 | |||
56 | Acrylamide | 00079-06-1 | 71.08 | 9.36 | 8.57E-05 | 11.293 | 3,939.9 | 273.16 | 379 | |||||
57 | Acrylic acid {2-propenoic acid} | 00079-10-7 | 72.06 | 8.77 | 1.344 | 5.652 | 648.6 | 154.68 | 68 | 158 | 282 |
58 | Acrylonitrile {2-propenenitrile} | 00107-13-1 | 53.06 | 6.73 | 1.383 | 6.942 | 1,255.9 | 231.30 | -60 | 172 | 172 | |||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
59 | Allyl alcohol | 00107-18-6 | 58.08 | 7.13 | 0.326 | 11.658 | 4,510.2 | 416.80 | 70 | 207 | 206 | |||
60 | Allyl chloride {3-chloro-1-propene} | 00107-05-1 | 76.52 | 7.83 | 4.702 | 5.297 | 418.4 | 128.68 | 55 | 111 | 113 | |||
61 | Aniline | 00062-53-3 | 93.13 | 8.53 | 0.0058 | 7.221 | 1,661.9 | 199.10 | 88 | 363 | 363 | |||
62 | Benzene | 00071-43-2 | 78.11 | 7.32 | 1.171 | 6.906 | 1,211.0 | 220.79 | 46 | 217 | 176 | |||
63 | Benz[a]anthracene | 00056-55-3 | 228.29 | 7.92E-10 | 11.528 | 5,461.0 | 273.15 | 219 | 260 | 820 | ||||
64 | Benzo[a]pyrene | 00050-32-8 | 252.31 | 2.29E-11 | 12.482 | 6,181.0 | 273.15 | 185 | 316 | 923 | ||||
65 | Benzo[ghi]perylene | 00191-24-2 | 276.33 | 2.07E-13 | 11.820 | 6,580.0 | 273.15 | 391 | 513 | |||||
66 | Biphenyl | 00092-52-4 | 154.21 | 8.68 | 2.37E-04 | 7.245 | 1,998.7 | 202.73 | 156 | 520 | 489 | |||
67 | Butadiene (1,3) {divinyl} | 00106-99-0 | 54.09 | 5.13 | 77 | 30.22 | 6.873 | 941.7 | 240.40 | -104 | 29 | 24 | ||
68 | Butane (n) | 00106-97-8 | 58.12 | 4.78 | 77 | 25.67 | 6.725 | 909.7 | 237.00 | -108 | 31 | 32 | ||
69 | Butene (1) | 00106-98-9 | 56.11 | 4.91 | 77 | 30.83 | 7.122 | 1,099.2 | 264.89 | -108 | 25 | 21 | ||
70 | Butene (cis-2) | 00590-18-1 | 56.11 | 5.14 | 77 | 22.62 | 6.863 | 957.1 | 236.65 | -94 | 73 | 39 | ||
71 | Butene (2-methyl-1) | 00563-46-2 | 70.13 | 5.43 | 8.257 | 6.862 | 1,047.8 | 232.06 | 34 | 145 | 88 | |||
72 | Butene (trans-2) | 00624-64-6 | 56.11 | 5.00 | 77 | 24.97 | 6.919 | 982.2 | 242.38 | -97 | 34 | 34 | ||
73 | Butyl alcohol (n) {butanol (1)} | 00071-36-3 | 74.12 | 6.76 | 0.062 | 7.421 | 1,351.6 | 179.81 | 73 | 244 | 243 | |||
74 | Butyl alcohol (tert) {1,1-dimethyl ethanol} | 00075-65-0 | 74.12 | 6.58 | 0.424 | 7.373 | 1,174.9 | 179.23 | 103 | 180 | 180 | |||
75 | Butyl chloride (-n) {1-chloro-butane} | 00109-69-3 | 92.57 | 7.40 | 1.255 | 6.871 | 1,182.9 | 218.27 | 2 | 173 | 170 | |||
76 | Butyl ether (di-tert) | 06163-66-2 | 130.23 | 6.39 | 0.381 | 6.590 | 1,157.7 | 203.05 | 39 | 228 | 224 | |||
77 | Carbon disulfide | 00075-15-0 | 76.14 | 10.50 | 4.817 | 6.942 | 1,168.6 | 241.53 | 38 | 176 | 115 | |||
78 | Carbon tetrachloride | 00056-23-5 | 153.82 | 13.30 | 1.431 | 6.898 | 1,221.8 | 227.41 | 68 | 172 | 170 | |||
79 | Chlorobenzene | 00108-90-7 | 112.56 | 9.23 | 0.134 | 6.986 | 1,435.7 | 218.03 | 144 | 269 | 269 | |||
80 | Chlorobutane (2) | 00078-86-4 | 92.57 | 7.27 | 1.255 | 6.871 | 1,182.9 | 218.27 | 2 | 173 | 170 | |||
81 | Chloroform | 00067-66-3 | 119.38 | 12.30 | 2.468 | 7.083 | 1,233.1 | 232.20 | -73 | 142 | 142 | |||
82 | Chloroprene {2-chloro-1,3-butadiene} | 00126-99-8 | 88.54 | 7.98 | 2.736 | 6.291 | 841.9 | 187.79 | 68 | 140 | 140 | |||
83 | Chlorotoluene (o) {1-chloro-2methylbenzene} | 00095-49-8 | 126.58 | 9.04 | 0.039 | 7.363 | 1,768.1 | 234.76 | 42 | 319 | 318 | |||
84 | Chrysene {benzo[a]phenanthrene} | 00218-01-9 | 228.29 | 10.60 | 1.86E-11 | 12.320 | 6,160.0 | 273.15 | 185 | 374 | 838 | |||
85 | Cresol (m) {3-methyl-phenol} | 00108-39-4 | 108.14 | 8.63 | 0.0013 | 7.477 | 1,833.1 | 196.74 | 301 | 394 | 396 | |||
86 | Cresol (o) {2-methyl-phenol} | 00095-48-7 | 108.14 | 9.47 | 77 | 0.0016 | 6.843 | 1,391.3 | 160.18 | 248 | 376 | 376 | ||
87 | Cresol (p) {4-methyl-phenol} | 00106-44-5 | 108.14 | 8.50 | 104 | 0.00062 | 7.016 | 1,498.6 | 160.55 | 262 | 395 | 395 | ||
88 | Cyclohexane | 00110-82-7 | 84.16 | 6.46 | 77 | 1.212 | 6.845 | 1,203.5 | 222.86 | 68 | 179 | 177 | ||
89 | Cyclohexanol | 00108-93-0 | 100.16 | 8.03 | 0.0009 | 5.956 | 777.4 | 91.11 | 201 | 321 | 320 | |||
90 | Cyclohexanone | 00108-94-1 | 98.14 | 7.91 | 0.0042 | 5.978 | 1,495.5 | 209.55 | 193 | 330 | 311 | |||
91 | Cyclohexene | 00110-83-8 | 82.14 | 6.77 | 0.11 | 5.872 | 1,221.9 | 223.17 | 98 | 196 | 181 | |||
92 | Cyclopentane | 00287-92-3 | 70.13 | 6.22 | 4.171 | 6.878 | 1,119.2 | 230.74 | 60 | 122 | 121 | |||
93 | Cyclopentanone | 00120-92-3 | 84.12 | 7.92 | 0.13 | 3.958 | 376.4 | 104.65 | 32 | 78 | 266 | |||
94 | Cyclopentene | 00142-29-0 | 68.12 | 6.44 | 3.264 | 6.921 | 1,121.8 | 223.45 | 111 | |||||
95 | Decane (-n) | 00124-18-5 | 142.28 | 6.09 | 0.011 | 3.085 | 440.6 | 116.25 | -21 | 99 | 345 | |||
96 | Dibromopropane (1,2) | 00078-75-1 | 201.89 | 16.10 | 0.088 | 7.314 | 1,667.0 | 234.85 | 19 | 287 | 286 | |||
97 | Dibromopropane (1,3) | 00109-64-8 | 201.89 | 16.50 | 0.029 | 7.309 | 1,776.7 | 233.46 | 49 | 333 | 314 | |||
98 | Dichloroethane (1,1) | 00075-34-3 | 98.96 | 9.81 | 2.863 | 7.097 | 1,229.2 | 233.95 | -77 | 135 | 135 | |||
99 | Dichloroethane (1,2) | 00107-06-2 | 98.96 | 10.40 | 77 | 0.961 | 7.460 | 1,521.8 | 248.48 | -23 | 211 | 182 | ||
100 | Dichloroethylene (1,2) {1,2 dichloroethene} | 00540-59-0 | 96.94 | 10.70 | 2.579 | 7.022 | 1,205.4 | 230.60 | 32 | 183 | 141 | |||
101 | Dichloroethylene (trans-1,2) | 00156-60-5 | 96.94 | 10.40 | 4.333 | 6.965 | 1,141.9 | 231.90 | -36 | 185 | 118 | |||
102 | Dichlorotoluene (3,4) | 00095-75-0 | 161.03 | 10.40 | 0.0029 | 7.344 | 1,882.5 | 215.00 | 32 | 221 | 408 | |||
103 | Diethoxyethane (1,1) | 00105-57-7 | 118.17 | 6.89 | 0.307 | 7.625 | 1,574.0 | 229.47 | -10 | 216 | 212 | |||
104 | Diethoxymethane | 00462-95-3 | 104.15 | 6.94 | 0.81 | 6.986 | 1,270.2 | 221.26 | 32 | 167 | 191 | |||
105 | Diethyl (n,n) aniline {N,N-diethylbenzenamine} | 00091-66-7 | 149.23 | 7.77 | 0.0031 | 8.258 | 2,652.8 | 277.32 | 122 | 425 | 422 | |||
106 | Diethyl ketone {3-pentanone} | 00096-22-0 | 86.13 | 6.76 | 77 | 0.423 | 5.741 | 716.2 | 147.17 | 97 | 215 | 215 | ||
107 | Diethyl sulfide | 00352-93-2 | 90.19 | 6.98 | 0.749 | 7.541 | 1,560.5 | 246.59 | -39 | 190 | 197 |
108 | Diethylamine {N-ethyl ethanamine} | 00109-89-7 | 73.14 | 5.89 | 2.712 | 5.737 | 559.1 | 140.18 | 89 | 141 | 132 | |||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
109 | Diethylbenzene (1,2) | 00135-01-3 | 134.22 | 7.34 | 0.0094 | 6.990 | 1,577.9 | 200.55 | 206 | 364 | 361 | |||
110 | Diethylbenzene (1,3) | 00141-93-5 | 134.22 | 7.18 | 0.01 | 7.006 | 1,576.3 | 201.00 | 203 | 360 | 358 | |||
111 | Diethylbenzene (1,4) | 00105-05-5 | 134.22 | 7.20 | 0.01 | 7.001 | 1,589.3 | 202.02 | 206 | 365 | 363 | |||
112 | Di-isopropyl ether | 00108-20-3 | 102.17 | 6.04 | 1.877 | 6.842 | 1,135.0 | 218.23 | 74 | 153 | 155 | |||
113 | Dimethoxyethane (1,2) | 00110-71-4 | 90.12 | 7.25 | 0.966 | 6.713 | 1,260.5 | 235.83 | -55 | 199 | 185 | |||
114 | Dimethyl formamide (n,n) | 00068-12-2 | 73.09 | 7.88 | 77 | 0.04 | 6.806 | 1,337.7 | 190.50 | 86 | 194 | 307 | ||
115 | Dimethyl hydrazine (1,1) | 00057-14-7 | 60.1 | 6.60 | 72 | 1.896 | 7.588 | 1,388.5 | 232.54 | -32 | 68 | 146 | ||
116 | Dimethyl phthalate | 00131-11-3 | 194.18 | 9.94 | 2.25E-08 | 4.522 | 700.3 | 51.42 | 180 | 304 | 540 | |||
117 | Dimethylbutane (2,3) | 00079-29-8 | 86.18 | 5.52 | 3.064 | 6.810 | 1,127.2 | 228.95 | 58 | 138 | 136 | |||
118 | Dimethylcyclopentane (1,1) | 01638-26-2 | 98.19 | 6.26 | 77 | 0.932 | 6.830 | 1,226.6 | 222.76 | 60 | 192 | 190 | ||
119 | Dimethylpentane (2,2) | 00590-35-2 | 100.2 | 5.63 | 1.315 | 6.815 | 1,190.3 | 223.34 | 60 | 176 | 174 | |||
120 | Dimethylpentane (2,3) | 00565-59-3 | 100.2 | 5.80 | 0.842 | 6.862 | 1,242.6 | 222.34 | 64 | 195 | 194 | |||
121 | Dimethylpentane (2,4) | 00108-08-7 | 100.2 | 5.62 | 1.221 | 6.836 | 1,197.6 | 222.27 | 57 | 178 | 177 | |||
122 | Dimethylpentane (3,3) | 00562-49-2 | 100.2 | 5.79 | 1.029 | 6.831 | 1,231.0 | 225.58 | 56 | 189 | 187 | |||
123 | Dioxane (1,4) | 00123-91-1 | 88.11 | 8.63 | 0.439 | 7.456 | 1,570.1 | 241.85 | 68 | 221 | 214 | |||
124 | Dipropyl ether {di-n-propyl ether} | 00111-43-3 | 102.17 | 6.23 | 0.754 | 6.945 | 1,254.8 | 218.82 | 80 | 192 | 194 | |||
125 | Dodecane (n) | 00112-40-3 | 170.33 | 6.25 | 0.00093 | 6.981 | 1,625.9 | 180.31 | 259 | 423 | 421 | |||
126 | Epichlorohydrin {chloromethyl oxirane} | 00106-89-8 | 92.52 | 9.85 | 0.194 | 8.229 | 2,086.8 | 273.16 | 241 | |||||
127 | Ethane | 00074-84-0 | 30.07 | 472 | 6.813 | 659.7 | 256.43 | -215 | -100 | -127 | ||||
128 | Ethanolamine (mono) | 00141-43-5 | 61.08 | 8.50 | 0.002 | 7.168 | 1,408.9 | 157.06 | 150 | 340 | 339 | |||
129 | Ethyl acetate | 00141-78-6 | 88.11 | 7.51 | 1.135 | 7.103 | 1,245.7 | 217.96 | 60 | 168 | 171 | |||
130 | Ethyl acrylate {ethyl ester 2-propenoic acid} | 00140-88-5 | 100.12 | 7.71 | 0.445 | 7.150 | 1,366.1 | 220.47 | -21 | 211 | 211 | |||
131 | Ethyl alcohol {ethanol} | 00064-17-5 | 46.07 | 6.59 | 0.648 | 8.247 | 1,670.4 | 232.96 | 32 | 173 | 173 | |||
132 | Ethyl chloride | 00075-00-3 | 64.51 | 7.43 | 77 | 16.63 | 7.037 | 1,052.8 | 241.07 | -69 | 55 | 61 | ||
133 | Ethyl ether {diethyl ether} | 00060-29-7 | 74.12 | 5.96 | 6.675 | 6.897 | 1,062.6 | 228.22 | -10 | 132 | 94 | |||
134 | Ethylamine | 00075-04-7 | 45.08 | 5.65 | 77 | 14.08 | 7.405 | 1,203.8 | 249.43 | 62 | 349 | 64 | ||
135 | Ethylbenzene | 00100-41-4 | 106.17 | 7.24 | 0.104 | 6.950 | 1,419.3 | 212.61 | 134 | 279 | 277 | |||
136 | Ethylcyclopentane | 01640-89-7 | 98.19 | 6.40 | 0.475 | 6.898 | 1,305.0 | 221.40 | 84 | 220 | 218 | |||
137 | Ethylene {ethene} | 00074-85-1 | 28.05 | 4.74 | -155 | 749 | 6.748 | 584.1 | 254.84 | -191 | -120 | -155 | ||
138 | Ethyleneoxide | 00075-21-8 | 44.05 | 7.36 | 17.84 | 8.722 | 2,022.8 | 335.81 | 32 | 89 | 53 | |||
139 | Ethylpentane (3) | 00617-78-7 | 100.2 | 5.83 | 0.701 | 6.880 | 1,254.1 | 220.15 | 70 | 202 | 200 | |||
140 | Fluoranthene | 00206-44-0 | 202.25 | 10.40 | 3.96E-08 | 12.836 | 5,348.1 | 273.15 | 77 | 230 | 723 | |||
141 | Fluorobenzene | 00462-06-6 | 96.1 | 8.53 | 0.936 | 7.237 | 1,409.8 | 238.36 | 0 | 183 | 185 | |||
142 | Formic acid | 00064-18-6 | 46.03 | 10.10 | 0.516 | 4.876 | 515.0 | 133.74 | 33 | 93 | 213 | |||
143 | Freon 11 {trichlorofluoromethane} | 00075-69-4 | 137.37 | 12.40 | 10.93 | 6.884 | 1,043.0 | 236.88 | 75 | |||||
144 | Furan | 00110-00-9 | 68.07 | 7.94 | 7.963 | 6.975 | 1,060.8 | 227.73 | 37 | 143 | 89 | |||
145 | Furfural {2-furancarboxaldehyde} | 00098-01-1 | 96.09 | 9.68 | 0.018 | 6.969 | 1,430.1 | 188.70 | 133 | 321 | 323 | |||
146 | Heneicosane (n) | 00629-94-7 | 296.57 | 6.61 | 6.23E-07 | 8.796 | 3,571.2 | 253.20 | 307 | 663 | 679 | |||
147 | Heptane (n) | 00142-82-5 | 100.2 | 5.71 | 0.541 | 6.903 | 1,268.6 | 216.95 | 79 | 211 | 209 | |||
148 | Heptene (1) | 00592-76-7 | 98.19 | 5.82 | 0.752 | 7.093 | 1,400.7 | 238.96 | 32 | 192 | 201 | |||
149 | Hexadiene (1,5) | 00592-42-7 | 82.14 | 5.74 | 77 | 2.89 | 6.563 | 1,008.1 | 214.16 | 32 | 138 | 140 | ||
150 | Hexane (n) | 00110-54-3 | 86.18 | 5.47 | 77 | 1.913 | 6.878 | 1,171.5 | 224.37 | 55 | 157 | 156 | ||
151 | Hexanol (1) | 00111-27-3 | 102.17 | 6.79 | 0.005 | 7.288 | 1,422.0 | 165.44 | 126 | 315 | 314 | |||
152 | Hexene (1) | 00592-41-6 | 84.16 | 5.62 | 2.378 | 6.866 | 1,153.0 | 225.85 | 61 | 148 | 147 | |||
153 | Hydrogen cyanide {hydrocyanic acid} | 00074-90-8 | 27.03 | 5.74 | 9.931 | 7.549 | 1,340.8 | 261.56 | 2 | 115 | 79 | |||
154 | Isobutane {methylpropane (2)} | 00075-28-5 | 58.12 | 4.60 | 77 | 38.22 | 6.819 | 912.1 | 243.34 | -121 | 11 | 12 | ||
155 | Isobutene {methylpropene (2)} | 00115-11-7 | 56.11 | 4.92 | 77 | 32.18 | 6.522 | 799.1 | 226.54 | -70 | 32 | 20 | ||
156 | Isobutyl alcohol {2-methyl 1-propanol} | 00078-83-1 | 74.12 | 6.69 | 0.096 | 7.306 | 1,237.0 | 171.62 | 176 | 240 | 226 | |||
157 | Isooctane {2,2,4-trimethylpentane} | 00540-84-1 | 114.23 | 5.74 | 77 | 0.596 | 6.812 | 1,257.8 | 220.74 | 76 | 212 | 211 |
158 | Isopentane {2-methyl butane} | 00078-78-4 | 72.15 | 5.18 | 9.426 | 6.790 | 1,020.0 | 233.10 | 61 | 83 | 82 | |||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
159 | Isopentene {2-methyl 2-butene} | 00513-35-9 | 70.13 | 5.53 | 6.21 | 6.922 | 1,098.6 | 233.26 | 37 | 159 | 100 | |||
160 | Isoprene {2-methyl 1,3-butadiene} | 00078-79-5 | 68.12 | 5.67 | 7.446 | 6.091 | 706.9 | 186.10 | 62 | 93 | 93 | |||
161 | Isopropyl alcohol {isopropanol} | 00067-63-0 | 60.1 | 6.52 | 77 | 0.443 | 7.736 | 1,357.4 | 197.34 | 134 | 193 | 180 | ||
162 | Isopropyl benzene {cumene} | 00098-82-8 | 120.19 | 7.19 | 0.048 | 6.929 | 1,455.8 | 207.20 | 158 | 308 | 305 | |||
163 | Isopropylbenzene (1-methyl-2) | 00527-84-4 | 134.22 | 7.32 | 0.017 | 7.417 | 1,880.5 | 236.27 | 178 | 355 | 350 | |||
164 | Methacrylonitrile {2-methyl 2-propenenitrile} | 00126-98-7 | 67.09 | 6.68 | 0.886 | 6.999 | 1,353.6 | 238.03 | -48 | 194 | 194 | |||
165 | Methane | 00074-82-8 | 16.04 | 3.53 | -260 | 4567 | 7.096 | 516.7 | 284.37 | -262 | -117 | -260 | ||
166 | Methyl acetate {methyl ester acetic acid} | 00079-20-9 | 74.08 | 7.80 | 2.703 | 7.079 | 1,164.4 | 220.46 | 35 | 133 | 134 | |||
167 | Methyl acrylate {methyl ester 2-propenoic acid} | 00096-33-3 | 86.09 | 7.96 | 1.058 | 7.198 | 1,338.7 | 229.63 | -47 | 176 | 177 | |||
168 | Methyl alcohol {methanol} | 00067-56-1 | 32.04 | 6.61 | 1.476 | 8.079 | 1,581.3 | 239.65 | 59 | 183 | 148 | |||
169 | Methyl ethyl ketone {2-butanone} | 00078-93-3 | 72.11 | 6.68 | 77 | 1.081 | 6.864 | 1,150.2 | 209.25 | 106 | 207 | 176 | ||
170 | Methyl isobutyl ketone | 00108-10-1 | 100.16 | 6.65 | 77 | 0.219 | 6.828 | 1,254.1 | 201.61 | 71 | 241 | 241 | ||
171 | Methyl methacrylate | 00080-62-6 | 100.12 | 7.88 | 0.416 | 8.253 | 1,945.6 | 265.58 | 102 | 192 | 213 | |||
172 | Methyl propyl ether | 00557-17-5 | 74.12 | 6.14 | 55 | 6.017 | 6.563 | 903.6 | 206.46 | 31 | 103 | 102 | ||
173 | Methyl styrene (alpha) | 00098-83-9 | 118.18 | 7.60 | 0.024 | 6.924 | 1,486.9 | 202.40 | 329 | |||||
174 | Methylcyclohexane | 00108-87-2 | 98.19 | 6.42 | 0.558 | 6.823 | 1,270.8 | 221.42 | 27 | 261 | 214 | |||
175 | Methylcyclopentane | 00096-37-7 | 84.16 | 6.25 | 1.738 | 6.863 | 1,186.1 | 226.04 | 59 | 163 | 161 | |||
176 | Methyldichlorosilane | 20156-50-7 | 115.03 | 8.91 | 5.718 | 7.028 | 1,167.8 | 240.70 | 34 | 106 | ||||
177 | Methylene chloride | 00075-09-2 | 84.93 | 11.00 | 5.64 | 7.412 | 1,327.0 | 252.68 | -40 | 104 | 104 | |||
178 | Methylhexane (2) | 00591-76-4 | 100.2 | 5.66 | 0.799 | 6.882 | 1,240.9 | 220.10 | 65 | 196 | 194 | |||
179 | Methylhexane (3) | 00589-34-4 | 100.2 | 5.72 | 0.744 | 6.874 | 1,243.8 | 219.63 | 68 | 199 | 197 | |||
180 | Methylpentane (2) | 00107-83-5 | 86.18 | 5.43 | 77 | 2.73 | 6.839 | 1,135.4 | 226.57 | 55 | 142 | 142 | ||
181 | Methyl-tert-butyl ether {MTBE} | 01634-04-4 | 88.15 | 6.18 | 3.226 | 6.867 | 1,116.1 | 224.74 | 125 | 431 | 131 | |||
182 | Morpholine | 00110-91-8 | 87.12 | 8.35 | 0.109 | 7.718 | 1,745.8 | 235.00 | 32 | 111 | 263 | |||
183 | Naphthalene | 00091-20-3 | 128.17 | 8.56 | 0.0024 | 7.146 | 1,831.6 | 211.82 | 177 | 354 | 422 | |||
184 | Nitrobenzene | 00098-95-3 | 123.11 | 10.00 | 0.0022 | 7.091 | 1,727.6 | 199.71 | 273 | 411 | 412 | |||
185 | Nitromethane | 00075-52-5 | 61.04 | 9.49 | 0.415 | 7.281 | 1,446.2 | 227.52 | 132 | 277 | 214 | |||
186 | Nonadecane (n) | 00629-92-5 | 268.52 | 6.56 | 3.64E-07 | 33.303 | 28,197.0 | 725.94 | 91 | 131 | 624 | |||
187 | Nonane (n) | 00111-84-2 | 128.26 | 5.99 | 0.037 | 6.700 | 1,492.9 | 217.26 | -64 | 94 | 303 | |||
188 | Octadecane (n) | 00593-45-3 | 254.49 | 6.48 | 6.16E-07 | 7.207 | 2,069.0 | 161.22 | 346 | 602 | 592 | |||
189 | Octane (n) | 00111-65-9 | 114.23 | 5.83 | 0.142 | 8.076 | 1,936.3 | 253.01 | -70 | 75 | 258 | |||
190 | Octanol (1) | 00111-87-5 | 130.23 | 6.90 | 0.00061 | 9.352 | 2,603.4 | 224.35 | 68 | 176 | 383 | |||
191 | Octene (1) | 00111-66-0 | 112.21 | 5.97 | 0.196 | 6.933 | 1,353.5 | 212.76 | 113 | 252 | 251 | |||
192 | Pentachloroethane | 00076-01-7 | 202.29 | 14.00 | 0.04 | 6.643 | 1,342.3 | 196.51 | 77 | 324 | 324 | |||
193 | Pentadiene (1,2) | 00591-95-7 | 68.12 | 5.78 | 4.718 | 6.936 | 1,125.5 | 231.88 | -76 | -19 | 113 | |||
194 | Pentadiene (1,4) | 00591-93-5 | 68.12 | 5.52 | 10.06 | 7.035 | 1,108.2 | 241.05 | -110 | 65 | 79 | |||
195 | Pentadiene (2,3) | 00591-96-8 | 68.12 | 5.80 | 4.223 | 7.263 | 1,256.2 | 239.57 | -76 | -15 | 119 | |||
196 | Pentane (n) | 00109-66-0 | 72.15 | 5.23 | 6.884 | 6.864 | 1,070.6 | 232.70 | 24 | 155 | 97 | |||
197 | Pentene (1) | 00109-67-1 | 70.13 | 5.35 | 8.671 | 6.786 | 1,014.3 | 229.78 | 55 | 87 | 88 | |||
198 | Pentyne (1) | 00627-19-0 | 68.12 | 5.76 | 5.657 | 6.967 | 1,092.5 | 227.18 | -47 | 142 | 104 | |||
199 | Phenanthrene | 00085-01-8 | 178.23 | 8.18 | 3.37E-06 | 7.394 | 2,428.5 | 202.19 | 212 | 302 | 635 | |||
200 | Phenol | 00108-95-2 | 94.11 | 8.80 | 113 | 0.003 | 7.122 | 1,509.7 | 174.20 | 225 | 359 | 359 | ||
201 | Phosgene | 00075-44-5 | 98.92 | 11.40 | 77 | 19.43 | 7.146 | 1,072.7 | 243.30 | 47 | 345 | 46 | ||
202 | Picoline (3) {3-methyl pyridine} | 00108-99-6 | 93.13 | 7.98 | 0.064 | 7.054 | 1,484.3 | 211.54 | 165 | 364 | 291 | |||
203 | Propane | 00074-98-6 | 44.1 | 4.12 | 77 | 111 | 6.858 | 819.3 | 248.73 | -45 | 117 | -44 | ||
204 | Propanethiol (1) | 00107-03-9 | 76.16 | 7.02 | 1.943 | 6.929 | 1,183.4 | 224.63 | 76 | 216 | 154 | |||
205 | Propanethiol (2) | 00075-33-2 | 76.16 | 6.80 | 3.59 | 6.877 | 1,113.9 | 226.16 | 51 | 186 | 131 | |||
206 | Propyl alcohol (n) {propanol (1)} | 00071-23-8 | 60.1 | 6.67 | 77 | 0.218 | 8.189 | 1,690.9 | 221.35 | 67 | 207 | 207 | ||
207 | Propyl nitrate (n) {propyl ester nitric acid} | 00627-13-4 | 105.09 | 8.80 | 0.261 | 6.955 | 1,294.4 | 206.70 | 32 | 158 | 231 |
208 | Propylamine (n) {1-propanamine} | 00107-10-8 | 59.11 | 5.99 | 3.99 | 6.926 | 1,044.0 | 210.84 | 73 | 172 | 120 | |||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
209 | Propylene {propene} | 00115-07-1 | 42.08 | 4.22 | 132 | 6.850 | 795.8 | 248.27 | -161 | -53 | -54 | |||
210 | Propylene glycol (1,2) {1,2 propanediol} | 00057-55-6 | 76.09 | 8.65 | 0.00094 | 8.208 | 2,085.9 | 203.54 | 368 | |||||
211 | Propylene oxide | 00075-56-9 | 58.08 | 7.17 | 32 | 7.101 | 6.970 | 1,065.3 | 226.28 | -100 | 94 | 95 | ||
212 | Pyridine | 00110-86-1 | 79.1 | 8.20 | 0.233 | 7.038 | 1,371.4 | 214.65 | 153 | 307 | 240 | |||
213 | Resorcinol | 00108-46-3 | 110.11 | 10.60 | 77 | 6.65E-06 | 8.398 | 2,687.2 | 210.99 | 305 | 530 | 532 | ||
214 | Styrene | 00100-42-5 | 104.15 | 7.56 | 0.066 | 7.095 | 1,525.1 | 216.77 | 86 | 293 | 295 | |||
215 | Tetrachloroethane (1,1,1,2) | 00630-20-6 | 167.85 | 12.80 | 0.133 | 6.906 | 1,370.4 | 210.25 | 139 | 266 | 271 | |||
216 | Tetrachloroethane (1,1,2,2) | 00079-34-5 | 167.85 | 13.30 | 0.037 | 6.091 | 959.6 | 149.78 | 77 | 266 | 295 | |||
217 | Tetrachloroethylene | 00127-18-4 | 165.83 | 13.50 | 0.213 | 7.056 | 1,440.8 | 223.98 | 82 | 226 | 250 | |||
218 | Tetrahydrofuran | 00109-99-9 | 72.11 | 7.42 | 2.039 | 6.996 | 1,202.9 | 226.33 | 74 | 211 | 151 | |||
219 | Toluene | 00108-88-3 | 92.14 | 7.24 | 0.331 | 7.017 | 1,377.6 | 222.64 | 32 | 122 | 231 | |||
220 | Trichloroethane (1,1,1) | 00071-55-6 | 133.4 | 11.10 | 1.65 | 8.761 | 2,210.2 | 308.05 | 22 | 62 | 165 | |||
221 | Trichloroethane (1,1,2) | 00079-00-5 | 133.4 | 12.00 | 0.245 | 6.945 | 1,310.3 | 208.74 | 122 | 237 | 237 | |||
222 | Trichloroethylene | 00079-01-6 | 131.39 | 12.20 | 0.817 | 6.429 | 974.5 | 187.34 | 64 | 188 | 189 | |||
223 | Trichloropropane (1,2,3) | 00096-18-4 | 147.43 | 11.50 | 0.031 | 7.532 | 1,818.9 | 232.52 | 48 | 316 | 313 | |||
224 | Tridecane (n) | 00629-50-5 | 184.36 | 6.31 | 2.46E-04 | 7.003 | 1,689.1 | 174.28 | 283 | 457 | 453 | |||
225 | Trifluoroethane (1,1,2-trichloro-1,2,2) | 00076-13-1 | 187.37 | 13.05 | 77 | 4.376 | 6.880 | 1,099.9 | 227.50 | -13 | 181 | 118 | ||
226 | Trimethylbenzene (1,2,4) | 00095-63-6 | 120.19 | 7.31 | 0.02 | 7.044 | 1,573.3 | 208.56 | 126 | 388 | 337 | |||
227 | Trimethylchlorosilane {chlorotrimethylsilane} | 00075-77-4 | 108.64 | 7.15 | 77 | 3.068 | 6.951 | 1,191.0 | 235.15 | 37 | 132 | 136 | ||
228 | Trimethylpentane (2,2,3) | 00564-02-3 | 114.23 | 5.74 | 77 | 0.378 | 6.825 | 1,294.9 | 218.42 | 230 | ||||
229 | Trimethylpentane (2,3,3) | 00560-21-4 | 114.23 | 6.06 | 0.317 | 6.844 | 1,328.1 | 220.38 | 238 | |||||
230 | Trimethylpentane (2,3,4) | 00565-75-3 | 114.23 | 6.00 | 0.314 | 7.031 | 1,420.7 | 228.53 | -59 | 308 | 237 | |||
231 | Undecane (n) | 01120-21-4 | 156.31 | 6.18 | 0.0035 | 6.977 | 1,572.5 | 188.02 | 220 | 387 | 383 | |||
232 | Vinyl acetate {acetic acid ethenyl ester} | 00108-05-4 | 86.09 | 7.78 | 1.396 | 7.215 | 1,299.1 | 226.97 | 71 | 162 | 163 | |||
233 | Vinylidene chloride {1,1-dichloro ethene} | 00075-35-4 | 96.94 | 10.10 | 8.096 | 6.983 | 1,104.7 | 237.75 | -19 | 90 | 88 | |||
234 | Xylene (m) {1,3-dimethyl benzene} | 00108-38-3 | 106.17 | 7.21 | 0.09 | 7.009 | 1,462.3 | 215.11 | 82 | 331 | 283 | |||
235 | Xylene (o) {1,2-dimethyl benzene} | 00095-47-6 | 106.17 | 7.35 | 50 | 0.071 | 6.999 | 1,474.7 | 213.69 | 90 | 342 | 291 | ||
236 | Xylene (p) {1,4-dimethyl benzene} | 00106-42-3 | 106.17 | 7.19 | 0.097 | 7.021 | 1,474.4 | 217.77 | 56 | 355 | 281 | |||
238 | a Reference 22 of AP-42 Section 7.1. | |||||||||||||
239 | b (use the equation provided in footnote b to Table 7.1-3 to calculate vapor pressure in psia) | |||||||||||||
240 | c Use of this equation for temperature outside the indicated temperature range may result in loss of accuracy. | |||||||||||||
241 | d The superscript denotes temperature in °F; if no superscript is given the density is for 68 °F. |
A | B | C | D | E | F | G | H | I | J | K | L | M | N | O | P | Q | R | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | Table 7.1-7 Daily average maximum, daily average minimum liquid temperature, and insolation factor | |||||||||||||||||
2 | Location | Symbol | Units | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec | Annual | Order | Average |
3 | Birmingham, AL | TAN | °F | 35.0 | 37.5 | 44.1 | 51.7 | 60.6 | 68.1 | 71.7 | 71.1 | 64.7 | 53.3 | 43.3 | 36.7 | 53.2 | 1 | 53.2 |
4 | Huntsville, AL | TAN | °F | 32.7 | 35.2 | 42.1 | 50.6 | 59.6 | 67.2 | 70.3 | 69.2 | 62.6 | 51.1 | 41.2 | 34.5 | 51.4 | 1 | 51.4 |
5 | Mobile, AL | TAN | °F | 41.4 | 43.8 | 49.7 | 56.3 | 64.7 | 71.0 | 73.3 | 73.1 | 68.9 | 58.4 | 48.3 | 42.4 | 57.6 | 1 | 57.6 |
6 | Montgomery, AL | TAN | °F | 37.1 | 39.9 | 46.1 | 52.6 | 61.8 | 68.9 | 72.2 | 71.7 | 66.2 | 54.4 | 44.0 | 38.0 | 54.4 | 1 | 54.4 |
7 | Phoenix, AZ | TAN | °F | 46.5 | 49.5 | 54.0 | 60.1 | 69.8 | 78.1 | 84.3 | 83.4 | 78.1 | 65.4 | 53.3 | 45.6 | 64.0 | 1 | 64.0 |
8 | Prescott, AZ | TAN | °F | 26.8 | 29.5 | 33.5 | 38.9 | 48.0 | 55.9 | 63.3 | 61.9 | 54.9 | 42.7 | 32.3 | 26.2 | 42.8 | 1 | 42.8 |
9 | Tucson, AZ | TAN | °F | 40.7 | 43.1 | 47.0 | 52.4 | 61.6 | 70.4 | 75.7 | 74.4 | 70.1 | 58.4 | 47.0 | 40.0 | 56.8 | 1 | 56.7 |
10 | Fort Smith, AR | TAN | °F | 30.7 | 34.3 | 41.8 | 50.5 | 60.4 | 68.4 | 72.4 | 71.4 | 63.0 | 51.6 | 41.0 | 32.8 | 51.5 | 1 | 51.5 |
11 | Little Rock, AR | TAN | °F | 33.3 | 36.3 | 43.8 | 52.4 | 61.6 | 69.7 | 73.2 | 72.2 | 64.4 | 53.1 | 42.9 | 35.0 | 53.2 | 1 | 53.2 |
12 | Arcata, CA | TAN | °F | 40.7 | 41.4 | 41.1 | 42.4 | 46.0 | 48.4 | 51.4 | 51.4 | 48.3 | 45.1 | 42.5 | 40.2 | 44.9 | 1 | 44.9 |
13 | Bakersfield, CA | TAN | °F | 40.3 | 43.7 | 46.9 | 49.8 | 57.8 | 64.2 | 70.7 | 69.3 | 64.5 | 55.3 | 45.3 | 39.7 | 54.0 | 1 | 54.0 |
14 | Bishop, CA | TAN | °F | 24.0 | 27.4 | 32.1 | 36.8 | 45.1 | 51.9 | 57.7 | 54.8 | 47.6 | 38.5 | 28.3 | 22.9 | 38.9 | 1 | 38.9 |
15 | Daggett, CA | TAN | °F | 37.5 | 41.2 | 46.2 | 51.3 | 60.6 | 68.0 | 74.7 | 73.6 | 66.5 | 55.3 | 43.2 | 36.1 | 54.5 | 1 | 54.5 |
16 | Fresno, CA | TAN | °F | 39.9 | 43.1 | 46.5 | 49.6 | 56.9 | 62.4 | 68.3 | 66.7 | 62.2 | 53.7 | 44.6 | 39.4 | 52.8 | 1 | 52.8 |
17 | Long Beach, CA | TAN | °F | 47.6 | 49.0 | 51.5 | 53.6 | 58.2 | 61.4 | 64.7 | 65.3 | 63.5 | 58.8 | 51.8 | 46.8 | 56.0 | 1 | 56.0 |
18 | Los Angeles AP, CA | TAN | °F | 50.0 | 50.9 | 52.4 | 54.1 | 57.8 | 61.0 | 64.0 | 64.6 | 63.4 | 59.6 | 54.0 | 49.7 | 56.8 | 1 | 56.8 |
19 | Redding, CA | TAN | °F | 38.2 | 40.6 | 43.7 | 46.6 | 55.0 | 62.0 | 67.0 | 63.8 | 58.7 | 50.4 | 41.8 | 37.6 | 50.4 | 1 | 50.5 |
20 | Sacramento, CA | TAN | °F | 40.0 | 42.7 | 44.7 | 46.8 | 52.1 | 56.5 | 59.1 | 58.9 | 56.4 | 50.7 | 43.3 | 39.5 | 49.2 | 1 | 49.2 |
21 | San Diego, CA | TAN | °F | 50.1 | 51.6 | 53.9 | 56.2 | 59.8 | 62.3 | 65.4 | 66.9 | 65.4 | 61.0 | 54.4 | 49.5 | 58.0 | 1 | 58.0 |
22 | San Francisco AP, CA | TAN | °F | 45.2 | 47.2 | 48.3 | 49.4 | 52.2 | 54.0 | 55.8 | 56.6 | 56.2 | 53.9 | 49.4 | 45.6 | 51.1 | 1 | 51.2 |
23 | Santa Barbara, CA | TAN | °F | 41.9 | 44.6 | 46.8 | 48.2 | 52.1 | 54.8 | 57.9 | 58.0 | 56.3 | 51.7 | 45.4 | 41.1 | 49.9 | 1 | 49.9 |
24 | Santa Maria, CA | TAN | °F | 41.1 | 43.0 | 44.2 | 44.6 | 48.2 | 50.9 | 54.0 | 54.3 | 53.0 | 49.3 | 44.0 | 40.2 | 47.2 | 1 | 47.2 |
25 | Stockton, CA | TAN | °F | 39.5 | 42.2 | 44.3 | 47.0 | 52.8 | 57.6 | 60.9 | 60.4 | 57.5 | 50.9 | 43.1 | 38.9 | 49.6 | 1 | 49.6 |
26 | Alamosa, CO | TAN | °F | 0.5 | 7.4 | 18.0 | 25.4 | 34.8 | 41.4 | 47.7 | 46.7 | 37.4 | 25.4 | 12.7 | 2.0 | 24.9 | 1 | 25.0 |
27 | Colorado Springs, CO | TAN | °F | 18.8 | 20.9 | 27.1 | 34.1 | 43.8 | 52.2 | 57.8 | 56.4 | 47.9 | 36.8 | 26.0 | 19.4 | 36.8 | 1 | 36.8 |
28 | Denver, CO | TAN | °F | 19.2 | 21.7 | 28.2 | 34.8 | 44.7 | 53.2 | 60.4 | 58.7 | 49.6 | 37.7 | 26.7 | 19.6 | 37.9 | 1 | 37.9 |
29 | Grand Junction, CO | TAN | °F | 19.3 | 25.9 | 32.7 | 39.5 | 48.8 | 57.9 | 65.2 | 62.8 | 53.4 | 41.3 | 28.8 | 19.9 | 41.3 | 1 | 41.3 |
30 | Limon, CO | TAN | °F | 12.4 | 15.2 | 22.0 | 29.2 | 39.4 | 49.3 | 54.8 | 53.9 | 43.7 | 31.6 | 19.9 | 12.7 | 32.0 | 1 | 32.0 |
31 | Pueblo, CO | TAN | °F | 15.3 | 18.5 | 26.5 | 34.8 | 45.2 | 53.6 | 59.6 | 58.3 | 48.3 | 35.1 | 23.4 | 15.9 | 36.2 | 1 | 36.2 |
32 | Bridgeport, CT | TAN | °F | 24.4 | 25.9 | 32.1 | 41.8 | 51.1 | 61.4 | 67.0 | 66.6 | 59.2 | 47.4 | 38.9 | 29.5 | 45.4 | 1 | 45.4 |
33 | Hartford, CT | TAN | °F | 19.4 | 21.4 | 28.8 | 39.2 | 48.3 | 58.4 | 63.3 | 61.9 | 53.9 | 42.2 | 34.1 | 24.6 | 41.3 | 1 | 41.3 |
34 | Wilmington_DE, DE | TAN | °F | 26.3 | 27.2 | 34.3 | 43.8 | 53.0 | 63.2 | 67.9 | 66.9 | 58.9 | 46.8 | 38.4 | 30.1 | 46.4 | 1 | 46.4 |
35 | Daytona Beach, FL | TAN | °F | 49.0 | 50.6 | 55.0 | 59.8 | 66.4 | 72.1 | 73.7 | 74.0 | 73.2 | 66.9 | 57.7 | 52.3 | 62.5 | 1 | 62.6 |
36 | Fort Myers, FL | TAN | °F | 54.4 | 56.1 | 59.8 | 64.0 | 69.3 | 73.8 | 75.0 | 75.4 | 74.7 | 69.4 | 61.8 | 56.7 | 65.9 | 1 | 65.9 |
37 | Gainesville, FL | TAN | °F | 43.4 | 45.5 | 50.2 | 55.6 | 63.2 | 69.8 | 72.1 | 72.1 | 69.4 | 61.1 | 51.4 | 45.5 | 58.3 | 1 | 58.3 |
38 | Jacksonville, FL | TAN | °F | 42.9 | 45.1 | 50.1 | 55.5 | 63.7 | 70.5 | 72.9 | 73.1 | 70.1 | 61.0 | 50.8 | 44.4 | 58.3 | 1 | 58.3 |
39 | Key West, FL | TAN | °F | 64.9 | 66.2 | 68.7 | 72.2 | 76.2 | 79.4 | 80.6 | 80.5 | 79.2 | 76.5 | 71.8 | 67.1 | 73.6 | 1 | 73.6 |
40 | Miami, FL | TAN | °F | 61.2 | 62.6 | 65.8 | 69.4 | 73.9 | 76.6 | 78.1 | 78.2 | 77.3 | 74.3 | 68.4 | 63.6 | 70.8 | 1 | 70.8 |
41 | Orlando, FL | TAN | °F | 50.5 | 52.5 | 56.5 | 61.0 | 67.3 | 72.4 | 74.0 | 74.4 | 73.2 | 66.8 | 58.7 | 52.9 | 63.4 | 1 | 63.4 |
42 | Pensacola, FL | TAN | °F | 43.5 | 46.0 | 52.0 | 58.6 | 67.0 | 73.3 | 75.2 | 74.8 | 71.1 | 61.1 | 51.0 | 44.6 | 59.9 | 1 | 59.9 |
43 | Tallahassee, FL | TAN | °F | 40.5 | 42.4 | 47.9 | 53.7 | 62.8 | 70.3 | 72.8 | 72.8 | 69.1 | 58.2 | 47.6 | 41.5 | 56.6 | 1 | 56.6 |
44 | Tampa, FL | TAN | °F | 52.3 | 54.1 | 58.5 | 63.5 | 70.2 | 74.8 | 76.2 | 76.2 | 74.6 | 68.2 | 59.9 | 54.3 | 65.2 | 1 | 65.2 |
45 | Vero Beach, FL | TAN | °F | 52.7 | 54.2 | 58.2 | 62.3 | 68.5 | 72.6 | 73.9 | 73.9 | 73.9 | 69.6 | 62.0 | 56.4 | 64.9 | 1 | 64.9 |
46 | West Palm Beach, FL | TAN | °F | 58.1 | 59.4 | 63.1 | 67.1 | 72.0 | 75.1 | 76.4 | 76.6 | 76.0 | 72.6 | 65.8 | 60.6 | 68.6 | 1 | 68.6 |
47 | Athens, GA | TAN | °F | 34.4 | 36.8 | 43.1 | 50.1 | 58.9 | 66.7 | 70.2 | 69.6 | 63.3 | 52.0 | 42.4 | 35.5 | 51.9 | 1 | 51.9 |
48 | Atlanta, GA | TAN | °F | 35.5 | 38.2 | 44.8 | 52.3 | 61.2 | 68.5 | 71.7 | 71.3 | 65.4 | 54.4 | 44.2 | 37.1 | 53.7 | 1 | 53.7 |
49 | Augusta, GA | TAN | °F | 34.7 | 36.7 | 43.0 | 49.6 | 58.6 | 67.2 | 70.5 | 70.0 | 63.7 | 51.9 | 41.8 | 35.3 | 51.9 | 1 | 51.9 |
50 | Columbus, GA | TAN | °F | 38.0 | 40.4 | 46.6 | 53.5 | 62.9 | 70.1 | 73.2 | 72.7 | 67.3 | 56.2 | 45.9 | 39.1 | 55.5 | 1 | 55.5 |
51 | Macon, GA | TAN | °F | 36.3 | 38.6 | 44.8 | 51.0 | 60.1 | 68.3 | 71.6 | 70.8 | 64.7 | 53.0 | 43.0 | 36.8 | 53.2 | 1 | 53.3 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | Savannah, GA | TAN | °F | 40.0 | 42.0 | 48.3 | 54.5 | 62.9 | 70.4 | 73.3 | 73.0 | 68.6 | 58.1 | 47.9 | 41.3 | 56.7 | 1 | 56.7 |
53 | Hilo, HI | TAN | °F | 64.1 | 64.0 | 65.1 | 65.9 | 67.2 | 68.5 | 69.5 | 70.0 | 69.4 | 68.8 | 67.5 | 65.6 | 67.1 | 1 | 67.1 |
54 | Honolulu, HI | TAN | °F | 67.1 | 67.3 | 68.5 | 70.3 | 71.8 | 74.3 | 75.3 | 76.0 | 75.1 | 74.2 | 72.1 | 69.5 | 71.8 | 1 | 71.8 |
55 | Kahului, HI | TAN | °F | 64.0 | 63.7 | 65.0 | 66.5 | 67.7 | 70.3 | 71.8 | 72.3 | 71.2 | 70.2 | 68.4 | 65.9 | 68.1 | 1 | 68.1 |
56 | Lihue, HI | TAN | °F | 66.0 | 66.3 | 67.4 | 69.3 | 71.0 | 73.7 | 74.6 | 75.2 | 74.7 | 73.7 | 71.3 | 68.7 | 71.0 | 1 | 71.0 |
57 | Boise, ID | TAN | °F | 26.2 | 29.0 | 34.5 | 39.3 | 47.2 | 53.9 | 61.5 | 60.5 | 52.2 | 41.3 | 31.9 | 26.2 | 42.0 | 1 | 42.0 |
58 | Lewiston, ID | TAN | °F | 30.7 | 32.4 | 36.4 | 41.2 | 48.1 | 54.1 | 61.3 | 60.3 | 52.4 | 42.0 | 34.7 | 29.9 | 43.6 | 1 | 43.6 |
59 | Pocatello, ID | TAN | °F | 18.0 | 20.7 | 27.9 | 33.5 | 40.8 | 47.0 | 53.2 | 51.5 | 42.9 | 33.8 | 24.4 | 18.7 | 34.4 | 1 | 34.4 |
60 | Chicago, IL | TAN | °F | 17.7 | 21.4 | 29.8 | 39.8 | 49.3 | 59.3 | 64.9 | 64.0 | 55.3 | 44.2 | 33.3 | 22.3 | 41.8 | 1 | 41.8 |
61 | Moline, IL | TAN | °F | 15.3 | 20.2 | 29.9 | 40.9 | 51.2 | 61.0 | 65.1 | 63.5 | 54.2 | 43.2 | 31.9 | 20.3 | 41.4 | 1 | 41.4 |
62 | Peoria, IL | TAN | °F | 17.8 | 22.2 | 31.4 | 42.4 | 52.4 | 62.0 | 65.8 | 64.6 | 55.7 | 44.3 | 33.3 | 22.5 | 42.9 | 1 | 42.9 |
63 | Rockford, IL | TAN | °F | 14.1 | 18.5 | 27.7 | 38.6 | 48.9 | 59.1 | 62.8 | 61.6 | 52.6 | 41.4 | 30.6 | 18.9 | 39.6 | 1 | 39.6 |
64 | Springfield_IL, IL | TAN | °F | 19.9 | 24.2 | 32.9 | 43.4 | 53.8 | 62.7 | 65.6 | 64.5 | 55.0 | 44.6 | 34.6 | 24.4 | 43.8 | 1 | 43.8 |
65 | Evansville, IN | TAN | °F | 25.9 | 28.6 | 36.3 | 46.3 | 56.2 | 65.2 | 68.6 | 66.8 | 58.1 | 47.1 | 37.4 | 28.8 | 47.1 | 1 | 47.1 |
66 | Fort Wayne, IN | TAN | °F | 18.6 | 21.5 | 29.6 | 40.0 | 50.0 | 60.4 | 63.2 | 61.6 | 53.1 | 42.9 | 33.5 | 23.5 | 41.5 | 1 | 41.5 |
67 | Indianapolis, IN | TAN | °F | 21.5 | 24.7 | 33.3 | 43.8 | 53.5 | 63.1 | 66.2 | 65.5 | 57.2 | 45.7 | 35.7 | 25.9 | 44.7 | 1 | 44.7 |
68 | South Bend, IN | TAN | °F | 18.6 | 21.4 | 28.9 | 39.2 | 49.2 | 59.4 | 63.3 | 62.2 | 54.0 | 43.4 | 33.5 | 23.6 | 41.4 | 1 | 41.4 |
69 | Des Moines, IA | TAN | °F | 14.1 | 19.3 | 29.6 | 41.3 | 52.4 | 62.4 | 66.6 | 64.9 | 55.1 | 43.6 | 30.9 | 19.3 | 41.6 | 1 | 41.6 |
70 | Dubuque, IA | TAN | °F | 11.8 | 16.7 | 27.0 | 38.4 | 49.0 | 58.9 | 62.3 | 60.9 | 52.1 | 40.7 | 29.2 | 17.0 | 38.7 | 1 | 38.7 |
71 | Mason City, IA | TAN | °F | 7.8 | 12.9 | 24.1 | 35.7 | 47.4 | 57.7 | 61.0 | 58.6 | 48.9 | 37.7 | 25.5 | 13.5 | 35.9 | 1 | 35.9 |
72 | Sioux City, IA | TAN | °F | 11.0 | 16.5 | 26.3 | 37.9 | 49.7 | 59.7 | 63.9 | 61.6 | 51.2 | 39.2 | 26.2 | 15.3 | 38.2 | 1 | 38.2 |
73 | Waterloo, IA | TAN | °F | 9.7 | 15.3 | 26.2 | 37.7 | 49.4 | 59.7 | 62.8 | 60.4 | 51.0 | 39.6 | 27.4 | 15.3 | 37.9 | 1 | 37.9 |
74 | Concordia, KS | TAN | °F | 19.3 | 23.3 | 31.9 | 42.0 | 52.8 | 62.7 | 68.0 | 66.1 | 56.5 | 44.6 | 32.0 | 22.1 | 43.4 | 1 | 43.4 |
75 | Dodge City, KS | TAN | °F | 20.8 | 24.4 | 31.6 | 40.9 | 52.1 | 61.4 | 66.7 | 65.4 | 56.1 | 43.7 | 30.7 | 22.6 | 43.0 | 1 | 43.0 |
76 | Goodland, KS | TAN | °F | 17.7 | 20.4 | 27.1 | 35.3 | 46.3 | 56.3 | 62.0 | 60.5 | 50.6 | 38.1 | 26.5 | 18.8 | 38.3 | 1 | 38.3 |
77 | Russell, KS | TAN | °F | 18.8 | 22.8 | 31.4 | 40.9 | 52.3 | 62.4 | 67.6 | 66.3 | 56.5 | 43.7 | 30.5 | 21.3 | 42.9 | 1 | 42.9 |
78 | Topeka, KS | TAN | °F | 20.3 | 25.1 | 33.7 | 44.3 | 55.0 | 64.6 | 69.3 | 67.4 | 57.0 | 45.8 | 33.8 | 24.0 | 45.0 | 1 | 45.0 |
79 | Wichita, KS | TAN | °F | 23.1 | 27.4 | 35.7 | 45.2 | 56.2 | 65.5 | 70.3 | 69.3 | 60.0 | 47.7 | 35.5 | 25.8 | 46.8 | 1 | 46.8 |
80 | Cincinnati, KY | TAN | °F | 23.8 | 26.2 | 34.1 | 44.3 | 53.7 | 62.5 | 66.1 | 65.4 | 57.4 | 45.9 | 36.2 | 27.4 | 45.2 | 1 | 45.3 |
81 | Jackson_KY, KY | TAN | °F | 27.9 | 30.5 | 37.8 | 47.7 | 55.4 | 63.1 | 66.6 | 65.7 | 58.9 | 48.7 | 39.6 | 31.4 | 47.8 | 1 | 47.8 |
82 | Lexington, KY | TAN | °F | 25.9 | 28.5 | 35.9 | 45.6 | 55.0 | 63.4 | 66.9 | 65.8 | 58.3 | 47.1 | 37.4 | 28.9 | 46.5 | 1 | 46.6 |
83 | Louisville, KY | TAN | °F | 27.7 | 30.5 | 38.2 | 48.2 | 57.8 | 66.8 | 70.3 | 69.4 | 61.2 | 49.7 | 39.7 | 30.9 | 49.2 | 1 | 49.2 |
84 | Paducah, KY | TAN | °F | 27.4 | 30.6 | 38.3 | 47.8 | 57.2 | 65.7 | 69.1 | 66.8 | 58.2 | 47.5 | 38.2 | 30.0 | 48.1 | 1 | 48.1 |
85 | Baton Rouge, LA | TAN | °F | 42.2 | 44.5 | 50.5 | 56.9 | 65.5 | 71.4 | 73.9 | 73.2 | 68.6 | 58.1 | 48.2 | 42.8 | 58.0 | 1 | 58.0 |
86 | Lake Charles, LA | TAN | °F | 43.4 | 46.1 | 52.1 | 59.0 | 67.5 | 73.4 | 75.4 | 74.6 | 69.9 | 60.3 | 50.5 | 44.6 | 59.7 | 1 | 59.7 |
87 | New Orleans, LA | TAN | °F | 45.7 | 48.1 | 53.8 | 60.5 | 68.6 | 73.9 | 75.7 | 75.6 | 72.7 | 63.4 | 52.9 | 46.9 | 61.5 | 1 | 61.5 |
88 | Shreveport, LA | TAN | °F | 38.2 | 41.3 | 47.8 | 54.9 | 64.3 | 70.9 | 74.0 | 73.4 | 67.2 | 56.1 | 46.0 | 39.2 | 56.1 | 1 | 56.1 |
89 | Bangor, ME | TAN | °F | 8.5 | 11.1 | 21.7 | 32.9 | 43.3 | 53.3 | 58.8 | 57.1 | 48.7 | 37.8 | 29.5 | 17.3 | 35.0 | 1 | 35.0 |
90 | Caribou, ME | TAN | °F | 1.7 | 4.4 | 15.9 | 29.6 | 40.9 | 50.6 | 55.9 | 53.4 | 45.3 | 35.2 | 25.5 | 12.1 | 30.9 | 1 | 30.9 |
91 | Portland, ME | TAN | °F | 14.9 | 17.1 | 25.8 | 35.3 | 44.8 | 54.8 | 60.2 | 59.2 | 51.5 | 40.0 | 31.9 | 21.9 | 38.1 | 1 | 38.1 |
92 | Baltimore , MD | TAN | °F | 26.6 | 27.4 | 34.8 | 44.3 | 53.2 | 63.1 | 68.0 | 66.6 | 59.1 | 46.6 | 37.7 | 29.6 | 46.4 | 1 | 46.4 |
93 | Boston, MA | TAN | °F | 23.1 | 25.0 | 31.7 | 41.2 | 50.4 | 60.3 | 66.0 | 65.2 | 58.2 | 47.2 | 38.6 | 29.1 | 44.7 | 1 | 44.7 |
94 | Worchester, MA | TAN | °F | 17.7 | 19.6 | 26.9 | 37.5 | 47.2 | 56.9 | 62.0 | 61.1 | 53.7 | 42.4 | 33.8 | 23.8 | 40.2 | 1 | 40.2 |
95 | Alpena, MI | TAN | °F | 12.7 | 12.1 | 19.8 | 31.5 | 41.4 | 51.3 | 56.1 | 54.7 | 47.4 | 37.7 | 29.3 | 19.4 | 34.4 | 1 | 34.5 |
96 | Detroit Metro_AP, MI | TAN | °F | 19.6 | 21.6 | 28.8 | 39.9 | 49.9 | 60.5 | 64.1 | 63.4 | 55.2 | 44.0 | 34.6 | 24.9 | 42.2 | 1 | 42.2 |
97 | Detroit - City, MI | TAN | °F | 20.9 | 22.5 | 29.3 | 40.1 | 50.3 | 61.1 | 65.5 | 64.6 | 56.6 | 45.4 | 35.8 | 26.1 | 43.2 | 1 | 43.2 |
98 | Flint, MI | TAN | °F | 16.7 | 18.2 | 25.7 | 36.6 | 46.6 | 56.9 | 60.0 | 59.1 | 50.8 | 40.8 | 32.0 | 22.3 | 38.8 | 1 | 38.8 |
99 | Grand Rapids, MI | TAN | °F | 18.2 | 19.7 | 26.7 | 37.5 | 47.8 | 58.0 | 61.7 | 60.8 | 52.4 | 41.8 | 32.6 | 23.7 | 40.1 | 1 | 40.1 |
100 | Houghton Lake, MI | TAN | °F | 12.3 | 12.3 | 20.3 | 32.1 | 42.9 | 52.2 | 55.7 | 54.2 | 46.6 | 37.7 | 29.0 | 19.2 | 34.5 | 1 | 34.5 |
101 | Lansing, MI | TAN | °F | 16.5 | 17.9 | 25.4 | 36.2 | 46.2 | 56.4 | 59.5 | 58.7 | 50.3 | 40.4 | 31.7 | 22.1 | 38.4 | 1 | 38.4 |
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102 | Muskegon, MI | TAN | °F | 20.2 | 20.8 | 26.7 | 37.0 | 46.7 | 56.7 | 61.3 | 60.8 | 52.4 | 42.6 | 33.7 | 25.2 | 40.3 | 1 | 40.3 |
103 | Sault Ste Marie, MI | TAN | °F | 8.1 | 9.5 | 18.2 | 30.9 | 40.9 | 49.8 | 54.8 | 55.0 | 48.4 | 38.3 | 28.5 | 17.0 | 33.3 | 1 | 33.3 |
104 | Traverse City, MI | TAN | °F | 17.0 | 16.5 | 23.3 | 33.3 | 43.2 | 54.2 | 58.7 | 58.2 | 51.0 | 40.9 | 31.7 | 22.8 | 37.6 | 1 | 37.6 |
105 | Duluth, MN | TAN | °F | 2.6 | 7.1 | 18.2 | 30.7 | 41.4 | 50.6 | 55.9 | 55.4 | 47.2 | 35.7 | 23.0 | 9.4 | 31.4 | 1 | 31.4 |
106 | International Falls, MN | TAN | °F | -4.5 | 0.3 | 13.7 | 28.4 | 39.8 | 50.0 | 53.4 | 51.8 | 43.2 | 32.5 | 19.4 | 3.7 | 27.6 | 1 | 27.6 |
107 | Minneapolis-St Paul, MN | TAN | °F | 8.3 | 13.6 | 24.6 | 37.9 | 49.6 | 59.7 | 64.5 | 62.5 | 53.3 | 40.9 | 27.5 | 14.4 | 38.1 | 1 | 38.1 |
108 | Rochester_MN, MN | TAN | °F | 7.3 | 12.2 | 23.6 | 36.0 | 47.4 | 57.5 | 60.7 | 58.8 | 50.1 | 38.6 | 26.2 | 13.3 | 36.0 | 1 | 36.0 |
109 | St Cloud, MN | TAN | °F | 2.8 | 7.8 | 20.1 | 33.1 | 44.5 | 54.8 | 58.6 | 56.5 | 47.6 | 35.9 | 23.1 | 9.6 | 32.9 | 1 | 32.9 |
110 | Jackson, MS | TAN | °F | 37.0 | 39.3 | 45.9 | 53.3 | 62.5 | 69.2 | 72.1 | 71.4 | 65.5 | 53.9 | 43.9 | 37.9 | 54.3 | 1 | 54.3 |
111 | Meridian, MS | TAN | °F | 35.8 | 38.1 | 44.5 | 51.5 | 60.8 | 67.8 | 70.8 | 70.2 | 64.2 | 52.5 | 42.5 | 36.9 | 53.0 | 1 | 53.0 |
112 | Tupelo, MS | TAN | °F | 33.2 | 35.9 | 43.0 | 51.0 | 60.2 | 68.1 | 71.5 | 70.6 | 63.4 | 51.6 | 42.0 | 34.8 | 52.1 | 1 | 52.1 |
113 | Columbia_MO, MO | TAN | °F | 21.4 | 26.0 | 34.2 | 44.8 | 54.6 | 63.3 | 67.3 | 65.9 | 56.7 | 46.0 | 35.4 | 25.3 | 45.1 | 1 | 45.1 |
114 | Kansas City, MO | TAN | °F | 20.4 | 25.2 | 33.9 | 44.9 | 55.1 | 64.3 | 68.8 | 67.5 | 57.6 | 46.8 | 34.9 | 24.5 | 45.3 | 1 | 45.3 |
115 | Springfield_MO, MO | TAN | °F | 24.3 | 28.5 | 35.8 | 45.6 | 55.5 | 63.9 | 68.3 | 67.3 | 58.2 | 47.3 | 36.6 | 27.1 | 46.5 | 1 | 46.5 |
116 | St Louis - Lambert, MO | TAN | °F | 24.6 | 28.7 | 37.2 | 47.9 | 58.2 | 67.2 | 71.3 | 70.0 | 60.9 | 49.6 | 38.5 | 28.5 | 48.5 | 1 | 48.6 |
117 | St Louis - Spirit, MO | TAN | °F | 22.6 | 26.7 | 34.6 | 44.9 | 55.0 | 63.9 | 67.9 | 66.0 | 56.3 | 45.4 | 35.4 | 26.2 | 45.4 | 1 | 45.4 |
118 | Billings, MT | TAN | °F | 18.0 | 21.8 | 27.3 | 35.2 | 44.2 | 52.5 | 59.6 | 58.0 | 48.8 | 37.7 | 27.3 | 19.6 | 37.5 | 1 | 37.5 |
119 | Glasgow, MT | TAN | °F | 3.8 | 9.8 | 20.6 | 32.3 | 42.2 | 51.5 | 57.4 | 56.3 | 45.6 | 32.9 | 19.9 | 8.3 | 31.7 | 1 | 31.7 |
120 | Great Falls, MT | TAN | °F | 15.9 | 18.8 | 23.7 | 31.6 | 39.9 | 47.0 | 53.0 | 51.7 | 44.0 | 34.2 | 25.2 | 17.7 | 33.5 | 1 | 33.6 |
121 | Harve City, MT | TAN | °F | 6.4 | 12.0 | 20.7 | 31.4 | 40.8 | 48.9 | 54.1 | 52.5 | 42.6 | 31.1 | 20.4 | 9.9 | 30.9 | 1 | 30.9 |
122 | Helena, MT | TAN | °F | 13.5 | 18.4 | 24.9 | 32.8 | 41.8 | 49.0 | 55.3 | 53.0 | 44.4 | 33.5 | 23.1 | 14.5 | 33.7 | 1 | 33.7 |
123 | Kalispell, MT | TAN | °F | 17.2 | 20.0 | 25.5 | 31.9 | 39.4 | 45.2 | 49.1 | 47.2 | 39.6 | 30.5 | 24.8 | 18.3 | 32.4 | 1 | 32.4 |
124 | Missoula, MT | TAN | °F | 19.0 | 22.1 | 27.8 | 33.2 | 40.5 | 47.0 | 52.7 | 50.9 | 43.0 | 33.4 | 25.3 | 19.0 | 34.5 | 1 | 34.5 |
125 | Grand Island, NE | TAN | °F | 14.9 | 19.4 | 28.0 | 38.4 | 50.2 | 60.0 | 65.1 | 63.2 | 52.8 | 40.4 | 27.6 | 18.3 | 39.9 | 1 | 39.9 |
126 | Lincoln, NE | TAN | °F | 14.3 | 19.3 | 28.4 | 39.5 | 51.1 | 61.6 | 66.5 | 64.2 | 53.6 | 41.4 | 28.4 | 18.1 | 40.5 | 1 | 40.5 |
127 | Norfolk_NE, NE | TAN | °F | 13.0 | 18.0 | 26.9 | 38.1 | 49.2 | 59.4 | 64.1 | 62.2 | 52.0 | 39.7 | 26.7 | 16.8 | 38.8 | 1 | 38.8 |
128 | North Platte, NE | TAN | °F | 12.7 | 16.5 | 24.5 | 34.2 | 45.3 | 55.5 | 61.7 | 59.7 | 48.3 | 35.0 | 22.3 | 14.1 | 35.8 | 1 | 35.8 |
129 | Omaha, NE | TAN | °F | 14.2 | 19.5 | 28.8 | 40.7 | 52.0 | 62.1 | 67.0 | 64.8 | 54.6 | 42.7 | 29.8 | 18.9 | 41.3 | 1 | 41.3 |
130 | Scottsbluff, NE | TAN | °F | 14.8 | 17.7 | 24.6 | 32.6 | 43.5 | 52.9 | 59.1 | 57.1 | 46.2 | 33.7 | 22.5 | 14.9 | 35.0 | 1 | 35.0 |
131 | Valentine, NE | TAN | °F | 11.5 | 15.7 | 23.8 | 33.8 | 44.6 | 54.7 | 60.8 | 59.2 | 48.3 | 34.8 | 22.2 | 13.5 | 35.2 | 1 | 35.2 |
132 | Ely, NV | TAN | °F | 13.1 | 16.9 | 22.9 | 27.7 | 34.4 | 42.0 | 49.2 | 48.1 | 38.7 | 28.9 | 19.8 | 12.6 | 29.5 | 1 | 29.5 |
133 | Las Vegas, NV | TAN | °F | 39.4 | 43.2 | 49.2 | 55.6 | 65.8 | 74.3 | 81.2 | 79.8 | 71.4 | 58.7 | 46.3 | 38.7 | 58.6 | 1 | 58.6 |
134 | Lovelock, NV | TAN | °F | 20.8 | 25.3 | 29.2 | 35.2 | 44.8 | 51.9 | 58.3 | 54.6 | 45.3 | 35.2 | 24.4 | 19.3 | 37.0 | 1 | 37.0 |
135 | Mercury, NV | TAN | °F | 35.1 | 38.2 | 42.8 | 48.2 | 57.9 | 66.2 | 73.7 | 72.4 | 64.0 | 52.0 | 41.1 | 34.2 | 52.2 | 1 | 52.2 |
136 | Reno, NV | TAN | °F | 25.1 | 28.6 | 32.8 | 37.0 | 45.5 | 52.3 | 59.2 | 56.7 | 48.7 | 39.0 | 30.0 | 25.1 | 40.0 | 1 | 40.0 |
137 | Tonopah, NV | TAN | °F | 21.9 | 25.6 | 29.9 | 34.9 | 44.2 | 52.3 | 58.8 | 56.8 | 49.1 | 38.4 | 27.5 | 20.2 | 38.3 | 1 | 38.3 |
138 | Winnemucca, NV | TAN | °F | 20.5 | 24.4 | 27.5 | 31.4 | 39.4 | 46.3 | 53.5 | 49.9 | 40.7 | 30.5 | 23.1 | 18.8 | 33.8 | 1 | 33.8 |
139 | Concord, NH | TAN | °F | 12.3 | 14.6 | 23.2 | 33.2 | 43.2 | 53.8 | 58.5 | 57.1 | 48.4 | 36.8 | 29.0 | 18.8 | 35.7 | 1 | 35.7 |
140 | Atlantic City, NJ | TAN | °F | 25.5 | 25.9 | 32.7 | 41.9 | 50.5 | 61.0 | 66.5 | 65.0 | 57.5 | 45.6 | 37.1 | 28.7 | 44.8 | 1 | 44.8 |
141 | Newark, NJ | TAN | °F | 26.3 | 27.7 | 34.8 | 44.8 | 54.1 | 64.3 | 69.5 | 68.6 | 60.9 | 49.0 | 40.3 | 31.0 | 47.6 | 1 | 47.6 |
142 | Albuquerque, NM | TAN | °F | 27.6 | 31.4 | 36.4 | 43.7 | 53.8 | 62.3 | 67.1 | 65.4 | 58.6 | 46.7 | 35.0 | 27.5 | 46.3 | 1 | 46.3 |
143 | Gallup, NM | TAN | °F | 14.9 | 19.5 | 22.7 | 28.4 | 37.5 | 45.1 | 54.3 | 53.3 | 43.8 | 30.9 | 19.9 | 13.8 | 32.0 | 1 | 32.0 |
144 | Roswell, NM | TAN | °F | 27.8 | 32.5 | 38.5 | 46.1 | 56.4 | 64.5 | 68.5 | 67.0 | 59.5 | 47.9 | 35.2 | 27.7 | 47.6 | 1 | 47.6 |
145 | Albany, NY | TAN | °F | 16.1 | 18.1 | 26.4 | 37.7 | 47.7 | 57.9 | 62.0 | 60.9 | 52.7 | 40.8 | 32.5 | 22.4 | 39.6 | 1 | 39.6 |
146 | Binghamton, NY | TAN | °F | 16.6 | 17.6 | 25.1 | 36.3 | 46.5 | 56.1 | 59.9 | 59.1 | 51.3 | 40.9 | 32.0 | 22.0 | 38.6 | 1 | 38.6 |
147 | Buffalo, NY | TAN | °F | 19.3 | 19.7 | 26.5 | 37.2 | 47.9 | 58.4 | 62.6 | 61.7 | 54.2 | 43.7 | 34.7 | 24.9 | 40.9 | 1 | 40.9 |
148 | Long Island, NY | TAN | °F | 24.7 | 25.3 | 31.8 | 41.1 | 50.1 | 60.7 | 66.5 | 65.6 | 58.1 | 46.1 | 38.0 | 29.4 | 44.8 | 1 | 44.8 |
149 | Massena, NY | TAN | °F | 6.6 | 8.0 | 19.5 | 33.8 | 44.8 | 54.8 | 59.3 | 57.2 | 48.9 | 38.2 | 28.6 | 16.0 | 34.6 | 1 | 34.6 |
150 | New York-LaGuardia, NY | TAN | °F | 28.3 | 29.4 | 35.9 | 45.7 | 55.1 | 65.4 | 71.0 | 70.5 | 63.7 | 52.4 | 43.3 | 33.6 | 49.5 | 1 | 49.5 |
151 | New York-Kennedy, NY | TAN | °F | 27.1 | 28.1 | 34.6 | 43.9 | 53.0 | 63.1 | 68.9 | 68.3 | 61.5 | 50.1 | 41.2 | 32.0 | 47.6 | 1 | 47.7 |
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152 | Rochester, NY | TAN | °F | 18.7 | 19.3 | 26.4 | 37.2 | 47.0 | 57.1 | 61.2 | 60.3 | 52.7 | 42.4 | 33.7 | 24.4 | 40.0 | 1 | 40.0 |
153 | Syracuse, NY | TAN | °F | 17.0 | 18.0 | 25.7 | 36.9 | 47.0 | 57.2 | 61.7 | 60.6 | 52.7 | 42.2 | 33.5 | 23.4 | 39.7 | 1 | 39.7 |
154 | Asheville, NC | TAN | °F | 28.4 | 30.3 | 36.1 | 44.0 | 52.3 | 60.3 | 64.0 | 63.5 | 56.7 | 45.2 | 36.0 | 29.7 | 45.6 | 1 | 45.5 |
155 | Charlotte, NC | TAN | °F | 33.1 | 35.2 | 41.9 | 49.7 | 58.4 | 66.7 | 70.1 | 69.3 | 62.7 | 50.9 | 41.2 | 34.3 | 51.1 | 1 | 51.1 |
156 | Raleigh-Durham, NC | TAN | °F | 32.1 | 33.8 | 40.3 | 48.6 | 56.9 | 66.0 | 69.9 | 68.7 | 61.9 | 49.7 | 40.4 | 33.5 | 50.2 | 1 | 50.2 |
157 | Greensboro, NC | TAN | °F | 30.9 | 32.7 | 39.7 | 48.1 | 56.7 | 65.6 | 69.3 | 68.2 | 61.1 | 49.3 | 39.8 | 32.5 | 49.5 | 1 | 49.5 |
158 | Wilmington, NC | TAN | °F | 36.9 | 38.0 | 44.2 | 52.5 | 60.7 | 69.2 | 73.0 | 71.5 | 66.2 | 55.1 | 45.3 | 38.1 | 54.2 | 1 | 54.2 |
159 | Bismarck, ND | TAN | °F | 2.1 | 8.4 | 19.3 | 31.3 | 43.0 | 52.9 | 57.8 | 56.1 | 46.1 | 33.1 | 20.0 | 8.4 | 31.5 | 1 | 31.5 |
160 | Fargo, ND | TAN | °F | 0.3 | 5.7 | 19.3 | 33.5 | 45.3 | 56.0 | 59.6 | 57.8 | 48.6 | 36.1 | 21.6 | 7.9 | 32.6 | 1 | 32.6 |
161 | Minot, ND | TAN | °F | 3.5 | 8.8 | 19.3 | 32.1 | 43.3 | 53.4 | 58.2 | 56.2 | 47.0 | 34.4 | 20.9 | 8.9 | 32.2 | 1 | 32.2 |
162 | Williston, ND | TAN | °F | 0.5 | 7.4 | 18.4 | 30.9 | 40.9 | 50.6 | 56.6 | 54.9 | 43.8 | 31.3 | 18.1 | 6.0 | 29.9 | 1 | 30.0 |
163 | Akron, OH | TAN | °F | 20.1 | 21.7 | 29.0 | 39.7 | 49.2 | 58.9 | 62.5 | 61.5 | 53.9 | 43.0 | 34.1 | 24.7 | 41.5 | 1 | 41.5 |
164 | Cleveland, OH | TAN | °F | 21.6 | 23.2 | 29.8 | 40.4 | 50.0 | 60.1 | 64.1 | 63.2 | 55.8 | 45.3 | 36.3 | 26.4 | 43.0 | 1 | 43.0 |
165 | Columbus_OH, OH | TAN | °F | 23.0 | 25.0 | 32.7 | 43.1 | 52.4 | 62.3 | 65.7 | 64.6 | 56.8 | 45.2 | 36.2 | 27.2 | 44.5 | 1 | 44.5 |
166 | Dayton, OH | TAN | °F | 21.1 | 23.6 | 31.6 | 42.3 | 52.2 | 61.9 | 64.9 | 63.6 | 55.4 | 44.7 | 34.9 | 25.4 | 43.5 | 1 | 43.5 |
167 | Mansfield, OH | TAN | °F | 19.4 | 21.3 | 28.8 | 39.3 | 48.9 | 58.6 | 61.9 | 61.0 | 53.2 | 42.9 | 33.6 | 24.4 | 41.1 | 1 | 41.1 |
168 | Toledo, OH | TAN | °F | 19.4 | 21.5 | 28.9 | 39.7 | 49.4 | 59.5 | 62.8 | 61.8 | 53.5 | 42.9 | 33.7 | 24.1 | 41.5 | 1 | 41.4 |
169 | Youngstown, OH | TAN | °F | 20.1 | 21.3 | 28.2 | 38.8 | 47.3 | 56.6 | 60.2 | 59.2 | 52.1 | 42.0 | 34.3 | 24.7 | 40.4 | 1 | 40.4 |
170 | Oklahoma City, OK | TAN | °F | 28.7 | 32.8 | 40.5 | 49.1 | 59.3 | 67.4 | 71.5 | 70.6 | 62.5 | 51.0 | 39.5 | 30.9 | 50.3 | 1 | 50.3 |
171 | Tulsa, OK | TAN | °F | 28.9 | 32.9 | 40.9 | 50.1 | 60.2 | 68.6 | 73.4 | 72.2 | 62.6 | 51.3 | 40.4 | 31.3 | 51.1 | 1 | 51.1 |
172 | Astoria, OR | TAN | °F | 38.7 | 38.1 | 39.5 | 41.9 | 46.5 | 50.7 | 54.1 | 54.1 | 50.4 | 45.3 | 41.0 | 38.6 | 44.9 | 1 | 44.9 |
173 | Burns, OR | TAN | °F | 17.3 | 19.4 | 25.6 | 29.5 | 37.3 | 42.5 | 48.4 | 45.6 | 37.3 | 28.3 | 22.3 | 16.0 | 30.8 | 1 | 30.8 |
174 | Eugene, OR | TAN | °F | 35.6 | 36.0 | 38.0 | 40.5 | 44.7 | 48.3 | 52.7 | 52.2 | 48.4 | 42.4 | 38.6 | 35.5 | 42.7 | 1 | 42.7 |
175 | Medford, OR | TAN | °F | 33.0 | 34.5 | 37.2 | 40.6 | 47.0 | 52.1 | 58.7 | 57.5 | 50.8 | 42.2 | 36.4 | 33.1 | 43.6 | 1 | 43.6 |
176 | Pendleton, OR | TAN | °F | 29.5 | 31.4 | 35.4 | 39.6 | 46.4 | 52.0 | 58.4 | 57.5 | 50.6 | 40.8 | 34.0 | 29.1 | 42.1 | 1 | 42.1 |
177 | Salem, OR | TAN | °F | 36.0 | 35.9 | 38.3 | 40.9 | 46.1 | 50.3 | 54.9 | 54.3 | 50.2 | 43.7 | 39.4 | 35.7 | 43.8 | 1 | 43.8 |
178 | Allentown, PA | TAN | °F | 22.0 | 23.1 | 30.5 | 40.3 | 49.7 | 59.7 | 63.9 | 62.5 | 54.6 | 42.8 | 34.5 | 25.9 | 42.5 | 1 | 42.5 |
179 | Bradford, PA | TAN | °F | 15.5 | 15.9 | 22.9 | 33.2 | 41.6 | 50.7 | 54.1 | 53.5 | 46.4 | 36.9 | 30.0 | 20.0 | 35.1 | 1 | 35.1 |
180 | Erie, PA | TAN | °F | 22.0 | 22.0 | 28.3 | 39.0 | 49.1 | 59.7 | 64.2 | 63.4 | 56.5 | 46.1 | 37.3 | 27.5 | 42.9 | 1 | 42.9 |
181 | Middletown, PA | TAN | °F | 24.1 | 25.3 | 33.2 | 43.2 | 53.1 | 63.2 | 67.5 | 66.1 | 58.0 | 45.5 | 37.1 | 28.4 | 45.4 | 1 | 45.4 |
182 | Philadelphia, PA | TAN | °F | 27.4 | 28.3 | 35.5 | 45.4 | 54.8 | 64.9 | 70.2 | 69.0 | 61.6 | 49.6 | 40.5 | 31.5 | 48.2 | 1 | 48.2 |
183 | Pittsburgh, PA | TAN | °F | 22.2 | 23.5 | 30.8 | 41.3 | 50.2 | 59.6 | 63.5 | 62.5 | 54.8 | 43.4 | 35.3 | 26.2 | 42.8 | 1 | 42.8 |
184 | Scranton, PA | TAN | °F | 20.3 | 21.5 | 28.7 | 39.2 | 48.6 | 57.8 | 61.7 | 60.7 | 53.2 | 42.2 | 34.5 | 25.0 | 41.1 | 1 | 41.1 |
185 | Williamsport, PA | TAN | °F | 20.8 | 21.8 | 29.5 | 39.5 | 48.5 | 58.6 | 62.3 | 61.3 | 53.7 | 42.0 | 34.0 | 25.0 | 41.4 | 1 | 41.4 |
186 | Providence, RI | TAN | °F | 22.5 | 24.0 | 30.7 | 40.2 | 49.2 | 59.3 | 64.9 | 64.0 | 56.6 | 44.9 | 36.8 | 27.6 | 43.4 | 1 | 43.4 |
187 | Charleston, SC | TAN | °F | 39.6 | 41.6 | 47.8 | 54.8 | 63.2 | 70.7 | 74.0 | 73.3 | 68.3 | 57.7 | 48.0 | 41.1 | 56.7 | 1 | 56.7 |
188 | Columbia, SC | TAN | °F | 35.3 | 37.4 | 43.9 | 51.7 | 60.7 | 68.8 | 72.2 | 71.5 | 65.2 | 52.7 | 42.4 | 35.7 | 53.1 | 1 | 53.1 |
189 | Greer, SC | TAN | °F | 33.5 | 35.5 | 41.9 | 49.5 | 58.1 | 66.1 | 69.8 | 69.2 | 62.5 | 51.1 | 41.6 | 34.7 | 51.1 | 1 | 51.1 |
190 | Aberdeen, SD | TAN | °F | 2.2 | 8.2 | 20.4 | 32.9 | 45.2 | 55.7 | 60.1 | 57.3 | 47.2 | 34.4 | 20.4 | 8.5 | 32.7 | 1 | 32.7 |
191 | Huron, SD | TAN | °F | 6.7 | 12.0 | 22.6 | 34.6 | 46.5 | 57.0 | 61.9 | 59.9 | 49.7 | 36.3 | 23.1 | 11.9 | 35.2 | 1 | 35.2 |
192 | Pierre, SD | TAN | °F | 10.0 | 14.7 | 23.7 | 34.8 | 45.9 | 56.0 | 62.1 | 60.4 | 50.5 | 37.2 | 24.6 | 14.6 | 36.2 | 1 | 36.2 |
193 | Rapid City, SD | TAN | °F | 13.6 | 16.6 | 23.8 | 32.7 | 43.0 | 52.3 | 59.1 | 57.6 | 47.4 | 35.4 | 23.4 | 15.5 | 35.0 | 1 | 35.0 |
194 | Sioux Falls, SD | TAN | °F | 7.9 | 13.1 | 23.5 | 35.4 | 47.2 | 57.9 | 62.5 | 60.6 | 50.6 | 37.8 | 24.2 | 12.7 | 36.1 | 1 | 36.1 |
195 | Bristol, TN | TAN | °F | 27.2 | 29.5 | 35.5 | 44.0 | 52.5 | 61.2 | 64.9 | 63.7 | 56.4 | 44.7 | 35.6 | 28.9 | 45.3 | 1 | 45.3 |
196 | Chattanooga, TN | TAN | °F | 32.7 | 34.8 | 41.6 | 49.7 | 58.5 | 66.8 | 70.6 | 70.0 | 63.0 | 50.8 | 40.5 | 34.2 | 51.1 | 1 | 51.1 |
197 | Knoxville, TN | TAN | °F | 30.8 | 33.3 | 40.0 | 48.7 | 57.3 | 65.6 | 69.2 | 68.3 | 61.4 | 49.2 | 39.3 | 32.4 | 49.6 | 1 | 49.6 |
198 | Memphis, TN | TAN | °F | 34.0 | 37.1 | 44.7 | 53.9 | 63.1 | 70.9 | 74.1 | 73.2 | 65.8 | 54.6 | 43.9 | 36.2 | 54.3 | 1 | 54.3 |
199 | Nashville, TN | TAN | °F | 30.5 | 32.9 | 40.2 | 49.3 | 58.5 | 66.7 | 70.8 | 69.8 | 62.1 | 50.3 | 40.2 | 32.8 | 50.3 | 1 | 50.3 |
200 | Abilene, TX | TAN | °F | 34.2 | 37.8 | 44.9 | 52.6 | 62.1 | 69.1 | 72.6 | 72.0 | 64.4 | 54.6 | 43.4 | 35.2 | 53.6 | 1 | 53.6 |
201 | Amarillo, TX | TAN | °F | 24.9 | 28.0 | 34.1 | 42.4 | 52.8 | 61.7 | 65.8 | 64.8 | 56.9 | 45.3 | 33.2 | 25.8 | 44.7 | 1 | 44.6 |
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202 | Austin, TX | TAN | °F | 40.3 | 43.9 | 49.9 | 57.5 | 66.3 | 71.9 | 73.8 | 73.5 | 68.2 | 58.8 | 48.3 | 41.0 | 57.8 | 1 | 57.8 |
203 | Brownsville, TX | TAN | °F | 52.8 | 56.0 | 60.7 | 66.6 | 72.7 | 76.4 | 76.9 | 76.8 | 73.6 | 67.6 | 59.9 | 53.5 | 66.1 | 1 | 66.1 |
204 | Corpus Christi, TX | TAN | °F | 48.4 | 51.9 | 57.3 | 63.9 | 70.6 | 74.5 | 75.3 | 75.5 | 72.5 | 65.3 | 56.2 | 49.6 | 63.4 | 1 | 63.4 |
205 | Dallas-Fort Worth, TX | TAN | °F | 37.0 | 40.8 | 47.8 | 55.8 | 65.4 | 72.6 | 76.3 | 76.1 | 68.6 | 57.8 | 47.1 | 38.8 | 57.0 | 1 | 57.0 |
206 | El Paso, TX | TAN | °F | 34.6 | 38.8 | 44.3 | 52.2 | 62.3 | 69.8 | 72.2 | 70.6 | 64.5 | 53.3 | 40.8 | 33.9 | 53.1 | 1 | 53.1 |
207 | Houston, TX | TAN | °F | 43.8 | 47.0 | 52.7 | 59.6 | 67.9 | 73.4 | 75.1 | 74.7 | 69.9 | 61.0 | 51.2 | 44.9 | 60.1 | 1 | 60.1 |
208 | Lubbock, TX | TAN | °F | 28.0 | 31.6 | 38.2 | 46.8 | 57.3 | 65.4 | 69.0 | 67.5 | 59.6 | 48.6 | 36.6 | 28.5 | 48.1 | 1 | 48.1 |
209 | Lufkin, TX | TAN | °F | 39.3 | 42.4 | 48.6 | 55.6 | 64.7 | 70.7 | 72.8 | 72.1 | 66.8 | 56.5 | 46.8 | 40.3 | 56.4 | 1 | 56.4 |
210 | Midland, TX | TAN | °F | 31.8 | 35.9 | 42.1 | 50.1 | 60.9 | 68.5 | 71.0 | 69.7 | 62.7 | 52.4 | 39.8 | 32.1 | 51.4 | 1 | 51.4 |
211 | Port Arthur, TX | TAN | °F | 44.6 | 47.7 | 53.2 | 60.1 | 68.0 | 73.5 | 75.0 | 74.7 | 70.6 | 61.5 | 51.7 | 45.7 | 60.5 | 1 | 60.5 |
212 | San Angelo, TX | TAN | °F | 34.4 | 38.0 | 45.2 | 52.8 | 62.8 | 69.6 | 72.1 | 71.3 | 64.0 | 53.8 | 42.7 | 35.1 | 53.5 | 1 | 53.5 |
213 | San Antonio, TX | TAN | °F | 42.0 | 45.8 | 51.8 | 59.1 | 67.6 | 73.2 | 75.2 | 75.3 | 69.8 | 60.8 | 50.5 | 43.1 | 59.5 | 1 | 59.5 |
214 | Victoria, TX | TAN | °F | 44.5 | 48.0 | 53.7 | 60.5 | 68.3 | 73.3 | 74.8 | 74.4 | 70.1 | 61.6 | 51.9 | 45.5 | 60.5 | 1 | 60.6 |
215 | Waco, TX | TAN | °F | 37.6 | 41.3 | 48.1 | 55.7 | 64.7 | 71.7 | 75.0 | 74.4 | 67.3 | 57.2 | 46.9 | 39.0 | 56.6 | 1 | 56.6 |
216 | Cedar City, UT | TAN | °F | 19.2 | 23.3 | 28.3 | 33.5 | 42.2 | 50.9 | 59.0 | 57.7 | 47.7 | 36.0 | 25.0 | 18.7 | 36.8 | 1 | 36.8 |
217 | Salt Lake City, UT | TAN | °F | 23.3 | 26.9 | 34.4 | 40.2 | 49.0 | 57.3 | 66.4 | 64.9 | 54.3 | 42.2 | 31.1 | 24.1 | 42.9 | 1 | 42.8 |
218 | Burlington, VT | TAN | °F | 11.6 | 13.1 | 22.7 | 35.1 | 46.1 | 56.4 | 61.0 | 59.2 | 51.5 | 40.2 | 31.6 | 19.8 | 37.4 | 1 | 37.4 |
219 | DC-Dulles, VA | TAN | °F | 25.8 | 26.7 | 33.9 | 43.4 | 52.3 | 61.9 | 66.5 | 65.4 | 57.6 | 44.8 | 36.2 | 28.2 | 45.2 | 1 | 45.2 |
220 | DC-Reagan, VA | TAN | °F | 30.0 | 31.2 | 38.3 | 47.9 | 57.0 | 66.7 | 71.5 | 70.4 | 63.2 | 51.2 | 41.7 | 33.3 | 50.2 | 1 | 50.2 |
221 | Lynchburg, VA | TAN | °F | 27.6 | 29.1 | 35.9 | 44.7 | 53.0 | 61.9 | 65.8 | 64.7 | 57.5 | 45.5 | 36.5 | 29.1 | 46.0 | 1 | 45.9 |
222 | Norfolk, VA | TAN | °F | 34.5 | 35.2 | 41.6 | 50.2 | 58.7 | 68.1 | 72.7 | 71.6 | 66.4 | 54.8 | 45.1 | 37.2 | 53.0 | 1 | 53.0 |
223 | Richmond, VA | TAN | °F | 30.2 | 31.0 | 38.0 | 47.2 | 55.8 | 65.2 | 69.5 | 68.3 | 61.2 | 49.2 | 40.2 | 32.3 | 49.0 | 1 | 49.0 |
224 | Roanoke, VA | TAN | °F | 29.4 | 31.0 | 37.9 | 46.7 | 54.7 | 63.4 | 67.2 | 66.2 | 58.8 | 47.7 | 38.7 | 31.3 | 47.8 | 1 | 47.8 |
225 | Olympia, WA | TAN | °F | 33.8 | 32.9 | 35.3 | 38.0 | 43.4 | 47.8 | 51.3 | 50.9 | 46.4 | 40.9 | 36.6 | 33.4 | 40.9 | 1 | 40.9 |
226 | Quillayute, WA | TAN | °F | 36.4 | 35.6 | 37.0 | 39.1 | 43.5 | 47.9 | 51.2 | 51.0 | 47.5 | 42.4 | 38.6 | 35.7 | 42.2 | 1 | 42.2 |
227 | Seattle, WA | TAN | °F | 37.6 | 37.8 | 39.7 | 42.8 | 48.0 | 52.4 | 56.4 | 56.5 | 52.9 | 46.5 | 40.5 | 36.8 | 45.7 | 1 | 45.7 |
228 | Spokane, WA | TAN | °F | 24.3 | 26.4 | 30.9 | 36.4 | 43.8 | 49.9 | 56.7 | 55.7 | 47.7 | 37.3 | 29.3 | 23.7 | 38.5 | 1 | 38.5 |
229 | Stampede Pass, WA | TAN | °F | 24.0 | 25.7 | 28.6 | 31.8 | 37.8 | 42.4 | 49.0 | 49.3 | 45.5 | 36.7 | 29.2 | 23.5 | 35.3 | 1 | 35.3 |
230 | Yakima, WA | TAN | °F | 24.1 | 27.1 | 30.8 | 35.5 | 43.5 | 49.6 | 55.1 | 53.0 | 45.0 | 35.2 | 27.5 | 23.4 | 37.5 | 1 | 37.5 |
231 | Beckley, WV | TAN | °F | 24.2 | 26.2 | 32.9 | 42.7 | 50.3 | 58.6 | 62.0 | 61.1 | 54.2 | 43.8 | 35.2 | 27.0 | 43.2 | 1 | 43.2 |
232 | Charleston, WV | TAN | °F | 26.8 | 28.6 | 35.1 | 44.9 | 52.6 | 61.6 | 65.2 | 64.3 | 56.6 | 45.0 | 36.4 | 29.2 | 45.5 | 1 | 45.5 |
233 | Elkins, WV | TAN | °F | 20.6 | 21.5 | 28.1 | 37.0 | 45.9 | 55.1 | 58.9 | 58.3 | 50.7 | 38.1 | 30.3 | 22.9 | 39.0 | 1 | 39.0 |
234 | Huntington, WV | TAN | °F | 26.7 | 28.9 | 35.9 | 45.8 | 53.7 | 62.5 | 66.1 | 65.0 | 57.1 | 45.7 | 37.2 | 29.4 | 46.2 | 1 | 46.2 |
235 | Eau Claire, WI | TAN | °F | 6.6 | 11.2 | 22.0 | 34.8 | 46.1 | 56.4 | 60.5 | 58.9 | 49.8 | 38.1 | 25.7 | 12.8 | 35.2 | 1 | 35.2 |
236 | Green Bay, WI | TAN | °F | 10.7 | 14.0 | 23.7 | 35.1 | 45.5 | 55.9 | 59.2 | 58.0 | 49.6 | 39.1 | 28.4 | 16.9 | 36.3 | 1 | 36.3 |
237 | La Crosse, WI | TAN | °F | 9.9 | 15.0 | 25.7 | 38.7 | 49.5 | 59.6 | 63.6 | 61.9 | 53.2 | 41.6 | 29.3 | 16.5 | 38.7 | 1 | 38.7 |
238 | Madison, WI | TAN | °F | 12.1 | 16.2 | 25.4 | 36.7 | 47.3 | 57.6 | 61.5 | 59.8 | 51.0 | 40.1 | 29.3 | 17.6 | 37.9 | 1 | 37.9 |
239 | Milwaukee, WI | TAN | °F | 16.9 | 20.6 | 28.5 | 38.1 | 47.7 | 58.5 | 64.2 | 64.1 | 55.9 | 44.6 | 33.0 | 21.9 | 41.2 | 1 | 41.2 |
240 | Casper, WY | TAN | °F | 16.2 | 18.1 | 23.7 | 30.0 | 38.7 | 46.7 | 54.4 | 53.3 | 43.4 | 32.7 | 23.8 | 16.4 | 33.1 | 1 | 33.1 |
241 | Cheyenne, WY | TAN | °F | 18.8 | 19.8 | 25.1 | 31.3 | 40.7 | 49.2 | 56.1 | 54.6 | 45.4 | 34.4 | 25.1 | 19.1 | 35.0 | 1 | 35.0 |
242 | Lander, WY | TAN | °F | 12.5 | 16.2 | 24.9 | 32.5 | 41.6 | 49.6 | 57.5 | 56.1 | 46.4 | 34.2 | 21.8 | 13.2 | 33.9 | 1 | 33.9 |
243 | Rock Springs, WY | TAN | °F | 13.6 | 15.5 | 23.8 | 29.7 | 38.6 | 46.8 | 55.0 | 53.3 | 43.6 | 33.2 | 22.1 | 14.2 | 32.5 | 1 | 32.5 |
244 | Sheridan, WY | TAN | °F | 13.0 | 16.8 | 23.4 | 31.4 | 39.8 | 47.9 | 54.8 | 53.2 | 43.5 | 32.5 | 21.5 | 13.6 | 32.6 | 1 | 32.6 |
245 | Birmingham, AL | TAX | °F | 53.7 | 57.8 | 65.9 | 73.9 | 80.9 | 86.8 | 90.0 | 89.8 | 84.5 | 74.7 | 64.2 | 55.3 | 73.1 | 2 | 73.1 |
246 | Huntsville, AL | TAX | °F | 50.3 | 54.4 | 63.1 | 72.3 | 79.9 | 86.3 | 88.9 | 89.2 | 83.7 | 73.4 | 61.6 | 52.1 | 71.3 | 2 | 71.3 |
247 | Mobile, AL | TAX | °F | 60.8 | 64.2 | 70.4 | 76.7 | 84.0 | 88.3 | 90.1 | 89.9 | 86.4 | 78.5 | 69.5 | 62.1 | 76.7 | 2 | 76.7 |
248 | Montgomery, AL | TAX | °F | 57.7 | 62.0 | 69.4 | 76.6 | 83.9 | 89.4 | 91.8 | 91.5 | 86.9 | 77.7 | 67.9 | 59.1 | 76.2 | 2 | 76.2 |
249 | Phoenix, AZ | TAX | °F | 66.7 | 69.8 | 76.1 | 83.6 | 93.8 | 102.6 | 105.4 | 103.6 | 99.6 | 87.8 | 75.1 | 65.6 | 85.8 | 2 | 85.8 |
250 | Prescott, AZ | TAX | °F | 51.4 | 54.4 | 60.0 | 66.4 | 76.5 | 85.6 | 89.2 | 86.5 | 82.2 | 71.4 | 60.1 | 51.1 | 69.6 | 2 | 69.6 |
251 | Tucson, AZ | TAX | °F | 65.8 | 68.4 | 74.2 | 81.7 | 91.7 | 99.9 | 99.6 | 97.3 | 94.7 | 85.1 | 74.1 | 65.0 | 83.1 | 2 | 83.1 |
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252 | Fort Smith, AR | TAX | °F | 49.4 | 55.3 | 63.7 | 73.0 | 79.8 | 87.1 | 92.3 | 92.8 | 84.4 | 74.3 | 61.8 | 51.6 | 72.1 | 2 | 72.1 |
253 | Little Rock, AR | TAX | °F | 50.6 | 55.5 | 63.7 | 73.1 | 80.8 | 88.1 | 91.8 | 92.2 | 84.9 | 74.4 | 62.1 | 52.3 | 72.5 | 2 | 72.5 |
254 | Arcata, CA | TAX | °F | 55.1 | 55.6 | 55.5 | 56.2 | 58.9 | 61.1 | 62.2 | 63.2 | 63.2 | 61.9 | 57.5 | 54.9 | 58.8 | 2 | 58.8 |
255 | Bakersfield, CA | TAX | °F | 56.9 | 62.9 | 69.0 | 74.1 | 83.3 | 90.6 | 96.9 | 95.7 | 90.4 | 79.0 | 65.7 | 57.3 | 76.8 | 2 | 76.8 |
256 | Bishop, CA | TAX | °F | 53.0 | 56.2 | 64.5 | 70.5 | 80.8 | 90.4 | 97.5 | 95.5 | 87.6 | 75.2 | 61.9 | 52.5 | 73.8 | 2 | 73.8 |
257 | Daggett, CA | TAX | °F | 60.8 | 64.4 | 71.7 | 78.3 | 88.9 | 98.0 | 104.6 | 103.1 | 95.7 | 82.5 | 69.1 | 59.6 | 81.4 | 2 | 81.4 |
258 | Fresno, CA | TAX | °F | 55.0 | 61.1 | 67.4 | 73.1 | 83.2 | 90.9 | 97.7 | 96.3 | 90.7 | 78.5 | 64.7 | 55.1 | 76.1 | 2 | 76.1 |
259 | Long Beach, CA | TAX | °F | 66.5 | 65.9 | 67.7 | 70.4 | 72.6 | 75.7 | 80.3 | 82.5 | 81.0 | 76.0 | 71.4 | 66.0 | 73.0 | 2 | 73.0 |
260 | Los Angeles AP, CA | TAX | °F | 64.9 | 64.4 | 64.7 | 66.5 | 68.5 | 71.0 | 73.9 | 75.3 | 74.5 | 72.3 | 69.3 | 64.8 | 69.2 | 2 | 69.2 |
261 | Redding, CA | TAX | °F | 55.0 | 58.3 | 64.9 | 69.6 | 80.4 | 89.3 | 98.1 | 96.2 | 90.4 | 77.1 | 62.5 | 54.0 | 74.7 | 2 | 74.7 |
262 | Sacramento, CA | TAX | °F | 54.3 | 59.6 | 65.4 | 70.3 | 79.3 | 86.1 | 91.4 | 90.9 | 87.4 | 77.1 | 63.8 | 54.4 | 73.3 | 2 | 73.3 |
263 | San Diego, CA | TAX | °F | 64.5 | 64.3 | 65.0 | 66.6 | 67.9 | 70.1 | 73.4 | 75.6 | 75.0 | 72.0 | 68.6 | 64.2 | 68.9 | 2 | 68.9 |
264 | San Francisco AP, CA | TAX | °F | 55.9 | 58.6 | 61.4 | 63.3 | 66.3 | 69.2 | 70.6 | 71.6 | 72.5 | 69.4 | 62.3 | 56.2 | 64.8 | 2 | 64.8 |
265 | Santa Barbara, CA | TAX | °F | 63.7 | 63.8 | 64.8 | 67.2 | 69.0 | 70.7 | 73.2 | 74.2 | 73.9 | 71.9 | 68.7 | 63.7 | 68.8 | 2 | 68.7 |
266 | Santa Maria, CA | TAX | °F | 63.2 | 63.6 | 64.9 | 66.5 | 68.3 | 69.9 | 71.7 | 72.4 | 73.3 | 72.2 | 68.5 | 63.1 | 68.1 | 2 | 68.1 |
267 | Stockton, CA | TAX | °F | 54.5 | 60.4 | 66.5 | 71.7 | 80.6 | 87.8 | 93.4 | 92.3 | 88.5 | 78.0 | 64.6 | 54.7 | 74.4 | 2 | 74.4 |
268 | Alamosa, CO | TAX | °F | 34.2 | 39.7 | 50.1 | 58.5 | 69.1 | 78.0 | 81.7 | 78.9 | 72.6 | 61.3 | 46.5 | 34.9 | 58.8 | 2 | 58.8 |
269 | Colorado Springs, CO | TAX | °F | 42.6 | 45.0 | 51.9 | 58.6 | 68.8 | 78.1 | 84.1 | 80.9 | 74.2 | 62.6 | 50.1 | 42.5 | 61.6 | 2 | 61.6 |
270 | Denver, CO | TAX | °F | 42.9 | 45.7 | 53.7 | 60.1 | 70.6 | 80.9 | 88.0 | 85.2 | 77.3 | 64.0 | 51.1 | 43.0 | 63.5 | 2 | 63.5 |
271 | Grand Junction, CO | TAX | °F | 37.4 | 45.3 | 56.5 | 64.4 | 76.2 | 86.9 | 93.4 | 89.3 | 79.9 | 66.0 | 49.9 | 38.0 | 65.3 | 2 | 65.3 |
272 | Limon, CO | TAX | °F | 41.7 | 44.2 | 52.7 | 59.5 | 69.7 | 79.6 | 86.2 | 82.7 | 75.8 | 63.4 | 49.6 | 41.8 | 62.2 | 2 | 62.2 |
273 | Pueblo, CO | TAX | °F | 47.2 | 50.8 | 58.9 | 66.1 | 76.7 | 86.3 | 92.3 | 88.8 | 81.4 | 68.9 | 55.1 | 46.8 | 68.3 | 2 | 68.3 |
274 | Bridgeport, CT | TAX | °F | 37.2 | 39.1 | 46.3 | 57.1 | 66.8 | 76.4 | 81.4 | 80.4 | 73.7 | 62.7 | 52.4 | 42.1 | 59.6 | 2 | 59.6 |
275 | Hartford, CT | TAX | °F | 34.4 | 37.5 | 46.7 | 60.2 | 70.4 | 79.1 | 83.6 | 82.2 | 74.4 | 62.3 | 50.8 | 39.5 | 60.1 | 2 | 60.1 |
276 | Wilmington_DE, DE | TAX | °F | 40.5 | 42.7 | 51.6 | 63.1 | 72.1 | 80.9 | 85.1 | 83.9 | 76.8 | 65.5 | 55.0 | 44.7 | 63.5 | 2 | 63.5 |
277 | Daytona Beach, FL | TAX | °F | 68.4 | 69.9 | 74.2 | 78.8 | 84.5 | 87.7 | 89.5 | 88.8 | 86.3 | 81.5 | 75.1 | 70.2 | 79.6 | 2 | 79.6 |
278 | Fort Myers, FL | TAX | °F | 74.2 | 76.2 | 79.6 | 83.5 | 88.5 | 90.3 | 90.7 | 90.8 | 89.3 | 85.8 | 80.2 | 75.5 | 83.7 | 2 | 83.7 |
279 | Gainesville, FL | TAX | °F | 66.3 | 69.0 | 74.4 | 80.0 | 86.4 | 89.0 | 90.2 | 89.4 | 86.6 | 80.7 | 73.6 | 67.6 | 79.4 | 2 | 79.4 |
280 | Jacksonville, FL | TAX | °F | 64.5 | 67.2 | 72.7 | 78.3 | 84.8 | 88.7 | 91.0 | 89.6 | 85.8 | 79.6 | 72.2 | 65.4 | 78.3 | 2 | 78.3 |
281 | Key West, FL | TAX | °F | 74.4 | 75.7 | 78.2 | 81.0 | 84.6 | 87.7 | 89.0 | 89.4 | 87.7 | 84.5 | 79.6 | 75.7 | 82.3 | 2 | 82.3 |
282 | Miami, FL | TAX | °F | 75.5 | 77.0 | 79.6 | 82.4 | 86.2 | 88.4 | 89.9 | 90.0 | 88.2 | 85.1 | 80.5 | 76.9 | 83.3 | 2 | 83.3 |
283 | Orlando, FL | TAX | °F | 70.7 | 72.8 | 77.2 | 81.7 | 87.2 | 89.5 | 90.8 | 90.5 | 88.3 | 83.4 | 77.0 | 71.8 | 81.8 | 2 | 81.7 |
284 | Pensacola, FL | TAX | °F | 61.0 | 63.9 | 69.8 | 75.6 | 83.4 | 88.4 | 89.9 | 89.4 | 86.6 | 79.0 | 70.1 | 62.6 | 76.6 | 2 | 76.6 |
285 | Tallahassee, FL | TAX | °F | 63.6 | 66.8 | 73.3 | 79.4 | 86.7 | 90.1 | 91.6 | 90.9 | 87.9 | 80.9 | 72.0 | 64.7 | 79.0 | 2 | 79.0 |
286 | Tampa, FL | TAX | °F | 69.8 | 71.6 | 75.9 | 80.8 | 86.7 | 89.1 | 89.5 | 89.6 | 88.4 | 83.8 | 77.1 | 71.4 | 81.2 | 2 | 81.1 |
287 | Vero Beach, FL | TAX | °F | 72.3 | 73.9 | 77.1 | 80.2 | 84.6 | 87.9 | 89.4 | 89.3 | 87.5 | 83.7 | 78.3 | 74.1 | 81.5 | 2 | 81.5 |
288 | West Palm Beach, FL | TAX | °F | 74.0 | 75.6 | 78.4 | 81.2 | 85.3 | 87.8 | 89.2 | 89.3 | 87.6 | 84.4 | 79.4 | 75.5 | 82.3 | 2 | 82.3 |
289 | Athens, GA | TAX | °F | 53.2 | 56.8 | 64.8 | 72.9 | 80.2 | 86.7 | 89.8 | 88.6 | 82.7 | 73.1 | 63.5 | 54.5 | 72.2 | 2 | 72.2 |
290 | Atlanta, GA | TAX | °F | 52.8 | 56.5 | 64.1 | 72.2 | 79.5 | 85.5 | 88.4 | 87.6 | 81.9 | 72.4 | 62.7 | 53.9 | 71.5 | 2 | 71.5 |
291 | Augusta, GA | TAX | °F | 57.7 | 61.1 | 68.7 | 76.4 | 83.8 | 89.2 | 91.8 | 90.6 | 85.5 | 76.6 | 67.6 | 58.9 | 75.7 | 2 | 75.7 |
292 | Columbus, GA | TAX | °F | 57.4 | 61.2 | 68.7 | 76.0 | 83.4 | 88.5 | 91.3 | 90.4 | 85.5 | 76.4 | 67.2 | 58.4 | 75.4 | 2 | 75.4 |
293 | Macon, GA | TAX | °F | 57.8 | 61.3 | 68.8 | 76.1 | 83.9 | 89.0 | 91.7 | 90.5 | 85.5 | 76.6 | 67.6 | 58.9 | 75.7 | 2 | 75.6 |
294 | Savannah, GA | TAX | °F | 60.5 | 63.5 | 70.2 | 76.9 | 83.6 | 88.3 | 91.3 | 89.7 | 85.2 | 77.6 | 69.5 | 61.8 | 76.5 | 2 | 76.5 |
295 | Hilo, HI | TAX | °F | 78.6 | 78.1 | 78.5 | 78.7 | 80.7 | 81.9 | 82.7 | 83.0 | 83.0 | 82.3 | 80.4 | 79.0 | 80.6 | 2 | 80.6 |
296 | Honolulu, HI | TAX | °F | 79.5 | 79.6 | 80.4 | 82.3 | 84.1 | 86.3 | 87.2 | 88.0 | 87.6 | 86.0 | 83.2 | 80.8 | 83.8 | 2 | 83.8 |
297 | Kahului, HI | TAX | °F | 79.7 | 79.7 | 80.3 | 81.6 | 83.9 | 85.5 | 86.3 | 87.0 | 87.0 | 86.0 | 83.1 | 80.9 | 83.4 | 2 | 83.4 |
298 | Lihue, HI | TAX | °F | 77.1 | 76.6 | 77.3 | 78.2 | 80.5 | 82.4 | 83.4 | 83.9 | 84.0 | 82.7 | 80.0 | 78.2 | 80.4 | 2 | 80.4 |
299 | Boise, ID | TAX | °F | 38.5 | 45.3 | 54.4 | 61.0 | 71.3 | 80.0 | 91.3 | 89.3 | 79.1 | 64.0 | 47.8 | 38.5 | 63.4 | 2 | 63.4 |
300 | Lewiston, ID | TAX | °F | 41.1 | 46.7 | 54.1 | 60.9 | 70.1 | 77.1 | 88.9 | 88.1 | 78.2 | 61.6 | 47.4 | 39.7 | 62.8 | 2 | 62.8 |
301 | Pocatello, ID | TAX | °F | 33.4 | 38.1 | 49.0 | 57.4 | 67.9 | 76.7 | 87.9 | 86.8 | 76.0 | 60.7 | 44.5 | 33.8 | 59.3 | 2 | 59.4 |
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302 | Chicago, IL | TAX | °F | 30.7 | 35.2 | 46.0 | 58.4 | 69.1 | 78.9 | 83.0 | 81.0 | 74.2 | 61.8 | 47.7 | 34.9 | 58.4 | 2 | 58.4 |
303 | Moline, IL | TAX | °F | 30.5 | 35.8 | 48.7 | 62.1 | 72.3 | 81.6 | 84.5 | 82.8 | 76.2 | 63.8 | 48.7 | 34.9 | 60.2 | 2 | 60.2 |
304 | Peoria, IL | TAX | °F | 32.1 | 37.8 | 50.0 | 62.6 | 72.3 | 81.4 | 84.5 | 83.0 | 76.5 | 64.1 | 49.7 | 36.4 | 60.9 | 2 | 60.9 |
305 | Rockford, IL | TAX | °F | 28.3 | 33.4 | 45.7 | 59.4 | 70.1 | 79.5 | 82.5 | 81.0 | 74.2 | 61.7 | 46.5 | 32.8 | 57.9 | 2 | 57.9 |
306 | Springfield_IL, IL | TAX | °F | 34.3 | 40.2 | 51.7 | 64.3 | 73.9 | 82.1 | 85.0 | 84.1 | 78.2 | 66.1 | 51.7 | 38.7 | 62.5 | 2 | 62.5 |
307 | Evansville, IN | TAX | °F | 40.7 | 45.6 | 55.6 | 67.2 | 76.0 | 84.4 | 87.2 | 87.3 | 80.6 | 69.2 | 55.5 | 43.8 | 66.1 | 2 | 66.1 |
308 | Fort Wayne, IN | TAX | °F | 32.0 | 36.2 | 47.4 | 60.7 | 70.9 | 80.1 | 83.2 | 81.3 | 75.5 | 63.1 | 49.0 | 36.1 | 59.6 | 2 | 59.6 |
309 | Indianapolis, IN | TAX | °F | 35.6 | 40.2 | 51.2 | 63.3 | 72.3 | 81.1 | 84.1 | 83.6 | 77.3 | 65.1 | 51.6 | 39.3 | 62.0 | 2 | 62.1 |
310 | South Bend, IN | TAX | °F | 31.3 | 35.4 | 46.5 | 59.5 | 69.6 | 79.1 | 82.3 | 80.5 | 73.9 | 61.7 | 47.8 | 35.5 | 58.6 | 2 | 58.6 |
311 | Des Moines, IA | TAX | °F | 29.6 | 35.5 | 48.0 | 61.3 | 71.2 | 80.5 | 84.3 | 82.7 | 75.5 | 62.9 | 47.4 | 34.5 | 59.5 | 2 | 59.5 |
312 | Dubuque, IA | TAX | °F | 26.0 | 31.1 | 43.6 | 57.6 | 68.4 | 77.6 | 80.4 | 78.9 | 71.9 | 59.5 | 44.3 | 30.6 | 55.8 | 2 | 55.8 |
313 | Mason City, IA | TAX | °F | 23.6 | 29.0 | 41.6 | 57.7 | 68.9 | 78.5 | 81.6 | 79.4 | 72.9 | 59.8 | 42.9 | 28.7 | 55.4 | 2 | 55.4 |
314 | Sioux City, IA | TAX | °F | 28.9 | 34.7 | 46.7 | 61.1 | 72.2 | 81.2 | 84.4 | 82.6 | 76.0 | 63.0 | 46.2 | 32.7 | 59.1 | 2 | 59.1 |
315 | Waterloo, IA | TAX | °F | 26.3 | 31.5 | 44.6 | 59.6 | 70.6 | 80.0 | 82.7 | 80.8 | 74.7 | 61.5 | 45.3 | 31.2 | 57.4 | 2 | 57.4 |
316 | Concordia, KS | TAX | °F | 37.6 | 43.2 | 53.9 | 64.0 | 73.7 | 84.3 | 89.7 | 87.9 | 79.3 | 66.8 | 51.6 | 40.0 | 64.3 | 2 | 64.3 |
317 | Dodge City, KS | TAX | °F | 43.6 | 48.3 | 57.2 | 66.7 | 76.6 | 86.0 | 91.9 | 89.7 | 81.5 | 69.2 | 55.1 | 44.6 | 67.6 | 2 | 67.5 |
318 | Goodland, KS | TAX | °F | 41.8 | 45.4 | 54.4 | 62.7 | 72.9 | 83.2 | 89.2 | 86.3 | 78.5 | 65.6 | 51.7 | 42.9 | 64.5 | 2 | 64.6 |
319 | Russell, KS | TAX | °F | 40.7 | 45.6 | 55.6 | 65.2 | 75.1 | 85.6 | 91.6 | 89.1 | 80.7 | 68.3 | 53.9 | 42.3 | 66.1 | 2 | 66.1 |
320 | Topeka, KS | TAX | °F | 39.0 | 45.3 | 55.7 | 65.9 | 75.4 | 83.9 | 89.0 | 88.5 | 79.6 | 68.1 | 53.9 | 42.3 | 65.6 | 2 | 65.6 |
321 | Wichita, KS | TAX | °F | 42.2 | 48.5 | 57.3 | 67.0 | 76.3 | 85.8 | 91.3 | 90.4 | 81.7 | 69.6 | 55.7 | 44.0 | 67.5 | 2 | 67.5 |
322 | Cincinnati, KY | TAX | °F | 38.3 | 42.3 | 52.2 | 64.2 | 72.9 | 81.2 | 84.4 | 84.2 | 77.5 | 65.6 | 52.9 | 41.4 | 63.1 | 2 | 63.1 |
323 | Jackson_KY, KY | TAX | °F | 43.1 | 46.9 | 56.2 | 67.4 | 73.7 | 80.4 | 83.2 | 83.4 | 77.3 | 67.4 | 55.9 | 46.2 | 65.1 | 2 | 65.1 |
324 | Lexington, KY | TAX | °F | 40.8 | 44.8 | 54.2 | 65.4 | 73.6 | 81.8 | 84.9 | 84.9 | 78.3 | 66.9 | 54.4 | 43.5 | 64.5 | 2 | 64.5 |
325 | Louisville, KY | TAX | °F | 42.3 | 46.8 | 56.6 | 67.9 | 76.0 | 84.1 | 87.3 | 87.4 | 80.6 | 69.2 | 56.6 | 44.9 | 66.7 | 2 | 66.6 |
326 | Paducah, KY | TAX | °F | 43.4 | 48.5 | 58.3 | 69.0 | 77.5 | 85.4 | 88.3 | 88.2 | 81.5 | 70.6 | 57.3 | 46.0 | 67.8 | 2 | 67.8 |
327 | Baton Rouge, LA | TAX | °F | 61.6 | 65.2 | 71.4 | 78.0 | 85.0 | 89.4 | 90.9 | 91.3 | 87.6 | 79.7 | 70.1 | 63.1 | 77.8 | 2 | 77.8 |
328 | Lake Charles, LA | TAX | °F | 61.4 | 64.7 | 70.8 | 77.2 | 84.2 | 89.0 | 90.6 | 91.2 | 87.8 | 80.3 | 70.5 | 63.3 | 77.6 | 2 | 77.6 |
329 | New Orleans, LA | TAX | °F | 61.8 | 65.1 | 70.9 | 77.5 | 84.7 | 88.9 | 90.6 | 90.4 | 87.0 | 79.5 | 70.5 | 63.6 | 77.5 | 2 | 77.5 |
330 | Shreveport, LA | TAX | °F | 57.2 | 61.4 | 68.5 | 76.1 | 83.3 | 89.6 | 92.9 | 93.3 | 87.6 | 77.8 | 66.5 | 58.4 | 76.0 | 2 | 76.1 |
331 | Bangor, ME | TAX | °F | 27.0 | 30.5 | 39.7 | 52.7 | 64.9 | 74.4 | 79.1 | 78.3 | 69.7 | 56.8 | 45.1 | 33.8 | 54.3 | 2 | 54.3 |
332 | Caribou, ME | TAX | °F | 19.0 | 22.9 | 33.5 | 46.8 | 61.6 | 71.2 | 75.1 | 73.9 | 65.4 | 51.4 | 38.5 | 26.5 | 48.8 | 2 | 48.8 |
333 | Portland, ME | TAX | °F | 30.8 | 33.7 | 41.3 | 52.8 | 62.8 | 72.6 | 77.7 | 77.2 | 69.4 | 57.9 | 47.4 | 37.2 | 55.1 | 2 | 55.1 |
334 | Baltimore , MD | TAX | °F | 42.2 | 44.7 | 53.5 | 65.1 | 73.9 | 82.8 | 86.9 | 85.3 | 78.0 | 66.7 | 56.2 | 45.5 | 65.0 | 2 | 65.1 |
335 | Boston, MA | TAX | °F | 36.2 | 38.3 | 45.1 | 55.8 | 65.7 | 75.8 | 80.8 | 79.3 | 72.1 | 61.3 | 51.1 | 41.4 | 58.6 | 2 | 58.6 |
336 | Worchester, MA | TAX | °F | 31.2 | 34.0 | 42.2 | 55.0 | 65.2 | 73.5 | 77.9 | 76.7 | 68.9 | 57.8 | 47.3 | 36.6 | 55.5 | 2 | 55.5 |
337 | Alpena, MI | TAX | °F | 26.9 | 29.1 | 38.3 | 51.6 | 63.9 | 74.3 | 78.0 | 76.8 | 69.1 | 56.1 | 43.1 | 32.3 | 53.3 | 2 | 53.3 |
338 | Detroit Metro_AP, MI | TAX | °F | 31.9 | 34.9 | 45.4 | 58.7 | 69.1 | 78.9 | 82.3 | 80.7 | 73.7 | 61.4 | 48.1 | 36.1 | 58.4 | 2 | 58.4 |
339 | Detroit - City, MI | TAX | °F | 32.3 | 35.3 | 45.0 | 58.1 | 68.9 | 79.0 | 82.8 | 81.0 | 73.8 | 61.2 | 48.1 | 36.5 | 58.5 | 2 | 58.5 |
340 | Flint, MI | TAX | °F | 29.8 | 33.0 | 43.4 | 57.1 | 68.1 | 77.9 | 81.1 | 79.4 | 72.4 | 59.7 | 46.5 | 34.4 | 56.9 | 2 | 56.9 |
341 | Grand Rapids, MI | TAX | °F | 29.8 | 32.8 | 43.4 | 57.2 | 68.2 | 77.9 | 81.1 | 79.4 | 72.2 | 59.5 | 46.1 | 34.4 | 56.8 | 2 | 56.8 |
342 | Houghton Lake, MI | TAX | °F | 26.1 | 29.1 | 39.7 | 53.5 | 65.5 | 75.5 | 78.6 | 76.9 | 69.1 | 55.8 | 42.3 | 31.0 | 53.6 | 2 | 53.6 |
343 | Lansing, MI | TAX | °F | 29.8 | 32.9 | 43.6 | 57.3 | 67.9 | 77.7 | 81.0 | 79.2 | 72.3 | 59.6 | 46.3 | 34.3 | 56.8 | 2 | 56.8 |
344 | Muskegon, MI | TAX | °F | 30.6 | 33.1 | 42.5 | 55.2 | 65.9 | 75.3 | 78.9 | 77.9 | 70.9 | 58.5 | 45.9 | 35.2 | 55.8 | 2 | 55.8 |
345 | Sault Ste Marie, MI | TAX | °F | 22.2 | 25.2 | 34.2 | 47.8 | 61.1 | 70.8 | 74.2 | 73.8 | 65.8 | 52.4 | 39.6 | 29.0 | 49.7 | 2 | 49.7 |
346 | Traverse City, MI | TAX | °F | 28.3 | 30.6 | 40.3 | 53.7 | 65.6 | 75.9 | 79.4 | 78.0 | 70.4 | 57.5 | 44.3 | 33.4 | 54.8 | 2 | 54.8 |
347 | Duluth, MN | TAX | °F | 18.5 | 23.9 | 34.3 | 48.0 | 61.0 | 69.8 | 74.7 | 73.6 | 64.7 | 51.0 | 35.6 | 23.0 | 48.2 | 2 | 48.2 |
348 | International Falls, MN | TAX | °F | 15.0 | 21.9 | 34.5 | 50.4 | 63.3 | 72.4 | 76.2 | 75.0 | 65.4 | 50.6 | 33.8 | 20.0 | 48.2 | 2 | 48.2 |
349 | Minneapolis-St Paul, MN | TAX | °F | 22.8 | 28.5 | 40.6 | 56.7 | 68.3 | 77.8 | 81.9 | 79.8 | 71.5 | 57.8 | 41.0 | 27.7 | 54.5 | 2 | 54.5 |
350 | Rochester_MN, MN | TAX | °F | 21.8 | 26.8 | 39.1 | 55.3 | 67.0 | 76.4 | 79.0 | 77.0 | 70.3 | 57.4 | 40.7 | 27.1 | 53.2 | 2 | 53.2 |
351 | St Cloud, MN | TAX | °F | 20.4 | 26.3 | 38.2 | 55.0 | 67.6 | 76.4 | 80.7 | 78.8 | 70.3 | 56.2 | 38.9 | 25.4 | 52.9 | 2 | 52.9 |
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352 | Jackson, MS | TAX | °F | 56.5 | 60.8 | 68.1 | 75.7 | 83.0 | 89.0 | 91.1 | 91.2 | 86.5 | 77.1 | 66.3 | 58.1 | 75.3 | 2 | 75.3 |
353 | Meridian, MS | TAX | °F | 57.1 | 61.4 | 68.8 | 76.2 | 83.4 | 88.8 | 91.4 | 91.1 | 86.5 | 77.3 | 66.9 | 58.5 | 75.6 | 2 | 75.6 |
354 | Tupelo, MS | TAX | °F | 51.3 | 55.8 | 64.3 | 73.0 | 80.6 | 87.4 | 90.1 | 90.1 | 84.2 | 74.2 | 62.9 | 52.8 | 72.2 | 2 | 72.2 |
355 | Columbia_MO, MO | TAX | °F | 37.6 | 43.9 | 54.5 | 65.4 | 74.0 | 82.2 | 86.6 | 86.5 | 77.8 | 66.7 | 53.2 | 41.4 | 64.2 | 2 | 64.2 |
356 | Kansas City, MO | TAX | °F | 37.1 | 43.4 | 54.2 | 64.8 | 74.2 | 82.7 | 87.2 | 86.8 | 78.1 | 66.5 | 52.5 | 40.8 | 64.0 | 2 | 64.0 |
357 | Springfield_MO, MO | TAX | °F | 42.3 | 48.2 | 56.8 | 66.6 | 74.5 | 82.9 | 87.4 | 87.9 | 79.2 | 68.4 | 55.7 | 44.8 | 66.2 | 2 | 66.2 |
358 | St Louis - Lambert, MO | TAX | °F | 39.2 | 45.1 | 55.5 | 67.0 | 75.7 | 84.3 | 88.1 | 87.3 | 79.4 | 68.2 | 54.7 | 42.8 | 65.6 | 2 | 65.6 |
359 | St Louis - Spirit, MO | TAX | °F | 39.6 | 45.5 | 56.3 | 67.5 | 75.8 | 84.1 | 88.0 | 87.2 | 79.4 | 68.6 | 55.3 | 43.3 | 65.9 | 2 | 65.9 |
360 | Billings, MT | TAX | °F | 34.9 | 40.1 | 48.0 | 56.1 | 66.4 | 75.1 | 85.7 | 84.8 | 73.0 | 58.1 | 44.8 | 35.3 | 58.5 | 2 | 58.5 |
361 | Glasgow, MT | TAX | °F | 21.7 | 28.4 | 41.4 | 56.4 | 66.5 | 74.7 | 83.9 | 83.7 | 72.1 | 55.9 | 39.4 | 26.3 | 54.2 | 2 | 54.2 |
362 | Great Falls, MT | TAX | °F | 34.1 | 38.1 | 45.2 | 53.9 | 63.7 | 71.1 | 82.7 | 81.5 | 70.5 | 56.5 | 42.7 | 35.0 | 56.2 | 2 | 56.3 |
363 | Harve City, MT | TAX | °F | 26.6 | 33.1 | 43.8 | 56.9 | 66.4 | 74.0 | 84.3 | 83.5 | 72.0 | 57.3 | 41.6 | 30.6 | 55.8 | 2 | 55.8 |
364 | Helena, MT | TAX | °F | 31.2 | 37.6 | 46.8 | 55.6 | 65.6 | 73.3 | 84.6 | 83.3 | 72.2 | 57.0 | 41.8 | 31.6 | 56.7 | 2 | 56.7 |
365 | Kalispell, MT | TAX | °F | 30.2 | 35.6 | 44.4 | 54.4 | 64.0 | 70.0 | 80.7 | 80.3 | 69.5 | 53.9 | 39.1 | 30.0 | 54.4 | 2 | 54.3 |
366 | Missoula, MT | TAX | °F | 31.5 | 37.6 | 48.0 | 55.9 | 65.6 | 72.4 | 84.7 | 83.5 | 72.2 | 56.0 | 39.9 | 30.8 | 56.5 | 2 | 56.5 |
367 | Grand Island, NE | TAX | °F | 34.7 | 39.7 | 50.4 | 61.8 | 72.0 | 81.9 | 86.5 | 84.7 | 77.6 | 64.3 | 49.1 | 37.4 | 61.7 | 2 | 61.7 |
368 | Lincoln, NE | TAX | °F | 34.1 | 39.8 | 51.5 | 63.2 | 73.5 | 82.9 | 87.8 | 86.1 | 78.3 | 65.4 | 49.7 | 37.8 | 62.5 | 2 | 62.5 |
369 | Norfolk_NE, NE | TAX | °F | 31.9 | 37.1 | 48.3 | 60.8 | 71.7 | 80.9 | 85.5 | 83.5 | 76.3 | 63.2 | 47.2 | 34.8 | 60.1 | 2 | 60.1 |
370 | North Platte, NE | TAX | °F | 38.7 | 43.0 | 52.1 | 60.8 | 71.1 | 80.7 | 87.2 | 85.1 | 77.3 | 63.7 | 49.9 | 40.0 | 62.5 | 2 | 62.5 |
371 | Omaha, NE | TAX | °F | 31.7 | 37.7 | 49.9 | 62.7 | 73.0 | 82.3 | 86.2 | 84.4 | 77.2 | 64.5 | 48.4 | 35.9 | 61.2 | 2 | 61.2 |
372 | Scottsbluff, NE | TAX | °F | 39.8 | 44.0 | 52.2 | 60.0 | 70.8 | 80.8 | 88.7 | 86.5 | 77.2 | 63.0 | 49.2 | 40.1 | 62.7 | 2 | 62.7 |
373 | Valentine, NE | TAX | °F | 35.5 | 39.5 | 48.6 | 58.8 | 69.9 | 79.4 | 87.3 | 86.1 | 76.7 | 62.0 | 47.4 | 37.2 | 60.7 | 2 | 60.7 |
374 | Ely, NV | TAX | °F | 38.9 | 41.6 | 49.8 | 56.0 | 67.0 | 77.7 | 86.9 | 84.6 | 75.6 | 62.1 | 48.1 | 38.8 | 60.6 | 2 | 60.6 |
375 | Las Vegas, NV | TAX | °F | 57.6 | 61.9 | 69.8 | 77.1 | 88.2 | 97.7 | 103.7 | 101.8 | 94.0 | 80.2 | 66.0 | 56.3 | 79.5 | 2 | 79.5 |
376 | Lovelock, NV | TAX | °F | 43.4 | 50.5 | 59.3 | 64.7 | 75.4 | 84.8 | 95.4 | 92.8 | 83.9 | 69.3 | 53.9 | 43.4 | 68.1 | 2 | 68.1 |
377 | Mercury, NV | TAX | °F | 55.2 | 58.3 | 65.8 | 72.0 | 82.9 | 92.2 | 99.0 | 97.3 | 89.6 | 76.4 | 63.3 | 54.1 | 75.5 | 2 | 75.5 |
378 | Reno, NV | TAX | °F | 45.5 | 50.3 | 57.7 | 62.3 | 72.6 | 81.9 | 91.7 | 89.7 | 81.8 | 68.5 | 54.8 | 45.2 | 66.8 | 2 | 66.8 |
379 | Tonopah, NV | TAX | °F | 44.5 | 48.3 | 56.5 | 62.7 | 73.5 | 83.5 | 91.4 | 89.2 | 80.6 | 67.6 | 53.7 | 43.8 | 66.3 | 2 | 66.3 |
380 | Winnemucca, NV | TAX | °F | 41.4 | 47.0 | 55.3 | 60.4 | 71.3 | 81.5 | 92.8 | 90.4 | 81.1 | 66.1 | 51.3 | 41.1 | 65.0 | 2 | 65.0 |
381 | Concord, NH | TAX | °F | 30.5 | 34.0 | 43.0 | 57.0 | 68.1 | 77.0 | 81.4 | 80.6 | 72.3 | 59.8 | 47.8 | 36.3 | 57.3 | 2 | 57.3 |
382 | Atlantic City, NJ | TAX | °F | 42.4 | 44.0 | 51.4 | 62.0 | 71.0 | 79.9 | 84.8 | 83.4 | 76.9 | 66.2 | 55.9 | 46.1 | 63.7 | 2 | 63.7 |
383 | Newark, NJ | TAX | °F | 39.6 | 42.1 | 50.5 | 62.0 | 72.0 | 81.3 | 85.7 | 84.2 | 76.7 | 65.2 | 54.6 | 43.8 | 63.1 | 2 | 63.1 |
384 | Albuquerque, NM | TAX | °F | 48.1 | 53.7 | 61.2 | 69.4 | 79.8 | 88.8 | 90.5 | 87.8 | 81.4 | 69.9 | 56.6 | 47.1 | 69.5 | 2 | 69.5 |
385 | Gallup, NM | TAX | °F | 44.1 | 48.7 | 56.4 | 64.0 | 74.3 | 83.9 | 87.5 | 84.3 | 78.5 | 67.0 | 54.2 | 44.0 | 65.6 | 2 | 65.6 |
386 | Roswell, NM | TAX | °F | 55.6 | 61.3 | 68.4 | 77.0 | 86.1 | 93.7 | 93.9 | 91.9 | 86.0 | 76.0 | 64.0 | 55.3 | 75.8 | 2 | 75.8 |
387 | Albany, NY | TAX | °F | 31.0 | 34.1 | 43.8 | 57.8 | 68.7 | 77.6 | 81.3 | 80.0 | 72.0 | 59.3 | 47.7 | 35.9 | 57.4 | 2 | 57.4 |
388 | Binghamton, NY | TAX | °F | 29.2 | 31.7 | 40.5 | 54.1 | 65.2 | 73.6 | 77.1 | 76.2 | 68.4 | 56.4 | 44.8 | 33.5 | 54.2 | 2 | 54.2 |
389 | Buffalo, NY | TAX | °F | 31.5 | 32.9 | 41.3 | 54.7 | 66.1 | 75.3 | 78.9 | 78.1 | 71.1 | 58.7 | 47.4 | 36.1 | 56.0 | 2 | 56.0 |
390 | Long Island, NY | TAX | °F | 38.9 | 40.4 | 47.3 | 58.0 | 67.6 | 76.6 | 81.8 | 80.5 | 73.8 | 63.2 | 53.3 | 43.9 | 60.5 | 2 | 60.4 |
391 | Massena, NY | TAX | °F | 24.3 | 27.4 | 37.9 | 53.7 | 66.9 | 75.7 | 79.4 | 78.1 | 70.1 | 56.5 | 44.2 | 31.3 | 53.8 | 2 | 53.8 |
392 | New York-LaGuardia, NY | TAX | °F | 39.6 | 41.6 | 49.0 | 60.5 | 70.3 | 79.8 | 84.7 | 83.2 | 75.9 | 64.7 | 54.1 | 44.1 | 62.3 | 2 | 62.3 |
393 | New York-Kennedy, NY | TAX | °F | 39.2 | 41.0 | 48.2 | 58.5 | 67.8 | 77.2 | 82.4 | 81.4 | 75.0 | 63.8 | 53.5 | 43.6 | 61.0 | 2 | 61.0 |
394 | Rochester, NY | TAX | °F | 31.9 | 33.8 | 42.1 | 55.6 | 67.1 | 76.4 | 80.0 | 78.8 | 71.5 | 59.3 | 47.7 | 36.6 | 56.7 | 2 | 56.7 |
395 | Syracuse, NY | TAX | °F | 31.3 | 33.2 | 42.1 | 56.5 | 68.0 | 77.1 | 80.6 | 79.7 | 72.0 | 59.4 | 47.9 | 36.4 | 57.0 | 2 | 57.0 |
396 | Asheville, NC | TAX | °F | 47.5 | 50.3 | 57.7 | 67.3 | 74.0 | 80.0 | 83.0 | 82.1 | 76.2 | 67.4 | 57.9 | 48.8 | 66.0 | 2 | 66.0 |
397 | Charlotte, NC | TAX | °F | 51.5 | 55.0 | 62.9 | 71.9 | 78.7 | 85.5 | 88.6 | 87.4 | 81.3 | 71.8 | 62.1 | 52.9 | 70.8 | 2 | 70.8 |
398 | Raleigh-Durham, NC | TAX | °F | 51.0 | 54.2 | 62.4 | 71.6 | 78.5 | 85.9 | 89.1 | 87.7 | 81.2 | 71.7 | 62.3 | 52.8 | 70.7 | 2 | 70.7 |
399 | Greensboro, NC | TAX | °F | 48.4 | 51.7 | 60.0 | 69.7 | 76.5 | 83.7 | 86.8 | 85.6 | 79.0 | 69.6 | 59.8 | 50.1 | 68.4 | 2 | 68.4 |
400 | Wilmington, NC | TAX | °F | 56.3 | 58.8 | 65.5 | 73.7 | 79.7 | 85.7 | 88.7 | 87.2 | 82.6 | 74.8 | 66.7 | 58.4 | 73.2 | 2 | 73.2 |
401 | Bismarck, ND | TAX | °F | 21.6 | 27.6 | 39.9 | 55.9 | 67.3 | 76.2 | 83.4 | 83.0 | 72.3 | 56.7 | 39.5 | 26.8 | 54.2 | 2 | 54.2 |
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402 | Fargo, ND | TAX | °F | 16.7 | 22.7 | 35.2 | 54.3 | 67.6 | 76.3 | 80.5 | 80.0 | 70.8 | 55.2 | 37.1 | 22.7 | 51.6 | 2 | 51.6 |
403 | Minot, ND | TAX | °F | 19.4 | 24.9 | 36.4 | 53.9 | 65.4 | 73.7 | 80.2 | 80.5 | 70.1 | 54.4 | 36.7 | 23.9 | 51.6 | 2 | 51.6 |
404 | Williston, ND | TAX | °F | 20.3 | 26.9 | 39.3 | 55.5 | 66.0 | 74.9 | 82.9 | 82.8 | 71.5 | 55.2 | 37.7 | 25.0 | 53.2 | 2 | 53.2 |
405 | Akron, OH | TAX | °F | 33.4 | 36.1 | 46.0 | 59.6 | 69.0 | 77.8 | 81.3 | 80.1 | 72.8 | 60.8 | 48.5 | 36.9 | 58.5 | 2 | 58.5 |
406 | Cleveland, OH | TAX | °F | 34.2 | 36.7 | 45.2 | 58.3 | 68.5 | 77.9 | 81.3 | 80.0 | 73.3 | 61.7 | 49.7 | 37.9 | 58.7 | 2 | 58.7 |
407 | Columbus_OH, OH | TAX | °F | 36.5 | 39.9 | 50.3 | 63.4 | 72.5 | 81.1 | 84.1 | 83.3 | 76.7 | 64.7 | 51.9 | 40.1 | 62.0 | 2 | 62.0 |
408 | Dayton, OH | TAX | °F | 34.9 | 38.7 | 49.1 | 62.1 | 71.3 | 80.0 | 83.2 | 82.4 | 75.9 | 63.9 | 50.7 | 38.4 | 60.9 | 2 | 60.9 |
409 | Mansfield, OH | TAX | °F | 32.8 | 35.6 | 45.4 | 59.1 | 68.9 | 77.7 | 80.8 | 79.5 | 72.9 | 61.3 | 48.1 | 37.1 | 58.3 | 2 | 58.3 |
410 | Toledo, OH | TAX | °F | 32.4 | 35.7 | 46.2 | 59.8 | 70.3 | 80.1 | 83.5 | 81.6 | 75.1 | 62.5 | 48.9 | 36.3 | 59.4 | 2 | 59.4 |
411 | Youngstown, OH | TAX | °F | 33.3 | 36.0 | 45.5 | 59.3 | 68.9 | 77.5 | 80.9 | 79.8 | 72.4 | 60.6 | 48.7 | 36.9 | 58.3 | 2 | 58.3 |
412 | Oklahoma City, OK | TAX | °F | 48.7 | 54.1 | 62.1 | 70.8 | 78.9 | 86.9 | 92.8 | 92.1 | 83.2 | 72.6 | 60.3 | 50.4 | 71.1 | 2 | 71.1 |
413 | Tulsa, OK | TAX | °F | 47.4 | 53.4 | 61.7 | 71.0 | 78.7 | 86.5 | 92.3 | 92.4 | 83.2 | 72.6 | 60.2 | 49.6 | 70.8 | 2 | 70.8 |
414 | Astoria, OR | TAX | °F | 49.1 | 51.3 | 52.7 | 55.3 | 59.8 | 63.2 | 66.8 | 67.7 | 66.8 | 60.0 | 53.2 | 48.6 | 57.9 | 2 | 57.9 |
415 | Burns, OR | TAX | °F | 35.1 | 39.3 | 49.0 | 55.6 | 65.8 | 74.0 | 86.0 | 84.4 | 76.0 | 61.2 | 45.0 | 34.7 | 58.8 | 2 | 58.8 |
416 | Eugene, OR | TAX | °F | 47.1 | 50.9 | 55.4 | 59.6 | 66.2 | 72.1 | 82.5 | 82.0 | 76.7 | 63.4 | 51.8 | 45.9 | 62.8 | 2 | 62.8 |
417 | Medford, OR | TAX | °F | 47.6 | 54.3 | 58.8 | 63.4 | 72.6 | 80.0 | 90.7 | 89.6 | 83.9 | 69.2 | 52.9 | 45.8 | 67.4 | 2 | 67.4 |
418 | Pendleton, OR | TAX | °F | 41.1 | 46.2 | 54.3 | 60.8 | 69.4 | 77.1 | 87.9 | 86.2 | 77.4 | 62.6 | 48.3 | 40.1 | 62.6 | 2 | 62.6 |
419 | Salem, OR | TAX | °F | 47.4 | 51.6 | 55.6 | 59.9 | 67.1 | 72.6 | 81.8 | 81.3 | 76.3 | 63.4 | 52.2 | 46.6 | 63.0 | 2 | 63.0 |
420 | Allentown, PA | TAX | °F | 36.7 | 39.5 | 49.0 | 61.4 | 71.1 | 79.8 | 83.8 | 82.5 | 75.0 | 63.3 | 52.1 | 40.8 | 61.3 | 2 | 61.3 |
421 | Bradford, PA | TAX | °F | 29.2 | 31.7 | 40.9 | 54.6 | 64.9 | 73.0 | 75.8 | 74.9 | 67.6 | 56.1 | 44.3 | 32.9 | 53.8 | 2 | 53.8 |
422 | Erie, PA | TAX | °F | 33.7 | 35.0 | 42.6 | 55.4 | 65.8 | 75.4 | 78.9 | 78.0 | 71.3 | 60.2 | 49.0 | 38.0 | 56.9 | 2 | 56.9 |
423 | Middletown, PA | TAX | °F | 37.9 | 40.9 | 50.4 | 62.9 | 72.5 | 81.4 | 85.4 | 83.8 | 76.0 | 64.4 | 53.3 | 42.2 | 62.6 | 2 | 62.6 |
424 | Philadelphia, PA | TAX | °F | 40.7 | 43.2 | 52.1 | 63.9 | 73.3 | 82.3 | 86.5 | 85.0 | 77.7 | 66.1 | 55.3 | 44.5 | 64.2 | 2 | 64.2 |
425 | Pittsburgh, PA | TAX | °F | 36.2 | 38.9 | 48.7 | 62.0 | 70.6 | 78.9 | 81.9 | 81.2 | 73.9 | 62.4 | 50.7 | 39.5 | 60.4 | 2 | 60.4 |
426 | Scranton, PA | TAX | °F | 33.8 | 36.5 | 45.8 | 59.1 | 69.5 | 77.6 | 81.6 | 80.2 | 72.4 | 60.4 | 49.2 | 37.7 | 58.6 | 2 | 58.7 |
427 | Williamsport, PA | TAX | °F | 34.9 | 37.9 | 47.9 | 61.3 | 71.4 | 79.8 | 83.5 | 82.0 | 73.8 | 62.1 | 50.2 | 38.6 | 60.3 | 2 | 60.3 |
428 | Providence, RI | TAX | °F | 37.4 | 39.5 | 47.0 | 58.1 | 67.7 | 76.9 | 82.2 | 80.9 | 73.5 | 62.5 | 52.4 | 42.2 | 60.0 | 2 | 60.0 |
429 | Charleston, SC | TAX | °F | 59.2 | 62.1 | 68.9 | 75.8 | 82.3 | 87.3 | 90.2 | 88.7 | 84.1 | 76.5 | 68.6 | 60.9 | 75.4 | 2 | 75.4 |
430 | Columbia, SC | TAX | °F | 56.2 | 59.6 | 67.4 | 75.7 | 82.9 | 88.6 | 91.6 | 90.0 | 84.5 | 75.3 | 66.1 | 57.4 | 74.6 | 2 | 74.6 |
431 | Greer, SC | TAX | °F | 51.7 | 55.2 | 62.9 | 71.7 | 78.6 | 85.4 | 88.8 | 87.3 | 81.1 | 71.4 | 61.9 | 52.8 | 70.7 | 2 | 70.7 |
432 | Aberdeen, SD | TAX | °F | 21.1 | 27.6 | 39.7 | 56.2 | 68.3 | 77.2 | 82.2 | 81.0 | 72.4 | 57.6 | 40.1 | 26.5 | 54.1 | 2 | 54.2 |
433 | Huron, SD | TAX | °F | 25.0 | 31.3 | 42.9 | 57.8 | 69.2 | 78.4 | 84.6 | 83.1 | 74.4 | 59.9 | 42.6 | 29.3 | 56.5 | 2 | 56.5 |
434 | Pierre, SD | TAX | °F | 28.7 | 34.7 | 45.4 | 58.9 | 69.5 | 79.2 | 87.7 | 86.7 | 77.2 | 60.6 | 44.6 | 32.6 | 58.8 | 2 | 58.8 |
435 | Rapid City, SD | TAX | °F | 35.5 | 39.0 | 47.3 | 56.5 | 66.6 | 76.4 | 85.9 | 85.7 | 75.5 | 60.6 | 46.4 | 37.2 | 59.4 | 2 | 59.4 |
436 | Sioux Falls, SD | TAX | °F | 25.2 | 31.2 | 42.5 | 57.5 | 68.9 | 78.4 | 82.9 | 81.0 | 73.2 | 59.6 | 42.7 | 29.4 | 56.0 | 2 | 56.0 |
437 | Bristol, TN | TAX | °F | 45.5 | 49.2 | 58.0 | 67.9 | 75.5 | 82.1 | 84.6 | 84.5 | 78.8 | 68.8 | 57.7 | 47.9 | 66.7 | 2 | 66.7 |
438 | Chattanooga, TN | TAX | °F | 50.4 | 54.3 | 63.0 | 72.5 | 79.4 | 86.1 | 89.2 | 89.0 | 83.0 | 72.8 | 61.4 | 51.9 | 71.1 | 2 | 71.1 |
439 | Knoxville, TN | TAX | °F | 47.3 | 51.4 | 60.2 | 69.8 | 77.5 | 84.2 | 87.2 | 87.0 | 81.1 | 70.4 | 59.1 | 49.1 | 68.7 | 2 | 68.7 |
440 | Memphis, TN | TAX | °F | 49.7 | 54.3 | 62.9 | 72.4 | 80.7 | 88.1 | 90.8 | 90.7 | 84.6 | 74.0 | 61.6 | 51.7 | 71.8 | 2 | 71.8 |
441 | Nashville, TN | TAX | °F | 47.2 | 51.5 | 60.5 | 70.4 | 77.9 | 85.2 | 88.6 | 88.6 | 82.2 | 71.4 | 59.5 | 49.5 | 69.4 | 2 | 69.4 |
442 | Abilene, TX | TAX | °F | 56.5 | 60.6 | 68.0 | 76.6 | 83.9 | 89.9 | 93.6 | 92.8 | 85.9 | 76.8 | 65.4 | 57.4 | 75.6 | 2 | 75.6 |
443 | Amarillo, TX | TAX | °F | 50.1 | 54.4 | 61.9 | 70.0 | 78.9 | 87.1 | 90.5 | 88.3 | 81.8 | 71.3 | 59.0 | 50.1 | 70.3 | 2 | 70.3 |
444 | Austin, TX | TAX | °F | 61.6 | 65.3 | 71.6 | 78.9 | 85.9 | 91.5 | 94.4 | 95.5 | 89.8 | 81.4 | 70.5 | 63.1 | 79.1 | 2 | 79.1 |
445 | Brownsville, TX | TAX | °F | 70.6 | 73.7 | 78.1 | 82.8 | 88.0 | 91.6 | 92.8 | 93.5 | 89.6 | 84.7 | 78.0 | 71.6 | 82.9 | 2 | 82.9 |
446 | Corpus Christi, TX | TAX | °F | 66.9 | 70.6 | 75.5 | 81.1 | 86.2 | 90.4 | 92.4 | 93.8 | 89.3 | 83.7 | 75.1 | 68.5 | 81.1 | 2 | 81.1 |
447 | Dallas-Fort Worth, TX | TAX | °F | 56.2 | 60.7 | 67.8 | 75.7 | 83.4 | 91.0 | 95.3 | 95.3 | 87.8 | 78.0 | 66.2 | 57.7 | 76.3 | 2 | 76.3 |
448 | El Paso, TX | TAX | °F | 58.2 | 63.2 | 70.3 | 78.7 | 88.2 | 95.4 | 94.4 | 92.4 | 87.4 | 78.3 | 66.1 | 57.3 | 77.5 | 2 | 77.5 |
449 | Houston, TX | TAX | °F | 62.6 | 66.4 | 72.3 | 78.7 | 85.9 | 90.7 | 93.1 | 93.4 | 88.9 | 81.2 | 71.2 | 64.1 | 79.0 | 2 | 79.0 |
450 | Lubbock, TX | TAX | °F | 54.0 | 58.8 | 66.1 | 74.7 | 83.3 | 90.3 | 92.3 | 90.6 | 84.0 | 74.8 | 62.7 | 54.6 | 73.9 | 2 | 73.9 |
451 | Lufkin, TX | TAX | °F | 59.8 | 64.0 | 70.5 | 77.5 | 84.6 | 90.0 | 93.1 | 93.6 | 88.3 | 79.5 | 68.8 | 61.1 | 77.6 | 2 | 77.6 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
452 | Midland, TX | TAX | °F | 57.4 | 62.2 | 69.4 | 78.4 | 87.1 | 93.0 | 93.8 | 92.4 | 86.0 | 77.5 | 65.6 | 58.1 | 76.7 | 2 | 76.7 |
453 | Port Arthur, TX | TAX | °F | 61.9 | 65.3 | 71.2 | 77.3 | 84.3 | 89.1 | 91.0 | 91.5 | 87.8 | 80.2 | 70.5 | 63.4 | 77.8 | 2 | 77.8 |
454 | San Angelo, TX | TAX | °F | 59.5 | 63.7 | 70.7 | 79.5 | 87.4 | 92.4 | 95.1 | 94.0 | 87.4 | 78.6 | 67.4 | 60.5 | 78.0 | 2 | 78.0 |
455 | San Antonio, TX | TAX | °F | 62.9 | 67.2 | 73.1 | 79.9 | 86.6 | 91.9 | 94.0 | 95.0 | 89.5 | 81.6 | 71.3 | 64.3 | 79.8 | 2 | 79.8 |
456 | Victoria, TX | TAX | °F | 64.6 | 68.2 | 73.5 | 79.6 | 86.1 | 91.0 | 93.1 | 94.0 | 89.5 | 82.7 | 73.1 | 66.1 | 80.1 | 2 | 80.1 |
457 | Waco, TX | TAX | °F | 58.4 | 62.4 | 69.2 | 77.1 | 84.7 | 91.5 | 95.8 | 96.0 | 89.4 | 79.8 | 68.0 | 59.7 | 77.7 | 2 | 77.7 |
458 | Cedar City, UT | TAX | °F | 41.9 | 46.0 | 54.6 | 61.1 | 72.3 | 82.5 | 89.5 | 87.2 | 79.3 | 65.7 | 51.7 | 41.5 | 64.4 | 2 | 64.4 |
459 | Salt Lake City, UT | TAX | °F | 37.7 | 43.1 | 53.4 | 60.3 | 71.5 | 81.8 | 92.4 | 90.1 | 78.9 | 64.0 | 48.7 | 38.0 | 63.3 | 2 | 63.3 |
460 | Burlington, VT | TAX | °F | 27.0 | 29.8 | 39.6 | 54.1 | 66.8 | 76.2 | 79.9 | 78.6 | 70.3 | 56.6 | 45.1 | 33.2 | 54.8 | 2 | 54.8 |
461 | DC-Dulles, VA | TAX | °F | 42.4 | 45.2 | 54.4 | 66.3 | 74.0 | 82.5 | 86.4 | 85.9 | 78.3 | 67.0 | 56.2 | 45.2 | 65.3 | 2 | 65.3 |
462 | DC-Reagan, VA | TAX | °F | 43.6 | 46.3 | 55.2 | 66.3 | 74.6 | 83.3 | 87.6 | 86.3 | 79.0 | 67.6 | 57.0 | 46.5 | 66.1 | 2 | 66.1 |
463 | Lynchburg, VA | TAX | °F | 45.5 | 48.3 | 57.2 | 67.9 | 74.6 | 82.2 | 85.6 | 84.7 | 77.9 | 67.9 | 57.7 | 47.4 | 66.4 | 2 | 66.4 |
464 | Norfolk, VA | TAX | °F | 49.3 | 50.9 | 58.3 | 68.1 | 75.1 | 83.1 | 87.2 | 85.2 | 79.3 | 70.0 | 60.6 | 52.1 | 68.3 | 2 | 68.3 |
465 | Richmond, VA | TAX | °F | 47.5 | 50.5 | 59.0 | 69.7 | 76.6 | 84.7 | 88.5 | 86.9 | 80.3 | 70.2 | 60.2 | 50.1 | 68.7 | 2 | 68.7 |
466 | Roanoke, VA | TAX | °F | 45.8 | 48.7 | 57.3 | 67.8 | 75.0 | 82.3 | 85.9 | 85.1 | 78.0 | 68.4 | 57.7 | 47.4 | 66.6 | 2 | 66.6 |
467 | Olympia, WA | TAX | °F | 45.7 | 49.3 | 53.2 | 58.0 | 64.9 | 69.7 | 76.7 | 76.6 | 71.5 | 59.7 | 50.2 | 44.5 | 60.0 | 2 | 60.0 |
468 | Quillayute, WA | TAX | °F | 47.1 | 49.5 | 50.8 | 54.2 | 59.1 | 62.7 | 66.9 | 67.6 | 65.8 | 57.9 | 50.7 | 46.5 | 56.6 | 2 | 56.6 |
469 | Seattle, WA | TAX | °F | 46.4 | 49.4 | 52.4 | 57.2 | 63.7 | 68.5 | 75.1 | 74.8 | 69.5 | 58.6 | 50.3 | 45.4 | 59.3 | 2 | 59.3 |
470 | Spokane, WA | TAX | °F | 34.1 | 39.7 | 48.1 | 56.0 | 65.8 | 72.5 | 83.2 | 82.2 | 72.8 | 57.2 | 41.5 | 33.0 | 57.2 | 2 | 57.2 |
471 | Stampede Pass, WA | TAX | °F | 30.7 | 33.8 | 37.9 | 43.1 | 51.0 | 56.6 | 65.7 | 65.7 | 60.0 | 47.3 | 36.2 | 30.1 | 46.5 | 2 | 46.5 |
472 | Yakima, WA | TAX | °F | 38.1 | 46.0 | 55.3 | 62.6 | 71.8 | 78.6 | 87.9 | 86.2 | 77.9 | 63.0 | 47.3 | 36.6 | 62.6 | 2 | 62.6 |
473 | Beckley, WV | TAX | °F | 39.5 | 42.2 | 50.7 | 62.6 | 69.3 | 76.0 | 78.7 | 78.4 | 72.3 | 62.8 | 51.9 | 41.6 | 60.5 | 2 | 60.5 |
474 | Charleston, WV | TAX | °F | 43.1 | 46.3 | 55.5 | 68.1 | 74.5 | 81.6 | 84.4 | 83.9 | 77.7 | 67.6 | 56.3 | 45.5 | 65.4 | 2 | 65.4 |
475 | Elkins, WV | TAX | °F | 39.7 | 42.3 | 51.2 | 63.3 | 70.5 | 77.7 | 80.5 | 80.3 | 73.9 | 64.0 | 52.7 | 42.2 | 61.5 | 2 | 61.5 |
476 | Huntington, WV | TAX | °F | 42.4 | 45.9 | 55.5 | 67.7 | 74.7 | 82.0 | 85.0 | 84.7 | 78.2 | 67.6 | 55.7 | 44.9 | 65.3 | 2 | 65.4 |
477 | Eau Claire, WI | TAX | °F | 22.7 | 28.6 | 40.7 | 56.9 | 68.6 | 77.6 | 81.4 | 79.6 | 71.2 | 57.7 | 41.2 | 27.9 | 54.5 | 2 | 54.5 |
478 | Green Bay, WI | TAX | °F | 24.9 | 29.1 | 39.9 | 54.3 | 66.2 | 75.7 | 79.6 | 78.1 | 70.8 | 57.5 | 43.1 | 30.3 | 54.1 | 2 | 54.1 |
479 | La Crosse, WI | TAX | °F | 25.6 | 31.4 | 43.7 | 58.7 | 70.1 | 79.5 | 83.2 | 81.0 | 73.2 | 60.0 | 43.8 | 30.4 | 56.7 | 2 | 56.7 |
480 | Madison, WI | TAX | °F | 26.7 | 31.6 | 43.3 | 57.0 | 68.3 | 77.8 | 81.0 | 79.2 | 72.1 | 59.4 | 44.5 | 31.4 | 56.0 | 2 | 56.0 |
481 | Milwaukee, WI | TAX | °F | 29.5 | 33.1 | 42.5 | 53.6 | 64.5 | 75.0 | 79.6 | 78.4 | 71.5 | 59.6 | 46.1 | 33.8 | 55.6 | 2 | 55.6 |
482 | Casper, WY | TAX | °F | 35.1 | 38.5 | 47.8 | 55.6 | 66.5 | 77.7 | 87.6 | 85.6 | 74.2 | 59.0 | 44.7 | 35.1 | 58.9 | 2 | 59.0 |
483 | Cheyenne, WY | TAX | °F | 38.8 | 40.4 | 47.3 | 53.7 | 63.9 | 74.3 | 82.6 | 80.2 | 71.3 | 58.0 | 45.8 | 38.6 | 57.9 | 2 | 57.9 |
484 | Lander, WY | TAX | °F | 32.0 | 36.2 | 46.9 | 55.1 | 65.7 | 76.0 | 86.2 | 84.3 | 73.0 | 57.8 | 42.6 | 32.3 | 57.3 | 2 | 57.3 |
485 | Rock Springs, WY | TAX | °F | 29.2 | 32.3 | 42.8 | 51.9 | 62.7 | 73.0 | 82.9 | 80.2 | 69.4 | 55.5 | 39.9 | 29.6 | 54.1 | 2 | 54.1 |
486 | Sheridan, WY | TAX | °F | 34.4 | 38.5 | 47.5 | 55.7 | 65.4 | 74.8 | 85.9 | 85.2 | 74.0 | 58.8 | 45.5 | 35.4 | 58.4 | 2 | 58.4 |
487 | Birmingham, AL | V | mi/hr | 7.2 | 7.4 | 7.8 | 7.4 | 6.3 | 5.4 | 5.1 | 4.7 | 5.4 | 5.4 | 6.0 | 6.7 | 6.3 | 3 | 6.2 |
488 | Huntsville, AL | V | mi/hr | 8.3 | 8.3 | 8.9 | 8.5 | 7.4 | 5.8 | 4.9 | 4.9 | 5.8 | 6.3 | 7.2 | 7.8 | 7.2 | 3 | 7.0 |
489 | Mobile, AL | V | mi/hr | 8.5 | 8.5 | 8.7 | 8.3 | 7.4 | 6.0 | 5.4 | 5.4 | 6.7 | 6.9 | 7.2 | 7.8 | 7.2 | 3 | 7.2 |
490 | Montgomery, AL | V | mi/hr | 7.2 | 7.4 | 7.6 | 6.5 | 5.8 | 4.9 | 4.7 | 4.7 | 5.6 | 5.4 | 5.8 | 6.7 | 6.0 | 3 | 6.0 |
491 | Phoenix, AZ | V | mi/hr | 4.9 | 5.6 | 6.3 | 6.9 | 6.9 | 6.7 | 6.9 | 6.7 | 6.0 | 5.6 | 4.9 | 4.7 | 6.0 | 3 | 6.0 |
492 | Prescott, AZ | V | mi/hr | 6.5 | 7.2 | 8.1 | 8.9 | 8.7 | 8.7 | 7.4 | 6.7 | 6.9 | 6.9 | 6.5 | 6.3 | 7.4 | 3 | 7.4 |
493 | Tucson, AZ | V | mi/hr | 6.9 | 7.4 | 7.8 | 8.3 | 8.1 | 8.1 | 7.8 | 7.4 | 7.6 | 7.6 | 7.2 | 6.9 | 7.6 | 3 | 7.6 |
494 | Fort Smith, AR | V | mi/hr | 7.6 | 8.1 | 8.7 | 8.3 | 6.9 | 6.0 | 5.4 | 5.6 | 6.0 | 6.3 | 7.2 | 7.6 | 6.9 | 3 | 7.0 |
495 | Little Rock, AR | V | mi/hr | 7.8 | 7.8 | 8.7 | 8.5 | 7.2 | 6.3 | 6.0 | 5.6 | 6.3 | 6.0 | 7.2 | 7.6 | 7.2 | 3 | 7.1 |
496 | Arcata, CA | V | mi/hr | 6.7 | 6.7 | 7.2 | 7.2 | 7.2 | 7.2 | 6.0 | 5.6 | 5.1 | 5.4 | 5.8 | 6.9 | 6.3 | 3 | 6.4 |
497 | Bakersfield, CA | V | mi/hr | 4.9 | 5.6 | 6.0 | 6.9 | 7.4 | 7.6 | 6.9 | 6.7 | 6.0 | 5.4 | 4.7 | 4.9 | 6.0 | 3 | 6.1 |
498 | Bishop, CA | V | mi/hr | 7.2 | 8.1 | 9.4 | 10.1 | 9.2 | 8.3 | 7.8 | 8.1 | 7.6 | 7.8 | 7.4 | 6.9 | 8.1 | 3 | 8.2 |
499 | Daggett, CA | V | mi/hr | 8.1 | 9.4 | 11.4 | 13.9 | 14.1 | 13.6 | 11.6 | 11.0 | 10.1 | 9.6 | 8.5 | 7.6 | 10.7 | 3 | 10.7 |
500 | Fresno, CA | V | mi/hr | 4.3 | 5.1 | 5.8 | 7.4 | 8.3 | 8.5 | 7.6 | 6.9 | 6.0 | 4.7 | 4.0 | 4.3 | 6.0 | 3 | 6.1 |
501 | Long Beach, CA | V | mi/hr | 4.5 | 5.1 | 5.6 | 6.3 | 6.0 | 6.0 | 6.0 | 5.8 | 5.4 | 4.7 | 4.3 | 4.3 | 5.4 | 3 | 5.3 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
502 | Los Angeles AP, CA | V | mi/hr | 6.5 | 7.6 | 8.1 | 8.7 | 8.1 | 8.1 | 8.1 | 7.6 | 7.4 | 6.7 | 6.3 | 6.5 | 7.4 | 3 | 7.5 |
503 | Redding, CA | V | mi/hr | 5.8 | 6.5 | 6.7 | 6.7 | 6.7 | 6.9 | 6.0 | 5.6 | 5.4 | 5.6 | 4.9 | 6.0 | 6.0 | 3 | 6.1 |
504 | Sacramento, CA | V | mi/hr | 5.6 | 6.0 | 6.7 | 7.4 | 7.6 | 8.1 | 7.6 | 6.9 | 5.8 | 5.4 | 4.9 | 5.8 | 6.5 | 3 | 6.5 |
505 | San Diego, CA | V | mi/hr | 5.4 | 6.3 | 6.7 | 7.4 | 7.2 | 7.4 | 7.2 | 6.9 | 6.7 | 5.8 | 4.9 | 4.9 | 6.5 | 3 | 6.4 |
506 | San Francisco AP, CA | V | mi/hr | 6.9 | 8.3 | 10.3 | 12.5 | 13.4 | 14.1 | 12.8 | 12.3 | 10.7 | 9.2 | 7.4 | 7.4 | 10.5 | 3 | 10.4 |
507 | Santa Barbara, CA | V | mi/hr | 4.5 | 5.6 | 5.8 | 6.7 | 6.5 | 6.0 | 6.0 | 5.6 | 5.1 | 4.7 | 4.3 | 4.3 | 5.4 | 3 | 5.4 |
508 | Santa Maria, CA | V | mi/hr | 6.0 | 6.7 | 7.6 | 8.3 | 8.3 | 7.8 | 6.5 | 6.3 | 5.8 | 6.0 | 6.0 | 6.0 | 6.7 | 3 | 6.8 |
509 | Stockton, CA | V | mi/hr | 6.7 | 7.2 | 7.6 | 8.9 | 9.6 | 10.1 | 8.9 | 8.3 | 7.4 | 6.5 | 5.8 | 6.9 | 7.8 | 3 | 7.8 |
510 | Alamosa, CO | V | mi/hr | 5.1 | 6.5 | 8.1 | 10.1 | 9.6 | 8.7 | 6.7 | 6.3 | 6.5 | 6.5 | 5.8 | 4.9 | 7.2 | 3 | 7.1 |
511 | Colorado Springs, CO | V | mi/hr | 8.7 | 9.4 | 10.3 | 11.6 | 10.7 | 10.1 | 8.9 | 8.5 | 8.9 | 9.4 | 8.7 | 8.9 | 9.6 | 3 | 9.5 |
512 | Denver, CO | V | mi/hr | 9.2 | 9.2 | 10.3 | 11.0 | 10.1 | 9.6 | 9.2 | 8.9 | 8.9 | 9.2 | 8.9 | 9.2 | 9.4 | 3 | 9.5 |
513 | Grand Junction, CO | V | mi/hr | 5.4 | 6.5 | 7.8 | 8.9 | 9.2 | 9.6 | 9.4 | 8.9 | 8.5 | 7.6 | 6.0 | 5.4 | 7.8 | 3 | 7.8 |
514 | Limon, CO | V | mi/hr | 8.7 | 9.4 | 10.7 | 11.9 | 11.0 | 10.1 | 9.2 | 8.7 | 8.9 | 9.4 | 8.9 | 8.9 | 9.6 | 3 | 9.7 |
515 | Pueblo, CO | V | mi/hr | 6.7 | 7.4 | 8.5 | 9.8 | 8.9 | 8.7 | 8.1 | 7.4 | 7.4 | 7.4 | 6.5 | 6.5 | 7.8 | 3 | 7.8 |
516 | Bridgeport, CT | V | mi/hr | 9.8 | 10.1 | 10.3 | 9.6 | 8.9 | 7.8 | 7.6 | 7.8 | 8.7 | 9.2 | 9.4 | 9.8 | 9.2 | 3 | 9.1 |
517 | Hartford, CT | V | mi/hr | 8.5 | 8.9 | 9.4 | 8.9 | 8.1 | 6.9 | 6.5 | 6.3 | 6.7 | 7.4 | 7.6 | 8.3 | 7.8 | 3 | 7.8 |
518 | Wilmington_DE, DE | V | mi/hr | 9.4 | 9.8 | 10.1 | 9.6 | 8.3 | 7.6 | 7.4 | 6.9 | 7.8 | 7.6 | 8.5 | 8.9 | 8.5 | 3 | 8.5 |
519 | Daytona Beach, FL | V | mi/hr | 7.2 | 7.6 | 8.3 | 7.8 | 7.4 | 6.3 | 5.6 | 5.6 | 6.7 | 7.4 | 6.9 | 6.7 | 6.9 | 3 | 7.0 |
520 | Fort Myers, FL | V | mi/hr | 7.4 | 7.8 | 8.3 | 8.1 | 7.2 | 6.3 | 5.4 | 5.6 | 6.3 | 7.2 | 7.4 | 7.2 | 6.9 | 3 | 7.0 |
521 | Gainesville, FL | V | mi/hr | 6.5 | 6.9 | 7.4 | 7.2 | 6.7 | 5.6 | 5.1 | 4.9 | 5.8 | 5.8 | 6.0 | 5.8 | 6.3 | 3 | 6.1 |
522 | Jacksonville, FL | V | mi/hr | 7.2 | 7.4 | 8.1 | 7.6 | 7.2 | 6.5 | 5.8 | 5.8 | 6.5 | 6.3 | 6.3 | 6.5 | 6.7 | 3 | 6.8 |
523 | Key West, FL | V | mi/hr | 11.0 | 10.5 | 11.0 | 11.2 | 9.8 | 8.7 | 8.5 | 8.3 | 8.7 | 10.1 | 11.2 | 10.5 | 10.1 | 3 | 10.0 |
524 | Miami, FL | V | mi/hr | 8.5 | 8.5 | 9.6 | 9.8 | 8.7 | 7.4 | 7.2 | 6.9 | 7.4 | 8.3 | 8.5 | 8.1 | 8.3 | 3 | 8.2 |
525 | Orlando, FL | V | mi/hr | 8.3 | 8.7 | 9.2 | 8.7 | 8.1 | 6.9 | 6.3 | 6.5 | 7.2 | 7.8 | 8.1 | 7.8 | 7.8 | 3 | 7.8 |
526 | Pensacola, FL | V | mi/hr | 8.7 | 8.7 | 9.2 | 9.2 | 8.3 | 7.2 | 6.5 | 6.3 | 7.2 | 7.4 | 7.8 | 8.1 | 7.8 | 3 | 7.9 |
527 | Tallahassee, FL | V | mi/hr | 5.8 | 6.3 | 6.5 | 6.3 | 6.0 | 5.1 | 4.5 | 4.7 | 5.6 | 5.4 | 5.4 | 5.4 | 5.6 | 3 | 5.6 |
528 | Tampa, FL | V | mi/hr | 7.2 | 7.4 | 8.1 | 7.8 | 7.2 | 6.5 | 5.6 | 5.6 | 6.3 | 6.7 | 6.9 | 6.7 | 6.7 | 3 | 6.8 |
529 | Vero Beach, FL | V | mi/hr | 8.5 | 8.7 | 9.6 | 9.6 | 8.9 | 7.6 | 6.7 | 6.7 | 7.4 | 8.5 | 8.5 | 8.1 | 8.3 | 3 | 8.2 |
530 | West Palm Beach, FL | V | mi/hr | 9.8 | 9.8 | 11.0 | 10.7 | 9.8 | 7.8 | 7.4 | 7.4 | 8.3 | 9.4 | 9.8 | 9.4 | 9.2 | 3 | 9.2 |
531 | Athens, GA | V | mi/hr | 7.4 | 7.4 | 7.6 | 6.9 | 6.0 | 5.4 | 5.1 | 4.9 | 5.6 | 5.6 | 6.0 | 6.7 | 6.3 | 3 | 6.2 |
532 | Atlanta, GA | V | mi/hr | 9.4 | 9.4 | 9.6 | 8.7 | 7.8 | 7.4 | 6.9 | 6.7 | 7.6 | 7.8 | 8.1 | 8.9 | 8.3 | 3 | 8.2 |
533 | Augusta, GA | V | mi/hr | 6.0 | 6.3 | 6.7 | 6.3 | 5.6 | 4.9 | 4.7 | 4.0 | 4.7 | 4.5 | 4.9 | 5.4 | 5.4 | 3 | 5.3 |
534 | Columbus, GA | V | mi/hr | 6.5 | 6.7 | 7.2 | 6.7 | 6.3 | 5.6 | 5.6 | 5.1 | 6.0 | 5.6 | 5.6 | 6.0 | 6.0 | 3 | 6.1 |
535 | Macon, GA | V | mi/hr | 6.7 | 6.7 | 6.9 | 6.5 | 6.0 | 5.4 | 4.9 | 4.7 | 5.4 | 5.1 | 5.4 | 6.0 | 5.8 | 3 | 5.8 |
536 | Savannah, GA | V | mi/hr | 7.2 | 7.4 | 7.8 | 7.4 | 6.7 | 6.3 | 5.6 | 5.6 | 6.5 | 6.3 | 6.0 | 6.5 | 6.5 | 3 | 6.6 |
537 | Hilo, HI | V | mi/hr | 6.7 | 7.2 | 7.2 | 6.9 | 6.7 | 6.5 | 6.5 | 6.3 | 6.3 | 6.3 | 6.3 | 6.5 | 6.5 | 3 | 6.6 |
538 | Honolulu, HI | V | mi/hr | 8.7 | 9.2 | 10.3 | 11.2 | 10.3 | 12.1 | 12.1 | 12.1 | 10.5 | 10.1 | 9.6 | 9.4 | 10.5 | 3 | 10.5 |
539 | Kahului, HI | V | mi/hr | 10.5 | 11.2 | 11.9 | 13.0 | 12.1 | 14.8 | 15.0 | 14.5 | 12.8 | 11.9 | 11.2 | 10.7 | 12.5 | 3 | 12.5 |
540 | Lihue, HI | V | mi/hr | 11.9 | 12.5 | 13.2 | 14.3 | 12.8 | 14.3 | 14.8 | 14.3 | 13.0 | 13.0 | 13.2 | 12.8 | 13.4 | 3 | 13.3 |
541 | Boise, ID | V | mi/hr | 6.9 | 7.6 | 8.7 | 8.7 | 8.3 | 8.1 | 7.6 | 7.4 | 7.2 | 7.2 | 6.9 | 7.4 | 7.6 | 3 | 7.7 |
542 | Lewiston, ID | V | mi/hr | 6.0 | 5.6 | 6.0 | 6.0 | 5.6 | 5.6 | 5.6 | 5.4 | 4.7 | 4.7 | 5.4 | 6.0 | 5.6 | 3 | 5.6 |
543 | Pocatello, ID | V | mi/hr | 9.4 | 8.9 | 10.5 | 11.2 | 10.3 | 9.6 | 8.5 | 8.5 | 8.3 | 9.4 | 9.4 | 9.4 | 9.4 | 3 | 9.5 |
544 | Chicago, IL | V | mi/hr | 11.0 | 10.7 | 11.0 | 11.2 | 9.8 | 8.5 | 8.3 | 7.8 | 8.3 | 9.6 | 10.5 | 10.3 | 9.8 | 3 | 9.8 |
545 | Moline, IL | V | mi/hr | 9.2 | 8.9 | 9.8 | 10.1 | 8.5 | 6.9 | 6.3 | 5.8 | 6.5 | 7.8 | 8.7 | 8.5 | 8.1 | 3 | 8.1 |
546 | Peoria, IL | V | mi/hr | 9.2 | 9.2 | 9.8 | 10.1 | 8.5 | 7.2 | 6.5 | 6.0 | 6.5 | 7.8 | 8.9 | 8.7 | 8.3 | 3 | 8.2 |
547 | Rockford, IL | V | mi/hr | 9.8 | 9.8 | 10.5 | 11.2 | 9.6 | 7.8 | 7.2 | 6.7 | 7.4 | 8.9 | 9.8 | 9.4 | 8.9 | 3 | 9.0 |
548 | Springfield_IL, IL | V | mi/hr | 10.7 | 10.7 | 11.2 | 11.4 | 9.4 | 7.6 | 6.5 | 6.3 | 6.7 | 8.7 | 10.5 | 10.3 | 9.2 | 3 | 9.2 |
549 | Evansville, IN | V | mi/hr | 8.3 | 8.3 | 8.3 | 8.5 | 6.9 | 6.0 | 5.6 | 5.1 | 5.4 | 6.0 | 7.4 | 7.6 | 6.9 | 3 | 7.0 |
550 | Fort Wayne, IN | V | mi/hr | 11.0 | 10.5 | 10.5 | 10.7 | 9.4 | 7.6 | 6.9 | 6.3 | 6.9 | 8.5 | 9.8 | 10.3 | 9.2 | 3 | 9.0 |
551 | Indianapolis, IN | V | mi/hr | 11.0 | 11.0 | 11.0 | 11.4 | 9.6 | 8.3 | 7.8 | 7.4 | 7.8 | 8.9 | 10.3 | 10.5 | 9.6 | 3 | 9.6 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
552 | South Bend, IN | V | mi/hr | 10.7 | 10.3 | 10.3 | 10.5 | 9.2 | 7.6 | 7.4 | 6.7 | 7.2 | 8.5 | 9.6 | 10.1 | 8.9 | 3 | 9.0 |
553 | Des Moines, IA | V | mi/hr | 10.3 | 10.1 | 11.0 | 11.2 | 10.1 | 8.7 | 8.1 | 7.6 | 8.5 | 9.6 | 10.3 | 9.8 | 9.6 | 3 | 9.6 |
554 | Dubuque, IA | V | mi/hr | 11.0 | 11.0 | 11.4 | 11.9 | 10.1 | 8.5 | 7.6 | 7.2 | 8.3 | 10.1 | 11.0 | 10.5 | 9.8 | 3 | 9.9 |
555 | Mason City, IA | V | mi/hr | 12.3 | 12.3 | 12.5 | 13.2 | 12.3 | 10.3 | 8.7 | 7.8 | 9.2 | 11.0 | 11.9 | 11.9 | 11.2 | 3 | 11.1 |
556 | Sioux City, IA | V | mi/hr | 11.0 | 11.0 | 11.4 | 12.5 | 11.6 | 9.6 | 8.3 | 7.8 | 9.2 | 10.1 | 10.7 | 10.7 | 10.3 | 3 | 10.3 |
557 | Waterloo, IA | V | mi/hr | 10.5 | 10.7 | 11.2 | 11.9 | 10.5 | 8.7 | 7.6 | 7.2 | 8.1 | 9.6 | 10.3 | 10.1 | 9.6 | 3 | 9.7 |
558 | Concordia, KS | V | mi/hr | 10.3 | 10.7 | 12.1 | 12.8 | 11.2 | 10.7 | 10.1 | 9.4 | 10.5 | 10.7 | 11.0 | 10.3 | 10.7 | 3 | 10.8 |
559 | Dodge City, KS | V | mi/hr | 12.1 | 12.8 | 14.1 | 14.8 | 13.6 | 13.2 | 12.1 | 11.4 | 12.8 | 12.8 | 12.5 | 12.1 | 13.0 | 3 | 12.9 |
560 | Goodland, KS | V | mi/hr | 11.6 | 12.1 | 13.2 | 13.9 | 13.0 | 12.3 | 11.0 | 10.5 | 11.4 | 11.9 | 11.6 | 11.6 | 12.1 | 3 | 12.0 |
561 | Russell, KS | V | mi/hr | 11.4 | 12.1 | 13.4 | 14.3 | 12.8 | 12.5 | 11.9 | 11.2 | 12.3 | 12.8 | 12.3 | 11.6 | 12.3 | 3 | 12.4 |
562 | Topeka, KS | V | mi/hr | 8.1 | 8.3 | 9.6 | 9.8 | 8.3 | 7.6 | 6.7 | 6.0 | 6.7 | 7.4 | 8.1 | 7.6 | 7.8 | 3 | 7.9 |
563 | Wichita, KS | V | mi/hr | 11.0 | 11.4 | 12.8 | 13.4 | 11.6 | 11.6 | 10.7 | 10.1 | 10.7 | 11.2 | 11.4 | 10.7 | 11.4 | 3 | 11.4 |
564 | Cincinnati, KY | V | mi/hr | 9.4 | 9.6 | 9.8 | 9.6 | 7.8 | 6.9 | 6.5 | 6.3 | 6.7 | 7.4 | 8.7 | 8.9 | 8.1 | 3 | 8.1 |
565 | Jackson_KY, KY | V | mi/hr | 6.0 | 6.0 | 6.3 | 6.3 | 4.5 | 3.6 | 3.4 | 3.1 | 3.8 | 4.3 | 5.4 | 5.6 | 4.9 | 3 | 4.9 |
566 | Lexington, KY | V | mi/hr | 9.4 | 9.2 | 9.2 | 9.2 | 7.6 | 6.5 | 6.0 | 5.8 | 6.3 | 7.2 | 8.3 | 8.7 | 7.8 | 3 | 7.8 |
567 | Louisville, KY | V | mi/hr | 8.9 | 8.9 | 8.9 | 8.9 | 7.6 | 6.9 | 6.7 | 6.3 | 6.3 | 6.7 | 7.8 | 8.1 | 7.6 | 3 | 7.7 |
568 | Paducah, KY | V | mi/hr | 8.3 | 8.3 | 8.9 | 8.5 | 6.9 | 5.8 | 5.4 | 4.7 | 5.1 | 6.0 | 7.4 | 7.8 | 6.9 | 3 | 6.9 |
569 | Baton Rouge, LA | V | mi/hr | 7.2 | 7.4 | 7.4 | 7.4 | 6.5 | 5.4 | 4.9 | 4.5 | 5.1 | 5.4 | 5.8 | 6.5 | 6.0 | 3 | 6.1 |
570 | Lake Charles, LA | V | mi/hr | 8.7 | 8.9 | 8.9 | 8.7 | 7.4 | 6.3 | 5.4 | 5.1 | 6.5 | 7.2 | 7.6 | 8.5 | 7.4 | 3 | 7.4 |
571 | New Orleans, LA | V | mi/hr | 9.2 | 9.2 | 9.4 | 9.4 | 8.1 | 6.5 | 5.8 | 5.8 | 7.4 | 8.1 | 8.1 | 8.7 | 8.1 | 3 | 8.0 |
572 | Shreveport, LA | V | mi/hr | 8.3 | 8.3 | 8.9 | 8.7 | 7.6 | 6.5 | 6.0 | 5.4 | 6.3 | 6.3 | 7.2 | 7.8 | 7.2 | 3 | 7.3 |
573 | Bangor, ME | V | mi/hr | 7.8 | 8.1 | 8.9 | 8.9 | 8.1 | 7.2 | 6.7 | 6.3 | 6.9 | 7.8 | 7.6 | 7.6 | 7.6 | 3 | 7.7 |
574 | Caribou, ME | V | mi/hr | 7.8 | 8.3 | 8.7 | 8.5 | 7.6 | 6.7 | 6.0 | 5.8 | 6.5 | 7.6 | 7.6 | 8.1 | 7.4 | 3 | 7.4 |
575 | Portland, ME | V | mi/hr | 8.1 | 8.5 | 9.2 | 9.2 | 8.1 | 7.2 | 6.7 | 6.5 | 6.9 | 7.6 | 7.6 | 8.1 | 7.8 | 3 | 7.8 |
576 | Baltimore , MD | V | mi/hr | 7.8 | 8.3 | 8.7 | 8.3 | 7.2 | 6.5 | 6.0 | 5.6 | 6.3 | 6.3 | 6.9 | 7.4 | 7.2 | 3 | 7.1 |
577 | Boston, MA | V | mi/hr | 12.5 | 12.8 | 13.0 | 12.1 | 11.2 | 10.3 | 10.1 | 9.8 | 10.5 | 11.2 | 11.4 | 12.5 | 11.4 | 3 | 11.5 |
578 | Worchester, MA | V | mi/hr | 11.4 | 11.9 | 11.4 | 10.7 | 10.1 | 9.2 | 8.9 | 8.5 | 8.9 | 10.1 | 10.5 | 11.6 | 10.3 | 3 | 10.3 |
579 | Alpena, MI | V | mi/hr | 8.3 | 8.3 | 8.3 | 8.7 | 7.8 | 6.5 | 6.3 | 6.0 | 6.7 | 7.4 | 7.8 | 7.8 | 7.4 | 3 | 7.5 |
580 | Detroit Metro_AP, MI | V | mi/hr | 11.0 | 10.3 | 10.1 | 10.3 | 8.9 | 8.1 | 8.1 | 7.2 | 7.6 | 9.2 | 10.1 | 10.3 | 9.2 | 3 | 9.3 |
581 | Detroit - City, MI | V | mi/hr | 10.1 | 9.8 | 9.6 | 9.8 | 8.7 | 7.6 | 7.6 | 6.9 | 7.4 | 8.5 | 9.2 | 9.6 | 8.7 | 3 | 8.7 |
582 | Flint, MI | V | mi/hr | 10.3 | 10.3 | 10.3 | 10.5 | 9.2 | 7.6 | 7.4 | 6.9 | 7.6 | 8.9 | 9.6 | 9.6 | 8.9 | 3 | 9.0 |
583 | Grand Rapids, MI | V | mi/hr | 11.0 | 10.5 | 10.5 | 11.0 | 9.8 | 8.3 | 8.1 | 7.4 | 7.8 | 9.4 | 10.1 | 10.3 | 9.6 | 3 | 9.5 |
584 | Houghton Lake, MI | V | mi/hr | 8.7 | 8.3 | 8.3 | 9.2 | 8.3 | 6.9 | 6.7 | 6.5 | 6.9 | 8.1 | 8.7 | 8.7 | 7.8 | 3 | 7.9 |
585 | Lansing, MI | V | mi/hr | 10.3 | 10.1 | 9.8 | 10.1 | 8.9 | 7.6 | 7.4 | 6.7 | 7.2 | 8.7 | 9.6 | 10.1 | 8.9 | 3 | 8.9 |
586 | Muskegon, MI | V | mi/hr | 11.2 | 10.7 | 10.3 | 10.7 | 9.4 | 8.3 | 8.1 | 7.8 | 8.3 | 9.8 | 11.0 | 11.0 | 9.6 | 3 | 9.7 |
587 | Sault Ste Marie, MI | V | mi/hr | 7.8 | 7.8 | 8.1 | 8.7 | 8.5 | 7.2 | 6.9 | 6.7 | 7.2 | 7.8 | 8.5 | 8.1 | 7.8 | 3 | 7.8 |
588 | Traverse City, MI | V | mi/hr | 8.3 | 8.3 | 7.6 | 8.1 | 6.9 | 6.3 | 6.5 | 6.0 | 6.5 | 7.6 | 8.1 | 7.8 | 7.4 | 3 | 7.3 |
589 | Duluth, MN | V | mi/hr | 10.5 | 10.3 | 10.5 | 11.0 | 10.7 | 9.4 | 8.7 | 8.7 | 9.6 | 10.5 | 10.7 | 10.3 | 10.1 | 3 | 10.1 |
590 | International Falls, MN | V | mi/hr | 7.8 | 7.8 | 8.5 | 8.5 | 8.7 | 7.6 | 6.9 | 6.7 | 7.6 | 8.3 | 8.3 | 7.6 | 7.8 | 3 | 7.9 |
591 | Minneapolis-St Paul, MN | V | mi/hr | 9.4 | 9.4 | 9.8 | 10.7 | 10.3 | 9.2 | 8.5 | 8.3 | 9.2 | 9.8 | 9.6 | 9.2 | 9.4 | 3 | 9.5 |
592 | Rochester_MN, MN | V | mi/hr | 13.0 | 13.0 | 13.0 | 13.4 | 12.8 | 10.7 | 9.6 | 8.9 | 10.3 | 11.6 | 12.8 | 13.0 | 11.9 | 3 | 11.8 |
593 | St Cloud, MN | V | mi/hr | 8.3 | 8.3 | 8.7 | 9.4 | 9.2 | 7.8 | 6.7 | 6.5 | 7.4 | 8.5 | 8.5 | 8.3 | 8.1 | 3 | 8.1 |
594 | Jackson, MS | V | mi/hr | 6.7 | 6.9 | 7.2 | 6.7 | 5.6 | 4.7 | 4.0 | 4.0 | 5.1 | 5.1 | 5.4 | 6.3 | 5.6 | 3 | 5.6 |
595 | Meridian, MS | V | mi/hr | 6.9 | 7.2 | 7.4 | 6.9 | 5.8 | 4.9 | 4.5 | 4.3 | 5.1 | 5.1 | 5.6 | 6.3 | 5.8 | 3 | 5.8 |
596 | Tupelo, MS | V | mi/hr | 7.6 | 7.8 | 8.1 | 7.6 | 6.3 | 5.4 | 4.7 | 4.7 | 5.6 | 5.6 | 6.0 | 6.9 | 6.3 | 3 | 6.4 |
597 | Columbia_MO, MO | V | mi/hr | 10.3 | 10.5 | 11.2 | 11.2 | 9.2 | 8.1 | 7.4 | 7.2 | 7.8 | 9.2 | 10.1 | 10.1 | 9.4 | 3 | 9.4 |
598 | Kansas City, MO | V | mi/hr | 10.7 | 10.7 | 11.9 | 12.3 | 10.3 | 9.6 | 8.7 | 8.5 | 9.2 | 10.3 | 10.7 | 10.5 | 10.3 | 3 | 10.3 |
599 | Springfield_MO, MO | V | mi/hr | 9.8 | 10.1 | 11.0 | 10.7 | 8.9 | 8.1 | 7.2 | 7.2 | 7.8 | 8.9 | 9.8 | 9.8 | 9.2 | 3 | 9.1 |
600 | St Louis - Lambert, MO | V | mi/hr | 9.8 | 10.1 | 10.5 | 10.5 | 9.2 | 8.1 | 7.6 | 7.2 | 7.4 | 8.5 | 9.4 | 9.6 | 8.9 | 3 | 9.0 |
601 | St Louis - Spirit, MO | V | mi/hr | 8.1 | 8.1 | 8.5 | 8.7 | 6.7 | 5.8 | 5.4 | 4.9 | 4.9 | 6.3 | 7.4 | 7.4 | 6.9 | 3 | 6.9 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
602 | Billings, MT | V | mi/hr | 12.8 | 11.6 | 10.7 | 10.5 | 9.8 | 9.4 | 8.9 | 8.9 | 9.4 | 10.5 | 11.9 | 12.5 | 10.5 | 3 | 10.6 |
603 | Glasgow, MT | V | mi/hr | 9.4 | 9.4 | 11.0 | 12.1 | 12.1 | 11.0 | 10.1 | 10.7 | 10.3 | 10.3 | 9.6 | 9.4 | 10.5 | 3 | 10.5 |
604 | Great Falls, MT | V | mi/hr | 13.4 | 11.9 | 11.9 | 11.2 | 10.5 | 9.8 | 8.9 | 8.9 | 10.1 | 11.9 | 13.4 | 13.6 | 11.4 | 3 | 11.3 |
605 | Harve City, MT | V | mi/hr | 9.6 | 9.2 | 9.8 | 10.5 | 10.5 | 9.6 | 8.7 | 8.7 | 8.9 | 9.4 | 10.1 | 9.8 | 9.6 | 3 | 9.6 |
606 | Helena, MT | V | mi/hr | 5.6 | 6.0 | 7.4 | 8.3 | 8.1 | 7.8 | 7.2 | 6.5 | 6.3 | 6.5 | 6.0 | 5.6 | 6.7 | 3 | 6.8 |
607 | Kalispell, MT | V | mi/hr | 4.0 | 4.3 | 5.8 | 6.7 | 6.5 | 5.8 | 5.4 | 5.1 | 4.7 | 4.5 | 4.0 | 3.8 | 5.1 | 3 | 5.1 |
608 | Missoula, MT | V | mi/hr | 3.8 | 4.3 | 5.8 | 6.5 | 6.3 | 6.5 | 6.3 | 5.8 | 4.9 | 4.5 | 4.0 | 4.0 | 5.1 | 3 | 5.2 |
609 | Grand Island, NE | V | mi/hr | 11.0 | 11.4 | 12.5 | 13.4 | 12.1 | 10.7 | 9.2 | 8.9 | 10.5 | 11.2 | 11.2 | 11.0 | 11.2 | 3 | 11.1 |
610 | Lincoln, NE | V | mi/hr | 8.9 | 9.6 | 11.0 | 11.9 | 10.5 | 9.6 | 8.7 | 8.3 | 9.2 | 9.6 | 9.4 | 8.9 | 9.6 | 3 | 9.6 |
611 | Norfolk_NE, NE | V | mi/hr | 10.5 | 11.0 | 11.6 | 12.5 | 11.2 | 9.8 | 8.9 | 8.7 | 9.8 | 10.3 | 10.5 | 10.5 | 10.5 | 3 | 10.4 |
612 | North Platte, NE | V | mi/hr | 8.3 | 8.9 | 10.3 | 11.4 | 10.3 | 9.4 | 8.5 | 8.1 | 8.9 | 8.9 | 8.7 | 8.3 | 9.2 | 3 | 9.2 |
613 | Omaha, NE | V | mi/hr | 10.1 | 10.3 | 11.2 | 11.9 | 10.5 | 9.4 | 8.3 | 8.1 | 8.9 | 9.6 | 10.1 | 9.8 | 9.8 | 3 | 9.9 |
614 | Scottsbluff, NE | V | mi/hr | 9.6 | 10.3 | 11.0 | 11.4 | 11.0 | 9.8 | 8.5 | 8.3 | 8.3 | 9.2 | 9.4 | 9.4 | 9.6 | 3 | 9.7 |
615 | Valentine, NE | V | mi/hr | 9.4 | 9.8 | 10.5 | 11.4 | 11.4 | 10.3 | 9.2 | 9.6 | 10.3 | 10.1 | 9.8 | 9.6 | 10.1 | 3 | 10.1 |
616 | Ely, NV | V | mi/hr | 9.2 | 8.9 | 9.6 | 9.8 | 9.4 | 9.6 | 9.4 | 9.6 | 9.2 | 9.2 | 8.7 | 8.9 | 9.4 | 3 | 9.3 |
617 | Las Vegas, NV | V | mi/hr | 6.5 | 7.2 | 8.7 | 10.3 | 10.1 | 10.1 | 8.9 | 8.5 | 7.8 | 7.2 | 6.5 | 6.5 | 8.3 | 3 | 8.2 |
618 | Lovelock, NV | V | mi/hr | 4.9 | 6.0 | 7.4 | 8.3 | 8.5 | 8.3 | 7.6 | 6.9 | 6.0 | 5.8 | 5.1 | 4.7 | 6.7 | 3 | 6.6 |
619 | Mercury, NV | V | mi/hr | 8.3 | 8.5 | 9.2 | 10.3 | 9.8 | 10.1 | 9.2 | 9.2 | 8.3 | 8.1 | 8.1 | 8.1 | 8.9 | 3 | 8.9 |
620 | Reno, NV | V | mi/hr | 4.7 | 5.6 | 6.9 | 8.3 | 7.8 | 7.6 | 7.2 | 6.5 | 5.4 | 4.7 | 4.9 | 5.1 | 6.3 | 3 | 6.2 |
621 | Tonopah, NV | V | mi/hr | 8.9 | 9.6 | 10.7 | 11.6 | 10.7 | 10.3 | 9.2 | 9.2 | 8.9 | 9.4 | 9.2 | 8.7 | 9.6 | 3 | 9.7 |
622 | Winnemucca, NV | V | mi/hr | 7.2 | 7.6 | 8.1 | 8.3 | 8.3 | 8.3 | 7.6 | 7.4 | 6.9 | 6.7 | 6.7 | 7.2 | 7.6 | 3 | 7.5 |
623 | Concord, NH | V | mi/hr | 6.7 | 7.4 | 7.4 | 7.2 | 6.3 | 5.6 | 5.1 | 4.7 | 4.9 | 5.6 | 5.6 | 6.5 | 6.0 | 3 | 6.1 |
624 | Atlantic City, NJ | V | mi/hr | 9.8 | 10.1 | 10.5 | 10.3 | 8.7 | 7.8 | 7.4 | 6.7 | 7.4 | 7.6 | 8.5 | 9.4 | 8.7 | 3 | 8.7 |
625 | Newark, NJ | V | mi/hr | 11.0 | 11.2 | 11.2 | 10.5 | 9.6 | 9.2 | 8.9 | 8.5 | 8.9 | 9.4 | 9.8 | 10.7 | 9.8 | 3 | 9.9 |
626 | Albuquerque, NM | V | mi/hr | 7.2 | 7.8 | 8.7 | 9.8 | 9.4 | 8.9 | 7.8 | 7.4 | 7.4 | 7.4 | 7.2 | 6.7 | 8.1 | 3 | 8.0 |
627 | Gallup, NM | V | mi/hr | 5.4 | 6.5 | 7.8 | 9.4 | 8.7 | 8.1 | 6.7 | 5.8 | 5.8 | 6.0 | 5.6 | 5.1 | 6.7 | 3 | 6.7 |
628 | Roswell, NM | V | mi/hr | 7.6 | 8.7 | 9.6 | 10.5 | 10.1 | 10.1 | 8.5 | 7.6 | 7.8 | 7.8 | 7.6 | 7.4 | 8.7 | 3 | 8.6 |
629 | Albany, NY | V | mi/hr | 8.5 | 8.9 | 9.4 | 9.2 | 7.8 | 6.9 | 6.7 | 5.8 | 6.3 | 7.2 | 7.8 | 8.5 | 7.8 | 3 | 7.8 |
630 | Binghamton, NY | V | mi/hr | 9.8 | 9.8 | 9.8 | 9.6 | 8.5 | 7.8 | 7.4 | 6.9 | 7.8 | 8.5 | 8.9 | 9.6 | 8.7 | 3 | 8.7 |
631 | Buffalo, NY | V | mi/hr | 12.1 | 11.6 | 10.7 | 10.5 | 9.8 | 8.9 | 8.9 | 8.1 | 8.7 | 9.6 | 10.5 | 11.4 | 10.1 | 3 | 10.1 |
632 | Long Island, NY | V | mi/hr | 10.1 | 10.3 | 10.5 | 10.1 | 8.9 | 8.3 | 7.8 | 7.4 | 8.1 | 8.5 | 9.2 | 9.8 | 8.9 | 3 | 9.1 |
633 | Massena, NY | V | mi/hr | 8.7 | 8.5 | 8.7 | 8.9 | 7.8 | 6.7 | 6.5 | 5.8 | 6.3 | 7.6 | 8.3 | 8.5 | 7.6 | 3 | 7.7 |
634 | New York-LaGuardia, NY | V | mi/hr | 12.8 | 12.8 | 12.8 | 11.6 | 10.7 | 10.1 | 9.6 | 9.4 | 10.3 | 10.7 | 11.6 | 12.5 | 11.2 | 3 | 11.2 |
635 | New York-Kennedy, NY | V | mi/hr | 12.5 | 12.8 | 12.8 | 11.9 | 10.5 | 10.1 | 9.8 | 9.4 | 9.8 | 10.7 | 11.4 | 12.8 | 11.2 | 3 | 11.2 |
636 | Rochester, NY | V | mi/hr | 10.7 | 10.5 | 10.3 | 10.1 | 8.9 | 8.1 | 7.8 | 7.2 | 7.6 | 8.7 | 9.4 | 10.3 | 9.2 | 3 | 9.1 |
637 | Syracuse, NY | V | mi/hr | 9.8 | 9.6 | 9.4 | 9.2 | 8.1 | 7.2 | 7.2 | 6.5 | 7.2 | 7.8 | 8.7 | 9.6 | 8.3 | 3 | 8.4 |
638 | Asheville, NC | V | mi/hr | 8.5 | 8.3 | 8.3 | 7.6 | 6.0 | 4.9 | 4.7 | 4.3 | 4.7 | 5.6 | 6.9 | 7.6 | 6.5 | 3 | 6.5 |
639 | Charlotte, NC | V | mi/hr | 6.5 | 6.9 | 7.6 | 7.4 | 6.7 | 5.8 | 5.6 | 5.4 | 6.0 | 5.4 | 5.8 | 6.0 | 6.3 | 3 | 6.3 |
640 | Raleigh-Durham, NC | V | mi/hr | 6.9 | 6.9 | 7.8 | 7.8 | 6.9 | 6.0 | 6.0 | 5.4 | 5.8 | 5.1 | 5.6 | 6.0 | 6.5 | 3 | 6.4 |
641 | Greensboro, NC | V | mi/hr | 8.1 | 8.1 | 8.7 | 8.7 | 7.6 | 6.7 | 6.3 | 5.8 | 6.3 | 6.3 | 6.7 | 6.9 | 7.2 | 3 | 7.2 |
642 | Wilmington, NC | V | mi/hr | 8.1 | 8.3 | 8.9 | 9.2 | 8.3 | 7.4 | 6.9 | 6.5 | 7.2 | 6.5 | 6.9 | 7.4 | 7.6 | 3 | 7.6 |
643 | Bismarck, ND | V | mi/hr | 8.9 | 9.2 | 10.1 | 10.7 | 10.7 | 9.6 | 8.7 | 8.9 | 9.2 | 9.4 | 8.9 | 9.2 | 9.4 | 3 | 9.5 |
644 | Fargo, ND | V | mi/hr | 11.0 | 11.4 | 12.1 | 12.3 | 12.3 | 10.3 | 9.2 | 9.6 | 10.5 | 11.4 | 11.4 | 11.2 | 11.0 | 3 | 11.1 |
645 | Minot, ND | V | mi/hr | 12.1 | 11.6 | 11.6 | 11.4 | 11.9 | 10.5 | 9.6 | 9.8 | 10.5 | 11.6 | 11.9 | 12.1 | 11.2 | 3 | 11.2 |
646 | Williston, ND | V | mi/hr | 8.3 | 8.5 | 9.2 | 10.1 | 10.3 | 9.4 | 8.3 | 8.7 | 8.7 | 8.9 | 8.5 | 8.5 | 8.9 | 3 | 9.0 |
647 | Akron, OH | V | mi/hr | 10.7 | 10.5 | 10.3 | 10.1 | 8.7 | 7.6 | 7.4 | 6.7 | 7.4 | 8.5 | 9.6 | 10.3 | 8.9 | 3 | 9.0 |
648 | Cleveland, OH | V | mi/hr | 11.2 | 10.5 | 10.5 | 10.3 | 9.2 | 8.3 | 8.1 | 7.6 | 8.3 | 9.4 | 10.5 | 11.0 | 9.6 | 3 | 9.6 |
649 | Columbus_OH, OH | V | mi/hr | 9.2 | 8.9 | 8.9 | 8.9 | 7.6 | 6.7 | 6.3 | 5.8 | 6.0 | 6.9 | 8.1 | 8.7 | 7.6 | 3 | 7.7 |
650 | Dayton, OH | V | mi/hr | 11.4 | 11.0 | 11.0 | 11.0 | 9.4 | 8.3 | 7.8 | 7.2 | 7.8 | 9.2 | 10.3 | 10.7 | 9.6 | 3 | 9.6 |
651 | Mansfield, OH | V | mi/hr | 11.2 | 10.7 | 10.5 | 10.7 | 9.2 | 7.8 | 7.4 | 6.7 | 7.4 | 8.9 | 10.3 | 10.7 | 9.4 | 3 | 9.3 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
652 | Toledo, OH | V | mi/hr | 10.5 | 9.8 | 9.8 | 10.3 | 8.7 | 7.2 | 6.9 | 6.3 | 6.7 | 8.3 | 9.4 | 9.6 | 8.7 | 3 | 8.6 |
653 | Youngstown, OH | V | mi/hr | 10.1 | 9.6 | 9.6 | 9.6 | 8.3 | 7.2 | 6.9 | 6.5 | 7.2 | 8.1 | 9.2 | 9.6 | 8.5 | 3 | 8.5 |
654 | Oklahoma City, OK | V | mi/hr | 11.4 | 11.9 | 13.4 | 13.4 | 11.4 | 10.7 | 9.8 | 9.2 | 9.6 | 11.0 | 11.6 | 11.4 | 11.2 | 3 | 11.2 |
655 | Tulsa, OK | V | mi/hr | 9.2 | 9.4 | 10.7 | 11.2 | 9.6 | 9.2 | 8.7 | 7.6 | 7.8 | 8.7 | 9.4 | 9.2 | 9.2 | 3 | 9.2 |
656 | Astoria, OR | V | mi/hr | 8.5 | 7.8 | 7.8 | 7.8 | 7.6 | 7.8 | 8.1 | 7.2 | 6.7 | 6.7 | 7.8 | 8.7 | 7.6 | 3 | 7.7 |
657 | Burns, OR | V | mi/hr | 5.1 | 5.6 | 6.9 | 7.8 | 7.6 | 7.2 | 6.7 | 6.5 | 6.0 | 5.8 | 5.4 | 5.1 | 6.3 | 3 | 6.3 |
658 | Eugene, OR | V | mi/hr | 6.9 | 6.9 | 7.2 | 6.9 | 6.5 | 6.9 | 7.4 | 7.2 | 6.7 | 6.5 | 6.7 | 7.2 | 6.9 | 3 | 6.9 |
659 | Medford, OR | V | mi/hr | 3.4 | 4.0 | 4.5 | 4.7 | 5.1 | 5.4 | 5.1 | 4.7 | 3.6 | 3.1 | 2.9 | 3.4 | 4.0 | 3 | 4.2 |
660 | Pendleton, OR | V | mi/hr | 7.2 | 7.2 | 8.9 | 9.4 | 9.2 | 9.2 | 8.7 | 8.5 | 8.1 | 7.6 | 7.4 | 7.2 | 8.3 | 3 | 8.2 |
661 | Salem, OR | V | mi/hr | 7.2 | 6.7 | 7.2 | 6.7 | 6.3 | 6.5 | 6.3 | 5.8 | 5.4 | 5.6 | 6.9 | 7.4 | 6.5 | 3 | 6.5 |
662 | Allentown, PA | V | mi/hr | 8.3 | 8.7 | 8.9 | 8.7 | 7.4 | 6.7 | 6.3 | 5.6 | 6.3 | 6.5 | 6.9 | 7.8 | 7.4 | 3 | 7.3 |
663 | Bradford, PA | V | mi/hr | 8.9 | 8.7 | 8.5 | 8.3 | 6.9 | 5.8 | 5.4 | 5.1 | 5.8 | 6.7 | 7.6 | 8.3 | 7.2 | 3 | 7.2 |
664 | Erie, PA | V | mi/hr | 11.9 | 10.7 | 10.5 | 10.1 | 9.2 | 8.3 | 8.1 | 7.8 | 8.9 | 9.8 | 11.2 | 11.6 | 9.8 | 3 | 9.8 |
665 | Middletown, PA | V | mi/hr | 8.9 | 9.2 | 9.8 | 9.2 | 7.6 | 6.7 | 6.3 | 5.8 | 6.3 | 6.5 | 7.8 | 8.5 | 7.6 | 3 | 7.7 |
666 | Philadelphia, PA | V | mi/hr | 10.3 | 10.5 | 11.0 | 10.3 | 8.9 | 8.7 | 8.5 | 8.1 | 8.5 | 8.7 | 9.2 | 10.1 | 9.4 | 3 | 9.4 |
667 | Pittsburgh, PA | V | mi/hr | 9.4 | 9.2 | 9.4 | 9.2 | 7.6 | 6.9 | 6.5 | 6.0 | 6.3 | 6.9 | 8.1 | 8.7 | 7.8 | 3 | 7.9 |
668 | Scranton, PA | V | mi/hr | 7.6 | 8.1 | 8.1 | 7.8 | 6.9 | 6.0 | 6.0 | 5.6 | 6.0 | 6.3 | 6.9 | 7.4 | 6.9 | 3 | 6.9 |
669 | Williamsport, PA | V | mi/hr | 7.6 | 7.8 | 7.8 | 7.6 | 6.5 | 5.6 | 5.4 | 4.7 | 5.1 | 5.6 | 6.5 | 7.2 | 6.5 | 3 | 6.5 |
670 | Providence, RI | V | mi/hr | 9.6 | 10.1 | 10.5 | 10.3 | 9.4 | 8.7 | 8.5 | 8.1 | 8.1 | 8.5 | 8.7 | 9.4 | 9.2 | 3 | 9.2 |
671 | Charleston, SC | V | mi/hr | 8.3 | 8.5 | 9.2 | 9.2 | 8.3 | 7.6 | 7.2 | 6.7 | 7.4 | 7.2 | 7.2 | 7.6 | 7.8 | 3 | 7.9 |
672 | Columbia, SC | V | mi/hr | 6.7 | 6.7 | 7.4 | 7.4 | 6.7 | 6.0 | 5.6 | 5.1 | 5.6 | 5.1 | 5.1 | 5.8 | 6.0 | 3 | 6.1 |
673 | Greer, SC | V | mi/hr | 7.4 | 7.6 | 8.3 | 7.8 | 6.9 | 6.0 | 5.8 | 5.4 | 5.8 | 5.8 | 6.3 | 6.7 | 6.7 | 3 | 6.7 |
674 | Aberdeen, SD | V | mi/hr | 10.1 | 10.5 | 11.2 | 12.1 | 12.1 | 10.3 | 8.7 | 8.7 | 10.1 | 10.3 | 10.3 | 10.3 | 10.5 | 3 | 10.4 |
675 | Huron, SD | V | mi/hr | 10.5 | 10.7 | 11.4 | 11.9 | 11.4 | 9.8 | 9.2 | 9.2 | 10.1 | 10.3 | 10.5 | 10.5 | 10.5 | 3 | 10.5 |
676 | Pierre, SD | V | mi/hr | 10.7 | 10.7 | 11.9 | 12.1 | 11.9 | 10.5 | 10.3 | 10.3 | 10.7 | 11.0 | 10.5 | 11.0 | 11.0 | 3 | 11.0 |
677 | Rapid City, SD | V | mi/hr | 9.8 | 10.7 | 11.4 | 12.1 | 11.6 | 10.1 | 9.4 | 9.4 | 9.8 | 10.7 | 10.3 | 9.8 | 10.5 | 3 | 10.4 |
678 | Sioux Falls, SD | V | mi/hr | 10.1 | 10.3 | 11.2 | 11.9 | 11.2 | 9.8 | 9.2 | 8.7 | 9.6 | 9.8 | 10.1 | 9.8 | 10.1 | 3 | 10.1 |
679 | Bristol, TN | V | mi/hr | 5.4 | 5.6 | 6.0 | 5.6 | 4.7 | 3.8 | 3.6 | 2.9 | 3.1 | 3.6 | 4.0 | 4.7 | 4.5 | 3 | 4.4 |
680 | Chattanooga, TN | V | mi/hr | 5.8 | 6.0 | 6.5 | 6.0 | 4.9 | 4.3 | 4.3 | 3.8 | 4.0 | 4.0 | 4.5 | 5.4 | 4.9 | 3 | 5.0 |
681 | Knoxville, TN | V | mi/hr | 6.5 | 6.7 | 7.2 | 6.9 | 6.3 | 5.4 | 5.4 | 4.5 | 4.7 | 4.7 | 5.4 | 6.0 | 5.8 | 3 | 5.8 |
682 | Memphis, TN | V | mi/hr | 9.2 | 9.2 | 9.8 | 9.6 | 8.5 | 7.4 | 6.9 | 6.7 | 7.2 | 7.2 | 8.1 | 8.7 | 8.3 | 3 | 8.2 |
683 | Nashville, TN | V | mi/hr | 8.1 | 8.1 | 8.3 | 8.1 | 6.7 | 6.0 | 5.8 | 5.6 | 5.8 | 6.3 | 7.2 | 7.6 | 6.9 | 3 | 7.0 |
684 | Abilene, TX | V | mi/hr | 11.0 | 11.4 | 12.5 | 13.2 | 11.9 | 11.2 | 10.1 | 8.7 | 8.9 | 10.3 | 10.7 | 10.7 | 11.0 | 3 | 10.9 |
685 | Amarillo, TX | V | mi/hr | 12.1 | 12.5 | 13.9 | 14.8 | 13.6 | 13.9 | 12.3 | 11.6 | 12.1 | 12.5 | 12.5 | 12.1 | 12.8 | 3 | 12.8 |
686 | Austin, TX | V | mi/hr | 8.3 | 8.7 | 9.2 | 8.9 | 8.5 | 8.1 | 7.4 | 6.5 | 6.3 | 6.9 | 7.6 | 7.8 | 7.8 | 3 | 7.9 |
687 | Brownsville, TX | V | mi/hr | 10.1 | 11.2 | 11.9 | 12.5 | 12.1 | 11.0 | 11.0 | 9.2 | 7.4 | 8.7 | 9.2 | 9.6 | 10.3 | 3 | 10.3 |
688 | Corpus Christi, TX | V | mi/hr | 12.1 | 12.5 | 13.4 | 14.1 | 12.5 | 10.5 | 10.7 | 9.8 | 9.2 | 10.7 | 11.4 | 11.6 | 11.6 | 3 | 11.5 |
689 | Dallas-Fort Worth, TX | V | mi/hr | 10.5 | 10.7 | 11.9 | 12.1 | 11.0 | 10.5 | 9.8 | 8.5 | 8.3 | 9.4 | 10.3 | 10.3 | 10.3 | 3 | 10.3 |
690 | El Paso, TX | V | mi/hr | 7.8 | 8.9 | 10.1 | 11.0 | 10.1 | 9.2 | 8.1 | 7.4 | 7.4 | 7.6 | 7.4 | 7.4 | 8.5 | 3 | 8.5 |
691 | Houston, TX | V | mi/hr | 7.8 | 8.3 | 8.5 | 8.9 | 8.1 | 6.7 | 5.8 | 5.6 | 6.0 | 6.7 | 7.2 | 7.6 | 7.4 | 3 | 7.3 |
692 | Lubbock, TX | V | mi/hr | 11.6 | 12.3 | 13.9 | 14.3 | 13.6 | 13.0 | 11.0 | 9.8 | 10.1 | 11.0 | 11.4 | 11.4 | 11.9 | 3 | 12.0 |
693 | Lufkin, TX | V | mi/hr | 6.9 | 7.4 | 7.6 | 7.6 | 6.9 | 5.8 | 5.4 | 4.9 | 5.4 | 5.8 | 6.3 | 6.5 | 6.5 | 3 | 6.4 |
694 | Midland, TX | V | mi/hr | 10.1 | 11.0 | 12.1 | 12.8 | 12.3 | 12.3 | 10.7 | 9.6 | 9.6 | 10.3 | 9.8 | 9.8 | 11.0 | 3 | 10.9 |
695 | Port Arthur, TX | V | mi/hr | 9.6 | 10.1 | 10.3 | 10.3 | 9.2 | 7.6 | 6.0 | 5.8 | 7.2 | 8.1 | 8.5 | 9.2 | 8.5 | 3 | 8.5 |
696 | San Angelo, TX | V | mi/hr | 9.6 | 10.1 | 10.7 | 11.4 | 10.5 | 10.1 | 9.2 | 8.1 | 7.8 | 8.5 | 9.2 | 9.4 | 9.6 | 3 | 9.6 |
697 | San Antonio, TX | V | mi/hr | 7.6 | 7.8 | 8.9 | 9.4 | 9.4 | 9.2 | 8.5 | 7.8 | 6.9 | 7.4 | 7.6 | 7.4 | 8.1 | 3 | 8.2 |
698 | Victoria, TX | V | mi/hr | 9.8 | 10.1 | 10.5 | 11.0 | 10.3 | 9.2 | 8.3 | 7.4 | 7.4 | 8.3 | 8.7 | 9.2 | 9.2 | 3 | 9.2 |
699 | Waco, TX | V | mi/hr | 9.8 | 10.1 | 11.0 | 11.2 | 10.1 | 9.6 | 9.6 | 8.5 | 7.8 | 8.7 | 9.4 | 9.4 | 9.6 | 3 | 9.6 |
700 | Cedar City, UT | V | mi/hr | 6.3 | 6.7 | 8.1 | 8.9 | 8.7 | 8.7 | 7.6 | 7.6 | 7.2 | 6.7 | 6.3 | 6.3 | 7.4 | 3 | 7.4 |
701 | Salt Lake City, UT | V | mi/hr | 6.7 | 7.2 | 8.7 | 9.6 | 8.9 | 9.2 | 8.9 | 9.6 | 8.7 | 8.1 | 7.4 | 7.2 | 8.3 | 3 | 8.4 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
702 | Burlington, VT | V | mi/hr | 8.9 | 8.5 | 8.5 | 8.7 | 8.1 | 7.4 | 6.9 | 6.9 | 7.6 | 8.1 | 8.7 | 8.9 | 8.1 | 3 | 8.1 |
703 | DC-Dulles, VA | V | mi/hr | 7.8 | 8.1 | 8.5 | 8.1 | 6.7 | 6.0 | 5.8 | 5.6 | 6.0 | 6.0 | 6.7 | 7.2 | 6.9 | 3 | 6.9 |
704 | DC-Reagan, VA | V | mi/hr | 9.6 | 9.6 | 10.5 | 9.8 | 8.9 | 8.5 | 8.1 | 7.8 | 8.3 | 8.1 | 8.7 | 8.9 | 8.9 | 3 | 8.9 |
705 | Lynchburg, VA | V | mi/hr | 6.0 | 6.0 | 6.7 | 6.5 | 5.6 | 4.7 | 4.3 | 3.8 | 4.3 | 4.3 | 4.9 | 5.1 | 5.1 | 3 | 5.2 |
706 | Norfolk, VA | V | mi/hr | 9.8 | 10.1 | 10.5 | 10.7 | 9.8 | 8.7 | 8.3 | 7.8 | 9.2 | 8.7 | 8.9 | 9.2 | 9.2 | 3 | 9.3 |
707 | Richmond, VA | V | mi/hr | 8.3 | 8.5 | 9.2 | 8.9 | 7.8 | 7.2 | 6.7 | 6.3 | 6.9 | 6.7 | 7.4 | 7.6 | 7.6 | 3 | 7.6 |
708 | Roanoke, VA | V | mi/hr | 8.1 | 8.1 | 8.3 | 7.8 | 6.5 | 5.8 | 5.6 | 4.9 | 5.1 | 5.6 | 6.5 | 7.4 | 6.7 | 3 | 6.6 |
709 | Olympia, WA | V | mi/hr | 6.0 | 5.6 | 6.3 | 6.3 | 6.0 | 6.0 | 5.4 | 4.9 | 4.7 | 5.1 | 6.0 | 6.0 | 5.6 | 3 | 5.7 |
710 | Quillayute, WA | V | mi/hr | 6.5 | 6.0 | 6.3 | 5.8 | 5.4 | 4.9 | 4.7 | 4.5 | 4.0 | 4.9 | 6.0 | 6.3 | 5.4 | 3 | 5.4 |
711 | Seattle, WA | V | mi/hr | 8.5 | 8.3 | 8.5 | 7.8 | 7.6 | 7.6 | 7.2 | 6.9 | 6.7 | 7.2 | 8.1 | 8.7 | 7.8 | 3 | 7.8 |
712 | Spokane, WA | V | mi/hr | 8.3 | 8.3 | 9.6 | 9.6 | 9.4 | 9.2 | 8.5 | 8.1 | 7.8 | 8.1 | 8.3 | 8.3 | 8.7 | 3 | 8.6 |
713 | Stampede Pass, WA | V | mi/hr | 7.4 | 7.4 | 6.9 | 6.7 | 6.9 | 7.4 | 7.4 | 6.9 | 6.7 | 6.7 | 6.9 | 7.4 | 7.2 | 3 | 7.1 |
714 | Yakima, WA | V | mi/hr | 4.3 | 5.4 | 6.7 | 7.4 | 7.4 | 7.6 | 7.2 | 6.7 | 6.3 | 5.6 | 4.7 | 4.0 | 6.0 | 3 | 6.1 |
715 | Beckley, WV | V | mi/hr | 8.3 | 8.1 | 8.1 | 7.8 | 6.7 | 5.6 | 5.1 | 4.9 | 5.6 | 6.3 | 6.9 | 7.6 | 6.7 | 3 | 6.8 |
716 | Charleston, WV | V | mi/hr | 5.4 | 5.1 | 5.1 | 5.1 | 4.0 | 3.4 | 3.1 | 2.7 | 2.9 | 3.1 | 4.0 | 4.7 | 4.0 | 3 | 4.1 |
717 | Elkins, WV | V | mi/hr | 5.8 | 5.8 | 5.8 | 5.8 | 4.5 | 3.6 | 3.1 | 2.7 | 2.9 | 3.6 | 4.7 | 5.1 | 4.5 | 3 | 4.5 |
718 | Huntington, WV | V | mi/hr | 6.9 | 6.7 | 6.9 | 6.7 | 5.6 | 4.9 | 4.7 | 4.3 | 4.5 | 4.9 | 5.8 | 6.3 | 5.6 | 3 | 5.7 |
719 | Eau Claire, WI | V | mi/hr | 7.4 | 7.6 | 7.6 | 8.7 | 8.3 | 7.2 | 6.5 | 6.3 | 6.9 | 7.6 | 7.6 | 7.2 | 7.4 | 3 | 7.4 |
720 | Green Bay, WI | V | mi/hr | 9.6 | 9.4 | 9.4 | 10.5 | 9.2 | 7.6 | 7.2 | 6.7 | 7.6 | 8.7 | 9.2 | 8.9 | 8.7 | 3 | 8.7 |
721 | La Crosse, WI | V | mi/hr | 8.7 | 8.9 | 9.2 | 9.8 | 9.2 | 8.1 | 7.6 | 7.4 | 8.3 | 9.2 | 9.4 | 8.7 | 8.7 | 3 | 8.7 |
722 | Madison, WI | V | mi/hr | 8.5 | 8.5 | 8.9 | 9.6 | 8.3 | 6.9 | 6.5 | 6.0 | 6.7 | 7.8 | 8.5 | 8.1 | 7.8 | 3 | 7.9 |
723 | Milwaukee, WI | V | mi/hr | 11.0 | 10.7 | 10.7 | 11.6 | 10.3 | 8.7 | 8.9 | 8.5 | 8.9 | 10.1 | 10.5 | 10.5 | 10.1 | 3 | 10.0 |
724 | Casper, WY | V | mi/hr | 14.8 | 13.4 | 12.5 | 11.6 | 10.5 | 10.3 | 9.2 | 9.4 | 9.8 | 11.0 | 13.4 | 15.0 | 11.6 | 3 | 11.7 |
725 | Cheyenne, WY | V | mi/hr | 14.1 | 13.6 | 13.6 | 13.2 | 12.1 | 11.0 | 9.8 | 9.8 | 10.5 | 11.9 | 13.2 | 13.9 | 12.3 | 3 | 12.2 |
726 | Lander, WY | V | mi/hr | 4.9 | 4.9 | 6.7 | 7.4 | 7.4 | 7.4 | 7.2 | 6.9 | 6.5 | 5.6 | 5.1 | 4.9 | 6.3 | 3 | 6.2 |
727 | Rock Springs, WY | V | mi/hr | 12.1 | 11.2 | 12.1 | 12.3 | 11.2 | 10.7 | 9.4 | 8.9 | 9.4 | 11.0 | 11.2 | 11.4 | 11.0 | 3 | 10.9 |
728 | Sheridan, WY | V | mi/hr | 6.5 | 6.9 | 7.8 | 8.9 | 8.3 | 7.2 | 6.5 | 6.0 | 6.3 | 6.7 | 6.5 | 6.5 | 6.9 | 3 | 7.0 |
729 | Birmingham, AL | I | Btu/ft2/day | 769 | 1013 | 1382 | 1720 | 1884 | 1928 | 1889 | 1760 | 1504 | 1212 | 890 | 699 | 1388 | 4 | 1387.5 |
730 | Huntsville, AL | I | Btu/ft2/day | 714 | 949 | 1314 | 1690 | 1868 | 1973 | 1948 | 1823 | 1508 | 1191 | 835 | 656 | 1372 | 4 | 1372.4 |
731 | Mobile, AL | I | Btu/ft2/day | 865 | 1114 | 1446 | 1774 | 1955 | 1925 | 1876 | 1767 | 1557 | 1304 | 1024 | 818 | 1452 | 4 | 1452.1 |
732 | Montgomery, AL | I | Btu/ft2/day | 823 | 1076 | 1421 | 1766 | 1952 | 1951 | 1943 | 1781 | 1530 | 1223 | 950 | 749 | 1430 | 4 | 1430.4 |
733 | Phoenix, AZ | I | Btu/ft2/day | 1058 | 1335 | 1774 | 2248 | 2495 | 2606 | 2379 | 2144 | 1910 | 1542 | 1172 | 967 | 1802 | 4 | 1802.5 |
734 | Prescott, AZ | I | Btu/ft2/day | 982 | 1245 | 1694 | 2156 | 2415 | 2571 | 2171 | 1903 | 1805 | 1493 | 1130 | 901 | 1705 | 4 | 1705.5 |
735 | Tucson, AZ | I | Btu/ft2/day | 1110 | 1370 | 1840 | 2279 | 2510 | 2582 | 2198 | 2007 | 1886 | 1595 | 1249 | 1033 | 1805 | 4 | 1804.9 |
736 | Fort Smith, AR | I | Btu/ft2/day | 738 | 977 | 1299 | 1674 | 1808 | 1991 | 2117 | 1918 | 1522 | 1177 | 811 | 674 | 1392 | 4 | 1392.2 |
737 | Little Rock, AR | I | Btu/ft2/day | 717 | 970 | 1302 | 1686 | 1820 | 2008 | 2009 | 1879 | 1534 | 1171 | 814 | 656 | 1380 | 4 | 1380.5 |
738 | Arcata, CA | I | Btu/ft2/day | 527 | 730 | 1139 | 1516 | 1822 | 1946 | 1809 | 1573 | 1327 | 971 | 613 | 460 | 1203 | 4 | 1202.8 |
739 | Bakersfield, CA | I | Btu/ft2/day | 717 | 1031 | 1543 | 2010 | 2358 | 2570 | 2500 | 2293 | 1911 | 1411 | 952 | 696 | 1666 | 4 | 1666.0 |
740 | Bishop, CA | I | Btu/ft2/day | 882 | 1186 | 1683 | 2080 | 2378 | 2564 | 2487 | 2278 | 1925 | 1457 | 1046 | 824 | 1732 | 4 | 1732.5 |
741 | Daggett, CA | I | Btu/ft2/day | 992 | 1270 | 1756 | 2197 | 2492 | 2656 | 2470 | 2259 | 1972 | 1544 | 1142 | 921 | 1806 | 4 | 1805.9 |
742 | Fresno, CA | I | Btu/ft2/day | 638 | 973 | 1519 | 2002 | 2368 | 2573 | 2534 | 2290 | 1895 | 1383 | 889 | 602 | 1639 | 4 | 1638.8 |
743 | Long Beach, CA | I | Btu/ft2/day | 894 | 1109 | 1548 | 1958 | 2066 | 2207 | 2264 | 2156 | 1767 | 1327 | 1039 | 843 | 1598 | 4 | 1598.2 |
744 | Los Angeles AP, CA | I | Btu/ft2/day | 895 | 1115 | 1537 | 1988 | 2045 | 2140 | 2117 | 2037 | 1662 | 1298 | 1036 | 834 | 1559 | 4 | 1558.7 |
745 | Redding, CA | I | Btu/ft2/day | 577 | 856 | 1354 | 1772 | 2198 | 2464 | 2526 | 2246 | 1786 | 1209 | 721 | 497 | 1517 | 4 | 1517.2 |
746 | Sacramento, CA | I | Btu/ft2/day | 563 | 877 | 1409 | 1891 | 2249 | 2510 | 2514 | 2239 | 1823 | 1269 | 790 | 518 | 1555 | 4 | 1554.3 |
747 | San Diego, CA | I | Btu/ft2/day | 990 | 1206 | 1604 | 1990 | 1993 | 2135 | 2127 | 2087 | 1774 | 1367 | 1107 | 922 | 1608 | 4 | 1608.5 |
748 | San Francisco AP, CA | I | Btu/ft2/day | 666 | 896 | 1353 | 1813 | 1981 | 2123 | 2023 | 1747 | 1488 | 1124 | 798 | 619 | 1386 | 4 | 1385.9 |
749 | Santa Barbara, CA | I | Btu/ft2/day | 907 | 1116 | 1543 | 1968 | 2115 | 2184 | 2153 | 2107 | 1749 | 1346 | 1051 | 839 | 1590 | 4 | 1589.8 |
750 | Santa Maria, CA | I | Btu/ft2/day | 892 | 1109 | 1563 | 2010 | 2253 | 2358 | 2261 | 2111 | 1784 | 1386 | 1036 | 828 | 1633 | 4 | 1632.6 |
751 | Stockton, CA | I | Btu/ft2/day | 573 | 907 | 1445 | 1879 | 2251 | 2525 | 2510 | 2256 | 1844 | 1308 | 824 | 552 | 1573 | 4 | 1572.8 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
752 | Alamosa, CO | I | Btu/ft2/day | 898 | 1191 | 1619 | 1987 | 2266 | 2427 | 2269 | 1992 | 1786 | 1397 | 1023 | 798 | 1638 | 4 | 1637.8 |
753 | Colorado Springs, CO | I | Btu/ft2/day | 843 | 1093 | 1467 | 1794 | 2012 | 2182 | 2108 | 1884 | 1667 | 1275 | 899 | 742 | 1497 | 4 | 1497.2 |
754 | Denver, CO | I | Btu/ft2/day | 764 | 1052 | 1463 | 1779 | 2049 | 2275 | 2213 | 1941 | 1658 | 1216 | 817 | 664 | 1491 | 4 | 1490.9 |
755 | Grand Junction, CO | I | Btu/ft2/day | 739 | 1039 | 1522 | 1876 | 2211 | 2434 | 2339 | 2020 | 1721 | 1281 | 874 | 662 | 1560 | 4 | 1559.8 |
756 | Limon, CO | I | Btu/ft2/day | 797 | 1066 | 1466 | 1773 | 2074 | 2301 | 2267 | 2003 | 1712 | 1264 | 860 | 693 | 1523 | 4 | 1523.0 |
757 | Pueblo, CO | I | Btu/ft2/day | 862 | 1144 | 1557 | 1897 | 2197 | 2399 | 2356 | 2093 | 1783 | 1344 | 950 | 779 | 1613 | 4 | 1613.4 |
758 | Bridgeport, CT | I | Btu/ft2/day | 560 | 847 | 1156 | 1490 | 1750 | 1862 | 1904 | 1685 | 1320 | 948 | 621 | 501 | 1220 | 4 | 1220.3 |
759 | Hartford, CT | I | Btu/ft2/day | 560 | 814 | 1133 | 1453 | 1700 | 1797 | 1833 | 1622 | 1289 | 905 | 582 | 482 | 1181 | 4 | 1180.8 |
760 | Wilmington_DE, DE | I | Btu/ft2/day | 629 | 911 | 1185 | 1528 | 1786 | 1909 | 1916 | 1680 | 1366 | 1016 | 678 | 556 | 1264 | 4 | 1263.3 |
761 | Daytona Beach, FL | I | Btu/ft2/day | 1018 | 1215 | 1579 | 1931 | 2049 | 1893 | 1911 | 1767 | 1518 | 1296 | 1063 | 916 | 1513 | 4 | 1513.0 |
762 | Fort Myers, FL | I | Btu/ft2/day | 1150 | 1426 | 1718 | 1993 | 2075 | 1880 | 1805 | 1740 | 1533 | 1415 | 1205 | 1054 | 1583 | 4 | 1582.8 |
763 | Gainesville, FL | I | Btu/ft2/day | 970 | 1213 | 1549 | 1890 | 2019 | 1865 | 1863 | 1704 | 1484 | 1276 | 1063 | 887 | 1482 | 4 | 1481.9 |
764 | Jacksonville, FL | I | Btu/ft2/day | 937 | 1186 | 1522 | 1890 | 2035 | 1911 | 1948 | 1756 | 1466 | 1237 | 1021 | 846 | 1480 | 4 | 1479.6 |
765 | Key West, FL | I | Btu/ft2/day | 1206 | 1462 | 1805 | 2069 | 2131 | 2035 | 2041 | 1943 | 1667 | 1465 | 1240 | 1098 | 1680 | 4 | 1680.2 |
766 | Miami, FL | I | Btu/ft2/day | 1118 | 1346 | 1625 | 1875 | 1938 | 1737 | 1813 | 1701 | 1456 | 1309 | 1113 | 1015 | 1504 | 4 | 1503.8 |
767 | Orlando, FL | I | Btu/ft2/day | 1043 | 1257 | 1588 | 1904 | 2021 | 1849 | 1854 | 1726 | 1506 | 1328 | 1096 | 944 | 1510 | 4 | 1509.7 |
768 | Pensacola, FL | I | Btu/ft2/day | 890 | 1144 | 1504 | 1813 | 2038 | 2019 | 1911 | 1783 | 1594 | 1327 | 1040 | 830 | 1491 | 4 | 1491.1 |
769 | Tallahassee, FL | I | Btu/ft2/day | 933 | 1195 | 1553 | 1904 | 2031 | 1925 | 1866 | 1764 | 1565 | 1327 | 1070 | 872 | 1500 | 4 | 1500.4 |
770 | Tampa, FL | I | Btu/ft2/day | 1073 | 1294 | 1656 | 1991 | 2124 | 1962 | 1851 | 1732 | 1561 | 1394 | 1158 | 990 | 1566 | 4 | 1565.5 |
771 | Vero Beach, FL | I | Btu/ft2/day | 1052 | 1300 | 1593 | 1906 | 2000 | 1848 | 1898 | 1752 | 1516 | 1318 | 1083 | 949 | 1518 | 4 | 1517.9 |
772 | West Palm Beach, FL | I | Btu/ft2/day | 1105 | 1342 | 1635 | 1912 | 1999 | 1852 | 1936 | 1789 | 1555 | 1352 | 1113 | 998 | 1549 | 4 | 1549.0 |
773 | Athens, GA | I | Btu/ft2/day | 819 | 1062 | 1390 | 1764 | 1951 | 1978 | 1946 | 1760 | 1487 | 1211 | 915 | 743 | 1419 | 4 | 1418.8 |
774 | Atlanta, GA | I | Btu/ft2/day | 801 | 1046 | 1379 | 1747 | 1925 | 1949 | 1925 | 1739 | 1477 | 1201 | 896 | 718 | 1400 | 4 | 1400.3 |
775 | Augusta, GA | I | Btu/ft2/day | 836 | 1084 | 1432 | 1806 | 1995 | 1979 | 1965 | 1782 | 1509 | 1214 | 935 | 775 | 1443 | 4 | 1442.7 |
776 | Columbus, GA | I | Btu/ft2/day | 823 | 1079 | 1409 | 1773 | 1936 | 1936 | 1936 | 1718 | 1491 | 1211 | 949 | 753 | 1418 | 4 | 1417.8 |
777 | Macon, GA | I | Btu/ft2/day | 852 | 1107 | 1460 | 1839 | 2026 | 1978 | 1981 | 1788 | 1523 | 1233 | 960 | 783 | 1461 | 4 | 1460.8 |
778 | Savannah, GA | I | Btu/ft2/day | 876 | 1134 | 1484 | 1847 | 2015 | 1947 | 1981 | 1765 | 1477 | 1224 | 993 | 817 | 1464 | 4 | 1463.3 |
779 | Hilo, HI | I | Btu/ft2/day | 1187 | 1316 | 1431 | 1617 | 1743 | 1820 | 1822 | 1748 | 1672 | 1413 | 1137 | 1076 | 1498 | 4 | 1498.5 |
780 | Honolulu, HI | I | Btu/ft2/day | 1279 | 1511 | 1737 | 1995 | 2071 | 2155 | 2127 | 2075 | 1901 | 1595 | 1318 | 1177 | 1745 | 4 | 1745.1 |
781 | Kahului, HI | I | Btu/ft2/day | 1335 | 1552 | 1727 | 1984 | 2126 | 2228 | 2164 | 2115 | 1932 | 1682 | 1377 | 1257 | 1790 | 4 | 1789.9 |
782 | Lihue, HI | I | Btu/ft2/day | 1193 | 1375 | 1566 | 1755 | 1941 | 2022 | 1956 | 1918 | 1779 | 1427 | 1161 | 1036 | 1594 | 4 | 1594.1 |
783 | Boise, ID | I | Btu/ft2/day | 492 | 831 | 1255 | 1705 | 2135 | 2360 | 2476 | 2163 | 1695 | 1102 | 580 | 427 | 1435 | 4 | 1435.1 |
784 | Lewiston, ID | I | Btu/ft2/day | 407 | 698 | 1068 | 1497 | 1870 | 2063 | 2307 | 2003 | 1473 | 882 | 448 | 326 | 1254 | 4 | 1253.5 |
785 | Pocatello, ID | I | Btu/ft2/day | 485 | 817 | 1292 | 1680 | 2084 | 2327 | 2398 | 2081 | 1634 | 1103 | 605 | 413 | 1410 | 4 | 1409.9 |
786 | Chicago, IL | I | Btu/ft2/day | 487 | 755 | 1103 | 1453 | 1718 | 1939 | 1898 | 1621 | 1332 | 913 | 549 | 423 | 1183 | 4 | 1182.6 |
787 | Moline, IL | I | Btu/ft2/day | 532 | 798 | 1181 | 1469 | 1756 | 1959 | 1949 | 1712 | 1400 | 946 | 593 | 456 | 1229 | 4 | 1229.3 |
788 | Peoria, IL | I | Btu/ft2/day | 553 | 845 | 1179 | 1503 | 1746 | 1990 | 1982 | 1724 | 1444 | 983 | 608 | 475 | 1253 | 4 | 1252.7 |
789 | Rockford, IL | I | Btu/ft2/day | 483 | 766 | 1123 | 1442 | 1700 | 1933 | 1881 | 1647 | 1337 | 902 | 545 | 401 | 1180 | 4 | 1180.0 |
790 | Springfield_IL, IL | I | Btu/ft2/day | 561 | 862 | 1179 | 1513 | 1747 | 1983 | 2017 | 1766 | 1459 | 1035 | 641 | 501 | 1272 | 4 | 1272.0 |
791 | Evansville, IN | I | Btu/ft2/day | 598 | 880 | 1173 | 1574 | 1796 | 2005 | 1994 | 1850 | 1484 | 1097 | 693 | 525 | 1306 | 4 | 1305.8 |
792 | Fort Wayne, IN | I | Btu/ft2/day | 490 | 750 | 1131 | 1458 | 1709 | 1923 | 1944 | 1677 | 1371 | 935 | 560 | 420 | 1197 | 4 | 1197.3 |
793 | Indianapolis, IN | I | Btu/ft2/day | 550 | 815 | 1165 | 1486 | 1757 | 1958 | 1934 | 1739 | 1441 | 1012 | 615 | 472 | 1245 | 4 | 1245.3 |
794 | South Bend, IN | I | Btu/ft2/day | 433 | 698 | 1130 | 1471 | 1729 | 1935 | 1898 | 1646 | 1335 | 889 | 518 | 389 | 1173 | 4 | 1172.6 |
795 | Des Moines, IA | I | Btu/ft2/day | 545 | 817 | 1181 | 1507 | 1782 | 1979 | 1995 | 1762 | 1435 | 986 | 613 | 482 | 1257 | 4 | 1257.0 |
796 | Dubuque, IA | I | Btu/ft2/day | 503 | 764 | 1135 | 1476 | 1718 | 1933 | 1904 | 1668 | 1348 | 903 | 551 | 422 | 1194 | 4 | 1193.8 |
797 | Mason City, IA | I | Btu/ft2/day | 469 | 722 | 1111 | 1479 | 1707 | 1902 | 1944 | 1678 | 1308 | 878 | 538 | 388 | 1177 | 4 | 1177.0 |
798 | Sioux City, IA | I | Btu/ft2/day | 522 | 787 | 1178 | 1532 | 1774 | 2010 | 2046 | 1787 | 1418 | 982 | 624 | 468 | 1260 | 4 | 1260.7 |
799 | Waterloo, IA | I | Btu/ft2/day | 505 | 755 | 1131 | 1451 | 1722 | 1924 | 1952 | 1698 | 1357 | 909 | 554 | 418 | 1198 | 4 | 1198.0 |
800 | Concordia, KS | I | Btu/ft2/day | 701 | 948 | 1319 | 1647 | 1881 | 2123 | 2140 | 1916 | 1544 | 1128 | 772 | 608 | 1394 | 4 | 1393.9 |
801 | Dodge City, KS | I | Btu/ft2/day | 816 | 1068 | 1439 | 1786 | 2049 | 2230 | 2272 | 1980 | 1636 | 1239 | 889 | 740 | 1512 | 4 | 1512.0 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
802 | Goodland, KS | I | Btu/ft2/day | 785 | 1014 | 1426 | 1762 | 2007 | 2274 | 2301 | 2013 | 1646 | 1216 | 826 | 681 | 1496 | 4 | 1495.9 |
803 | Russell, KS | I | Btu/ft2/day | 739 | 986 | 1343 | 1669 | 1944 | 2144 | 2176 | 1927 | 1571 | 1153 | 818 | 655 | 1427 | 4 | 1427.1 |
804 | Topeka, KS | I | Btu/ft2/day | 679 | 944 | 1277 | 1574 | 1809 | 2027 | 2069 | 1864 | 1497 | 1102 | 733 | 598 | 1348 | 4 | 1347.8 |
805 | Wichita, KS | I | Btu/ft2/day | 763 | 1050 | 1345 | 1701 | 1930 | 2132 | 2179 | 1961 | 1567 | 1173 | 831 | 666 | 1442 | 4 | 1441.5 |
806 | Cincinnati, KY | I | Btu/ft2/day | 553 | 832 | 1167 | 1532 | 1782 | 1956 | 1937 | 1768 | 1439 | 1027 | 644 | 487 | 1260 | 4 | 1260.3 |
807 | Jackson_KY, KY | I | Btu/ft2/day | 591 | 831 | 1165 | 1534 | 1745 | 1909 | 1882 | 1752 | 1416 | 1060 | 708 | 539 | 1261 | 4 | 1261.0 |
808 | Lexington, KY | I | Btu/ft2/day | 571 | 841 | 1177 | 1572 | 1814 | 1963 | 1925 | 1782 | 1444 | 1079 | 688 | 517 | 1281 | 4 | 1281.1 |
809 | Louisville, KY | I | Btu/ft2/day | 595 | 895 | 1206 | 1563 | 1816 | 1982 | 1963 | 1811 | 1471 | 1073 | 692 | 520 | 1299 | 4 | 1298.9 |
810 | Paducah, KY | I | Btu/ft2/day | 630 | 893 | 1224 | 1607 | 1820 | 2017 | 2031 | 1888 | 1494 | 1121 | 726 | 556 | 1334 | 4 | 1333.9 |
811 | Baton Rouge, LA | I | Btu/ft2/day | 822 | 1075 | 1375 | 1736 | 1894 | 1914 | 1896 | 1813 | 1553 | 1291 | 983 | 784 | 1428 | 4 | 1428.0 |
812 | Lake Charles, LA | I | Btu/ft2/day | 833 | 1046 | 1395 | 1727 | 1920 | 1977 | 1930 | 1825 | 1575 | 1321 | 987 | 786 | 1443 | 4 | 1443.5 |
813 | New Orleans, LA | I | Btu/ft2/day | 873 | 1114 | 1454 | 1798 | 1964 | 1928 | 1856 | 1791 | 1570 | 1328 | 1038 | 827 | 1462 | 4 | 1461.8 |
814 | Shreveport, LA | I | Btu/ft2/day | 783 | 1001 | 1342 | 1709 | 1837 | 2007 | 2049 | 1915 | 1575 | 1251 | 884 | 732 | 1424 | 4 | 1423.8 |
815 | Bangor, ME | I | Btu/ft2/day | 496 | 752 | 1059 | 1410 | 1639 | 1762 | 1751 | 1585 | 1227 | 792 | 491 | 411 | 1115 | 4 | 1114.6 |
816 | Caribou, ME | I | Btu/ft2/day | 428 | 674 | 1034 | 1390 | 1684 | 1800 | 1703 | 1542 | 1136 | 689 | 424 | 353 | 1071 | 4 | 1071.4 |
817 | Portland, ME | I | Btu/ft2/day | 530 | 803 | 1111 | 1471 | 1714 | 1838 | 1844 | 1688 | 1295 | 879 | 552 | 458 | 1182 | 4 | 1181.9 |
818 | Baltimore , MD | I | Btu/ft2/day | 653 | 929 | 1231 | 1555 | 1774 | 1918 | 1866 | 1681 | 1350 | 1036 | 709 | 580 | 1274 | 4 | 1273.5 |
819 | Boston, MA | I | Btu/ft2/day | 558 | 833 | 1113 | 1461 | 1703 | 1811 | 1830 | 1657 | 1284 | 913 | 576 | 475 | 1184 | 4 | 1184.5 |
820 | Worchester, MA | I | Btu/ft2/day | 567 | 821 | 1123 | 1454 | 1675 | 1764 | 1848 | 1619 | 1276 | 903 | 584 | 477 | 1176 | 4 | 1175.9 |
821 | Alpena, MI | I | Btu/ft2/day | 401 | 653 | 1103 | 1457 | 1771 | 1948 | 1896 | 1632 | 1232 | 752 | 439 | 346 | 1136 | 4 | 1135.8 |
822 | Detroit Metro_AP, MI | I | Btu/ft2/day | 479 | 755 | 1117 | 1442 | 1738 | 1922 | 1896 | 1620 | 1332 | 861 | 510 | 400 | 1173 | 4 | 1172.7 |
823 | Detroit - City, MI | I | Btu/ft2/day | 469 | 746 | 1120 | 1437 | 1711 | 1884 | 1850 | 1585 | 1316 | 870 | 507 | 409 | 1159 | 4 | 1158.7 |
824 | Flint, MI | I | Btu/ft2/day | 440 | 713 | 1104 | 1474 | 1747 | 1947 | 1921 | 1635 | 1309 | 839 | 491 | 394 | 1168 | 4 | 1167.8 |
825 | Grand Rapids, MI | I | Btu/ft2/day | 405 | 684 | 1109 | 1461 | 1746 | 1943 | 1913 | 1635 | 1306 | 819 | 487 | 367 | 1156 | 4 | 1156.3 |
826 | Houghton Lake, MI | I | Btu/ft2/day | 401 | 646 | 1089 | 1462 | 1708 | 1894 | 1874 | 1593 | 1219 | 763 | 439 | 363 | 1121 | 4 | 1120.9 |
827 | Lansing, MI | I | Btu/ft2/day | 459 | 729 | 1109 | 1441 | 1707 | 1905 | 1863 | 1595 | 1303 | 833 | 494 | 398 | 1153 | 4 | 1153.0 |
828 | Muskegon, MI | I | Btu/ft2/day | 391 | 659 | 1102 | 1479 | 1775 | 1986 | 1962 | 1671 | 1290 | 809 | 451 | 339 | 1160 | 4 | 1159.5 |
829 | Sault Ste Marie, MI | I | Btu/ft2/day | 357 | 617 | 1042 | 1473 | 1794 | 1962 | 1837 | 1611 | 1128 | 677 | 378 | 291 | 1097 | 4 | 1097.3 |
830 | Traverse City, MI | I | Btu/ft2/day | 403 | 648 | 1101 | 1462 | 1756 | 1921 | 1874 | 1619 | 1210 | 725 | 405 | 339 | 1122 | 4 | 1121.9 |
831 | Duluth, MN | I | Btu/ft2/day | 461 | 707 | 1083 | 1499 | 1770 | 1844 | 1899 | 1627 | 1179 | 724 | 441 | 365 | 1133 | 4 | 1133.3 |
832 | International Falls, MN | I | Btu/ft2/day | 402 | 667 | 1041 | 1501 | 1708 | 1788 | 1807 | 1574 | 1102 | 657 | 375 | 300 | 1077 | 4 | 1076.8 |
833 | Minneapolis-St Paul, MN | I | Btu/ft2/day | 490 | 752 | 1116 | 1476 | 1712 | 1856 | 1930 | 1655 | 1265 | 814 | 501 | 389 | 1163 | 4 | 1163.0 |
834 | Rochester_MN, MN | I | Btu/ft2/day | 474 | 708 | 1106 | 1489 | 1709 | 1891 | 1955 | 1664 | 1286 | 848 | 513 | 384 | 1169 | 4 | 1168.9 |
835 | St Cloud, MN | I | Btu/ft2/day | 453 | 700 | 1094 | 1527 | 1754 | 1906 | 1967 | 1669 | 1259 | 802 | 481 | 367 | 1165 | 4 | 1164.9 |
836 | Jackson, MS | I | Btu/ft2/day | 783 | 1039 | 1369 | 1762 | 1929 | 2025 | 1969 | 1849 | 1576 | 1262 | 922 | 726 | 1434 | 4 | 1434.3 |
837 | Meridian, MS | I | Btu/ft2/day | 783 | 1044 | 1380 | 1726 | 1918 | 1989 | 1945 | 1823 | 1544 | 1252 | 924 | 727 | 1421 | 4 | 1421.3 |
838 | Tupelo, MS | I | Btu/ft2/day | 730 | 964 | 1309 | 1682 | 1912 | 2026 | 1990 | 1849 | 1536 | 1201 | 832 | 648 | 1390 | 4 | 1389.9 |
839 | Columbia_MO, MO | I | Btu/ft2/day | 629 | 886 | 1251 | 1575 | 1808 | 2033 | 2027 | 1823 | 1490 | 1070 | 690 | 556 | 1320 | 4 | 1319.8 |
840 | Kansas City, MO | I | Btu/ft2/day | 641 | 929 | 1273 | 1566 | 1815 | 1999 | 2028 | 1823 | 1488 | 1074 | 701 | 566 | 1325 | 4 | 1325.3 |
841 | Springfield_MO, MO | I | Btu/ft2/day | 677 | 929 | 1242 | 1593 | 1783 | 1996 | 2030 | 1868 | 1494 | 1129 | 742 | 601 | 1340 | 4 | 1340.3 |
842 | St Louis - Lambert, MO | I | Btu/ft2/day | 598 | 882 | 1217 | 1557 | 1765 | 2007 | 1978 | 1802 | 1471 | 1076 | 703 | 537 | 1299 | 4 | 1299.4 |
843 | St Louis - Spirit, MO | I | Btu/ft2/day | 604 | 888 | 1226 | 1570 | 1763 | 2009 | 1992 | 1811 | 1467 | 1073 | 694 | 545 | 1303 | 4 | 1303.5 |
844 | Billings, MT | I | Btu/ft2/day | 478 | 784 | 1148 | 1514 | 1883 | 2048 | 2221 | 1912 | 1424 | 903 | 544 | 398 | 1271 | 4 | 1271.4 |
845 | Glasgow, MT | I | Btu/ft2/day | 366 | 628 | 1068 | 1545 | 1889 | 2051 | 2180 | 1872 | 1340 | 834 | 444 | 311 | 1211 | 4 | 1210.7 |
846 | Great Falls, MT | I | Btu/ft2/day | 428 | 706 | 1106 | 1450 | 1806 | 2001 | 2163 | 1857 | 1360 | 840 | 465 | 358 | 1212 | 4 | 1211.7 |
847 | Harve City, MT | I | Btu/ft2/day | 371 | 632 | 1091 | 1522 | 1828 | 2035 | 2166 | 1862 | 1333 | 826 | 435 | 318 | 1202 | 4 | 1201.6 |
848 | Helena, MT | I | Btu/ft2/day | 456 | 767 | 1185 | 1513 | 1832 | 2048 | 2214 | 1898 | 1420 | 889 | 503 | 390 | 1260 | 4 | 1259.6 |
849 | Kalispell, MT | I | Btu/ft2/day | 322 | 605 | 1031 | 1440 | 1761 | 1895 | 2166 | 1812 | 1300 | 742 | 377 | 259 | 1142 | 4 | 1142.5 |
850 | Missoula, MT | I | Btu/ft2/day | 387 | 676 | 1088 | 1451 | 1787 | 1966 | 2229 | 1883 | 1385 | 820 | 428 | 315 | 1201 | 4 | 1201.3 |
851 | Grand Island, NE | I | Btu/ft2/day | 637 | 908 | 1284 | 1619 | 1846 | 2102 | 2100 | 1855 | 1492 | 1080 | 711 | 554 | 1349 | 4 | 1349.0 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
852 | Lincoln, NE | I | Btu/ft2/day | 591 | 872 | 1205 | 1555 | 1782 | 1994 | 2017 | 1784 | 1465 | 1030 | 663 | 521 | 1290 | 4 | 1289.9 |
853 | Norfolk_NE, NE | I | Btu/ft2/day | 566 | 836 | 1226 | 1556 | 1807 | 2036 | 2063 | 1794 | 1452 | 1012 | 647 | 507 | 1292 | 4 | 1291.8 |
854 | North Platte, NE | I | Btu/ft2/day | 666 | 938 | 1324 | 1642 | 1899 | 2170 | 2191 | 1905 | 1546 | 1097 | 710 | 587 | 1390 | 4 | 1389.6 |
855 | Omaha, NE | I | Btu/ft2/day | 582 | 852 | 1204 | 1512 | 1776 | 1992 | 2001 | 1749 | 1447 | 1007 | 646 | 506 | 1273 | 4 | 1272.8 |
856 | Scottsbluff, NE | I | Btu/ft2/day | 672 | 923 | 1295 | 1647 | 1955 | 2180 | 2261 | 1963 | 1571 | 1089 | 715 | 559 | 1403 | 4 | 1402.5 |
857 | Valentine, NE | I | Btu/ft2/day | 601 | 853 | 1215 | 1539 | 1862 | 2066 | 2187 | 1883 | 1496 | 1011 | 643 | 514 | 1322 | 4 | 1322.5 |
858 | Ely, NV | I | Btu/ft2/day | 724 | 1006 | 1454 | 1843 | 2146 | 2418 | 2371 | 2173 | 1800 | 1303 | 875 | 669 | 1565 | 4 | 1565.2 |
859 | Las Vegas, NV | I | Btu/ft2/day | 965 | 1244 | 1732 | 2164 | 2466 | 2628 | 2439 | 2202 | 1938 | 1479 | 1093 | 885 | 1769 | 4 | 1769.6 |
860 | Lovelock, NV | I | Btu/ft2/day | 687 | 992 | 1414 | 1822 | 2189 | 2471 | 2533 | 2252 | 1833 | 1274 | 802 | 587 | 1571 | 4 | 1571.3 |
861 | Mercury, NV | I | Btu/ft2/day | 937 | 1212 | 1714 | 2151 | 2464 | 2664 | 2527 | 2313 | 1977 | 1482 | 1077 | 860 | 1781 | 4 | 1781.5 |
862 | Reno, NV | I | Btu/ft2/day | 715 | 992 | 1471 | 1889 | 2232 | 2473 | 2512 | 2249 | 1854 | 1310 | 859 | 633 | 1599 | 4 | 1599.1 |
863 | Tonopah, NV | I | Btu/ft2/day | 828 | 1128 | 1629 | 2056 | 2344 | 2586 | 2507 | 2304 | 1922 | 1430 | 997 | 779 | 1709 | 4 | 1709.2 |
864 | Winnemucca, NV | I | Btu/ft2/day | 652 | 964 | 1380 | 1762 | 2147 | 2437 | 2523 | 2232 | 1795 | 1248 | 760 | 555 | 1538 | 4 | 1537.9 |
865 | Concord, NH | I | Btu/ft2/day | 535 | 803 | 1097 | 1469 | 1684 | 1801 | 1844 | 1644 | 1267 | 869 | 556 | 446 | 1168 | 4 | 1167.9 |
866 | Atlantic City, NJ | I | Btu/ft2/day | 646 | 924 | 1224 | 1581 | 1800 | 1935 | 1927 | 1733 | 1394 | 1048 | 720 | 578 | 1292 | 4 | 1292.5 |
867 | Newark, NJ | I | Btu/ft2/day | 602 | 887 | 1195 | 1502 | 1748 | 1854 | 1838 | 1629 | 1324 | 975 | 638 | 521 | 1226 | 4 | 1226.1 |
868 | Albuquerque, NM | I | Btu/ft2/day | 1003 | 1270 | 1699 | 2126 | 2356 | 2479 | 2312 | 2082 | 1846 | 1469 | 1114 | 904 | 1722 | 4 | 1721.7 |
869 | Gallup, NM | I | Btu/ft2/day | 930 | 1194 | 1654 | 2095 | 2350 | 2507 | 2187 | 1943 | 1806 | 1466 | 1072 | 825 | 1669 | 4 | 1669.1 |
870 | Roswell, NM | I | Btu/ft2/day | 1013 | 1323 | 1744 | 2125 | 2301 | 2434 | 2302 | 2085 | 1822 | 1452 | 1127 | 939 | 1722 | 4 | 1722.3 |
871 | Albany, NY | I | Btu/ft2/day | 532 | 789 | 1096 | 1496 | 1739 | 1853 | 1872 | 1640 | 1300 | 882 | 534 | 422 | 1180 | 4 | 1179.6 |
872 | Binghamton, NY | I | Btu/ft2/day | 500 | 745 | 1056 | 1449 | 1722 | 1839 | 1818 | 1614 | 1224 | 833 | 498 | 406 | 1142 | 4 | 1142.0 |
873 | Buffalo, NY | I | Btu/ft2/day | 447 | 730 | 1070 | 1453 | 1793 | 1939 | 1865 | 1643 | 1273 | 808 | 478 | 382 | 1157 | 4 | 1156.8 |
874 | Long Island, NY | I | Btu/ft2/day | 591 | 878 | 1196 | 1527 | 1785 | 1896 | 1890 | 1694 | 1347 | 988 | 643 | 518 | 1246 | 4 | 1246.1 |
875 | Massena, NY | I | Btu/ft2/day | 445 | 741 | 1072 | 1452 | 1753 | 1876 | 1865 | 1646 | 1236 | 764 | 449 | 348 | 1137 | 4 | 1137.3 |
876 | New York-LaGuardia, NY | I | Btu/ft2/day | 583 | 863 | 1154 | 1499 | 1760 | 1878 | 1859 | 1636 | 1314 | 962 | 627 | 511 | 1220 | 4 | 1220.5 |
877 | New York-Kennedy, NY | I | Btu/ft2/day | 588 | 861 | 1175 | 1516 | 1760 | 1898 | 1867 | 1661 | 1328 | 969 | 630 | 513 | 1231 | 4 | 1230.5 |
878 | Rochester, NY | I | Btu/ft2/day | 463 | 719 | 1059 | 1432 | 1759 | 1886 | 1849 | 1621 | 1242 | 788 | 480 | 385 | 1140 | 4 | 1140.3 |
879 | Syracuse, NY | I | Btu/ft2/day | 457 | 685 | 1033 | 1468 | 1797 | 1896 | 1884 | 1651 | 1246 | 801 | 472 | 380 | 1147 | 4 | 1147.5 |
880 | Asheville, NC | I | Btu/ft2/day | 802 | 1054 | 1361 | 1697 | 1862 | 1887 | 1872 | 1723 | 1455 | 1186 | 870 | 717 | 1374 | 4 | 1373.8 |
881 | Charlotte, NC | I | Btu/ft2/day | 785 | 1029 | 1385 | 1741 | 1918 | 1996 | 1931 | 1731 | 1475 | 1177 | 866 | 707 | 1395 | 4 | 1395.1 |
882 | Raleigh-Durham, NC | I | Btu/ft2/day | 771 | 1029 | 1359 | 1725 | 1911 | 1969 | 1931 | 1744 | 1435 | 1155 | 853 | 699 | 1382 | 4 | 1381.8 |
883 | Greensboro, NC | I | Btu/ft2/day | 758 | 1023 | 1354 | 1701 | 1875 | 1956 | 1912 | 1717 | 1418 | 1146 | 851 | 692 | 1367 | 4 | 1366.9 |
884 | Wilmington, NC | I | Btu/ft2/day | 811 | 1068 | 1426 | 1808 | 1938 | 1942 | 1917 | 1722 | 1405 | 1178 | 910 | 747 | 1406 | 4 | 1406.0 |
885 | Bismarck, ND | I | Btu/ft2/day | 411 | 666 | 1092 | 1523 | 1811 | 1994 | 2092 | 1798 | 1335 | 859 | 488 | 348 | 1201 | 4 | 1201.4 |
886 | Fargo, ND | I | Btu/ft2/day | 383 | 606 | 1023 | 1562 | 1804 | 1914 | 1984 | 1716 | 1261 | 785 | 445 | 313 | 1149 | 4 | 1149.7 |
887 | Minot, ND | I | Btu/ft2/day | 380 | 628 | 1069 | 1537 | 1781 | 1928 | 2042 | 1735 | 1249 | 793 | 433 | 299 | 1156 | 4 | 1156.2 |
888 | Williston, ND | I | Btu/ft2/day | 369 | 634 | 1067 | 1545 | 1838 | 2010 | 2154 | 1817 | 1312 | 813 | 445 | 311 | 1193 | 4 | 1192.9 |
889 | Akron, OH | I | Btu/ft2/day | 490 | 720 | 1075 | 1421 | 1683 | 1840 | 1859 | 1645 | 1327 | 892 | 538 | 432 | 1160 | 4 | 1160.2 |
890 | Cleveland, OH | I | Btu/ft2/day | 462 | 689 | 1067 | 1430 | 1756 | 1944 | 1923 | 1672 | 1335 | 851 | 511 | 380 | 1168 | 4 | 1168.3 |
891 | Columbus_OH, OH | I | Btu/ft2/day | 527 | 743 | 1080 | 1472 | 1716 | 1889 | 1866 | 1692 | 1388 | 971 | 601 | 456 | 1200 | 4 | 1200.1 |
892 | Dayton, OH | I | Btu/ft2/day | 517 | 759 | 1122 | 1479 | 1747 | 1925 | 1936 | 1738 | 1409 | 993 | 607 | 456 | 1224 | 4 | 1224.0 |
893 | Mansfield, OH | I | Btu/ft2/day | 492 | 700 | 1071 | 1438 | 1709 | 1882 | 1904 | 1643 | 1329 | 918 | 553 | 423 | 1172 | 4 | 1171.8 |
894 | Toledo, OH | I | Btu/ft2/day | 485 | 754 | 1125 | 1446 | 1747 | 1939 | 1938 | 1656 | 1360 | 912 | 537 | 408 | 1192 | 4 | 1192.3 |
895 | Youngstown, OH | I | Btu/ft2/day | 476 | 714 | 1070 | 1410 | 1680 | 1842 | 1839 | 1631 | 1295 | 859 | 520 | 423 | 1147 | 4 | 1146.6 |
896 | Oklahoma City, OK | I | Btu/ft2/day | 831 | 1090 | 1389 | 1757 | 1898 | 2111 | 2215 | 1982 | 1600 | 1235 | 889 | 751 | 1479 | 4 | 1479.0 |
897 | Tulsa, OK | I | Btu/ft2/day | 748 | 1023 | 1320 | 1671 | 1822 | 2027 | 2152 | 1938 | 1523 | 1166 | 816 | 682 | 1407 | 4 | 1407.3 |
898 | Astoria, OR | I | Btu/ft2/day | 343 | 600 | 877 | 1252 | 1537 | 1627 | 1708 | 1492 | 1196 | 728 | 391 | 302 | 1005 | 4 | 1004.4 |
899 | Burns, OR | I | Btu/ft2/day | 475 | 707 | 1195 | 1606 | 2000 | 2285 | 2459 | 2155 | 1691 | 1098 | 573 | 384 | 1386 | 4 | 1385.7 |
900 | Eugene, OR | I | Btu/ft2/day | 396 | 673 | 998 | 1386 | 1739 | 1961 | 2238 | 1960 | 1491 | 839 | 449 | 322 | 1204 | 4 | 1204.3 |
901 | Medford, OR | I | Btu/ft2/day | 502 | 774 | 1143 | 1490 | 1917 | 2257 | 2415 | 2117 | 1649 | 1051 | 541 | 430 | 1357 | 4 | 1357.2 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
902 | Pendleton, OR | I | Btu/ft2/day | 376 | 678 | 1117 | 1628 | 1970 | 2228 | 2372 | 2058 | 1541 | 960 | 460 | 309 | 1308 | 4 | 1308.1 |
903 | Salem, OR | I | Btu/ft2/day | 370 | 638 | 951 | 1355 | 1703 | 1859 | 2099 | 1846 | 1392 | 807 | 416 | 307 | 1145 | 4 | 1145.3 |
904 | Allentown, PA | I | Btu/ft2/day | 568 | 845 | 1165 | 1495 | 1739 | 1841 | 1869 | 1636 | 1309 | 950 | 614 | 495 | 1210 | 4 | 1210.5 |
905 | Bradford, PA | I | Btu/ft2/day | 483 | 742 | 1056 | 1439 | 1651 | 1781 | 1759 | 1563 | 1218 | 820 | 508 | 412 | 1119 | 4 | 1119.3 |
906 | Erie, PA | I | Btu/ft2/day | 367 | 647 | 994 | 1425 | 1756 | 1946 | 1921 | 1661 | 1281 | 825 | 474 | 327 | 1135 | 4 | 1135.3 |
907 | Middletown, PA | I | Btu/ft2/day | 580 | 840 | 1164 | 1497 | 1754 | 1889 | 1852 | 1639 | 1304 | 967 | 630 | 512 | 1219 | 4 | 1219.0 |
908 | Philadelphia, PA | I | Btu/ft2/day | 611 | 911 | 1190 | 1537 | 1778 | 1917 | 1891 | 1698 | 1357 | 1015 | 678 | 549 | 1261 | 4 | 1261.0 |
909 | Pittsburgh, PA | I | Btu/ft2/day | 520 | 760 | 1080 | 1440 | 1691 | 1846 | 1823 | 1636 | 1306 | 919 | 566 | 459 | 1170 | 4 | 1170.5 |
910 | Scranton, PA | I | Btu/ft2/day | 538 | 789 | 1115 | 1455 | 1710 | 1843 | 1852 | 1616 | 1261 | 888 | 548 | 455 | 1173 | 4 | 1172.5 |
911 | Williamsport, PA | I | Btu/ft2/day | 550 | 803 | 1122 | 1457 | 1714 | 1846 | 1830 | 1603 | 1233 | 884 | 545 | 449 | 1170 | 4 | 1169.7 |
912 | Providence, RI | I | Btu/ft2/day | 579 | 859 | 1150 | 1477 | 1738 | 1847 | 1840 | 1640 | 1301 | 937 | 604 | 501 | 1206 | 4 | 1206.1 |
913 | Charleston, SC | I | Btu/ft2/day | 852 | 1111 | 1471 | 1856 | 1992 | 1943 | 1951 | 1723 | 1438 | 1210 | 972 | 797 | 1443 | 4 | 1443.0 |
914 | Columbia, SC | I | Btu/ft2/day | 824 | 1073 | 1415 | 1781 | 1944 | 1975 | 1949 | 1756 | 1497 | 1206 | 923 | 761 | 1425 | 4 | 1425.3 |
915 | Greer, SC | I | Btu/ft2/day | 812 | 1057 | 1401 | 1767 | 1936 | 1988 | 1945 | 1780 | 1493 | 1196 | 888 | 741 | 1417 | 4 | 1417.0 |
916 | Aberdeen, SD | I | Btu/ft2/day | 435 | 703 | 1115 | 1559 | 1815 | 1996 | 2073 | 1799 | 1358 | 880 | 520 | 372 | 1219 | 4 | 1218.8 |
917 | Huron, SD | I | Btu/ft2/day | 483 | 770 | 1131 | 1556 | 1845 | 2014 | 2094 | 1817 | 1404 | 919 | 562 | 403 | 1250 | 4 | 1249.8 |
918 | Pierre, SD | I | Btu/ft2/day | 506 | 772 | 1135 | 1521 | 1857 | 2054 | 2099 | 1853 | 1428 | 927 | 553 | 421 | 1261 | 4 | 1260.5 |
919 | Rapid City, SD | I | Btu/ft2/day | 599 | 844 | 1212 | 1588 | 1906 | 2092 | 2150 | 1920 | 1505 | 1016 | 619 | 503 | 1329 | 4 | 1329.5 |
920 | Sioux Falls, SD | I | Btu/ft2/day | 507 | 777 | 1169 | 1523 | 1751 | 1979 | 2046 | 1762 | 1393 | 947 | 576 | 442 | 1239 | 4 | 1239.3 |
921 | Bristol, TN | I | Btu/ft2/day | 682 | 901 | 1249 | 1616 | 1853 | 1928 | 1885 | 1780 | 1483 | 1128 | 790 | 611 | 1325 | 4 | 1325.5 |
922 | Chattanooga, TN | I | Btu/ft2/day | 722 | 965 | 1295 | 1662 | 1859 | 1950 | 1915 | 1796 | 1471 | 1170 | 824 | 654 | 1357 | 4 | 1356.9 |
923 | Knoxville, TN | I | Btu/ft2/day | 692 | 933 | 1270 | 1656 | 1877 | 1970 | 1925 | 1808 | 1484 | 1160 | 798 | 625 | 1350 | 4 | 1349.8 |
924 | Memphis, TN | I | Btu/ft2/day | 696 | 939 | 1275 | 1661 | 1860 | 2008 | 1967 | 1832 | 1508 | 1165 | 794 | 626 | 1361 | 4 | 1360.9 |
925 | Nashville, TN | I | Btu/ft2/day | 654 | 896 | 1261 | 1614 | 1798 | 1955 | 1886 | 1778 | 1467 | 1128 | 772 | 583 | 1316 | 4 | 1316.0 |
926 | Abilene, TX | I | Btu/ft2/day | 959 | 1205 | 1557 | 1936 | 2052 | 2245 | 2252 | 2006 | 1701 | 1375 | 1046 | 902 | 1603 | 4 | 1603.0 |
927 | Amarillo, TX | I | Btu/ft2/day | 882 | 1232 | 1607 | 1972 | 2156 | 2357 | 2313 | 2021 | 1748 | 1388 | 1057 | 877 | 1634 | 4 | 1634.2 |
928 | Austin, TX | I | Btu/ft2/day | 868 | 1085 | 1368 | 1699 | 1812 | 2094 | 2135 | 2023 | 1645 | 1313 | 956 | 806 | 1484 | 4 | 1483.7 |
929 | Brownsville, TX | I | Btu/ft2/day | 899 | 1152 | 1425 | 1673 | 1913 | 2051 | 2061 | 1951 | 1616 | 1386 | 1040 | 846 | 1501 | 4 | 1501.1 |
930 | Corpus Christi, TX | I | Btu/ft2/day | 891 | 1113 | 1385 | 1636 | 1850 | 2072 | 2110 | 1975 | 1662 | 1397 | 1040 | 838 | 1497 | 4 | 1497.4 |
931 | Dallas-Fort Worth, TX | I | Btu/ft2/day | 837 | 1089 | 1388 | 1744 | 1860 | 2087 | 2171 | 1981 | 1623 | 1263 | 933 | 795 | 1481 | 4 | 1480.9 |
932 | El Paso, TX | I | Btu/ft2/day | 1125 | 1406 | 1856 | 2259 | 2494 | 2537 | 2276 | 2106 | 1895 | 1574 | 1244 | 1048 | 1818 | 4 | 1818.3 |
933 | Houston, TX | I | Btu/ft2/day | 832 | 1022 | 1333 | 1635 | 1828 | 1915 | 1930 | 1804 | 1567 | 1288 | 930 | 767 | 1404 | 4 | 1404.3 |
934 | Lubbock, TX | I | Btu/ft2/day | 968 | 1252 | 1627 | 2008 | 2166 | 2352 | 2283 | 2060 | 1728 | 1406 | 1081 | 904 | 1653 | 4 | 1652.9 |
935 | Lufkin, TX | I | Btu/ft2/day | 796 | 1027 | 1342 | 1686 | 1856 | 1988 | 2043 | 1915 | 1590 | 1275 | 913 | 747 | 1432 | 4 | 1431.5 |
936 | Midland, TX | I | Btu/ft2/day | 1015 | 1294 | 1695 | 2089 | 2226 | 2365 | 2272 | 2073 | 1776 | 1458 | 1140 | 973 | 1698 | 4 | 1698.0 |
937 | Port Arthur, TX | I | Btu/ft2/day | 824 | 1017 | 1355 | 1646 | 1868 | 1931 | 1918 | 1801 | 1552 | 1300 | 955 | 773 | 1412 | 4 | 1411.7 |
938 | San Angelo, TX | I | Btu/ft2/day | 968 | 1229 | 1591 | 1961 | 2072 | 2236 | 2220 | 2021 | 1711 | 1382 | 1090 | 921 | 1617 | 4 | 1616.8 |
939 | San Antonio, TX | I | Btu/ft2/day | 893 | 1083 | 1377 | 1682 | 1821 | 2059 | 2081 | 1961 | 1640 | 1323 | 985 | 825 | 1477 | 4 | 1477.5 |
940 | Victoria, TX | I | Btu/ft2/day | 849 | 1038 | 1328 | 1597 | 1823 | 2009 | 2029 | 1887 | 1596 | 1328 | 989 | 801 | 1439 | 4 | 1439.5 |
941 | Waco, TX | I | Btu/ft2/day | 864 | 1081 | 1387 | 1732 | 1890 | 2135 | 2198 | 2022 | 1674 | 1302 | 958 | 823 | 1505 | 4 | 1505.5 |
942 | Cedar City, UT | I | Btu/ft2/day | 818 | 1072 | 1548 | 1969 | 2299 | 2534 | 2285 | 2082 | 1827 | 1355 | 944 | 741 | 1623 | 4 | 1622.8 |
943 | Salt Lake City, UT | I | Btu/ft2/day | 596 | 877 | 1348 | 1685 | 2071 | 2336 | 2338 | 2052 | 1689 | 1144 | 700 | 469 | 1442 | 4 | 1442.1 |
944 | Burlington, VT | I | Btu/ft2/day | 474 | 733 | 1046 | 1449 | 1720 | 1874 | 1835 | 1642 | 1239 | 770 | 464 | 377 | 1135 | 4 | 1135.3 |
945 | DC-Dulles, VA | I | Btu/ft2/day | 653 | 939 | 1233 | 1567 | 1771 | 1900 | 1862 | 1684 | 1376 | 1062 | 711 | 590 | 1279 | 4 | 1279.0 |
946 | DC-Reagan, VA | I | Btu/ft2/day | 653 | 934 | 1246 | 1578 | 1767 | 1903 | 1864 | 1712 | 1371 | 1045 | 718 | 587 | 1282 | 4 | 1281.5 |
947 | Lynchburg, VA | I | Btu/ft2/day | 740 | 1006 | 1334 | 1655 | 1855 | 2001 | 1913 | 1758 | 1439 | 1128 | 807 | 662 | 1358 | 4 | 1358.2 |
948 | Norfolk, VA | I | Btu/ft2/day | 723 | 962 | 1312 | 1674 | 1872 | 1989 | 1940 | 1743 | 1406 | 1101 | 807 | 655 | 1349 | 4 | 1348.7 |
949 | Richmond, VA | I | Btu/ft2/day | 723 | 993 | 1305 | 1650 | 1856 | 1986 | 1890 | 1735 | 1415 | 1099 | 798 | 649 | 1341 | 4 | 1341.6 |
950 | Roanoke, VA | I | Btu/ft2/day | 729 | 986 | 1293 | 1611 | 1795 | 1892 | 1860 | 1699 | 1395 | 1104 | 781 | 646 | 1316 | 4 | 1315.9 |
951 | Olympia, WA | I | Btu/ft2/day | 319 | 562 | 866 | 1257 | 1574 | 1721 | 1876 | 1624 | 1257 | 676 | 352 | 264 | 1029 | 4 | 1029.0 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
952 | Quillayute, WA | I | Btu/ft2/day | 304 | 556 | 831 | 1225 | 1520 | 1600 | 1681 | 1469 | 1170 | 653 | 351 | 257 | 968 | 4 | 968.1 |
953 | Seattle, WA | I | Btu/ft2/day | 316 | 595 | 882 | 1329 | 1678 | 1842 | 1951 | 1679 | 1235 | 671 | 356 | 267 | 1067 | 4 | 1066.8 |
954 | Spokane, WA | I | Btu/ft2/day | 345 | 650 | 1060 | 1497 | 1893 | 2071 | 2274 | 1947 | 1430 | 841 | 401 | 283 | 1224 | 4 | 1224.3 |
955 | Stampede Pass, WA | I | Btu/ft2/day | 345 | 595 | 857 | 1281 | 1599 | 1703 | 1946 | 1676 | 1218 | 678 | 366 | 286 | 1046 | 4 | 1045.8 |
956 | Yakima, WA | I | Btu/ft2/day | 399 | 740 | 1187 | 1639 | 1987 | 2252 | 2374 | 2033 | 1537 | 937 | 483 | 315 | 1324 | 4 | 1323.6 |
957 | Beckley, WV | I | Btu/ft2/day | 632 | 847 | 1144 | 1499 | 1680 | 1797 | 1752 | 1643 | 1346 | 1018 | 691 | 538 | 1216 | 4 | 1215.6 |
958 | Charleston, WV | I | Btu/ft2/day | 579 | 814 | 1126 | 1524 | 1737 | 1916 | 1843 | 1721 | 1378 | 1024 | 667 | 512 | 1237 | 4 | 1236.8 |
959 | Elkins, WV | I | Btu/ft2/day | 574 | 794 | 1113 | 1461 | 1619 | 1793 | 1738 | 1611 | 1293 | 972 | 618 | 498 | 1173 | 4 | 1173.7 |
960 | Huntington, WV | I | Btu/ft2/day | 570 | 828 | 1163 | 1545 | 1751 | 1915 | 1856 | 1725 | 1404 | 1045 | 676 | 519 | 1250 | 4 | 1249.8 |
961 | Eau Claire, WI | I | Btu/ft2/day | 485 | 734 | 1116 | 1485 | 1716 | 1866 | 1895 | 1616 | 1234 | 802 | 484 | 377 | 1151 | 4 | 1150.8 |
962 | Green Bay, WI | I | Btu/ft2/day | 426 | 678 | 1103 | 1501 | 1748 | 1923 | 1900 | 1624 | 1274 | 820 | 504 | 373 | 1156 | 4 | 1156.2 |
963 | La Crosse, WI | I | Btu/ft2/day | 507 | 767 | 1131 | 1445 | 1723 | 1887 | 1895 | 1615 | 1260 | 829 | 512 | 397 | 1164 | 4 | 1164.0 |
964 | Madison, WI | I | Btu/ft2/day | 441 | 718 | 1122 | 1478 | 1735 | 1931 | 1911 | 1634 | 1324 | 871 | 541 | 422 | 1177 | 4 | 1177.3 |
965 | Milwaukee, WI | I | Btu/ft2/day | 477 | 755 | 1096 | 1444 | 1729 | 1926 | 1894 | 1612 | 1322 | 873 | 536 | 411 | 1173 | 4 | 1172.9 |
966 | Casper, WY | I | Btu/ft2/day | 601 | 877 | 1259 | 1631 | 1980 | 2243 | 2292 | 1988 | 1552 | 1046 | 650 | 505 | 1385 | 4 | 1385.3 |
967 | Cheyenne, WY | I | Btu/ft2/day | 712 | 975 | 1360 | 1668 | 1919 | 2196 | 2163 | 1883 | 1588 | 1131 | 761 | 609 | 1414 | 4 | 1413.8 |
968 | Lander, WY | I | Btu/ft2/day | 640 | 920 | 1320 | 1658 | 2026 | 2242 | 2256 | 1966 | 1564 | 1086 | 696 | 551 | 1411 | 4 | 1410.4 |
969 | Rock Springs, WY | I | Btu/ft2/day | 654 | 928 | 1342 | 1738 | 2044 | 2307 | 2301 | 2019 | 1673 | 1186 | 716 | 564 | 1456 | 4 | 1456.0 |
970 | Sheridan, WY | I | Btu/ft2/day | 482 | 767 | 1145 | 1509 | 1850 | 2030 | 2152 | 1860 | 1419 | 909 | 569 | 429 | 1260 | 4 | 1260.1 |
971 | Birmingham, AL | PA | lb/in2 | 14.37 | 5 | |||||||||||||
972 | Huntsville, AL | PA | lb/in2 | 14.36 | 5 | |||||||||||||
973 | Mobile, AL | PA | lb/in2 | 14.58 | 5 | |||||||||||||
974 | Montgomery, AL | PA | lb/in2 | 14.59 | 5 | |||||||||||||
975 | Phoenix, AZ | PA | lb/in2 | 14.11 | 5 | |||||||||||||
976 | Prescott, AZ | PA | lb/in2 | 12.24 | 5 | |||||||||||||
977 | Tucson, AZ | PA | lb/in2 | 13.40 | 5 | |||||||||||||
978 | Fort Smith, AR | PA | lb/in2 | 14.46 | 5 | |||||||||||||
979 | Little Rock, AR | PA | lb/in2 | 14.56 | 5 | |||||||||||||
980 | Arcata, CA | PA | lb/in2 | 14.59 | 5 | |||||||||||||
981 | Bakersfield, CA | PA | lb/in2 | 14.43 | 5 | |||||||||||||
982 | Bishop, CA | PA | lb/in2 | 12.68 | 5 | |||||||||||||
983 | Daggett, CA | PA | lb/in2 | 13.71 | 5 | |||||||||||||
984 | Fresno, CA | PA | lb/in2 | 14.52 | 5 | |||||||||||||
985 | Long Beach, CA | PA | lb/in2 | 14.68 | 5 | |||||||||||||
986 | Los Angeles AP, CA | PA | lb/in2 | 14.63 | 5 | |||||||||||||
987 | Redding, CA | PA | lb/in2 | 14.43 | 5 | |||||||||||||
988 | Sacramento, CA | PA | lb/in2 | 14.68 | 5 | |||||||||||||
989 | San Diego, CA | PA | lb/in2 | 14.69 | 5 | |||||||||||||
990 | San Francisco AP, CA | PA | lb/in2 | 14.69 | 5 | |||||||||||||
991 | Santa Barbara, CA | PA | lb/in2 | 14.69 | 5 | |||||||||||||
992 | Santa Maria, CA | PA | lb/in2 | 14.56 | 5 | |||||||||||||
993 | Stockton, CA | PA | lb/in2 | 14.68 | 5 | |||||||||||||
994 | Alamosa, CO | PA | lb/in2 | 11.20 | 5 | |||||||||||||
995 | Colorado Springs, CO | PA | lb/in2 | 11.78 | 5 | |||||||||||||
996 | Denver, CO | PA | lb/in2 | 12.08 | 5 | |||||||||||||
997 | Grand Junction, CO | PA | lb/in2 | 12.34 | 5 | |||||||||||||
998 | Limon, CO | PA | lb/in2 | 12.02 | 5 | |||||||||||||
999 | Pueblo, CO | PA | lb/in2 | 12.40 | 5 | |||||||||||||
1000 | Bridgeport, CT | PA | lb/in2 | 14.69 | 5 |
1001 | Hartford, CT | PA | lb/in2 | 14.61 | 5 | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1002 | Wilmington_DE, DE | PA | lb/in2 | 14.65 | 5 | |||||||||||||
1003 | Daytona Beach, FL | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1004 | Fort Myers, FL | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1005 | Gainesville, FL | PA | lb/in2 | 14.62 | 5 | |||||||||||||
1006 | Jacksonville, FL | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1007 | Key West, FL | PA | lb/in2 | 14.69 | 5 | |||||||||||||
1008 | Miami, FL | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1009 | Orlando, FL | PA | lb/in2 | 14.65 | 5 | |||||||||||||
1010 | Pensacola, FL | PA | lb/in2 | 14.63 | 5 | |||||||||||||
1011 | Tallahassee, FL | PA | lb/in2 | 14.65 | 5 | |||||||||||||
1012 | Tampa, FL | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1013 | Vero Beach, FL | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1014 | West Palm Beach, FL | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1015 | Athens, GA | PA | lb/in2 | 14.27 | 5 | |||||||||||||
1016 | Atlanta, GA | PA | lb/in2 | 14.17 | 5 | |||||||||||||
1017 | Augusta, GA | PA | lb/in2 | 14.62 | 5 | |||||||||||||
1018 | Columbus, GA | PA | lb/in2 | 14.49 | 5 | |||||||||||||
1019 | Macon, GA | PA | lb/in2 | 14.50 | 5 | |||||||||||||
1020 | Savannah, GA | PA | lb/in2 | 14.66 | 5 | |||||||||||||
1021 | Hilo, HI | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1022 | Honolulu, HI | PA | lb/in2 | 14.69 | 5 | |||||||||||||
1023 | Kahului, HI | PA | lb/in2 | 14.66 | 5 | |||||||||||||
1024 | Lihue, HI | PA | lb/in2 | 14.63 | 5 | |||||||||||||
1025 | Boise, ID | PA | lb/in2 | 13.52 | 5 | |||||||||||||
1026 | Lewiston, ID | PA | lb/in2 | 13.95 | 5 | |||||||||||||
1027 | Pocatello, ID | PA | lb/in2 | 12.52 | 5 | |||||||||||||
1028 | Chicago, IL | PA | lb/in2 | 14.34 | 5 | |||||||||||||
1029 | Moline, IL | PA | lb/in2 | 14.39 | 5 | |||||||||||||
1030 | Peoria, IL | PA | lb/in2 | 14.34 | 5 | |||||||||||||
1031 | Rockford, IL | PA | lb/in2 | 14.32 | 5 | |||||||||||||
1032 | Springfield_IL, IL | PA | lb/in2 | 14.39 | 5 | |||||||||||||
1033 | Evansville, IN | PA | lb/in2 | 14.49 | 5 | |||||||||||||
1034 | Fort Wayne, IN | PA | lb/in2 | 14.29 | 5 | |||||||||||||
1035 | Indianapolis, IN | PA | lb/in2 | 14.29 | 5 | |||||||||||||
1036 | South Bend, IN | PA | lb/in2 | 14.29 | 5 | |||||||||||||
1037 | Des Moines, IA | PA | lb/in2 | 14.20 | 5 | |||||||||||||
1038 | Dubuque, IA | PA | lb/in2 | 14.14 | 5 | |||||||||||||
1039 | Mason City, IA | PA | lb/in2 | 14.07 | 5 | |||||||||||||
1040 | Sioux City, IA | PA | lb/in2 | 14.13 | 5 | |||||||||||||
1041 | Waterloo, IA | PA | lb/in2 | 14.24 | 5 | |||||||||||||
1042 | Concordia, KS | PA | lb/in2 | 13.94 | 5 | |||||||||||||
1043 | Dodge City, KS | PA | lb/in2 | 13.39 | 5 | |||||||||||||
1044 | Goodland, KS | PA | lb/in2 | 12.88 | 5 | |||||||||||||
1045 | Russell, KS | PA | lb/in2 | 13.74 | 5 | |||||||||||||
1046 | Topeka, KS | PA | lb/in2 | 14.23 | 5 | |||||||||||||
1047 | Wichita, KS | PA | lb/in2 | 14.01 | 5 | |||||||||||||
1048 | Cincinnati, KY | PA | lb/in2 | 14.24 | 5 | |||||||||||||
1049 | Jackson_KY, KY | PA | lb/in2 | 13.98 | 5 | |||||||||||||
1050 | Lexington, KY | PA | lb/in2 | 14.18 | 5 |
1051 | Louisville, KY | PA | lb/in2 | 14.45 | 5 | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1052 | Paducah, KY | PA | lb/in2 | 14.47 | 5 | |||||||||||||
1053 | Baton Rouge, LA | PA | lb/in2 | 14.66 | 5 | |||||||||||||
1054 | Lake Charles, LA | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1055 | New Orleans, LA | PA | lb/in2 | 14.69 | 5 | |||||||||||||
1056 | Shreveport, LA | PA | lb/in2 | 14.56 | 5 | |||||||||||||
1057 | Bangor, ME | PA | lb/in2 | 14.59 | 5 | |||||||||||||
1058 | Caribou, ME | PA | lb/in2 | 14.36 | 5 | |||||||||||||
1059 | Portland, ME | PA | lb/in2 | 14.66 | 5 | |||||||||||||
1060 | Baltimore , MD | PA | lb/in2 | 14.62 | 5 | |||||||||||||
1061 | Boston, MA | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1062 | Worchester, MA | PA | lb/in2 | 14.18 | 5 | |||||||||||||
1063 | Alpena, MI | PA | lb/in2 | 14.33 | 5 | |||||||||||||
1064 | Detroit Metro_AP, MI | PA | lb/in2 | 14.36 | 5 | |||||||||||||
1065 | Detroit - City, MI | PA | lb/in2 | 14.36 | 5 | |||||||||||||
1066 | Flint, MI | PA | lb/in2 | 14.29 | 5 | |||||||||||||
1067 | Grand Rapids, MI | PA | lb/in2 | 14.27 | 5 | |||||||||||||
1068 | Houghton Lake, MI | PA | lb/in2 | 14.10 | 5 | |||||||||||||
1069 | Lansing, MI | PA | lb/in2 | 14.26 | 5 | |||||||||||||
1070 | Muskegon, MI | PA | lb/in2 | 14.36 | 5 | |||||||||||||
1071 | Sault Ste Marie, MI | PA | lb/in2 | 14.32 | 5 | |||||||||||||
1072 | Traverse City, MI | PA | lb/in2 | 14.37 | 5 | |||||||||||||
1073 | Duluth, MN | PA | lb/in2 | 13.95 | 5 | |||||||||||||
1074 | International Falls, MN | PA | lb/in2 | 14.08 | 5 | |||||||||||||
1075 | Minneapolis-St Paul, MN | PA | lb/in2 | 14.26 | 5 | |||||||||||||
1076 | Rochester_MN, MN | PA | lb/in2 | 14.01 | 5 | |||||||||||||
1077 | St Cloud, MN | PA | lb/in2 | 14.16 | 5 | |||||||||||||
1078 | Jackson, MS | PA | lb/in2 | 14.53 | 5 | |||||||||||||
1079 | Meridian, MS | PA | lb/in2 | 14.53 | 5 | |||||||||||||
1080 | Tupelo, MS | PA | lb/in2 | 14.50 | 5 | |||||||||||||
1081 | Columbia_MO, MO | PA | lb/in2 | 14.23 | 5 | |||||||||||||
1082 | Kansas City, MO | PA | lb/in2 | 14.18 | 5 | |||||||||||||
1083 | Springfield_MO, MO | PA | lb/in2 | 14.04 | 5 | |||||||||||||
1084 | St Louis - Lambert, MO | PA | lb/in2 | 14.39 | 5 | |||||||||||||
1085 | St Louis - Spirit, MO | PA | lb/in2 | 14.45 | 5 | |||||||||||||
1086 | Billings, MT | PA | lb/in2 | 12.92 | 5 | |||||||||||||
1087 | Glasgow, MT | PA | lb/in2 | 13.53 | 5 | |||||||||||||
1088 | Great Falls, MT | PA | lb/in2 | 12.88 | 5 | |||||||||||||
1089 | Harve City, MT | PA | lb/in2 | 13.39 | 5 | |||||||||||||
1090 | Helena, MT | PA | lb/in2 | 12.79 | 5 | |||||||||||||
1091 | Kalispell, MT | PA | lb/in2 | 13.20 | 5 | |||||||||||||
1092 | Missoula, MT | PA | lb/in2 | 13.10 | 5 | |||||||||||||
1093 | Grand Island, NE | PA | lb/in2 | 13.75 | 5 | |||||||||||||
1094 | Lincoln, NE | PA | lb/in2 | 14.08 | 5 | |||||||||||||
1095 | Norfolk_NE, NE | PA | lb/in2 | 13.89 | 5 | |||||||||||||
1096 | North Platte, NE | PA | lb/in2 | 13.29 | 5 | |||||||||||||
1097 | Omaha, NE | PA | lb/in2 | 14.18 | 5 | |||||||||||||
1098 | Scottsbluff, NE | PA | lb/in2 | 12.75 | 5 | |||||||||||||
1099 | Valentine, NE | PA | lb/in2 | 13.39 | 5 | |||||||||||||
1100 | Ely, NV | PA | lb/in2 | 11.72 | 5 |
1101 | Las Vegas, NV | PA | lb/in2 | 13.60 | 5 | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1102 | Lovelock, NV | PA | lb/in2 | 12.76 | 5 | |||||||||||||
1103 | Mercury, NV | PA | lb/in2 | 13.16 | 5 | |||||||||||||
1104 | Reno, NV | PA | lb/in2 | 12.53 | 5 | |||||||||||||
1105 | Tonopah, NV | PA | lb/in2 | 12.08 | 5 | |||||||||||||
1106 | Winnemucca, NV | PA | lb/in2 | 12.57 | 5 | |||||||||||||
1107 | Concord, NH | PA | lb/in2 | 14.50 | 5 | |||||||||||||
1108 | Atlantic City, NJ | PA | lb/in2 | 14.66 | 5 | |||||||||||||
1109 | Newark, NJ | PA | lb/in2 | 14.69 | 5 | |||||||||||||
1110 | Albuquerque, NM | PA | lb/in2 | 12.13 | 5 | |||||||||||||
1111 | Gallup, NM | PA | lb/in2 | 11.63 | 5 | |||||||||||||
1112 | Roswell, NM | PA | lb/in2 | 12.88 | 5 | |||||||||||||
1113 | Albany, NY | PA | lb/in2 | 14.55 | 5 | |||||||||||||
1114 | Binghamton, NY | PA | lb/in2 | 13.87 | 5 | |||||||||||||
1115 | Buffalo, NY | PA | lb/in2 | 14.33 | 5 | |||||||||||||
1116 | Long Island, NY | PA | lb/in2 | 14.65 | 5 | |||||||||||||
1117 | Massena, NY | PA | lb/in2 | 14.58 | 5 | |||||||||||||
1118 | New York-LaGuardia, NY | PA | lb/in2 | 14.69 | 5 | |||||||||||||
1119 | New York-Kennedy, NY | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1120 | Rochester, NY | PA | lb/in2 | 14.37 | 5 | |||||||||||||
1121 | Syracuse, NY | PA | lb/in2 | 14.47 | 5 | |||||||||||||
1122 | Asheville, NC | PA | lb/in2 | 13.60 | 5 | |||||||||||||
1123 | Charlotte, NC | PA | lb/in2 | 14.32 | 5 | |||||||||||||
1124 | Raleigh-Durham, NC | PA | lb/in2 | 14.47 | 5 | |||||||||||||
1125 | Greensboro, NC | PA | lb/in2 | 14.23 | 5 | |||||||||||||
1126 | Wilmington, NC | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1127 | Bismarck, ND | PA | lb/in2 | 13.85 | 5 | |||||||||||||
1128 | Fargo, ND | PA | lb/in2 | 14.23 | 5 | |||||||||||||
1129 | Minot, ND | PA | lb/in2 | 13.81 | 5 | |||||||||||||
1130 | Williston, ND | PA | lb/in2 | 13.72 | 5 | |||||||||||||
1131 | Akron, OH | PA | lb/in2 | 14.07 | 5 | |||||||||||||
1132 | Cleveland, OH | PA | lb/in2 | 14.29 | 5 | |||||||||||||
1133 | Columbus_OH, OH | PA | lb/in2 | 14.27 | 5 | |||||||||||||
1134 | Dayton, OH | PA | lb/in2 | 14.17 | 5 | |||||||||||||
1135 | Mansfield, OH | PA | lb/in2 | 14.03 | 5 | |||||||||||||
1136 | Toledo, OH | PA | lb/in2 | 14.34 | 5 | |||||||||||||
1137 | Youngstown, OH | PA | lb/in2 | 14.08 | 5 | |||||||||||||
1138 | Oklahoma City, OK | PA | lb/in2 | 14.01 | 5 | |||||||||||||
1139 | Tulsa, OK | PA | lb/in2 | 14.36 | 5 | |||||||||||||
1140 | Astoria, OR | PA | lb/in2 | 14.69 | 5 | |||||||||||||
1141 | Burns, OR | PA | lb/in2 | 12.63 | 5 | |||||||||||||
1142 | Eugene, OR | PA | lb/in2 | 14.50 | 5 | |||||||||||||
1143 | Medford, OR | PA | lb/in2 | 13.69 | 5 | |||||||||||||
1144 | Pendleton, OR | PA | lb/in2 | 13.92 | 5 | |||||||||||||
1145 | Salem, OR | PA | lb/in2 | 14.59 | 5 | |||||||||||||
1146 | Allentown, PA | PA | lb/in2 | 14.49 | 5 | |||||||||||||
1147 | Bradford, PA | PA | lb/in2 | 13.62 | 5 | |||||||||||||
1148 | Erie, PA | PA | lb/in2 | 14.32 | 5 | |||||||||||||
1149 | Middletown, PA | PA | lb/in2 | 14.53 | 5 | |||||||||||||
1150 | Philadelphia, PA | PA | lb/in2 | 14.69 | 5 |
1151 | Pittsburgh, PA | PA | lb/in2 | 14.10 | 5 | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1152 | Scranton, PA | PA | lb/in2 | 14.21 | 5 | |||||||||||||
1153 | Williamsport, PA | PA | lb/in2 | 14.42 | 5 | |||||||||||||
1154 | Providence, RI | PA | lb/in2 | 14.66 | 5 | |||||||||||||
1155 | Charleston, SC | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1156 | Columbia, SC | PA | lb/in2 | 14.58 | 5 | |||||||||||||
1157 | Greer, SC | PA | lb/in2 | 14.20 | 5 | |||||||||||||
1158 | Aberdeen, SD | PA | lb/in2 | 14.01 | 5 | |||||||||||||
1159 | Huron, SD | PA | lb/in2 | 14.03 | 5 | |||||||||||||
1160 | Pierre, SD | PA | lb/in2 | 13.81 | 5 | |||||||||||||
1161 | Rapid City, SD | PA | lb/in2 | 13.11 | 5 | |||||||||||||
1162 | Sioux Falls, SD | PA | lb/in2 | 13.95 | 5 | |||||||||||||
1163 | Bristol, TN | PA | lb/in2 | 13.92 | 5 | |||||||||||||
1164 | Chattanooga, TN | PA | lb/in2 | 14.34 | 5 | |||||||||||||
1165 | Knoxville, TN | PA | lb/in2 | 14.18 | 5 | |||||||||||||
1166 | Memphis, TN | PA | lb/in2 | 14.55 | 5 | |||||||||||||
1167 | Nashville, TN | PA | lb/in2 | 14.39 | 5 | |||||||||||||
1168 | Abilene, TX | PA | lb/in2 | 13.79 | 5 | |||||||||||||
1169 | Amarillo, TX | PA | lb/in2 | 12.95 | 5 | |||||||||||||
1170 | Austin, TX | PA | lb/in2 | 14.33 | 5 | |||||||||||||
1171 | Brownsville, TX | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1172 | Corpus Christi, TX | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1173 | Dallas-Fort Worth, TX | PA | lb/in2 | 14.40 | 5 | |||||||||||||
1174 | El Paso, TX | PA | lb/in2 | 12.76 | 5 | |||||||||||||
1175 | Houston, TX | PA | lb/in2 | 14.65 | 5 | |||||||||||||
1176 | Lubbock, TX | PA | lb/in2 | 13.07 | 5 | |||||||||||||
1177 | Lufkin, TX | PA | lb/in2 | 14.55 | 5 | |||||||||||||
1178 | Midland, TX | PA | lb/in2 | 13.26 | 5 | |||||||||||||
1179 | Port Arthur, TX | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1180 | San Angelo, TX | PA | lb/in2 | 13.71 | 5 | |||||||||||||
1181 | San Antonio, TX | PA | lb/in2 | 14.27 | 5 | |||||||||||||
1182 | Victoria, TX | PA | lb/in2 | 14.63 | 5 | |||||||||||||
1183 | Waco, TX | PA | lb/in2 | 14.43 | 5 | |||||||||||||
1184 | Cedar City, UT | PA | lb/in2 | 12.01 | 5 | |||||||||||||
1185 | Salt Lake City, UT | PA | lb/in2 | 12.62 | 5 | |||||||||||||
1186 | Burlington, VT | PA | lb/in2 | 14.52 | 5 | |||||||||||||
1187 | DC-Dulles, VA | PA | lb/in2 | 14.55 | 5 | |||||||||||||
1188 | DC-Reagan, VA | PA | lb/in2 | 14.69 | 5 | |||||||||||||
1189 | Lynchburg, VA | PA | lb/in2 | 14.20 | 5 | |||||||||||||
1190 | Norfolk, VA | PA | lb/in2 | 14.68 | 5 | |||||||||||||
1191 | Richmond, VA | PA | lb/in2 | 14.61 | 5 | |||||||||||||
1192 | Roanoke, VA | PA | lb/in2 | 14.10 | 5 | |||||||||||||
1193 | Olympia, WA | PA | lb/in2 | 14.58 | 5 | |||||||||||||
1194 | Quillayute, WA | PA | lb/in2 | 14.59 | 5 | |||||||||||||
1195 | Seattle, WA | PA | lb/in2 | 14.47 | 5 | |||||||||||||
1196 | Spokane, WA | PA | lb/in2 | 13.40 | 5 | |||||||||||||
1197 | Stampede Pass, WA | PA | lb/in2 | 12.73 | 5 | |||||||||||||
1198 | Yakima, WA | PA | lb/in2 | 14.14 | 5 | |||||||||||||
1199 | Beckley, WV | PA | lb/in2 | 13.42 | 5 | |||||||||||||
1200 | Charleston, WV | PA | lb/in2 | 14.16 | 5 |
1201 | Elkins, WV | PA | lb/in2 | 13.69 | 5 | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1202 | Huntington, WV | PA | lb/in2 | 14.26 | 5 | |||||||||||||
1203 | Eau Claire, WI | PA | lb/in2 | 14.23 | 5 | |||||||||||||
1204 | Green Bay, WI | PA | lb/in2 | 14.33 | 5 | |||||||||||||
1205 | La Crosse, WI | PA | lb/in2 | 14.36 | 5 | |||||||||||||
1206 | Madison, WI | PA | lb/in2 | 14.24 | 5 | |||||||||||||
1207 | Milwaukee, WI | PA | lb/in2 | 14.34 | 5 | |||||||||||||
1208 | Casper, WY | PA | lb/in2 | 12.13 | 5 | |||||||||||||
1209 | Cheyenne, WY | PA | lb/in2 | 11.78 | 5 | |||||||||||||
1210 | Lander, WY | PA | lb/in2 | 12.02 | 5 | |||||||||||||
1211 | Rock Springs, WY | PA | lb/in2 | 13.05 | 5 | |||||||||||||
1212 | Sheridan, WY | PA | lb/in2 | 12.73 | 5 |
A | B | C | D | E | F | |
---|---|---|---|---|---|---|
1 | Cascade Steel Rolling Mills CAO ATEI | |||||
2 | Alloy Material Handling - Derivation of Overall Control Efficiency for a Three-Side Enclosure and Water Sprays During Truck Dump | |||||
3 | ||||||
4 | ||||||
5 | ||||||
6 | ||||||
7 | ||||||
8 | ||||||
9 | ||||||
10 | ||||||
11 | ||||||
12 | Control Efficiency by 3-sided Enclosure* | |||||
13 | *As provided by Nebraska Department of Environmental Quality | |||||
14 | See Attachment A to DEQ letter to CSRM 9/29/23 | |||||
15 | ||||||
16 | Control Efficiency (%) | |||||
17 | PM | PM10 | PM2.5 | |||
18 | 3-sided Enclosure Grain Receiving | 70% | 63% | 49% | ||
19 | ||||||
20 | ||||||
21 | Drop Equation Particle Size Multipliers** | |||||
22 | ||||||
23 | Particle Size Multiplier | |||||
24 | PM10 | PM5 | PM2.5 | |||
25 | **AP 42, 13.2.4-4 | 0.35 | 0.20 | 0.053 | ||
26 | Note: PM5 fraction assumed to also estimate PM6 fraction | |||||
27 | ||||||
28 | Control Efficiency of Water Sprays*** | |||||
29 | ||||||
30 | Control Efficiency (%) | |||||
31 | PM10 - PM6 | PM6 - PM2.5 | PM2.5 - 0 | |||
32 | ***AP 42, Appendix B, Table B.2-3 | 90% | 65% | 40% | ||
33 | ||||||
34 | ||||||
35 | Mass Unit of PM10 Calculated by Drop Equation | 1 | ||||
36 | PM6 Fraction of PM10 as Calculated by Drop Equation | 0.57 | ||||
37 | PM2.5 Fraction of PM10 as Calculated by Drop Equation | 0.15 | ||||
38 | ||||||
39 | Calculate Overall PM10 Control Efficiency for Water Spray | 72% | ||||
40 | ||||||
41 | Apply Water Spray PM10 Control to PM10 Emissions | |||||
42 | After Application of 3-sided Enclosure Control | 89.6% | Overall Control Efficiency of 3-sided Enclosure + Water Sprays |