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5 | Please save this file to your own computer before filling out this reporting form. | ||||||||||||||||
6 | Before completing this form please review the DEQ website for the most recent versions and instructions for this form: | ||||||||||||||||
7 | https://www.oregon.gov/deq/aq/aqPermits/Pages/CAO-reg.aspx | ||||||||||||||||
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9 | All DEQ and Lane Regional Air Protection Agency permitted facilities, or facilities applying for Air Quality permits, will need to complete and submit this form as the first step in the Cleaner Air Oregon Air Toxics Program. | ||||||||||||||||
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12 | Please fill out the following worksheets to complete an air toxic emissions inventory for your facility: | ||||||||||||||||
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14 | Worksheet 1 | Facility Information | Record facility name and address, contact person, source number, and number of employees in the boxes. | ||||||||||||||
15 | Worksheet 2 | Emission Units & Activities | Record all Toxics Emissions Units and activities that emit air toxics included in the list of associated Air Toxic contaminants. Provide both annual and maximum daily production and process rates, emission type, and control devices/efficiency for each emissions unit. | ||||||||||||||
16 | Worksheet 3 | Pollutant Emissions - EF | Record all Air Toxic pollutants CAS/DEQ ID and chemical names, pollutant-specifc emissions factors and control efficiencies, and calculated emissions. | ||||||||||||||
17 | Worksheet 4 | Material Balance Activities | Record all emission units and activities that emit air toxics included in the list of associated air toxic contaminants. Provide annual and maximum daily material usage and waste activities, material names and manufacturer, and emission type. | ||||||||||||||
18 | Worksheet 5 | Pollutant Emissions - MB | Record all Air Toxic pollutants CAS/DEQ ID and chemical names associated with recorded materials, pollutant-specifc percent composition and control efficiencies, and calculated emissions. | ||||||||||||||
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20 | Note: Emissions information will be entered on Worksheets 2&3 for EF-based emissions, and Worksheets 4&5 for Material Balance-based emissions. | ||||||||||||||||
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22 | |||||||||||||||||
23 | What you need (Existing Sources): | ||||||||||||||||
24 | 1. Current Permit and Permit Review Report | ||||||||||||||||
25 | 2. Emission Detail Sheets | ||||||||||||||||
26 | 3. Safety Data Sheets, Certified Product Data Sheets, Environmental Data Sheets, or any lab data for each material used. | ||||||||||||||||
27 | 4. Most Recent Annual Report[s] | ||||||||||||||||
28 | 5. Any other documentation needed to help fulfill request - e.g. emissions factor references, source test review reports, etc. | ||||||||||||||||
29 | |||||||||||||||||
30 | Worksheet 1: Facility Information | ||||||||||||||||
31 | |||||||||||||||||
32 | Please provide the facility name and address, contact person, and source number which is the first 6 digits of the permit number (existing sources) in the boxes provided. | ||||||||||||||||
33 | |||||||||||||||||
34 | Worksheet 2: Emission Units & Activities | ||||||||||||||||
35 | |||||||||||||||||
36 | 1. List all Toxics Emissions Units (TEUs), Activity IDs and descriptions, and Control Devices for all emission units or activities that emit air toxics at the facility. Use emission unit or activity ID from permits and create new IDs as necessary. For Material Balance activities proceed to Worksheet 4. | ||||||||||||||||
37 | 2. Record emissions type (i.e. Stack or Fugitive) and corresponding emission type ID. | ||||||||||||||||
38 | 3. Describe activity units (e.g. MM ft3, gallons, tons, MMBTU, pounds, etc.) and type (e.g. natural gas, wood, metal poured, etc.) for each specific emissions unit/activty. | ||||||||||||||||
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40 | 4. Record quantities, units of measurements, and types of Annual and Maximum Daily activity/production/process rates for each TEU/Activity for "Actual", "Requested PTE", and "Capacity" production scenarios. | ||||||||||||||||
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42 | Note: "Actual" is based on the reporting year (existing sources) or an estimate
of typical production (new sources); "Requested PTE" is the level requested by the source, which may be |
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43 | higher than "Actual" production values; and "Capacity" is based on the 100% uptime and production for the facility - this may be used for de Minimus screening. | ||||||||||||||||
44 | |||||||||||||||||
45 | Worksheet 3: Pollutant Emissions - EF | ||||||||||||||||
46 | |||||||||||||||||
47 | 1. Provide a row for each Air Toxic emitted from a specified TEU. Either select a CAS number or DEQ ID from the dropdown list or cut and paste both the CAS/DEQ ID and Chemical Name for each pollutant. | ||||||||||||||||
48 | |||||||||||||||||
49 | 2. Provide the Total Combined Control Efficiency for each pollutant from the specificied TEU - this value may be composed of multiple capture/transfer efficiencies and destruction/removal efficiencies. Note: These control efficiencies may differ for different pollutants from the same TEU. | ||||||||||||||||
50 |
51 | 3. Provide pollutant-specifc Emissions Factors (EF) for both Annual and Maximum Daily emissions (if different). Also provide the units for the EF values in pounds/activity units. Provide EF references (AP-42, WebFire, Source Tests, etc.) and any related notes (e.g. Control Efficiency references). | ||||||||||||||||
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52 | |||||||||||||||||
53 | 4. Calculate emissions using the following formula (Note: see the example calculations in red): | ||||||||||||||||
54 | E = (P)*(EF)*(1-CE) | ||||||||||||||||
55 | E | = | Annual or Maximum Daily air toxics emissions [Pounds/(Year|Day)] | ||||||||||||||
56 | P | = | Production or Process Usage Rate [Activity Units/(Year|Day)] | ||||||||||||||
57 | EF | = | Pollutant Emission Factor [Pounds/ Activity Unit] | ||||||||||||||
58 | CE | = | Overall Control Efficiency expressed as a decimal. | ||||||||||||||
59 | |||||||||||||||||
60 | Worksheet 4: Material Balance Activities | ||||||||||||||||
61 | |||||||||||||||||
62 | 1. List all TEU IDs and TEU/Activity descriptions with emissions from material balance activities. For Emission Factor-based activities proceed to Worksheet 2. | ||||||||||||||||
63 | |||||||||||||||||
64 | 2. List all materials (e.g. paints, coating materials, thinners, solvents, etc.) containing pollutants from the provided Air Toxics list - include product name and manufacturer for each specified TEU/Activity. | ||||||||||||||||
65 | |||||||||||||||||
66 | 3. Record emissions type (i.e. Stack or Fugitive) and corresponding emission type ID. | ||||||||||||||||
67 | |||||||||||||||||
68 | 4. Record "Material Usage" quantities in pounds for both annual and maximum daily activity/production/process rates for each TEU/activity for "Actual", "Requested PTE", and "Capacity" production scenarios. | ||||||||||||||||
69 | |||||||||||||||||
70 | Note: "Actual" is based on the reporting year (existing sources) or an estimate
of typical production (new sources); "Requested PTE" is the level requested by the source, which may be |
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71 | higher than "Actual" production values; and "Capacity" is based on the 100% uptime and production for the facility - this may be used for de Minimus screening. | ||||||||||||||||
72 | |||||||||||||||||
73 | 5. Record "Material Wasted" quantities in pounds for both annual and maximum daily activity/production/process rates for each TEU/activity for "Actual", "Requested PTE", and "Capacity" production scenarios. | ||||||||||||||||
74 | |||||||||||||||||
75 | Note: "Material Wasted" may consist of waste collected and shipped off-site, materials that drain as liquid to a collection/treatment system, material that may be retained in the product, | ||||||||||||||||
76 | or any material that should beexcluded from emissions calculations. | ||||||||||||||||
77 | |||||||||||||||||
78 | Worksheet 5: Pollutant Emissions - MB | ||||||||||||||||
79 | |||||||||||||||||
80 | 1. Provide a row for each Air Toxic emitted from a specified material and its associated TEU/Activity. Either select a CAS number or DEQ ID from the dropdown list or cut and paste both the CAS/DEQ ID and Chemical Name for each pollutant. | ||||||||||||||||
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82 | 2. Provide the Total Combined Control Efficiency for each pollutant contained in a specified material - this value may be composed of multiple capture/transfer efficiencies and destruction/removal efficiencies. Note: These control efficiencies may differ for different pollutants from the same material and TEU/Activity. | ||||||||||||||||
83 | |||||||||||||||||
84 | 3. Provide the percent composition for the Air Toxic in the specified material as provided by the manufacturer supplied data (e.g. SDS). | ||||||||||||||||
85 | Note: | ||||||||||||||||
86 | If percent weight is a range, use the mid-point of the range. (e.g., if range is 10-50% use 30%, or if the SDS lists < 5% use 2.5%) | ||||||||||||||||
87 | |||||||||||||||||
88 | 4. Provide any notes or references relevant to the pollutant emissions - e.g. technical references, details of control efficiencies, etc. | ||||||||||||||||
89 | |||||||||||||||||
90 | 5. Calculate emissions using the following formula (Note: see the example calculations in red): | ||||||||||||||||
91 | E = [(CX–WX)*KX]*(1–CE) | ||||||||||||||||
92 | E | = | Annual or Maximum Daily air toxic emissions [Pounds/(Year|Day)] | ||||||||||||||
93 | X | = | Subscript X represents a specific material | ||||||||||||||
94 | C | = | Material usage [Pounds/(Year|Day)] | ||||||||||||||
95 | W | = | Material waste [Pounds/(Year|Day)] | ||||||||||||||
96 | K | = | Percent weight air toxic pollutant concentration expressed as a decimal | ||||||||||||||
97 | CE | = | Control efficiency expressed as decimal |
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5 | Facility Information | ||
6 | Facility Name | Hollingsworth & Vose Fiber Company | |
7 | Facility Address | 1551 SE Crystal Lake Drive (Plant 1); 1220 SE Crystal Lake Drive (Plant 2) | |
8 | City | Corvallis | |
9 | Zip Code | 97339 | |
10 |
Source Number (for existing sources) |
02-2173 | |
11 | Facility Contact | Anita Ragan | |
12 | Phone Number | (541) 738-5382 |
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10 | Emissions Unit Information |
Stack/Fugitive Information |
Activity Information | ||||||||||
11 | Toxics Emissions Unit ID | Unit Description | Control Device[s] |
Emission Type (e.g. Point or Fugitive) |
Stack or Fugitive ID | Units (e.g. hours operation, tons material, gallons) |
Description/Type | Annual - Chronic [units/year] | Max Daily - Acute [units/day] | ||||
12 | Actual |
Requested PTE |
Capacity | Actual |
Requested PTE |
Capacity | |||||||
13 | TEU-1 | Widget Maker 1 (EXAMPLE) | Widget Waste RCO | Point | ST-1 | tons | Input Material X | 100 | 140 | 200 | 0.3 | 0.5 | 0.8 |
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15 | RF | Rotary Fine Fiber Production | Ceramic Filtration Unit (CFU) | Point | multiple | tons | glass fiber | 1,199 | 7,805 | -- | 5.7 | 21.38 | -- |
16 | RC | Rotary Coarse and Ultra Rotary Coarse Fiber Production | Ceramic Filtration Unit (CFU) | Point | multiple | tons | glass fiber | 6,006 | 0 | -- | 47.7 | 0.0 | -- |
17 | FB | Flameblown Production | Ceramic Filtration Unit (CFU) | Point | multiple | tons | glass fiber | 594 | 788 | -- | 2.16 | 2.16 | -- |
18 | GM | Glass Melt | Ceramic Filtration Unit (CFU) | Point | CFU-113 | tons | glass fiber | 8,078 | 23,652 | -- | 64.8 | 64.8 | -- |
19 | CFU_RF | Ceramic Filtration Unit Particulate Emissions - Rotary Fine | none | Point | multiple | tons | glass fiber | 1,199 | 7,805 | -- | 5.7 | 21.4 | -- |
20 | CFU_RC | Ceramic Filtration Unit Particulate Emissions - Rotary Coarse | none | Point | multiple | tons | glass fiber | 6,006 | 0 | -- | 47.7 | 0.0 | -- |
21 | CFU_FB | Ceramic Filtration Unit Particulate Emissions - Flameblown | none | Point | multiple | tons | glass fiber | 594 | 788 | -- | 2.16 | 2.2 | -- |
22 | CFU_GM | Ceramic Filtration Unit Particulate Emissions - Glass Melt | none | Point | CFU-113 | tons | glass fiber | 8,078 | 23,652 | -- | 64.8 | 64.8 | -- |
23 | SSF_RF | Ceramic Filtration Unit Super Sack Filling - Rotary Fine | Fabric Filtration | Point | multiple | tons | waste generation | 3,111 | 5,000 | -- | 12 | 29.6 | -- |
24 | SSF_RC | Ceramic Filtration Unit Super Sack Filling - Rotary Coarse | Fabric Filtration | Point | multiple | tons | waste generation | 3,111 | 5,000 | -- | 12 | 29.6 | -- |
25 | SSF_FB | Ceramic Filtration Unit Super Sack Filling - Flameblown | Fabric Filtration | Point | multiple | tons | waste generation | 3,111 | 5,000 | -- | 12 | 29.6 | -- |
26 | SSF_GM | Ceramic Filtration Unit Super Sack Filling - Glass Melt | Fabric Filtration | Point | SSF13 | tons | waste generation | 3,111 | 5,000 | -- | 12 | 29.6 | -- |
27 | BALING | Glass Plant Baling | none | Fugitive | multiple | tons | glass fiber | 7,799 | 29,827 | -- | 55.56 | 81.8 | -- |
28 | SILO1 | Bulking Agent Storage Silo, Glass Plant 1 | Fabric Filtration | Point | SILO1 | hrs | filling hours of operation | 52.0 | 200.0 | -- | 1.50 | 1.50 | -- |
29 | SILO2 | Bulking Agent Storage Silo, Glass Plant 2 | Fabric Filtration | Point | SILO2 | hrs | filling hours of operation | 65.0 | 200.0 | -- | 1.50 | 1.50 | -- |
30 | RMH_BA | Raw Material Handling, Barium Carbonate | Fabric Filtration | Point | multiple | tons | barium carbonate | 257 | 1459 | -- | 0.84 | 4.80 | -- |
31 | RMH_ZN | Raw Material Handling, Zinc Oxide | Fabric Filtration | Point | multiple | tons | zinc oxide | 162 | 919 | -- | 0.53 | 3.02 | -- |
32 | |||||||||||||
33 | RMH_F | Raw Material Handling, Fluorspar | Fabric Filtration | Point | multiple | tons | fluorspar | -- | -- | ||||
34 | RMH_S | Raw Material Handling, Sand | Fabric Filtration | Point | multiple | tons | sand | -- | -- | ||||
35 | RMH_D | Raw Material Handling, Dolomite | Fabric Filtration | Point | multiple | tons | dolomite | -- | -- | ||||
36 | RMH_L | Raw Material Handling, Limestone | Fabric Filtration | Point | multiple | tons | limestone | -- | -- | ||||
37 | RMH_N | Raw Material Handling, Nepheline Syenite | Fabric Filtration | Point | multiple | tons | nepheline syenite | -- | -- | ||||
38 | |||||||||||||
39 | RMH_OFF | Raw Material Handling Off Specification | Fabric Filtration | Point | BHBH | tons | raw materials | 12 | 12 | -- | 1.00 | 1.00 | -- |
40 | PAINT | Shipping and Receiving Paint Usage | none | Fugitive | multiple | lb | paint usage | 342 | 936 | -- | 1.00 | 3.00 | -- |
41 | EGEN1 | Emergency Generator, Line 1 | none | Point | EGEN1 | gal | diesel usage | 164 | 2,340 | -- | 46.8 | 46.8 | -- |
42 | EGEN2 | Emergency Generator, Line 2 | none | Point | EGEN2 | gal | diesel usage | 132 | 1,650 | -- | 33.0 | 33.0 | -- |
43 | CT1_2 | Cooling Tower, Lines 1 and 2 | none | Point | CT1_2 | hrs | hours of operation | 8,760 | 8,760 | -- | 24 | 24 | -- |
44 | CT3 | Cooling Tower, Line 3 | none | Point | CT3 | hrs | hours of operation | 8,760 | 8,760 | -- | 24 | 24 | -- |
45 | CT4 | Cooling Tower, Line 4 | none | Point | CT4 | hrs | hours of operation | 8,760 | 8,760 | -- | 24 | 24 | -- |
46 | NG_GP | Glass Plant Natural Gas Combustion (Excluding Forehearths) | none | Point | multiple | MMscf | natural gas usage | 376 | 982 | -- | 2.37 | 2.68 | -- |
47 | NG_FH | Forehearth Natural Combustion | none | Point | multiple | MMscf | natural gas usage | 15.3 | 38.4 | -- | 0.105 | 0.105 | -- |
48 | NG | Non-Production Natural Combustion | none | Point | multiple | MMscf | natural gas usage | 9.77 | 25.5 | -- | 0.062 | 0.07 | -- |
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9 | Calculated Emissions | ||||||||||||||
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Toxic Emissions Unit ID |
Pollutant Information |
Control Efficiency |
Emission Factor Information | Annual - Chronic [lb/yr] | Max Daily - Acute [lb/day] | |||||||||
11 | EF Values | Units | Reference/Notes | ||||||||||||
12 | CAS or DEQ ID | Chemical Name | Annual - Chronic | Max Daily - Acute | Actual | Requested PTE | Capacity | Actual | Requested PTE | Capacity | |||||
13 | TEU-1 | 61-82-5 | Amitrole | 97.50% | 2.5 | lb/ton | Annual and max daily EF values are the same for this TEU and its pollutants | 6.25 | 8.75 | 12.5 | 0.01875 | 0.03125 | 0.05 | ||
14 | TEU-1 | 7440-38-2 | Arsenic and compounds | 0.00% | 0.1 | lb/ton | The control efficiency does not apply to this pollutant | 10 | 14 | 20 | 0.03 | 0.05 | 0.08 | ||
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16 | RF | 7440-36-0 | Antimony and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
17 | RF | 7440-38-2 | Arsenic and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
18 | RF | 7440-39-3 | Barium and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.06 | 0.41 | -- | 0.00 | 0.00 | -- | ||
19 | RF | 7440-41-7 | Beryllium and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
20 | RF | 7440-43-9 | Cadmium and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
21 | RF | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00 | 0.00 | lb/ton | Conservatively assumes 100 percent of chromium emissions are hexavalent chromium. | 0.02 | 0.14 | -- | 0.00 | 0.00 | -- | ||
22 | RF | 7440-48-4 | Cobalt and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
23 | RF | 7440-50-8 | Copper and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.53 | 3.43 | -- | 0.00 | 0.01 | -- | ||
24 | RF | 7439-92-1 | Lead and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
25 | RF | 7439-96-5 | Manganese and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.10 | 0.68 | -- | 0.00 | 0.00 | -- | ||
26 | RF | 7439-97-6 | Mercury and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.01 | 0.04 | -- | 0.00 | 0.00 | -- | ||
27 | RF | 7440-02-0 | Nickel and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.05 | 0.30 | -- | 0.00 | 0.00 | -- | ||
28 | RF | 504 | Phosphorus and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.87 | 5.66 | -- | 0.00 | 0.02 | -- | ||
29 | RF | 7782-49-2 | Selenium and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
30 | RF | 7440-66-6 | Zinc and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 1.29 | 8.43 | -- | 0.01 | 0.02 | -- | ||
31 | RF | 239 | Fluorides | 0.00 | 0.00 | lb/ton | Summary of 2018 source tests provided by DEQ with draft PSD permit (June 2020). Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. Represents emission factor for total fluorides minus hydrogen fluoride. If difference is less than zero, shown as zero. | -- | -- | -- | -- | -- | -- | ||
32 | RF | 7664-39-3 | Hydrogen fluoride | 0.03 | 0.03 | lb/ton | Summary of 2018 source tests provided by DEQ with draft PSD permit (June 2020). Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 39.27 | 255.61 | -- | 0.19 | 0.70 | -- | ||
33 | RF | 352 | Glasswool fibers | 0.01 | 0.01 | lb/ton | Results of 2022 microscopy analysis indicate that total glass content of CFU emissions is less than 1 percent. Conservatively assume 1 percent of filterable particulate matter as glasswool fiber. Filterable PM emission factor from 2018 source test results. Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 6.11 | 39.81 | -- | 0.03 | 0.11 | -- | ||
34 | RF | 67-64-1 | Acetone | 0.05 | 0.05 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 59.59 | 387.91 | -- | 0.28 | 1.06 | -- | ||
35 | RF | 71-43-2 | Benzene | 0.01 | 0.01 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 11.85 | 77.11 | -- | 0.06 | 0.21 | -- | ||
36 | RF | 50-00-0 | Formaldehyde | 0.78 | 0.78 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 935.22 | 6087.90 | -- | 4.45 | 16.68 | -- | ||
37 | RF | 110-54-3 | Hexane | 0.05 | 0.05 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 58.27 | 379.32 | -- | 0.28 | 1.04 | -- | ||
38 | RF | 74-87-3 | Chloromethane (methyl chloride) | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 4.60 | 29.97 | -- | 0.02 | 0.08 | -- | ||
39 | RF | 78-93-3 | 2-Butanone (methyl ethyl ketone) | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 2.25 | 14.67 | -- | 0.01 | 0.04 | -- | ||
40 | RF | 108-88-3 | Toluene | 0.02 | 0.02 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 28.06 | 182.64 | -- | 0.13 | 0.50 | -- | ||
41 | RC | 7440-36-0 | Antimony and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 0.32 | -- | -- | 0.00 | -- | -- | ||
42 | RC | 7440-38-2 | Arsenic and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | -- | -- | -- | -- | -- | -- | ||
43 | RC | 7440-39-3 | Barium and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 0.20 | -- | -- | 0.00 | -- | -- | ||
44 | RC | 7440-41-7 | Beryllium and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | -- | -- | -- | -- | -- | -- | ||
45 | RC | 7440-43-9 | Cadmium and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 0.21 | -- | -- | 0.00 | -- | -- | ||
46 | RC | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. Conservatively assumes 100 percent of chromium emissions are hexavalent chromium. | 0.19 | -- | -- | 0.00 | -- | -- | ||
47 | RC | 7440-48-4 | Cobalt and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 0.01 | -- | -- | 0.00 | -- | -- | ||
48 | RC | 7440-50-8 | Copper and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 1.14 | -- | -- | 0.01 | -- | -- | ||
49 | RC | 7439-92-1 | Lead and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 1.82 | -- | -- | 0.01 | -- | -- | ||
50 | RC | 7439-96-5 | Manganese and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 0.29 | -- | -- | 0.00 | -- | -- |
51 | RC | 7439-97-6 | Mercury and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 0.02 | -- | -- | 0.00 | -- | -- | ||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
52 | RC | 7440-02-0 | Nickel and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 0.44 | -- | -- | 0.00 | -- | -- | ||
53 | RC | 504 | Phosphorus and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 5.17 | -- | -- | 0.04 | -- | -- | ||
54 | RC | 7782-49-2 | Selenium and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | -- | -- | -- | -- | -- | -- | ||
55 | RC | 7440-66-6 | Zinc and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 3.24 | -- | -- | 0.03 | -- | -- | ||
56 | RC | 239 | Fluorides | 0.01 | 0.01 | lb/ton | Summary of 2018 source tests provided by DEQ with draft PSD permit (June 2020). Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. Represents emission factor for total fluorides minus hydrogen fluoride. If difference is less than zero, shown as zero. | 37.14 | -- | -- | 0.29 | -- | -- | ||
57 | RC | 7664-39-3 | Hydrogen fluoride | 0.00 | 0.00 | lb/ton | Summary of 2018 source tests provided by DEQ with draft PSD permit (June 2020). Controlled production-based emission factors represent the average emission factor The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 4.31 | -- | -- | 0.03 | -- | -- | ||
58 | RC | 352 | Glasswool fibers | 0.00 | 0.00 | lb/ton | Results of 2022 microscopy analysis indicate that total glass content of CFU emissions is less than 1 percent. Conservatively assume 1 percent of filterable particulate matter as glasswool fiber. Filterable PM emission factor from 2018 source test results. Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 10.81 | -- | -- | 0.09 | -- | -- | ||
59 | RC | 67-64-1 | Acetone | 0.02 | 0.02 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 115.32 | -- | -- | 0.92 | -- | -- | ||
60 | RC | 71-43-2 | Benzene | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 25.47 | -- | -- | 0.20 | -- | -- | ||
61 | RC | 106-99-0 | 1,3-Butadiene | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 1.33 | -- | -- | 0.01 | -- | -- | ||
62 | RC | 100-41-4 | Ethyl benzene | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 5.32 | -- | -- | 0.04 | -- | -- | ||
63 | RC | 50-00-0 | Formaldehyde | 0.07 | 0.07 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. The maximum of emission factor of either rotary coarse and ultra rotary coarse will be used for emissions estimates. | 390.39 | -- | -- | 3.10 | -- | -- | ||
64 | RC | 110-54-3 | Hexane | 0.02 | 0.02 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 98.50 | -- | -- | 0.78 | -- | -- | ||
65 | RC | 78-93-3 | 2-Butanone (methyl ethyl ketone) | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 4.70 | -- | -- | 0.04 | -- | -- | ||
66 | RC | 108-88-3 | Toluene | 0.01 | 0.01 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 75.68 | -- | -- | 0.60 | -- | -- | ||
67 | RC | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 12.61 | -- | -- | 0.10 | -- | -- | ||
68 | RC | 95-47-6 | o-Xylene | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 5.98 | -- | -- | 0.05 | -- | -- | ||
69 | FB | 7440-36-0 | Antimony and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.19 | 0.26 | -- | 0.00 | 0.00 | -- | ||
70 | FB | 7440-38-2 | Arsenic and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
71 | FB | 7440-39-3 | Barium and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.13 | 0.17 | -- | 0.00 | 0.00 | -- | ||
72 | FB | 7440-41-7 | Beryllium and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
73 | FB | 7440-43-9 | Cadmium and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.04 | 0.05 | -- | 0.00 | 0.00 | -- | ||
74 | FB | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00 | 0.00 | lb/ton | Conservatively assumes 100 percent of chromium emissions are hexavalent chromium. | 0.04 | 0.05 | -- | 0.00 | 0.00 | -- | ||
75 | FB | 7440-48-4 | Cobalt and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
76 | FB | 7440-50-8 | Copper and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.59 | 0.78 | -- | 0.00 | 0.00 | -- | ||
77 | FB | 7439-92-1 | Lead and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
78 | FB | 7439-96-5 | Manganese and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.13 | 0.18 | -- | 0.00 | 0.00 | -- | ||
79 | FB | 7439-97-6 | Mercury and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.01 | 0.01 | -- | 0.00 | 0.00 | -- | ||
80 | FB | 7440-02-0 | Nickel and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.22 | 0.29 | -- | 0.00 | 0.00 | -- | ||
81 | FB | 504 | Phosphorus and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 1.10 | 1.46 | -- | 0.00 | 0.00 | -- | ||
82 | FB | 7782-49-2 | Selenium and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
83 | FB | 7440-66-6 | Zinc and compounds | 0.01 | 0.01 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 3.54 | 4.70 | -- | 0.01 | 0.01 | -- | ||
84 | FB | 239 | Fluorides | 0.00 | 0.00 | lb/ton | Summary of 2018 source tests provided by DEQ with draft PSD permit (June 2020). Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. Represents emission factor for total fluorides minus hydrogen fluoride. If difference is less than zero, shown as zero. | 2.14 | 2.84 | -- | 0.01 | 0.01 | -- | ||
85 | FB | 7664-39-3 | Hydrogen fluoride | 0.05 | 0.05 | lb/ton | Summary of 2018 source tests provided by DEQ with draft PSD permit (June 2020). Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 28.75 | 38.14 | -- | 0.10 | 0.10 | -- | ||
86 | FB | 352 | Glasswool fibers | 0.01 | 0.01 | lb/ton | Results of 2022 microscopy analysis indicate that total glass content of CFU emissions is less than 1 percent. Conservatively assume 1 percent of filterable particulate matter as glasswool fiber. Filterable PM emission factor from 2018 source test results. Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 6.18 | 8.20 | -- | 0.02 | 0.02 | -- | ||
87 | FB | 67-64-1 | Acetone | 0.43 | 0.43 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 256.01 | 339.63 | -- | 0.93 | 0.93 | -- | ||
88 | FB | 71-43-2 | Benzene | 0.11 | 0.11 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 64.15 | 85.10 | -- | 0.23 | 0.23 | -- | ||
89 | FB | 110-82-7 | Cyclohexane | 0.01 | 0.01 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 3.95 | 5.24 | -- | 0.01 | 0.01 | -- | ||
90 | FB | 100-41-4 | Ethyl benzene | 0.01 | 0.01 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 3.36 | 4.46 | -- | 0.01 | 0.01 | -- | ||
91 | FB | 75-00-3 | Chloroethane (ethyl chloride) | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 1.81 | 2.40 | -- | 0.01 | 0.01 | -- | ||
92 | FB | 50-00-0 | Formaldehyde | 0.47 | 0.47 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 276.21 | 366.42 | -- | 1.00 | 1.00 | -- | ||
93 | FB | 110-54-3 | Hexane | 0.63 | 0.63 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 371.25 | 492.50 | -- | 1.35 | 1.35 | -- | ||
94 | FB | 74-87-3 | Chloromethane (methyl chloride) | 0.04 | 0.04 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 24.24 | 32.15 | -- | 0.09 | 0.09 | -- | ||
95 | FB | 78-93-3 | 2-Butanone (methyl ethyl ketone) | 0.01 | 0.01 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 8.14 | 10.80 | -- | 0.03 | 0.03 | -- | ||
96 | FB | 108-10-1 | Methyl isobutyl ketone (MIBK, hexone) | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 2.96 | 3.93 | -- | 0.01 | 0.01 | -- | ||
97 | FB | 108-88-3 | Toluene | 0.11 | 0.11 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 64.75 | 85.89 | -- | 0.24 | 0.24 | -- | ||
98 | FB | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.01 | 0.01 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 6.95 | 9.22 | -- | 0.03 | 0.03 | -- | ||
99 | GM | 7440-36-0 | Antimony and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.03 | 0.08 | -- | 0.00 | 0.00 | -- | ||
100 | GM | 7440-38-2 | Arsenic and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- |
101 | GM | 7440-39-3 | Barium and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.02 | 0.06 | -- | 0.00 | 0.00 | -- | ||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
102 | GM | 7440-41-7 | Beryllium and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
103 | GM | 7440-43-9 | Cadmium and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.02 | 0.07 | -- | 0.00 | 0.00 | -- | ||
104 | GM | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00 | 0.00 | lb/ton | Conservatively assumes 100 percent of chromium emissions are hexavalent chromium. | 0.01 | 0.03 | -- | 0.00 | 0.00 | -- | ||
105 | GM | 7440-48-4 | Cobalt and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | ||
106 | GM | 7440-50-8 | Copper and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.16 | 0.46 | -- | 0.00 | 0.00 | -- | ||
107 | GM | 7439-92-1 | Lead and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.21 | 0.62 | -- | 0.00 | 0.00 | -- | ||
108 | GM | 7439-96-5 | Manganese and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.01 | 0.02 | -- | 0.00 | 0.00 | -- | ||
109 | GM | 7439-97-6 | Mercury and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 2.90 | 8.49 | -- | 0.02 | 0.02 | -- | ||
110 | GM | 7440-02-0 | Nickel and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
111 | GM | 504 | Phosphorus and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.62 | 1.82 | -- | 0.00 | 0.00 | -- | ||
112 | GM | 7782-49-2 | Selenium and compounds | 0.00 | 0.00 | lb/ton | Results of all source tests runs were below the minimum detection limit. The pollutant assumed not to be present in a measurable quantity. | -- | -- | -- | -- | -- | -- | ||
113 | GM | 7440-66-6 | Zinc and compounds | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.33 | 0.96 | -- | 0.00 | 0.00 | -- | ||
114 | GM | 239 | Fluorides | 0.00 | 0.00 | lb/ton | Summary of 2018 source tests provided by DEQ with draft PSD permit (June 2020). Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. Represents emission factor for total fluorides minus hydrogen fluoride. If difference is less than zero, shown as zero. | 1.11 | 3.26 | -- | 0.01 | 0.01 | -- | ||
115 | GM | 7664-39-3 | Hydrogen fluoride | 0.00 | 0.00 | lb/ton | Summary of 2018 source tests provided by DEQ with draft PSD permit (June 2020). Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 0.16 | 0.48 | -- | 0.00 | 0.00 | -- | ||
116 | GM | 67-64-1 | Acetone | 0.01 | 0.01 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 44.27 | 129.61 | -- | 0.36 | 0.36 | -- | ||
117 | GM | 71-43-2 | Benzene | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 10.58 | 30.98 | -- | 0.08 | 0.08 | -- | ||
118 | GM | 106-99-0 | 1,3-Butadiene | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 4.68 | 13.69 | -- | 0.04 | 0.04 | -- | ||
119 | GM | 75-15-0 | Carbon disulfide | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 0.31 | 0.90 | -- | 0.00 | 0.00 | -- | ||
120 | GM | 50-00-0 | Formaldehyde | 0.00 | 0.00 | lb/ton | Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. | 23.43 | 68.59 | -- | 0.19 | 0.19 | -- | ||
121 | GM | 110-54-3 | Hexane | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 6.37 | 18.66 | -- | 0.05 | 0.05 | -- | ||
122 | GM | 78-93-3 | 2-Butanone (methyl ethyl ketone) | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 0.58 | 1.71 | -- | 0.00 | 0.00 | -- | ||
123 | GM | 108-88-3 | Toluene | 0.00 | 0.00 | lb/ton | Emission Factor from 2022 source test conducted by Bison Engineering. | 2.65 | 7.76 | -- | 0.02 | 0.02 | -- | ||
124 | CFU_RF | 7631-86-9 | Silica, crystalline (respirable) | 0.01 | 0.01 | lb/ton | Conservatively assume 99% of filterable PM is bulking agent. Filterable PM emission factor from 2018 source test results. Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. " | 6.05 | 39.41 | -- | 0.03 | 0.11 | -- | ||
125 | CFU_RC | 7631-86-9 | Silica, crystalline (respirable) | 0.00 | 0.00 | lb/ton | Conservatively assume 99% of filterable PM is bulking agent. Filterable PM emission factor from 2018 source test results. Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. " | 10.70 | -- | -- | 0.09 | -- | -- | ||
126 | CFU_FB | 7631-86-9 | Silica, crystalline (respirable) | 0.01 | 0.01 | lb/ton | Conservatively assume 99% of filterable PM is bulking agent. Filterable PM emission factor from 2018 source test results. Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. " | 6.12 | 8.11 | -- | 0.02 | 0.02 | -- | ||
127 | CFU_GM | 7631-86-9 | Silica, crystalline (respirable) | 0.00 | 0.00 | lb/ton | Conservatively assume 99% of filterable PM is bulking agent. Filterable PM emission factor from 2018 source test results. Controlled production-based emission factors represent the average emission factor derived from multiple source tests conducted at the CFU outlet. " | 0.28 | 0.82 | -- | 0.00 | 0.00 | -- | ||
128 | SSF_RF | 7440-39-3 | Barium and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
129 | SSF_RF | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
130 | SSF_RF | 7440-50-8 | Copper and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
131 | SSF_RF | 7439-96-5 | Manganese and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
132 | SSF_RF | 7439-97-6 | Mercury and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
133 | SSF_RF | 7440-02-0 | Nickel and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
134 | SSF_RF | 504 | Phosphorus and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.01 | 0.01 | -- | 0.00 | 0.00 | -- | ||
135 | SSF_RF | 7440-66-6 | Zinc and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.01 | 0.01 | -- | 0.00 | 0.00 | -- | ||
136 | SSF_RF | 7631-86-9 | Silica, crystalline (respirable) | 0.00 | 0.00 | lb/ton | TAC content from vendor safety data sheets. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.10 | 0.16 | -- | 0.00 | 0.00 | -- | ||
137 | SSF_RC | 7440-36-0 | Antimony and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | ||
138 | SSF_RC | 7440-39-3 | Barium and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
139 | SSF_RC | 7440-43-9 | Cadmium and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
140 | SSF_RC | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
141 | SSF_RC | 7440-48-4 | Cobalt and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
142 | SSF_RC | 7440-50-8 | Copper and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.01 | 0.02 | -- | 0.00 | 0.00 | -- | ||
143 | SSF_RC | 7439-92-1 | Lead and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.02 | 0.03 | -- | 0.00 | 0.00 | -- | ||
144 | SSF_RC | 7439-96-5 | Manganese and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | ||
145 | SSF_RC | 7439-97-6 | Mercury and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
146 | SSF_RC | 7440-02-0 | Nickel and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.01 | 0.01 | -- | 0.00 | 0.00 | -- | ||
147 | SSF_RC | 504 | Phosphorus and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.06 | 0.10 | -- | 0.00 | 0.00 | -- | ||
148 | SSF_RC | 7440-66-6 | Zinc and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.04 | 0.06 | -- | 0.00 | 0.00 | -- | ||
149 | SSF_RC | 239 | Fluorides | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.44 | 0.71 | -- | 0.00 | 0.00 | -- | ||
150 | SSF_RC | 7631-86-9 | Silica, crystalline (respirable) | 0.00 | 0.00 | lb/ton | TAC content from vendor safety data sheets. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.10 | 0.16 | -- | 0.00 | 0.00 | -- |
151 | SSF_FB | 7440-36-0 | Antimony and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
152 | SSF_FB | 7440-39-3 | Barium and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
153 | SSF_FB | 7440-43-9 | Cadmium and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
154 | SSF_FB | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
155 | SSF_FB | 7440-50-8 | Copper and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | ||
156 | SSF_FB | 7439-96-5 | Manganese and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
157 | SSF_FB | 7439-97-6 | Mercury and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
158 | SSF_FB | 7440-02-0 | Nickel and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
159 | SSF_FB | 504 | Phosphorus and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.01 | 0.01 | -- | 0.00 | 0.00 | -- | ||
160 | SSF_FB | 7440-66-6 | Zinc and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.02 | 0.03 | -- | 0.00 | 0.00 | -- | ||
161 | SSF_FB | 239 | Fluorides | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.01 | 0.02 | -- | 0.00 | 0.00 | -- | ||
162 | SSF_FB | 7631-86-9 | Silica, crystalline (respirable) | 0.00 | 0.00 | lb/ton | TAC content from vendor safety data sheets. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.10 | 0.16 | -- | 0.00 | 0.00 | -- | ||
163 | SSF_GM | 7440-36-0 | Antimony and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
164 | SSF_GM | 7440-39-3 | Barium and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
165 | SSF_GM | 7440-43-9 | Cadmium and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
166 | SSF_GM | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
167 | SSF_GM | 7440-48-4 | Cobalt and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
168 | SSF_GM | 7440-50-8 | Copper and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.02 | 0.03 | -- | 0.00 | 0.00 | -- | ||
169 | SSF_GM | 7439-92-1 | Lead and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.02 | 0.04 | -- | 0.00 | 0.00 | -- | ||
170 | SSF_GM | 7439-96-5 | Manganese and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
171 | SSF_GM | 7439-97-6 | Mercury and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.30 | 0.49 | -- | 0.00 | 0.00 | -- | ||
172 | SSF_GM | 504 | Phosphorus and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.06 | 0.10 | -- | 0.00 | 0.00 | -- | ||
173 | SSF_GM | 7440-66-6 | Zinc and compounds | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.03 | 0.05 | -- | 0.00 | 0.00 | -- | ||
174 | SSF_GM | 239 | Fluorides | 0.00 | 0.00 | lb/ton | TAC percent of PM determined from ratio of Glass Plant PM TAC emission factors to Glass Plant PM emission factors. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.12 | 0.19 | -- | 0.00 | 0.00 | -- | ||
175 | SSF_GM | 7631-86-9 | Silica, crystalline (respirable) | 0.00 | 0.00 | lb/ton | TAC content from vendor safety data sheets. Bulk loading PM emission factor from AP-42 Chapter 11.26 (November 1995), Table 11.26-1 "Emission Factors for Talc Processing." Emission factor for ground talc storage bin loading, with fabric filter. Emission factor used as representative of CFU super sack loading with fabric filter control. Emission factor converted from 0.0016 lb/Mlb to 0.0032 lb/ton. | 0.10 | 0.16 | -- | 0.00 | 0.00 | -- | ||
176 | BALING | 352 | Glasswool fibers | 0.04 | 0.04 | lb/ton | Emission factor developed based on engineering judgement. Assume less than 0.01% of all fiber produced becomes airborne. Assume 20% of airborne fiber leaves the production building. | 311.96 | 1193.08 | -- | 2.22 | 3.27 | -- | ||
177 | SILO1 | 7631-86-9 | Silica, crystalline (respirable) | 0.00 | 0.00 | lb/hr | Emission factor based on PM10 emissions for silo filling activities and composition information provided from vendor SDS. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | ||
178 | SILO2 | 7631-86-9 | Silica, crystalline (respirable) | 0.00 | 0.00 | lb/hr | Emission factor based on PM10 emissions for silo filling activities and composition information provided from vendor SDS. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | ||
179 | RMH_BA | 7440-39-3 | Barium and compounds | 0.04 | 0.04 | lb/ton | Emission factor based on total PM emissions for raw material handling and composition information provided from vendor SDS. | 9.47 | 53.78 | -- | 0.03 | 0.18 | -- | ||
180 | RMH_ZN | 1314-13-2 | Zinc oxide | 0.04 | 0.04 | lb/ton | Emission factor based on total PM emissions for raw material handling and composition information provided from vendor SDS. | 6.00 | 34.05 | -- | 0.02 | 0.11 | -- | ||
181 | RMH_ZN | 7439-92-1 | Lead and compounds | 0.00 | 0.00 | lb/ton | Emission factor based on total PM emissions for raw material handling and composition information provided from vendor SDS. | 0.01 | 0.03 | -- | 0.00 | 0.00 | -- | ||
182 | RMH_ZN | 7440-43-9 | Cadmium and compounds | 0.00 | 0.00 | lb/ton | Emission factor based on total PM emissions for raw material handling and composition information provided from vendor SDS. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | ||
183 | |||||||||||||||
184 | RMH_F | 239 | Fluorides | 4.51 | 14.85 | -- | 0.01 | 0.05 | -- | ||||||
185 | RMH_F | 7631-86-9 | Silica, crystalline (respirable) | 0.07 | 0.22 | -- | 0.00 | 0.00 | -- | ||||||
186 | RMH_S | 7631-86-9 | Silica, crystalline (respirable) | 154.26 | 520.38 | -- | 0.51 | 1.71 | -- | ||||||
187 | RMH_S | 7429-90-5 | Aluminum and compounds | 0.51 | 1.73 | -- | 0.00 | 0.01 | -- | ||||||
188 | RMH_D | 7631-86-9 | Silica, crystalline (respirable) | 0.42 | 2.05 | -- | 0.00 | 0.01 | -- | ||||||
189 | RMH_L | 7631-86-9 | Silica, crystalline (respirable) | 0.01 | 0.03 | -- | 0.00 | 0.00 | -- | ||||||
190 | RMH_N | 7429-90-5 | Aluminum and compounds | 59.51 | 205.39 | -- | 0.20 | 0.68 | -- | ||||||
191 | |||||||||||||||
192 | RMH_OFF | 7440-39-3 | Barium and compounds | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | 0.00 | -- | -- | 0.00 | -- | -- | ||
193 | RMH_OFF | 1314-13-2 | Zinc oxide | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | 0.00 | -- | -- | 0.00 | -- | -- | ||
194 | RMH_OFF | 7439-92-1 | Lead and compounds | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | 0.00 | -- | -- | 0.00 | -- | -- | ||
195 | RMH_OFF | 7440-43-9 | Cadmium and compounds | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | 0.00 | -- | -- | 0.00 | -- | -- | ||
196 | RMH_OFF | 239 | Fluorides | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | 0.00 | -- | -- | 0.00 | -- | -- | ||
197 | RMH_OFF | 7631-86-9 | Silica, crystalline (respirable) | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | 0.01 | -- | -- | 0.00 | -- | -- | ||
198 | RMH_OFF | 7429-90-5 | Aluminum and compounds | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | 0.01 | -- | -- | 0.00 | -- | -- | ||
199 | RMH_OFF | 7440-39-3 | Barium and compounds | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | -- | 0.00 | -- | -- | 0.00 | -- | ||
200 | RMH_OFF | 1314-13-2 | Zinc oxide | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | -- | 0.00 | -- | -- | 0.00 | -- |
201 | RMH_OFF | 7439-92-1 | Lead and compounds | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | -- | 0.00 | -- | -- | 0.00 | -- | ||
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202 | RMH_OFF | 7440-43-9 | Cadmium and compounds | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | -- | 0.00 | -- | -- | 0.00 | -- | ||
203 | RMH_OFF | 239 | Fluorides | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | -- | 0.00 | -- | -- | 0.00 | -- | ||
204 | RMH_OFF | 7631-86-9 | Silica, crystalline (respirable) | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | -- | 0.01 | -- | -- | 0.00 | -- | ||
205 | RMH_OFF | 7429-90-5 | Aluminum and compounds | 0.00 | 0.00 | lb/ton | Emission factor based on PM emission factor for Off Specification, annual raw material mix, and composition information provided from vendor SDS. | -- | 0.01 | -- | -- | 0.00 | -- | ||
206 | PAINT | 67-64-1 | Acetone | 0.00% | 0.26 | 0.36 | lb/lb | Emission factor based on composition information from vendor SDS. | 89.60 | 245.23 | -- | 0.36 | 1.08 | -- | |
207 | PAINT | 7440-39-3 | Barium and compounds | 0.00% | 0.02 | 0.02 | lb/lb | Emission factor based on composition information from vendor SDS and paint transfer efficiency. | 5.39 | 14.74 | -- | 0.02 | 0.07 | -- | |
208 | PAINT | 7440-48-4 | Cobalt and compounds | 0.00% | 0.00 | 0.00 | lb/lb | Emission factor based on composition information from vendor SDS and paint transfer efficiency. | 0.26 | 0.70 | -- | 0.00 | 0.00 | -- | |
209 | PAINT | 100-41-4 | Ethyl benzene | 0.00% | 0.01 | 0.02 | lb/lb | Emission factor based on composition information from vendor SDS. | 3.76 | 10.30 | -- | 0.02 | 0.05 | -- | |
210 | PAINT | 95-63-6 | 1,2,4-Trimethylbenzene | 0.00% | 0.01 | 0.01 | lb/lb | Emission factor based on composition information from vendor SDS. | 4.79 | 13.10 | -- | 0.01 | 0.04 | -- | |
211 | PAINT | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.00% | 0.05 | 0.06 | lb/lb | Emission factor based on composition information from vendor SDS. | 15.39 | 42.12 | -- | 0.06 | 0.19 | -- | |
212 | EGEN1 | 7440-38-2 | Arsenic and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
213 | EGEN1 | 7440-43-9 | Cadmium and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
214 | EGEN1 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
215 | EGEN1 | 7440-50-8 | Copper and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
216 | EGEN1 | 7439-92-1 | Lead and compounds | 0.00% | 0.01 | 0.01 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.02 | -- | 0.00 | 0.00 | -- | |
217 | EGEN1 | 7439-96-5 | Manganese and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
218 | EGEN1 | 7439-97-6 | Mercury and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
219 | EGEN1 | 7440-02-0 | Nickel and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
220 | EGEN1 | 7782-49-2 | Selenium and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
221 | EGEN1 | 75-07-0 | Acetaldehyde | 0.00% | 0.78 | 0.78 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.13 | 1.83 | -- | 0.04 | 0.04 | -- | |
222 | EGEN1 | 107-02-8 | Acrolein | 0.00% | 0.03 | 0.03 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.01 | 0.08 | -- | 0.00 | 0.00 | -- | |
223 | EGEN1 | 71-43-2 | Benzene | 0.00% | 0.19 | 0.19 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.03 | 0.44 | -- | 0.01 | 0.01 | -- | |
224 | EGEN1 | 106-99-0 | 1,3-Butadiene | 0.00% | 0.22 | 0.22 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.04 | 0.51 | -- | 0.01 | 0.01 | -- | |
225 | EGEN1 | 100-41-4 | Ethyl benzene | 0.00% | 0.01 | 0.01 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.03 | -- | 0.00 | 0.00 | -- | |
226 | EGEN1 | 50-00-0 | Formaldehyde | 0.00% | 1.73 | 1.73 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.28 | 4.04 | -- | 0.08 | 0.08 | -- | |
227 | EGEN1 | 110-54-3 | Hexane | 0.00% | 0.03 | 0.03 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.06 | -- | 0.00 | 0.00 | -- | |
228 | EGEN1 | 108-88-3 | Toluene | 0.00% | 0.11 | 0.11 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.02 | 0.25 | -- | 0.00 | 0.00 | -- | |
229 | EGEN1 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.00% | 0.04 | 0.04 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.01 | 0.10 | -- | 0.00 | 0.00 | -- | |
230 | EGEN1 | 7664-41-7 | Ammonia | 0.00% | 0.80 | 0.80 | lb/Mgal | Reporting Procedures for AB2588 Facilities for Reporting their Quadrennial Air Toxics Emissions Inventory published by the South Coast Air Quality Management District (SCAQMD) in December 2016. See Appendix B, Table B-2 "Default EF for Diesel/Distillate Oil Fuel Combustion (lb/1000 gal)" for stationary and portable internal combustion engines (ICE). Assumes no control. | 0.13 | 1.87 | -- | 0.04 | 0.04 | -- | |
231 | EGEN1 | 7647-01-0 | Hydrochloric acid | 0.00% | 0.19 | 0.19 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.03 | 0.44 | -- | 0.01 | 0.01 | -- | |
232 | EGEN1 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.00% | 0.04 | 0.04 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.01 | 0.08 | -- | 0.00 | 0.00 | -- | |
233 | EGEN1 | 50-32-8 | Benzo[a]pyrene | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
234 | EGEN1 | 91-20-3 | Naphthalene | 0.00% | 0.02 | 0.02 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.05 | -- | 0.00 | 0.00 | -- | |
235 | EGEN1 | 200 | Diesel particulate matter | 0.00% | 33.50 | 33.50 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 5.49 | 78.39 | -- | 1.57 | 1.57 | -- | |
236 | EGEN2 | 7440-38-2 | Arsenic and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
237 | EGEN2 | 7440-43-9 | Cadmium and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
238 | EGEN2 | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
239 | EGEN2 | 7440-50-8 | Copper and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
240 | EGEN2 | 7439-92-1 | Lead and compounds | 0.00% | 0.01 | 0.01 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
241 | EGEN2 | 7439-96-5 | Manganese and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
242 | EGEN2 | 7439-97-6 | Mercury and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
243 | EGEN2 | 7440-02-0 | Nickel and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
244 | EGEN2 | 7782-49-2 | Selenium and compounds | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
245 | EGEN2 | 75-07-0 | Acetaldehyde | 0.00% | 0.78 | 0.78 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.10 | 1.29 | -- | 0.03 | 0.03 | -- | |
246 | EGEN2 | 107-02-8 | Acrolein | 0.00% | 0.03 | 0.03 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.06 | -- | 0.00 | 0.00 | -- | |
247 | EGEN2 | 71-43-2 | Benzene | 0.00% | 0.19 | 0.19 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.02 | 0.31 | -- | 0.01 | 0.01 | -- | |
248 | EGEN2 | 106-99-0 | 1,3-Butadiene | 0.00% | 0.22 | 0.22 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.03 | 0.36 | -- | 0.01 | 0.01 | -- | |
249 | EGEN2 | 100-41-4 | Ethyl benzene | 0.00% | 0.01 | 0.01 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.02 | -- | 0.00 | 0.00 | -- | |
250 | EGEN2 | 50-00-0 | Formaldehyde | 0.00% | 1.73 | 1.73 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.23 | 2.85 | -- | 0.06 | 0.06 | -- |
251 | EGEN2 | 110-54-3 | Hexane | 0.00% | 0.03 | 0.03 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.04 | -- | 0.00 | 0.00 | -- | |
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252 | EGEN2 | 108-88-3 | Toluene | 0.00% | 0.11 | 0.11 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.01 | 0.17 | -- | 0.00 | 0.00 | -- | |
253 | EGEN2 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.00% | 0.04 | 0.04 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.01 | 0.07 | -- | 0.00 | 0.00 | -- | |
254 | EGEN2 | 7664-41-7 | Ammonia | 0.00% | 0.80 | 0.80 | lb/Mgal | Reporting Procedures for AB2588 Facilities for Reporting their Quadrennial Air Toxics Emissions Inventory published by the South Coast Air Quality Management District (SCAQMD) in December 2016. See Appendix B, Table B-2 "Default EF for Diesel/Distillate Oil Fuel Combustion (lb/1000 gal)" for stationary and portable internal combustion engines (ICE). Assumes no control. | 0.11 | 1.32 | -- | 0.03 | 0.03 | -- | |
255 | EGEN2 | 7647-01-0 | Hydrochloric acid | 0.00% | 0.19 | 0.19 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.02 | 0.31 | -- | 0.01 | 0.01 | -- | |
256 | EGEN2 | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.00% | 0.04 | 0.04 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.06 | -- | 0.00 | 0.00 | -- | |
257 | EGEN2 | 50-32-8 | Benzo[a]pyrene | 0.00% | 0.00 | 0.00 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
258 | EGEN2 | 91-20-3 | Naphthalene | 0.00% | 0.02 | 0.02 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 0.00 | 0.03 | -- | 0.00 | 0.00 | -- | |
259 | EGEN2 | 200 | Diesel particulate matter | 0.00% | 33.50 | 33.50 | lb/Mgal | DEQ approved diesel combustion emission factors for stationary and portable internal combustion engines. | 4.42 | 55.28 | -- | 1.11 | 1.11 | -- | |
260 | CT1_2 | 7664-38-2 | Phosphoric acid | 0.00% | 0.00 | 0.00 | lb/hr | Hourly emission rates estimated based on vendor drift eliminator efficiency and cooling tower makeup water chemical composition. | 1.42 | 1.42 | -- | 0.00 | 0.00 | -- | |
261 | CT1_2 | 7664-93-9 | Sulfuric acid | 0.00% | 0.00 | 0.00 | lb/hr | Hourly emission rates estimated based on vendor drift eliminator efficiency and cooling tower makeup water chemical composition. | 1.42 | 1.42 | -- | 0.00 | 0.00 | -- | |
262 | CT3 | 7664-38-2 | Phosphoric acid | 0.00% | 0.00 | 0.00 | lb/hr | Hourly emission rates estimated based on vendor drift eliminator efficiency and cooling tower makeup water chemical composition. | 1.58 | 1.58 | -- | 0.00 | 0.00 | -- | |
263 | CT3 | 7664-93-9 | Sulfuric acid | 0.00% | 0.00 | 0.00 | lb/hr | Hourly emission rates estimated based on vendor drift eliminator efficiency and cooling tower makeup water chemical composition. | 1.58 | 1.58 | -- | 0.00 | 0.00 | -- | |
264 | CT4 | 7664-38-2 | Phosphoric acid | 0.00% | 0.00 | 0.00 | lb/hr | Hourly emission rates estimated based on vendor drift eliminator efficiency and cooling tower makeup water chemical composition. | 1.26 | 1.26 | -- | 0.00 | 0.00 | -- | |
265 | CT4 | 7664-93-9 | Sulfuric acid | 0.00% | 0.00 | 0.00 | lb/hr | Hourly emission rates estimated based on vendor drift eliminator efficiency and cooling tower makeup water chemical composition. | 1.26 | 1.26 | -- | 0.00 | 0.00 | -- | |
266 | NG_GP | 7440-38-2 | Arsenic and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
267 | NG_GP | 7440-39-3 | Barium and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
268 | NG_GP | 7440-41-7 | Beryllium and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
269 | NG_GP | 7440-43-9 | Cadmium and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
270 | NG_GP | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
271 | NG_GP | 7440-48-4 | Cobalt and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
272 | NG_GP | 7440-50-8 | Copper and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
273 | NG_GP | 7439-92-1 | Lead and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
274 | NG_GP | 7439-96-5 | Manganese and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
275 | NG_GP | 7439-97-6 | Mercury and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
276 | NG_GP | 1313-27-5 | Molybdenum trioxide | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.62 | 1.62 | -- | 0.00 | 0.00 | -- | |
277 | NG_GP | 7440-02-0 | Nickel and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
278 | NG_GP | 7782-49-2 | Selenium and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
279 | NG_GP | 7440-62-2 | Vanadium (fume or dust) | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.86 | 2.26 | -- | 0.01 | 0.01 | -- | |
280 | NG_GP | 7440-66-6 | Zinc and compounds | 0.00% | 0.03 | 0.03 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
281 | NG_GP | 7664-41-7 | Ammonia | 0.00% | 3.20 | 3.20 | lb/MMscf | EPA Webfire Clearinghouse for Inventories and Emission Factors. Assumes uncontrolled natural gas combustion. | 1202.25 | 3141.12 | -- | 7.60 | 8.59 | -- | |
282 | NG_GP | 75-07-0 | Acetaldehyde | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 1.62 | 4.22 | -- | 0.01 | 0.01 | -- | |
283 | NG_GP | 107-02-8 | Acrolein | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 1.01 | 2.65 | -- | 0.01 | 0.01 | -- | |
284 | NG_GP | 71-43-2 | Benzene | 0.00% | 0.01 | 0.01 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
285 | NG_GP | 100-41-4 | Ethyl benzene | 0.00% | 0.01 | 0.01 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | -- | -- | -- | -- | -- | -- | |
286 | NG_GP | 50-00-0 | Formaldehyde | 0.00% | 0.02 | 0.02 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
287 | NG_GP | 110-54-3 | Hexane | 0.00% | 0.01 | 0.01 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
288 | NG_GP | 108-88-3 | Toluene | 0.00% | 0.04 | 0.04 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
289 | NG_GP | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.00% | 0.03 | 0.03 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | -- | -- | -- | -- | -- | -- | |
290 | NG_GP | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.04 | 0.10 | -- | 0.00 | 0.00 | -- | |
291 | NG_GP | 50-32-8 | Benzo[a]pyrene | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
292 | NG_GP | 91-20-3 | Naphthalene | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.11 | 0.29 | -- | 0.00 | 0.00 | -- | |
293 | NG_FH | 7440-38-2 | Arsenic and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
294 | NG_FH | 7440-39-3 | Barium and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
295 | NG_FH | 7440-41-7 | Beryllium and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
296 | NG_FH | 7440-43-9 | Cadmium and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
297 | NG_FH | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
298 | NG_FH | 7440-48-4 | Cobalt and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
299 | NG_FH | 7440-50-8 | Copper and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
300 | NG_FH | 7439-92-1 | Lead and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- |
301 | NG_FH | 7439-96-5 | Manganese and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
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302 | NG_FH | 7439-97-6 | Mercury and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
303 | NG_FH | 1313-27-5 | Molybdenum trioxide | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.03 | 0.06 | -- | 0.00 | 0.00 | -- | |
304 | NG_FH | 7440-02-0 | Nickel and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
305 | NG_FH | 7782-49-2 | Selenium and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
306 | NG_FH | 7440-62-2 | Vanadium (fume or dust) | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.04 | 0.09 | -- | 0.00 | 0.00 | -- | |
307 | NG_FH | 7440-66-6 | Zinc and compounds | 0.00% | 0.03 | 0.03 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
308 | NG_FH | 7664-41-7 | Ammonia | 0.00% | 3.20 | 3.20 | lb/MMscf | EPA Webfire Clearinghouse for Inventories and Emission Factors. Assumes uncontrolled natural gas combustion. | 48.95 | 122.88 | -- | 0.34 | 0.34 | -- | |
309 | NG_FH | 75-07-0 | Acetaldehyde | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.07 | 0.17 | -- | 0.00 | 0.00 | -- | |
310 | NG_FH | 107-02-8 | Acrolein | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.04 | 0.10 | -- | 0.00 | 0.00 | -- | |
311 | NG_FH | 71-43-2 | Benzene | 0.00% | 0.01 | 0.01 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.12 | 0.31 | -- | 0.00 | 0.00 | -- | |
312 | NG_FH | 100-41-4 | Ethyl benzene | 0.00% | 0.01 | 0.01 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.15 | 0.36 | -- | 0.00 | 0.00 | -- | |
313 | NG_FH | 50-00-0 | Formaldehyde | 0.00% | 0.02 | 0.02 | lb/MMscf | Emissions of this pollutant are included with the emission estimates for the production-based TEU emission factors. | -- | -- | -- | -- | -- | -- | |
314 | NG_FH | 110-54-3 | Hexane | 0.00% | 0.01 | 0.01 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.10 | 0.24 | -- | 0.00 | 0.00 | -- | |
315 | NG_FH | 108-88-3 | Toluene | 0.00% | 0.04 | 0.04 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.56 | 1.41 | -- | 0.00 | 0.00 | -- | |
316 | NG_FH | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.00% | 0.03 | 0.03 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.42 | 1.04 | -- | 0.00 | 0.00 | -- | |
317 | NG_FH | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
318 | NG_FH | 50-32-8 | Benzo[a]pyrene | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
319 | NG_FH | 91-20-3 | Naphthalene | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
320 | NG | 7440-38-2 | Arsenic and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
321 | NG | 7440-39-3 | Barium and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.04 | 0.11 | -- | 0.00 | 0.00 | -- | |
322 | NG | 7440-41-7 | Beryllium and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
323 | NG | 7440-43-9 | Cadmium and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.01 | 0.03 | -- | 0.00 | 0.00 | -- | |
324 | NG | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. Based on assumptions used by the EPA as outlined in the 2011 National Emissions Inventory. EPA assumes that 4% of chromium emitted during natural gas combustion is in the form of hexavalent chromium.. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
325 | NG | 7440-48-4 | Cobalt and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
326 | NG | 7440-50-8 | Copper and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.01 | 0.02 | -- | 0.00 | 0.00 | -- | |
327 | NG | 7439-92-1 | Lead and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
328 | NG | 7439-96-5 | Manganese and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
329 | NG | 7439-97-6 | Mercury and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
330 | NG | 1313-27-5 | Molybdenum trioxide | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.02 | 0.04 | -- | 0.00 | 0.00 | -- | |
331 | NG | 7440-02-0 | Nickel and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.02 | 0.05 | -- | 0.00 | 0.00 | -- | |
332 | NG | 7782-49-2 | Selenium and compounds | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
333 | NG | 7440-62-2 | Vanadium (fume or dust) | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.02 | 0.06 | -- | 0.00 | 0.00 | -- | |
334 | NG | 7440-66-6 | Zinc and compounds | 0.00% | 0.03 | 0.03 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.28 | 0.74 | -- | 0.00 | 0.00 | -- | |
335 | NG | 7664-41-7 | Ammonia | 0.00% | 3.20 | 3.20 | lb/MMscf | EPA Webfire Clearinghouse for Inventories and Emission Factors. Assumes uncontrolled natural gas combustion. | 31.26 | 81.56 | -- | 0.20 | 0.22 | -- | |
336 | NG | 75-07-0 | Acetaldehyde | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.04 | 0.11 | -- | 0.00 | 0.00 | -- | |
337 | NG | 107-02-8 | Acrolein | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.03 | 0.07 | -- | 0.00 | 0.00 | -- | |
338 | NG | 71-43-2 | Benzene | 0.00% | 0.01 | 0.01 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.08 | 0.20 | -- | 0.00 | 0.00 | -- | |
339 | NG | 100-41-4 | Ethyl benzene | 0.00% | 0.01 | 0.01 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.09 | 0.24 | -- | 0.00 | 0.00 | -- | |
340 | NG | 50-00-0 | Formaldehyde | 0.00% | 0.02 | 0.02 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.17 | 0.43 | -- | 0.00 | 0.00 | -- | |
341 | NG | 110-54-3 | Hexane | 0.00% | 0.01 | 0.01 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.06 | 0.16 | -- | 0.00 | 0.00 | -- | |
342 | NG | 108-88-3 | Toluene | 0.00% | 0.04 | 0.04 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.36 | 0.93 | -- | 0.00 | 0.00 | -- | |
343 | NG | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene | 0.00% | 0.03 | 0.03 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.27 | 0.69 | -- | 0.00 | 0.00 | -- | |
344 | NG | 401 | Polycyclic aromatic hydrocarbons (PAHs) | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
345 | NG | 50-32-8 | Benzo[a]pyrene | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.00 | -- | 0.00 | 0.00 | -- | |
346 | NG | 91-20-3 | Naphthalene | 0.00% | 0.00 | 0.00 | lb/MMscf | Emission factors provided by Oregon Department of Environmental Quality for Natural Gas External Combustion Sources. Emission factors for sources <10 MMBtu/hr were used. | 0.00 | 0.01 | -- | 0.00 | 0.00 | -- | |
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10 | Emissions Unit/Product Information |
Stack/Fugitive Information |
Material Usage | Material Waste | ||||||||||||||
11 |
Toxics Emissions Unit ID |
Emission Unit or Activity Description | Material Name | Manufacturer |
Emission Type (e.g. Point or Fugitive) |
Stack or Fugitive ID | Annual - Chronic [lb/year] | Max Daily - Acute [lb/day] | Annual - Chronic [lb/year] | Max Daily - Acute [lb/day] | ||||||||
12 | Actual |
Requested PTE |
Capacity | Actual |
Requested PTE |
Capacity | Actual |
Requested PTE |
Capacity | Actual |
Requested PTE |
Capacity | ||||||
13 | TEU-Booth | Widget Paint Booth - atomizer spray guns (EXAMPLE) | Widget Paint-A | Widget Paint Co. | Point | ST-4 | 12,000 | 14,000 | 20,000 | 36 | 40 | 52 | 2000 | 2600 | 5000 | 5 | 7 | 14 |
14 | TEU-Booth | Widget Paint Booth - atomizer spray guns (EXAMPLE) | Widget Paint-B | Widget Paint Co. | Point | ST-4 | 950 | 1200 | 1500 | 5 | 10 | 15 | 15 | 30 | 40 | 0.5 | 1 | 2 |
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16 | CT_MB | Cooling Tower, Shock Biocide | H-550 | Nalco | Point | multiple | 310 | -- | -- | 17.0 | -- | -- | -- | -- | -- | -- | -- | -- |
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Toxics Emissions Unit ID |
Material Name | Pollutant Information | Emissions Data | Annual Emissions - Chronic [lb/yr] | Total Daily Emissions - Acute [lb/day] | ||||||||
11 | CAS or DEQ ID | Chemical Name | Control Efficiency | Percent Composition | Reference/Notes | Actual | Requested PTE | Capacity | Actual | Requested PTE | Capacity | |||
12 | TEU-BOOTH | Widget Paint-A | 67-56-1 | Methanol | 0.00% | 35.00% | 3500 | 3990 | 5250 | 10.85 | 11.55 | 13.3 | ||
13 | TEU-BOOTH | Widget Paint-A | 100-40-3 | 4-Vinylcyclohexene | 0.00% | 48.00% | 4800 | 5472 | 7200 | 14.88 | 15.84 | 18.24 | ||
14 | TEU-BOOTH | Widget Paint-A | 18540-29-9 | Chromium VI, chromate and dichromate particulate | 99.72% | 5.00% | Includes Transfer Efficiency (72%) and Filter Removal Efficiency (99%) | 1.4 | 1.596 | 2.1 | 0.00434 | 0.00462 | 0.00532 | |
15 | TEU-BOOTH | Widget Paint-B | 90-43-7 | 2-Phenylphenol | 0.00% | 0.50% | 4.675 | 5.85 | 7.3 | 0.0225 | 0.045 | 0.065 | ||
16 | TEU-BOOTH | Widget Paint-B | 50-00-0 | Formaldehyde | 0.00% | 70.00% | 654.5 | 819 | 1022 | 3.15 | 6.3 | 9.1 | ||
17 | TEU-BOOTH | Widget Paint-B | 7440-36-0 | Antimony and compounds | 99.72% | 5.00% | Includes Transfer Efficiency (72%) and Filter Removal Efficiency (99%) | 0.1309 | 0.1638 | 0.2044 | 0.00063 | 0.00126 | 0.00182 | |
18 | ||||||||||||||
19 | CT_MB | H-550 | 111-30-8 | Glutaraldehyde | 0.00% | 45.00% | Composition information from vendor SDS. | 139.5 | -- | -- | 7.65 | -- | -- | |
20 | CT_MB | H-550 | 67-56-1 | Methanol | 0.00% | 0.50% | Composition information from vendor SDS. | 1.55 | -- | -- | 0.085 | -- | -- | |
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5 | ||
6 | CASRN | Chemical Name |
7 | 630-20-6 | 1,1,1,2-Tetrachloroethane |
8 | 811-97-2 | 1,1,1,2-Tetrafluoroethane |
9 | 71-55-6 | 1,1,1-Trichloroethane (methyl chloroform) |
10 | 79-34-5 | 1,1,2,2-Tetrachloroethane |
11 | 79-00-5 | 1,1,2-Trichloroethane (vinyl trichloride) |
12 | 75-34-3 | 1,1-Dichloroethane (ethylidene dichloride) |
13 | 75-37-6 | 1,1-Difluoroethane |
14 | 57-14-7 | 1,1-Dimethylhydrazine |
15 | 67562-39-4 | 1,2,3,4,6,7,8-Heptachlorodibenzofuran (HpCDF) |
16 | 35822-46-9 | 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (HpCDD) |
17 | 55673-89-7 | 1,2,3,4,7,8,9-Heptachlorodibenzofuran (HpCDF) |
18 | 70648-26-9 | 1,2,3,4,7,8-Hexachlorodibenzofuran (HxCDF) |
19 | 39227-28-6 | 1,2,3,4,7,8-Hexachlorodibenzo-p-dioxin (HxCDD) |
20 | 57117-44-9 | 1,2,3,6,7,8-Hexachlorodibenzofuran (HxCDF) |
21 | 57653-85-7 | 1,2,3,6,7,8-Hexachlorodibenzo-p-dioxin (HxCDD) |
22 | 72918-21-9 | 1,2,3,7,8,9-Hexachlorodibenzofuran (HxCDF) |
23 | 19408-74-3 | 1,2,3,7,8,9-Hexachlorodibenzo-p-dioxin (HxCDD) |
24 | 57117-41-6 | 1,2,3,7,8-Pentachlorodibenzofuran (PeCDF) |
25 | 40321-76-4 | 1,2,3,7,8-Pentachlorodibenzo-p-dioxin (PeCDD) |
26 | 96-18-4 | 1,2,3-Trichloropropane |
27 | 526-73-8 | 1,2,3-Trimethylbenzene |
28 | 120-82-1 | 1,2,4-Trichlorobenzene |
29 | 95-63-6 | 1,2,4-Trimethylbenzene |
30 | 96-12-8 | 1,2-Dibromo-3-chloropropane (DBCP) |
31 | 95-50-1 | 1,2-Dichlorobenzene |
32 | 78-87-5 | 1,2-Dichloropropane (propylene dichloride) |
33 | 540-73-8 | 1,2-Dimethylhydrazine |
34 | 122-66-7 | 1,2-Diphenylhydrazine (hydrazobenzene) |
35 | 106-88-7 | 1,2-Epoxybutane |
36 | 75-55-8 | 1,2-Propyleneimine (2-methylaziridine) |
37 | 108-67-8 | 1,3,5-Trimethylbenzene |
38 | 106-99-0 | 1,3-Butadiene |
39 | 541-73-1 | 1,3-Dichlorobenzene |
40 | 542-75-6 | 1,3-Dichloropropene |
41 | 1120-71-4 | 1,3-Propane sultone |
42 | 123-91-1 | 1,4-Dioxane |
43 | 42397-64-8 | 1,6-Dinitropyrene |
44 | 42397-65-9 | 1,8-Dinitropyrene |
45 | 555-84-0 | 1-[(5-Nitrofurfurylidene)-amino]-2-imidazolidinone |
46 | 82-28-0 | 1-Amino-2-methylanthraquinone |
47 | 106-94-5 | 1-Bromopropane (n-propyl bromide) |
48 | 75-68-3 | 1-Chloro-1,1-difluoroethane |
49 | 832-69-9 | 1-Methylphenanthrene |
50 | 2381-21-7 | 1-Methylpyrene |
51 | 5522-43-0 | 1-Nitropyrene |
---|---|---|
52 | 540-84-1 | 2,2,4-Trimethylpentane |
53 | 60851-34-5 | 2,3,4,6,7,8-Hexachlorodibenzofuran (HxCDF) |
54 | 58-90-2 | 2,3,4,6-Tetrachlorophenol |
55 | 57117-31-4 | 2,3,4,7,8-Pentachlorodibenzofuran (PeCDF) |
56 | 51207-31-9 | 2,3,7,8-Tetrachlorodibenzofuran (TcDF) |
57 | 1746-01-6 | 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) |
58 | 96-13-9 | 2,3-Dibromo-1-propanol |
59 | 95-95-4 | 2,4,5-Trichlorophenol |
60 | 88-06-2 | 2,4,6-Trichlorophenol |
61 | 53-19-0 | 2,4'-DDD (2,4'-dichlorodiphenyldichloroethane) |
62 | 3424-82-6 | 2,4'-DDE (2,4'-dichlorodiphenyldichloroethene) |
63 | 789-02-6 | 2,4'-DDT (2,4'-dichlorodiphenyltrichloroethane) |
64 | 615-05-4 | 2,4-Diaminoanisole |
65 | 39156-41-7 | 2,4-Diaminoanisole sulfate |
66 | 95-80-7 | 2,4-Diaminotoluene (2,4-toluene diamine) |
67 | 120-83-2 | 2,4-Dichlorophenol |
68 | 51-28-5 | 2,4-Dinitrophenol |
69 | 121-14-2 | 2,4-Dinitrotoluene |
70 | 606-20-2 | 2,6-Dinitrotoluene |
71 | 53-96-3 | 2-Acetylaminofluorene |
72 | 68006-83-7 | 2-Amino-3-methyl-9H pyrido[2,3-b]indole |
73 | 76180-96-6 | 2-Amino-3-methylimidazo-[4,5-f]quinoline |
74 | 712-68-5 | 2-Amino-5-(5-nitro-2-furyl)-1,3,4-thiadiazole |
75 | 117-79-3 | 2-Aminoanthraquinone |
76 | 78-93-3 | 2-Butanone (methyl ethyl ketone) |
77 | 532-27-4 | 2-Chloroacetophenone |
78 | 95-57-8 | 2-Chlorophenol |
79 | 91-57-6 | 2-Methyl naphthalene |
80 | 129-15-7 | 2-Methyl-1-nitroanthraquinone |
81 | 75-86-5 | 2-Methyllactonitrile (acetone cyanohydrin) |
82 | 109-06-8 | 2-Methylpyridine |
83 | 91-59-8 | 2-Naphthylamine |
84 | 607-57-8 | 2-Nitrofluorene |
85 | 79-46-9 | 2-Nitropropane |
86 | 90-43-7 | 2-Phenylphenol |
87 | 91-94-1 | 3,3'-Dichlorobenzidine |
88 | 119-90-4 | 3,3'-Dimethoxybenzidine |
89 | 119-93-7 | 3,3'-Dimethylbenzidine (o-tolidine) |
90 | 6109-97-3 | 3-Amino-9-ethylcarbazole hydrochloride |
91 | 563-47-3 | 3-Chloro-2-methyl-1-propene |
92 | 56-49-5 | 3-Methylcholanthrene |
93 | 72-54-8 | 4,4'-DDD (4,4'-dichlorodiphenyldichloroethane) |
94 | 72-55-9 | 4,4'-DDE (4,4'-dichlorodiphenyldichloroethene) |
95 | 101-80-4 | 4,4'-Diaminodiphenyl ether |
96 | 80-05-7 | 4,4'-Isopropylidenediphenol (bisphenol A) |
97 | 101-14-4 | 4,4'-Methylene bis(2-chloroaniline) (MOCA) |
98 | 838-88-0 | 4,4'-Methylene bis(2-methylaniline) |
99 | 101-61-1 | 4,4'-Methylene bis(N,N'-dimethyl)aniline |
100 | 101-77-9 | 4,4'-Methylenedianiline (and its dichloride) |
101 | 13552-44-8 | 4,4'-Methylenedianiline dihydrochloride |
---|---|---|
102 | 139-65-1 | 4,4'-Thiodianiline |
103 | 534-52-1 | 4,6-Dinitro-o-cresol (and salts) |
104 | 92-67-1 | 4-Aminobiphenyl |
105 | 95-83-0 | 4-Chloro-o-phenylenediamine |
106 | 60-11-7 | 4-Dimethylaminoazobenzene |
107 | 92-93-3 | 4-Nitrobiphenyl |
108 | 100-02-7 | 4-Nitrophenol |
109 | 57835-92-4 | 4-Nitropyrene |
110 | 104-40-5 | 4-Nonylphenol (and ethoxylates) |
111 | 100-40-3 | 4-Vinylcyclohexene |
112 | 3697-24-3 | 5-Methylchrysene |
113 | 602-87-9 | 5-Nitroacenaphthene |
114 | 99-59-2 | 5-Nitro-o-anisidine |
115 | 7496-02-8 | 6-Nitrochrysene |
116 | 57-97-6 | 7,12-Dimethylbenz[a]anthracene |
117 | 194-59-2 | 7H-Dibenzo[c,g]carbazole |
118 | 26148-68-5 | A-alpha-c(2-amino-9h-pyrido[2,3-b]indole) |
119 | 83-32-9 | Acenaphthene |
120 | 208-96-8 | Acenaphthylene |
121 | 75-07-0 | Acetaldehyde |
122 | 60-35-5 | Acetamide |
123 | 67-64-1 | Acetone |
124 | 75-05-8 | Acetonitrile |
125 | 98-86-2 | Acetophenone |
126 | 107-02-8 | Acrolein |
127 | 79-06-1 | Acrylamide |
128 | 79-10-7 | Acrylic acid |
129 | 107-13-1 | Acrylonitrile |
130 | 50-76-0 | Actinomycin D |
131 | 1596-84-5 | Alar |
132 | 309-00-2 | Aldrin |
133 | 107-05-1 | Allyl chloride |
134 | 319-84-6 | alpha-Hexachlorocyclohexane |
135 | 7429-90-5 | Aluminum and compounds |
136 | 1344-28-1 | Aluminum oxide (fibrous forms) |
137 | 61-82-5 | Amitrole |
138 | 7664-41-7 | Ammonia |
139 | 7803-63-6 | Ammonium bisulfate |
140 | 6484-52-2 | Ammonium nitrate |
141 | 7783-20-2 | Ammonium sulfate |
142 | 62-53-3 | Aniline |
143 | 191-26-4 | Anthanthrene |
144 | 120-12-7 | Anthracene |
145 | 7440-36-0 | Antimony and compounds |
146 | 1309-64-4 | Antimony trioxide |
147 | 140-57-8 | Aramite |
148 | 7440-38-2 | Arsenic and compounds |
149 | 7784-42-1 | Arsine |
150 | 1332-21-4 | Asbestos |
151 | 492-80-8 | Auramine |
---|---|---|
152 | 115-02-6 | Azaserine |
153 | 446-86-6 | Azathioprine |
154 | 103-33-3 | Azobenzene |
155 | 7440-39-3 | Barium and compounds |
156 | 56-55-3 | Benz[a]anthracene |
157 | 71-43-2 | Benzene |
158 | 92-87-5 | Benzidine (and its salts) |
159 | 50-32-8 | Benzo[a]pyrene |
160 | 205-99-2 | Benzo[b]fluoranthene |
161 | 205-12-9 | Benzo[c]fluorene |
162 | 192-97-2 | Benzo[e]pyrene |
163 | 191-24-2 | Benzo[g,h,i]perylene |
164 | 205-82-3 | Benzo[j]fluoranthene |
165 | 207-08-9 | Benzo[k]fluoranthene |
166 | 271-89-6 | Benzofuran |
167 | 98-07-7 | Benzoic trichloride (benzotrichloride) |
168 | 98-88-4 | Benzoyl chloride |
169 | 94-36-0 | Benzoyl peroxide |
170 | 100-44-7 | Benzyl chloride |
171 | 1694-09-3 | Benzyl Violet 4B |
172 | 7440-41-7 | Beryllium and compounds |
173 | 1304-56-9 | Beryllium oxide |
174 | 13510-49-1 | Beryllium sulfate |
175 | 3068-88-0 | beta-Butyrolactone |
176 | 319-85-7 | beta-Hexachlorocyclohexane |
177 | 57-57-8 | beta-Propiolactone |
178 | 92-52-4 | Biphenyl |
179 | 111-44-4 | bis(2-Chloroethyl) ether (BCEE) |
180 | 103-23-1 | bis(2-Ethylhexyl) adipate |
181 | 117-81-7 | bis(2-Ethylhexyl) phthalate (DEHP) |
182 | 542-88-1 | bis(Chloromethyl) ether |
183 | 7726-95-6 | Bromine and compounds |
184 | 7789-30-2 | Bromine pentafluoride |
185 | 75-27-4 | Bromodichloromethane |
186 | 75-25-2 | Bromoform |
187 | 74-83-9 | Bromomethane (methyl bromide) |
188 | 141-32-2 | Butyl acrylate |
189 | 85-68-7 | Butyl benzyl phthalate |
190 | 25013-16-5 | Butylated hydroxyanisole |
191 | 569-61-9 | C.I. Basic Red 9 monohydrochloride |
192 | 7440-43-9 | Cadmium and compounds |
193 | 156-62-7 | Calcium cyanamide |
194 | 105-60-2 | Caprolactam |
195 | 2425-06-1 | Captafol |
196 | 133-06-2 | Captan |
197 | 63-25-2 | Carbaryl |
198 | 86-74-8 | Carbazole |
199 | 89 | Carbon black extracts |
200 | 75-15-0 | Carbon disulfide |
201 | 56-23-5 | Carbon tetrachloride |
---|---|---|
202 | 463-58-1 | Carbonyl sulfide |
203 | 9000-07-1 | Carrageenan (degraded) |
204 | 120-80-9 | Catechol |
205 | 351 | Ceramic fibers |
206 | 133-90-4 | Chloramben |
207 | 305-03-3 | Chlorambucil |
208 | 57-74-9 | Chlordane |
209 | 143-50-0 | Chlordecone |
210 | 115-28-6 | Chlorendic acid |
211 | 76-13-1 | Chlorinated fluorocarbon (1,1,2-trichloro-1,2,2-trifluoroethane, CFC-113) |
212 | 108171-26-2 | Chlorinated paraffins |
213 | 7782-50-5 | Chlorine |
214 | 10049-04-4 | Chlorine dioxide |
215 | 79-11-8 | Chloroacetic acid |
216 | 85535-84-8 | Chloroalkanes C10-13 (chlorinated paraffins) |
217 | 108-90-7 | Chlorobenzene |
218 | 510-15-6 | Chlorobenzilate (ethyl-4,4'-dichlorobenzilate) |
219 | 75-45-6 | Chlorodifluoromethane (Freon 22) |
220 | 75-00-3 | Chloroethane (ethyl chloride) |
221 | 67-66-3 | Chloroform |
222 | 74-87-3 | Chloromethane (methyl chloride) |
223 | 107-30-2 | Chloromethyl methyl ether (technical grade) |
224 | 76-06-2 | Chloropicrin |
225 | 126-99-8 | Chloroprene |
226 | 1897-45-6 | Chlorothalonil |
227 | 54749-90-5 | Chlorozotocin |
228 | 7738-94-5 | Chromic(VI) acid, including chromic acid aerosol mist and chromium trioxide |
229 | 18540-29-9 | Chromium VI, chromate and dichromate particulate |
230 | 218-01-9 | Chrysene |
231 | 87-29-6 | Cinnamyl anthranilate |
232 | 7440-48-4 | Cobalt and compounds |
233 | 148 | Coke oven emissions |
234 | 7440-50-8 | Copper and compounds |
235 | 150 | Creosotes |
236 | 1319-77-3 | Cresols (mixture), including m-cresol, o-cresol, p-cresol |
237 | 4170-30-3 | Crotonaldehyde |
238 | 80-15-9 | Cumene hydroperoxide |
239 | 135-20-6 | Cupferron |
240 | 74-90-8 | Cyanide, hydrogen |
241 | 110-82-7 | Cyclohexane |
242 | 108-93-0 | Cyclohexanol |
243 | 66-81-9 | Cycloheximide |
244 | 27208-37-3 | Cyclopenta[c,d]pyrene |
245 | 50-18-0 | Cyclophosphamide (anhydrous) |
246 | 6055-19-2 | Cyclophosphamide (hydrated) |
247 | 5160-02-1 | D & C Red No. 9 |
248 | 4342-03-4 | Dacarbazine |
249 | 117-10-2 | Danthron (chrysazin) |
250 | 3547-04-4 | DDE (1-chloro-4-[1-(4-chlorophenyl)ethyl]benzene) |
251 | 50-29-3 | DDT |
---|---|---|
252 | 333-41-5 | Diazinon |
253 | 334-88-3 | Diazomethane |
254 | 226-36-8 | Dibenz[a,h]acridine |
255 | 53-70-3 | Dibenz[a,h]anthracene |
256 | 224-42-0 | Dibenz[a,j]acridine |
257 | 5385-75-1 | Dibenzo[a,e]fluoranthene |
258 | 192-65-4 | Dibenzo[a,e]pyrene |
259 | 189-64-0 | Dibenzo[a,h]pyrene |
260 | 189-55-9 | Dibenzo[a,i]pyrene |
261 | 191-30-0 | Dibenzo[a,l]pyrene |
262 | 132-64-9 | Dibenzofuran |
263 | 124-48-1 | Dibromochloromethane |
264 | 84-74-2 | Dibutyl phthalate |
265 | 75-71-8 | Dichlorodifluoromethane (Freon 12) |
266 | 75-43-4 | Dichlorofluoromethane (Freon 21) |
267 | 75-09-2 | Dichloromethane (methylene chloride) |
268 | 94-75-7 | Dichlorophenoxyacetic acid, salts and esters (2,4-D) |
269 | 62-73-7 | Dichlorvos (DDVP) |
270 | 115-32-2 | Dicofol |
271 | 84-61-7 | Di-cyclohexyl phthalate (DCHP) |
272 | 60-57-1 | Dieldrin |
273 | 200 | Diesel particulate matter |
274 | 111-42-2 | Diethanolamine |
275 | 64-67-5 | Diethyl sulfate |
276 | 111-46-6 | Diethylene glycol |
277 | 111-96-6 | Diethylene glycol dimethyl ether |
278 | 112-34-5 | Diethylene glycol monobutyl ether |
279 | 111-90-0 | Diethylene glycol monoethyl ether |
280 | 111-77-3 | Diethylene glycol monomethyl ether |
281 | 627-44-1 | Diethylmercury |
282 | 84-66-2 | Diethylphthalate |
283 | 101-90-6 | Diglycidyl resorcinol ether |
284 | 94-58-6 | Dihydrosafrole |
285 | 79-44-7 | Dimethyl carbamoyl chloride |
286 | 68-12-2 | Dimethyl formamide |
287 | 131-11-3 | Dimethyl phthalate |
288 | 77-78-1 | Dimethyl sulfate |
289 | 593-74-8 | Dimethylmercury |
290 | 513-37-1 | Dimethylvinylchloride |
291 | 630-93-3 | Diphenylhydantoin |
292 | 25265-71-8 | Dipropylene glycol |
293 | 34590-94-8 | Dipropylene glycol monomethyl ether |
294 | 1937-37-7 | Direct Black 38 |
295 | 2602-46-2 | Direct Blue 6 |
296 | 16071-86-6 | Direct Brown 95 (technical grade) |
297 | 2475-45-8 | Disperse Blue 1 |
298 | 298-04-4 | Disulfoton |
299 | 106-89-8 | Epichlorohydrin |
300 | 227 | Epoxy resins |
301 | 12510-42-8 | Erionite |
---|---|---|
302 | 140-88-5 | Ethyl acrylate |
303 | 100-41-4 | Ethyl benzene |
304 | 74-85-1 | Ethylene |
305 | 106-93-4 | Ethylene dibromide (EDB, 1,2-dibromoethane) |
306 | 107-06-2 | Ethylene dichloride (EDC, 1,2-dichloroethane) |
307 | 107-21-1 | Ethylene glycol |
308 | 629-14-1 | Ethylene glycol diethyl ether |
309 | 110-71-4 | Ethylene glycol dimethyl ether |
310 | 111-76-2 | Ethylene glycol monobutyl ether |
311 | 110-80-5 | Ethylene glycol monoethyl ether |
312 | 111-15-9 | Ethylene glycol monoethyl ether acetate |
313 | 109-86-4 | Ethylene glycol monomethyl ether |
314 | 110-49-6 | Ethylene glycol monomethyl ether acetate |
315 | 2807-30-9 | Ethylene glycol monopropyl ether |
316 | 75-21-8 | Ethylene oxide |
317 | 96-45-7 | Ethylene thiourea |
318 | 151-56-4 | Ethyleneimine (aziridine) |
319 | 10028-22-5 | Ferric sulfate |
320 | 206-44-0 | Fluoranthene |
321 | 86-73-7 | Fluorene |
322 | 239 | Fluorides |
323 | 7782-41-4 | Fluorine gas |
324 | 50-00-0 | Formaldehyde |
325 | 110-00-9 | Furan |
326 | 60568-05-0 | Furmecyclox |
327 | 3688-53-7 | Furylfuramide |
328 | 58-89-9 | gamma-Hexachlorocyclohexane (Lindane) |
329 | 352 | Glasswool fibers |
330 | 67730-11-4 | Glu-P-1 |
331 | 67730-10-3 | Glu-P-2 |
332 | 111-30-8 | Glutaraldehyde |
333 | 16568-02-8 | Gyromitrin |
334 | 2784-94-3 | HC Blue 1 |
335 | 76-44-8 | Heptachlor |
336 | 1024-57-3 | Heptachlor epoxide |
337 | 118-74-1 | Hexachlorobenzene |
338 | 87-68-3 | Hexachlorobutadiene |
339 | 608-73-1 | Hexachlorocyclohexanes (mixture) including but not limited to: |
340 | 77-47-4 | Hexachlorocyclopentadiene |
341 | 67-72-1 | Hexachloroethane |
342 | 822-06-0 | Hexamethylene-1,6-diisocyanate |
343 | 680-31-9 | Hexamethylphosphoramide |
344 | 110-54-3 | Hexane |
345 | 302-01-2 | Hydrazine |
346 | 10034-93-2 | Hydrazine sulfate |
347 | 7647-01-0 | Hydrochloric acid |
348 | 10035-10-6 | Hydrogen bromide |
349 | 7664-39-3 | Hydrogen fluoride |
350 | 7783-06-4 | Hydrogen sulfide |
351 | 123-31-9 | Hydroquinone |
---|---|---|
352 | 193-39-5 | Indeno[1,2,3-cd]pyrene |
353 | 10043-66-0 | Iodine-131 |
354 | 13463-40-6 | Iron pentacarbonyl |
355 | 78-59-1 | Isophorone |
356 | 78-79-5 | Isoprene, except from vegetative emission sources |
357 | 67-63-0 | Isopropyl alcohol |
358 | 98-82-8 | Isopropylbenzene (cumene) |
359 | 303-34-4 | Lasiocarpine |
360 | 7439-92-1 | Lead and compounds |
361 | 18454-12-1 | Lead chromate oxide |
362 | 108-31-6 | Maleic anhydride |
363 | 7439-96-5 | Manganese and compounds |
364 | 108-39-4 | m-Cresol |
365 | 148-82-3 | Melphalan |
366 | 3223-07-2 | Melphalan HCl |
367 | 7439-97-6 | Mercury and compounds |
368 | 67-56-1 | Methanol |
369 | 72-43-5 | Methoxychlor |
370 | 60-34-4 | Methyl hydrazine |
371 | 74-88-4 | Methyl iodide (iodomethane) |
372 | 108-10-1 | Methyl isobutyl ketone (MIBK, hexone) |
373 | 624-83-9 | Methyl isocyanate |
374 | 80-62-6 | Methyl methacrylate |
375 | 66-27-3 | Methyl methanesulfonate |
376 | 1634-04-4 | Methyl tert-butyl ether |
377 | 101-68-8 | Methylene diphenyl diisocyanate (MDI) |
378 | 22967-92-6 | Methylmercury |
379 | 56-04-2 | Methylthiouracil |
380 | 90-94-8 | Michler's ketone |
381 | 349 | Mineral fiber emissions from facilities manufacturing or processing glass, rock, or slag fibers (or other mineral derived fibers) of average diameter 1 micrometer or less. |
382 | 350 | Mineral fibers (fine mineral fibers which are man-made, and are airborne particles of a respirable size greater than 5 microns in length, less than or equal to 3.5 microns in diameter, with a length to diameter ratio of 3:1) |
383 | 2385-85-5 | Mirex |
384 | 50-07-7 | Mitomycin C |
385 | 1313-27-5 | Molybdenum trioxide |
386 | 315-22-0 | Monocrotaline |
387 | 108-38-3 | m-Xylene |
388 | 134-62-3 | N,N-Diethyltoluamide (DEET) |
389 | 121-69-7 | N,N-Dimethylaniline |
390 | 531-82-8 | N-[4-(5-Nitro-2-furyl)-2-thiazolyl]-acetamide |
391 | 91-20-3 | Naphthalene |
392 | 71-36-3 | n-Butyl alcohol |
393 | 373-02-4 | Nickel acetate |
394 | 7440-02-0 | Nickel and compounds |
395 | 3333-67-3 | Nickel carbonate |
396 | 12607-70-4 | Nickel carbonate hydroxide |
397 | 13463-39-3 | Nickel carbonyl |
398 | 7718-54-9 | Nickel chloride |
399 | 365 | Nickel compounds, insoluble |
400 | 368 | Nickel compounds, soluble |
401 | 12054-48-7 | Nickel hydroxide |
---|---|---|
402 | 13478-00-7 | Nickel nitrate hexahydrate |
403 | 1313-99-1 | Nickel oxide |
404 | 12035-72-2 | Nickel subsulfide |
405 | 7786-81-4 | Nickel sulfate |
406 | 10101-97-0 | Nickel sulfate hexahydrate |
407 | 11113-75-0 | Nickel sulfide |
408 | 1271-28-9 | Nickelocene |
409 | 3570-75-0 | Nifurthiazole |
410 | 7697-37-2 | Nitric acid |
411 | 139-13-9 | Nitrilotriacetic acid |
412 | 18662-53-8 | Nitrilotriacetic acid, trisodium salt monohydrate |
413 | 98-95-3 | Nitrobenzene |
414 | 1836-75-5 | Nitrofen |
415 | 59-87-0 | Nitrofurazone |
416 | 302-70-5 | Nitrogen mustard N-oxide |
417 | 70-25-7 | N-Methyl-N-nitro-N-nitrosoguanidine |
418 | 1116-54-7 | N-Nitrosodiethanolamine |
419 | 55-18-5 | N-Nitrosodiethylamine |
420 | 62-75-9 | N-Nitrosodimethylamine |
421 | 924-16-3 | N-Nitrosodi-n-butylamine |
422 | 86-30-6 | N-Nitrosodiphenylamine |
423 | 621-64-7 | N-Nitrosodipropylamine |
424 | 10595-95-6 | N-Nitrosomethylethylamine |
425 | 59-89-2 | N-Nitrosomorpholine |
426 | 759-73-9 | N-Nitroso-N-ethylurea |
427 | 684-93-5 | N-Nitroso-N-methylurea |
428 | 615-53-2 | N-Nitroso-N-methylurethane |
429 | 16543-55-8 | N-Nitrosonornicotine |
430 | 100-75-4 | N-Nitrosopiperidine |
431 | 930-55-2 | N-Nitrosopyrrolidine |
432 | 90-04-0 | o-Anisidine |
433 | 134-29-2 | o-Anisidine hydrochloride |
434 | 95-48-7 | o-Cresol |
435 | 39001-02-0 | Octachlorodibenzofuran (OCDF) |
436 | 3268-87-9 | Octachlorodibenzo-p-dioxin (OCDD) |
437 | 8014-95-7 | Oleum (fuming sulfuric acid) |
438 | 132-27-4 | o-Phenylphenate, sodium |
439 | 97-56-3 | ortho-Aminoazotoluene |
440 | 95-53-4 | o-Toluidine |
441 | 636-21-5 | o-Toluidine hydrochloride |
442 | 95-47-6 | o-Xylene |
443 | 56-38-2 | Parathion |
444 | 189084-64-8 | PBDE-100 [2,2’,4,4’,6-pentabromodiphenyl ether] |
445 | 182677-30-1 | PBDE-138 [2,2’,3,4,4’,5’-hexabromodiphenyl ether] |
446 | 68631-49-2 | PBDE-153 [2,2',4,4',5,5'-hexabromodiphenyl ether] |
447 | 207122-15-4 | PBDE-154 [2,2’,4,4’,5,6’-hexabromodiphenyl ether] |
448 | 207122-16-5 | PBDE-183 [2,2',3,4,4',5',6-heptabromodiphenyl ether] |
449 | 1163-19-5 | PBDE-209 [decabromodiphenyl ether] |
450 | 5436-43-1 | PBDE-47 [2,2',4,4'-tetrabromodiphenyl ether] |
451 | 60348-60-9 | PBDE-99 [2,2’,4,4’,5-pentabromodiphenyl ether] |
---|---|---|
452 | 32598-14-4 | PCB 105 [2,3,3',4,4'-pentachlorobiphenyl] |
453 | 74472-37-0 | PCB 114 [2,3,4,4',5-pentachlorobiphenyl] |
454 | 31508-00-6 | PCB 118 [2,3',4,4',5-pentachlorobiphenyl] |
455 | 65510-44-3 | PCB 123 [2,3',4,4',5'-pentachlorobiphenyl] |
456 | 57465-28-8 | PCB 126 [3,3',4,4',5-pentachlorobiphenyl] |
457 | 38380-08-4 | PCB 156 [2,3,3',4,4',5-hexachlorobiphenyl] |
458 | 69782-90-7 | PCB 157 [2,3,3',4,4',5'-hexachlorobiphenyl] |
459 | 52663-72-6 | PCB 167 [2,3',4,4',5,5'-hexachlorobiphenyl] |
460 | 32774-16-6 | PCB 169 [3,3',4,4',5,5'-hexachlorobiphenyl] |
461 | 37680-65-2 | PCB 18 [2,2',5-trichlorobiphenyl] |
462 | 39635-31-9 | PCB 189 [2,3,3',4,4',5,5'-heptachlorobiphenyl] |
463 | 32598-13-3 | PCB 77 [3,3',4,4'-tetrachlorobiphenyl] |
464 | 70362-50-4 | PCB 81 [3,4,4',5-tetrachlorobiphenyl] |
465 | 37680-73-2 | PCB-101 [2,2',4,5,5'-pentachlorobiphenyl] |
466 | 38380-07-3 | PCB-128 [2,2',3,3',4,4'-hexachlorobiphenyl] |
467 | 35065-28-2 | PCB-138 [2,2',3,4,4',5'-hexachlorobiphenyl] |
468 | 35065-27-1 | PCB-153 [2,2',4,4',5,5'-hexachlorobiphenyl] |
469 | 35065-30-6 | PCB-170 [2,2',3,3',4,4',5-heptachlorobiphenyl] |
470 | 35065-29-3 | PCB-180 [2,2',3,4,4',5,5'-heptachlorobiphenyl] |
471 | 52663-68-0 | PCB-187 [2,2',3,4',5,5',6-heptachlorobiphenyl] |
472 | 52663-78-2 | PCB-195 [2,2',3,3',4,4',5,6-octachlorobiphenyl] |
473 | 40186-72-9 | PCB-206 [2,2',3,3',4,4',5,5',6-nonachlorobiphenyl] |
474 | 2051-24-3 | PCB-209 [decachlorobiphenyl] |
475 | 7012-37-5 | PCB-28 [2,4,4'-trichlorobiphenyl] |
476 | 41464-39-5 | PCB-44 [2,2',3,5'-tetrachlorobiphenyl] |
477 | 35693-99-3 | PCB-52 [2,2',5,5'-tetrachlorobiphenyl] |
478 | 32598-10-0 | PCB-66 [2,3',4,4'-tetrachlorobiphenyl] |
479 | 34883-43-7 | PCB-8 [2,4'-dichlorobiphenyl] |
480 | 106-47-8 | p-Chloroaniline |
481 | 95-69-2 | p-Chloro-o-toluidine |
482 | 120-71-8 | p-Cresidine |
483 | 106-44-5 | p-Cresol |
484 | 106-46-7 | p-Dichlorobenzene (1,4-dichlorobenzene) |
485 | 32534-81-9 | Pentabromodiphenyl ether |
486 | 82-68-8 | Pentachloronitrobenzene (quintobenzene) |
487 | 87-86-5 | Pentachlorophenol |
488 | 79-21-0 | Peracetic acid |
489 | 489 | Perfluorinated compounds (PFCs) |
490 | 1763-23-1 | Perfluorooctanesulfonic acid (PFOS) |
491 | 335-67-1 | Perfluorooctanoic acid (PFOA) |
492 | 198-55-0 | Perylene |
493 | 62-44-2 | Phenacetin |
494 | 85-01-8 | Phenanthrene |
495 | 94-78-0 | Phenazopyridine |
496 | 136-40-3 | Phenazopyridine hydrochloride |
497 | 3546-10-9 | Phenesterin |
498 | 50-06-6 | Phenobarbital |
499 | 108-95-2 | Phenol |
500 | 59-96-1 | Phenoxybenzamine |
501 | 63-92-3 | Phenoxybenzamine hydrochloride |
---|---|---|
502 | 75-44-5 | Phosgene |
503 | 7803-51-2 | Phosphine |
504 | 7664-38-2 | Phosphoric acid |
505 | 504 | Phosphorus and compounds |
506 | 10025-87-3 | Phosphorus oxychloride |
507 | 10026-13-8 | Phosphorus pentachloride |
508 | 1314-56-3 | Phosphorus pentoxide |
509 | 7719-12-2 | Phosphorus trichloride |
510 | 12185-10-3 | Phosphorus, white |
511 | 518 | Phthalates |
512 | 85-44-9 | Phthalic anhydride |
513 | 156-10-5 | p-Nitrosodiphenylamine |
514 | 447 | Polybrominated diphenyl ethers (PBDEs) |
515 | 1336-36-3 | Polychlorinated biphenyls (PCBs) |
516 | 645 | Polychlorinated biphenyls (PCBs) TEQ |
517 | 646 | Polychlorinated dibenzo-p-dioxins (PCDDs) & dibenzofurans (PCDFs) TEQ |
518 | 432 | Polycyclic aromatic hydrocarbon derivatives [PAH-Derivatives] |
519 | 401 | Polycyclic aromatic hydrocarbons (PAHs) |
520 | 3564-09-8 | Ponceau 3R |
521 | 3761-53-3 | Ponceau MX |
522 | 7758-01-2 | Potassium bromate |
523 | 106-50-3 | p-Phenylenediamine |
524 | 671-16-9 | Procarbazine |
525 | 366-70-1 | Procarbazine hydrochloride |
526 | 123-38-6 | Propionaldehyde |
527 | 114-26-1 | Propoxur (Baygon) |
528 | 115-07-1 | Propylene |
529 | 6423-43-4 | Propylene glycol dinitrate |
530 | 107-98-2 | Propylene glycol monomethyl ether |
531 | 108-65-6 | Propylene glycol monomethyl ether acetate |
532 | 75-56-9 | Propylene oxide |
533 | 51-52-5 | Propylthiouracil |
534 | 106-42-3 | p-Xylene |
535 | 129-00-0 | Pyrene |
536 | 110-86-1 | Pyridine |
537 | 91-22-5 | Quinoline |
538 | 106-51-4 | Quinone |
539 | 571 | Radon and its decay products |
540 | 572 | Refractory ceramic fibers |
541 | 50-55-5 | Reserpine |
542 | 353 | Rockwool |
543 | 94-59-7 | Safrole |
544 | 78-92-2 | sec-Butyl alcohol |
545 | 7783-07-5 | Selenide, hydrogen |
546 | 7782-49-2 | Selenium and compounds |
547 | 7446-34-6 | Selenium sulfide |
548 | 7631-86-9 | Silica, crystalline (respirable) |
549 | 7440-22-4 | Silver and compounds |
550 | 354 | Slagwool |
551 | 1310-73-2 | Sodium hydroxide |
---|---|---|
552 | 10048-13-2 | Sterigmatocystin |
553 | 18883-66-4 | Streptozotocin |
554 | 100-42-5 | Styrene |
555 | 96-09-3 | Styrene oxide |
556 | 95-06-7 | Sulfallate |
557 | 505-60-2 | Sulfur mustard |
558 | 7446-11-9 | Sulfur trioxide |
559 | 7664-93-9 | Sulfuric acid |
560 | 358 | Talc containing asbestiform fibers |
561 | 540-88-5 | t-Butyl acetate |
562 | 100-21-0 | Terephthalic acid |
563 | 75-65-0 | tert-Butyl alcohol |
564 | 40088-47-9 | Tetrabromodiphenyl ether |
565 | 127-18-4 | Tetrachloroethene (perchloroethylene) |
566 | 7440-28-0 | Thallium and compounds |
567 | 62-55-5 | Thioacetamide |
568 | 62-56-6 | Thiourea |
569 | 7550-45-0 | Titanium tetrachloride |
570 | 108-88-3 | Toluene |
571 | 26471-62-5 | Toluene diisocyanates (2,4- and 2,6-) |
572 | 584-84-9 | Toluene-2,4-diisocyanate |
573 | 91-08-7 | Toluene-2,6-diisocyanate |
574 | 38998-75-3 | Total heptachlorodibenzofuran |
575 | 37871-00-4 | Total heptachlorodibenzo-p-dioxin |
576 | 55684-94-1 | Total hexachlorodibenzofuran |
577 | 34465-46-8 | Total hexachlorodibenzo-p-dioxin |
578 | 30402-15-4 | Total pentachlorodibenzofuran |
579 | 36088-22-9 | Total pentachlorodibenzo-p-dioxin |
580 | 55722-27-5 | Total tetrachlorodibenzofuran |
581 | 41903-57-5 | Total tetrachlorodibenzo-p-dioxin |
582 | 8001-35-2 | Toxaphene (polychlorinated camphenes) |
583 | 156-60-5 | trans-1,2-Dichloroethene |
584 | 55738-54-0 | trans-2[(Dimethylamino)-methylimino]-5-[2-(5-nitro-2-furyl)-vinyl]-1,3,4-oxadiazole |
585 | 39765-80-5 | trans-Nonachlor |
586 | 126-73-8 | Tributyl phosphate |
587 | 79-01-6 | Trichloroethene (TCE, trichloroethylene) |
588 | 75-69-4 | Trichlorofluoromethane (Freon 11) |
589 | 78-40-0 | Triethyl phosphate |
590 | 121-44-8 | Triethylamine |
591 | 112-49-2 | Triethylene glycol dimethyl ether |
592 | 1582-09-8 | Trifluralin |
593 | 512-56-1 | Trimethyl phosphate |
594 | 78-30-8 | Triorthocresyl phosphate |
595 | 115-86-6 | Triphenyl phosphate |
596 | 101-02-0 | Triphenyl phosphite |
597 | 52-24-4 | tris-(1-Aziridinyl)phosphine sulfide |
598 | 126-72-7 | tris(2,3-Dibromopropyl)phosphate |
599 | 62450-06-0 | Tryptophan-P-1 |
600 | 62450-07-1 | Tryptophan-P-2 |
601 | 51-79-6 | Urethane (ethyl carbamate) |
---|---|---|
602 | 7440-62-2 | Vanadium (fume or dust) |
603 | 1314-62-1 | Vanadium pentoxide |
604 | 108-05-4 | Vinyl acetate |
605 | 593-60-2 | Vinyl bromide |
606 | 75-01-4 | Vinyl chloride |
607 | 75-02-5 | Vinyl fluoride |
608 | 75-35-4 | Vinylidene chloride |
609 | 1330-20-7 | Xylene (mixture), including m-xylene, o-xylene, p-xylene |
610 | 7440-66-6 | Zinc and compounds |
611 | 1314-13-2 | Zinc oxide |