State of Oregon

Department of Environmental Quality  Memorandum

 

Date:  March 17, 2011

 

To:    Environmental Quality Commission

 

From:    Dick Pedersen, Director

 

Subject:  Agenda item X, Rule adoption: Amending water quality standards for arsenic

   April 21, 2011, EQC meeting

 

 

Why this is important

 

This rule amendment revises Oregon’s water quality criteria for arsenic and adds an arsenic reduction policy.

 

DEQ recommendation and EQC motion

 

The Department of Environmental Quality recommends that the commission amend Oregon’s water quality standards for arsenic as presented in attachment A, including revisions to the numeric arsenic criteria and adoption of an arsenic reduction policy. DEQ also recommends that the amendments not become applicable under state law under the criteria are approved by EPA and become effective under the federal Clean Water Act.

 

Background and need for rulemaking

 

The commission adopted the current arsenic criteria in the late 1980s when it adopted all of Environmental Protection Agency’s 1986 recommended toxics criteria. In response to public comment in October 2008, EQC directed DEQ to review the science behind the human health criteria for naturally occurring metals. DEQ’s review, which is summarized in attachment D, led to this proposed rule amendment. DEQ also recommended revisions to the human health criteria for iron and manganese, which the EQC adopted in December 2010.

 

Oregon’s current human health criteria for arsenic are not attainable in many Oregon waters, due at least in part to natural sources. Trying to implement criteria that are below natural background levels can result in costs to the state and regulated entities without yielding meaningful environmental results such as measurably reduced instream concentrations. The human health risks associated with natural arsenic concentrations are not new; they have been present since people have drunk water and eaten fish from Oregon streams.

 

Affected parties requested that DEQ revise the arsenic, iron and manganese criteria through a separate rulemaking more quickly than the larger human health toxics and implementation tools rulemaking process. The commission adopted iron and manganese revisions in December 2010. DEQ delayed the arsenic rulemaking to allow time to receive additional public comment and to consider and respond to the comments, which are now done. DEQ expects that several NPDES discharge permits due for renewal in the near future will need to consider limits for arsenic, and consequently, would use these revised criteria in determining whether limits are necessary and developing any subsequent limits.

Effect of rule

 

The rule amendment revises the numeric arsenic human health criteria as shown in the table below and adds a new arsenic reduction policy to the water quality standards rules. The changes are shown in attachment A as redline/strikeout changes to OAR 340-041-0033 and Table 20 for the arsenic criteria.

 

Human Health Criteria for Arsenic (µg/l)

 

Water + Fish Ingestion

Fish Consumption Only - Freshwater

Fish Consumption Only - Saltwater

Current criteria

(total arsenic)

 

0.0022

 

0.0175 a

 

0.0175

Criteria proposed Aug 2010

(inorganic arsenic)

 

2.3

 

2.7a

 

none

Recommended criteria

(inorganic arsenic)

 

2.1

 

2.1

 

1.0

 

a The current and initially proposed fish consumption only criteria applied to all waters.

 

The arsenic reduction policy requires industrial dischargers within proximity to drinking water sources that discharge arsenic to develop arsenic reduction plans under certain conditions. The objective of the policy is to minimize human health risk associated with human sources of arsenic to the extent feasible where background arsenic concentrations are lower than the numeric criteria. The policy targets potential risks to drinking water supplies because the water + fish ingestion criterion is based on a 10-4 risk level, which is greater than the risk level used for other human health criteria.

 

Commission authority

 

The commission has authority to take this action under ORS 468.020, 468B.010 and 468B.035.

Stakeholder involvement

 

During DEQ’s arsenic criteria, DEQ informed and obtained input from the Toxics Standards Rulemaking Workgroup, a stakeholder committee that DEQ assembled to provide input on the toxics standards rulemaking. The membership of this group is provided in the issue paper in attachment D. DEQ discussed the issue paper findings and its recommendations with the rulemaking workgroup prior to the formal public comment period and the group supported DEQ’s recommendations at that time.

 

Public comment

 

DEQ accepted public comment from Aug. 25 to Sept. 30, 2010, and held public hearings in Portland and Pendleton. DEQ then invited additional public comment on the proposed rule, including revised proposed numeric criteria, from Feb. 1 to 23, 2011. A summary and response to public comment is provided in attachment B; hearing reports are provided in attachment C. DEQ received comments from 28 individuals or organizations. The comments present a variety of perspectives. Overall, commenters support adopting less stringent criteria together with an arsenic reduction policy. Commenters from areas of the state with background arsenic concentrations that are higher than the proposed criteria, however, expressed concerns that the criteria do not adequately account for the conditions of their waters. The issues are summarized in the following “Key issues” section and in further detail in the Summary and Response to Comment in attachment B.

 

Key issues

1. An important objective of DEQ’s water quality toxics standards work has been to meet the EQC’s goals to protect public health, reduce toxic pollutants and achieve meaningful environmental results for the costs expended. The proposed rule amendments for arsenic are an incremental step toward meeting this goal.

 

2. DEQ must ensure that Oregon’s water quality criteria are based on relevant and available science. The recommended arsenic criteria are based on EPA’s human health toxics criteria calculation method with several adjusted factors to make the criteria more appropriate for Oregon:

 the fish consumption rate (based on 175 grams per day),

 the bioconcentration factor (a factor describing how much of a pollutant goes from the water column into fish tissue),

 an inorganic proportion factor (a factor describing how much of the arsenic accumulation in fish tissue is inorganic arsenic, arsenic’s most toxic form) and

 the cancer risk level.

DEQ used up-to-date data, information, and studies to determine the values of the factors used. The arsenic issue paper provided as attachment D contains detailed discussion of DEQ’s evaluation of the scientific information and rationale used to derive the recommended criteria. Key aspects of DEQ’s approach are summarized below relative to the fish consumption rate and the bioconcentration factor.

 

Fish consumption rate. The proposed arsenic criteria are based on a fish consumption rate of 175 grams per day. The current arsenic criteria are based on a rate of 6.5 g/d. This increased consumption rate has been the subject of substantial review and public debate. The EQC directed DEQ to use this rate as the basis for developing human health toxics criteria in October 2008. Using a rate of 175 g/d protects the ability of Oregonians to consume fish and shellfish on a regular basis without incurring unacceptable health risk.

 

Bioconcentration factor (BCF). The current arsenic criteria are based on a BCF of 44. DEQ used a BCF of 1 in its initial proposal based on an approach other states’ used to develop arsenic criteria. Based on public comment that additional data should be considered, including saltwater species, DEQ did further review of the available science and used additional BCF data. After the additional review, DEQ developed proposed criteria based on a BCF of 14 for the freshwater criteria and a BCF of 26 for the saltwater criterion. Rather than having one set of criteria that apply to both fresh and salt waters, the proposed criteria reflect the significantly higher bioconcentration rates of mollusks. The saltwater criterion incorporates the high bioconcentration rates of mollusks because people do eat marine mollusks, such as oysters and clams, and the freshwater criteria are based on the bioconcentration rates of finfish. DEQ has no data indicating that people in Oregon eat mollusks from fresh water.

 

3. DEQ’s proposed arsenic criteria are based on higher cancer risk levels than DEQ generally uses for criteria or risk assessment. DEQ uses a risk level of 1×10-6 for all the other current and proposed water quality toxics criteria. DEQ proposes a 1×10-4 risk level for the water + fish ingestion criterion and a 1.1×10-5 risk level for the fish consumption only criteria. The proposed criteria represent an appropriate balance of human health protection and recognition that arsenic is present in Oregon waters from natural sources in the range of concentrations associated with these risk levels due to the state’s geology and soils. The human health risk associated with natural arsenic levels has been present since people have been drinking water and eating fish from Oregon streams. Also, natural sources of arsenic cannot be practicably controlled. To list streams as impaired and develop TMDLs in these circumstances is not a wise use of public resources. According to EPA guidance, a higher risk level (up to 10-4) is acceptable when paired with a fish consumption rate that represents subsistence level consumption rather than the per capita consumption of the general population. See additional discussion in the issue paper in attachment D.

 

4. The recommended freshwater criteria are 2.1µg/l. While this is much less stringent than the current criteria, there are waters in the state with higher natural arsenic concentrations, particularly in areas of eastern and southern Oregon. Cities and others from these areas have expressed great concern that they will not be able to meet the new criteria and that the implementation tools that will be available to them will be costly and achieve to resulting water quality improvement but rather will be just a “paper exercise.” DEQ acknowledges the validity of these concerns and will work with these communities to identify appropriate solutions, whether that is to adopt site specific criteria or use a permitting tool. In some cases, it may mean removing drinking water supply as a designated beneficial use. In the meantime, it is DEQ’s priority to move ahead with adoption of the revised statewide criteria.

 

5. DEQ recommends an arsenic reduction policy to minimize human health risk associated with anthropogenic sources of arsenic. Where water bodies in Oregon have background levels below the proposed criteria, members of the stakeholder workgroup suggested that further anthropogenic loading to waters be limited in order to minimize any added risk from arsenic. The arsenic reduction policy will require dischargers on these water bodies that have the potential to impact a drinking water supply to develop an arsenic reduction plan and take feasible steps to reduce their arsenic loading. The policy targets individual industrial NPDES permit holders because municipalities are subject to similar requirements under SB737. The arsenic reduction policy includes a policy statement that nonpoint sources activities should also reduce inputs of inorganic arsenic to streams through erosion and runoff. Additional discussion of the arsenic reduction policy is provided in the issue paper in attachment D.

 

Next steps

If adopted by the commission, the rule amendments will be filed with the Secretary of State and submitted to EPA for approval.

 

DEQ proposes that the criteria revisions and the arsenic reduction policy not be applicable under state until the criteria are approved by EPA and effective under federal law and we have included language to the arsenic reduction policy to this effect. Once EPA approves the criteria, DEQ will post an updated Table 20 on DEQ’s website where it is available to the public. In addition, standards program staff will notify all DEQ staff and managers that implement water quality standards of the rule change.

 

DEQ will need to develop internal guidance for permit writers on how to implement the arsenic reduction policy for industrial dischargers. Finally, DEQ will need to communicate the EQC’s policy on arsenic reduction to other state agencies and federal land managers.

 

Attachments

A. Proposed rule revisions (OAR 340-041-0033)

B. Proposed criteria revisions (Table 20)

C. Summary of public comments and agency responses

D. Presiding Officer’s report on public hearings

E. Water Quality Standards Review and Recommendations: Arsenic

(Arsenic Issue Paper).

F. Statement of Need and Fiscal and Economic Impact and Addendum

 

Available upon request

1.  Relationship to Federal Requirements questions

2.  Land Use Evaluation Statement

3.  Legal notice of hearing

4.  Cover memorandum from public notice

5.  Written comment received

6.  Rule implementation plan

 
   

 

 

 Approved:

 

   Division: ____________________________

 

 

   Section: ____________________________

 

       Report Prepared By:  Debra Sturdevant

       Phone: 503-229-6691