TITLE 9. ENVIRONMENT
TITLE 9. ENVIRONMENT
STATE WATER CONTROL BOARD
Proposed Regulation
Title of Regulation: 9VAC25-260. Water Quality Standards (amending 9VAC25-260-310, 9VAC25-260-490).
Statutory Authority: § 62.1-44.15 of the Code of Virginia; 33 USC § 1251 et seq.; 40 CFR 131.
Public Hearing Information:
November 14, 2024 - 9:30 a.m. - Buchanan County Public Library, 1185 Poe Town Street, Grundy, VA 24614.
Public Comment Deadline: December 6, 2024.
Agency Contact: David Whitehurst, Water Quality Standards Coordinator, Department of Environmental Quality, 1111 East Main Street, Suite 1400, P.O. Box 1105, Richmond, VA 23218, telephone (804) 774-9180, or email david.whitehurst@deq.virginia.gov.
Basis: Section 62.1-44.2 requires the protection and restoration of the quality of state waters, safeguarding clean waters from pollution, prevention and reduction of pollution, and promotion of water conservation. Section 62.1-44.15 also requires the board to establish standards of quality consistent with its purpose and to modify, amend, or cancel any such standards or policies. 40 CFR 131 authorizes requirements and procedures for developing, reviewing, revising, and approving water quality standards by the states as authorized by § 303(c) of the Clean Water Act and requires the states to adopt criteria to protect designated uses.
Purpose: The purpose of the proposed amendments is to establish site-specific selenium aquatic life criteria that protect designated and beneficial uses of state waters by amending the regulation to be technically correct and reasonable. The proposed criteria are for the protection of aquatic life and are only indirectly related to the health, safety, and welfare of citizens. Proper water quality standards protect water quality and living resources of Virginia's waters for the designated uses of aquatic life, wildlife, recreation, public water supply, shellfish consumption, and fish consumption.
Substance: The proposed amendments include a site-specific freshwater aquatic life selenium criterion in 9VAC25-260-310 for several tributaries to Knox Creek in Buchanan County. Those tributaries are Race Fork and tributaries, Pounding Mill Creek and tributaries, Right Fork of Lester Fork and tributaries, and Abners Fork and tributaries. The site-specific criteria reflect EPA's recommended selenium water quality criterion for protection of aquatic life for the streams noted above in the Knox Creek watershed. EPA's recommended criterion was first published on July 13, 2016. EPA's recommended freshwater criterion is a chronic criterion expressed in terms of both fish tissue concentration (egg/ovary, whole body, and muscle) and two different water concentrations. The criterion elements are hierarchical with fish tissue values taking precedence should sufficient fish tissue data be available. This is EPA's first aquatic life criterion utilizing fish tissue as a direct expression of the recommended criterion. Accordingly, implementation of these criteria is substantially different from established Clean Water Act water quality programs, including the Virginia Pollutant Discharge Elimination System Permit (VPDES) program and the water quality assessment program. The proposed amendments to the regulation would amend the special standards section of the regulation (9VAC25-260-310) to include site site-specific selenium criterion. Additionally, a notation will be placed in Section 3 of the Big Sandy River basin table (9VAC25-260-490) to indicate the general geographic applicability of the special standard.
Issues: The primary advantage to the public is that the proposed selenium criteria are based on updated scientific information to protect aquatic life. The disadvantage is that criteria that become more stringent may result in increased costs to the regulated community. However, the goal is to set realistic, protective goals in water quality management and to maintain the most scientifically defensible criteria in the regulation. The advantage to the agency and the Commonwealth that will result from the adoption of these proposed amendments may be additional flexibility for developing accurate and scientifically defensible permit limits, assessments, and clean-up plans (total maximum daily load), which ensure protection of the water quality standards. The regulated community may find that the proposed amendments pertinent to its operations require additional capital or operating costs for control in discharge, particularly where the numerical criteria are more stringent. However, it is not known whether the proposed, site-specific criteria will be more or less stringent than the current selenium aquatic life criteria contained in the regulation. The proposed amendments produce indirect benefits through protection of water quality and living resources of Virginia's waters for the designated uses of aquatic life and wildlife while providing additional options for permittees in the subject watersheds to demonstrate compliance with water quality requirements contained in VPDES permits.
Department of Planning and Budget's Economic Impact Analysis:
The Department of Planning and Budget (DPB) has analyzed the economic impact of this proposed regulation in accordance with § 2.2-4007.04 of the Code of Virginia and Executive Order 19. The analysis presented represents DPB's best estimate of the potential economic impacts as of the date of this analysis.1
Summary of the Proposed Amendments to Regulation. In response to a petition for rulemaking,2 the State Water Control Board (board) proposes to adopt site-specific selenium criteria for the protection of freshwater aquatic life in four streams that are tributaries to Knox Creek in Buchanan County, Virginia.
Background. This action results from a 2023 petition for rulemaking, which requested the board to amend this regulation to incorporate site-specific selenium criteria for the protection of freshwater aquatic life in four streams that are tributaries to Knox Creek in Buchanan County, Virginia. The specific streams that are the focus of this rulemaking are Race Fork and tributaries, Pounding Mill Creek and tributaries, Right Fork of Lester Fork and tributaries, and Abners Fork and tributaries. The site-specific selenium criteria for consideration under this rulemaking reflect the Environmental Protection Agency (EPA) recommended selenium water quality criterion for protection of aquatic life and would apply to the streams noted in the Knox Creek watershed. The EPA's recommended criterion was first published on July 13, 2016, and updated in 2021.3 EPA's recommended freshwater criterion is a chronic criterion expressed in terms of both fish tissue concentration (egg/ovary, whole body, and muscle) and two different water concentrations. The criterion elements are hierarchical, with fish tissue values taking precedence over other values should sufficient fish tissue data be available.
According to the EPA,4 selenium is a naturally occurring element present in sedimentary rocks, shales, coal, and phosphate deposits and soils. Selenium can be released into water by natural sources via weathering and by anthropogenic sources, such as surface mining, coal-fired power plants, and irrigated agriculture. Notably, in this case, the petitioner is a coal mining operator. Selenium is a nutritionally essential element for animals in small amounts, but toxic at higher concentrations. Selenium bioaccumulates in the aquatic food chain and chronic exposure in fish and aquatic invertebrates can cause reproductive impairments (e.g., larval deformity or mortality). Selenium can also adversely affect juvenile growth and mortality. Furthermore, selenium is toxic to waterfowl and other birds that consume aquatic organisms that contain excessive levels of selenium.
Estimated Benefits and Costs. Generally, water quality standards are used to determine if a water body is impaired and, if so, to develop a total maximum daily load (TMDL). If the TMDL is exceeded, then cleanup actions are enforced through the Virginia Pollutant Discharge Elimination System (VPDES) permit. It is possible that standards pertinent to operations of the permittee may require additional capital or operating costs to control their discharge, particularly where the numerical criteria are more stringent. Therefore, whether the proposed standard is more or less stringent than the existing standard is critical to assessing its economic impact. However, it is not known whether the proposed, site-specific criteria will be more or less stringent than the current selenium aquatic life criteria contained in the regulation.
According to DEQ, the criterion based on fish tissue concentration is not comparable to the current standard, which is based only on the water column. While DEQ states the new criteria being adopted that are based on water column appear more stringent compared to the current water column standard, this may not matter because the proposed standard is hierarchical. As a result, the fish tissue criteria would take precedence over the water column criterion so long as fish tissue is available. In other words, the proposed revision of the water column criteria may not apply so long as fish tissue is available. Hence, whether the proposed change would be more or less stringent is not known. Consequently, whether the petitioner would face any restrictions through its VPDES permit and any potential costs is also not known. It is, however, worth noting that this regulatory action is being taken as a direct response to the petitioner's request for these specific criteria.
Aside from the potential compliance costs depending on the stringency, facilities with VPDES permits in the Knox Creek watershed subject to this site-specific selenium criteria would incur a cost to collect fish tissue data to demonstrate compliance with the criteria. Fish tissue samples are expected to cost approximately $4,000 per watershed sample according to a firm representing the petitioner. Additionally, this is EPA's first aquatic life criterion that uses fish tissue as a direct expression of the recommended criterion, as well as DEQ's first adoption of such criteria. Accordingly, implementation of these criteria would be substantially different from established Clean Water Act water quality programs, including the VPDES program and the water quality assessment program. Thus, DEQ and Virginia Energy, which is the VPDES enforcement agency for the mining operators, would have an opportunity to experiment with this type of criteria and learn from it. Furthermore, DEQ asserts that the primary advantage to the public is that the proposed selenium criteria are based on updated scientific information to protect aquatic life, which should help in developing accurate and scientifically defensible permit limits, assessments, and clean-up plans to ensure protection of the designated uses.
Businesses and Other Entities Affected. Due to the limited geographic application of the proposed criteria, DEQ anticipates that this action will only affect one surface coal mining facility. That facility, which is owned by the petitioner, may be disproportionately affected.
Additionally, it is anticipated Virginia Energy will be particularly affected by these regulations as related to discharge permits. Virgina Energy is the agency charged with implementing the VPDES program for coal mining operations in Virginia. Accordingly, they would have primary responsibility for implementing the amended criteria. DEQ reports that Virginia Energy has been actively involved in this rulemaking and is aware of the proposed criteria and the need to establish implementation procedures for incorporating the proposed criteria into its VPDES program.
The Code of Virginia requires DPB to assess whether an adverse impact may result from the proposed regulation.5 An adverse impact is indicated if there is any increase in net cost or reduction in net benefit for any entity, even if the benefits exceed the costs for all entities combined.6 As noted, the use of fish tissue criteria is expected to introduce $4,000 cost to the petitioner for collection of fish samples. However, given that the proposed standard may be less stringent and consequently may reduce compliance costs to offset the sample collection costs, and the fact that the petitioner asked for this standard, no adverse impact is indicated.
Small Businesses7 Affected.8 The proposed amendments do not appear to adversely affect small businesses.
Localities9 Affected.10 The proposed selenium criteria based on fish tissue samples apply specifically to Knox Creek, which is located in Buchanan County. However, the proposed amendments do not introduce costs for that county.
Projected Impact on Employment. There is not enough information available to determine whether the proposed amendments would affect total employment by a meaningful amount and in any certain direction.
Effects on the Use and Value of Private Property. Similarly, there is not enough information available to determine whether the proposed amendments would affect the use and value of private property by a meaningful amount and in any certain direction. No impact on real estate development costs is expected.
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1 Section 2.2-4007.04 of the Code of Virginia requires that such economic impact analyses determine the public benefits and costs of the proposed amendments. Further the analysis should include but not be limited to: (1) the projected number of businesses or other entities to whom the proposed regulatory action would apply, (2) the identity of any localities and types of businesses or other entities particularly affected, (3) the projected number of persons and employment positions to be affected, (4) the projected costs to affected businesses or entities to implement or comply with the regulation, and (5) the impact on the use and value of private property.
2 https://townhall.virginia.gov/l/viewpetition.cfm?petitionid=385.
3 Table 1 on page xv in https://www.epa.gov/system/files/documents/2021-08/selenium-freshwater2016-2021-revision.pdf.
4 https://www.epa.gov/wqc/aquatic-life-criterion-selenium.
5 Pursuant to § 2.2-4007.04 D: In the event this economic impact analysis reveals that the proposed regulation would have an adverse economic impact on businesses or would impose a significant adverse economic impact on a locality, business, or entity particularly affected, the Department of Planning and Budget shall advise the Joint Commission on Administrative Rules, the House Committee on Appropriations, and the Senate Committee on Finance. Statute does not define "adverse impact," state whether only Virginia entities should be considered, nor indicate whether an adverse impact results from regulatory requirements mandated by legislation.
6 Statute does not define "adverse impact," state whether only Virginia entities should be considered, nor indicate whether an adverse impact results from regulatory requirements mandated by legislation. As a result, DPB has adopted a definition of adverse impact that assesses changes in net costs and benefits for each affected Virginia entity that directly results from discretionary changes to the regulation.
7 Pursuant to § 2.2-4007.04, small business is defined as "a business entity, including its affiliates, that (i) is independently owned and operated and (ii) employs fewer than 500 full-time employees or has gross annual sales of less than $6 million."
8 If the proposed regulatory action may have an adverse effect on small businesses, § 2.2-4007.04 requires that such economic impact analyses include: (1) an identification and estimate of the number of small businesses subject to the proposed regulation, (2) the projected reporting, recordkeeping, and other administrative costs required for small businesses to comply with the proposed regulation, including the type of professional skills necessary for preparing required reports and other documents, (3) a statement of the probable effect of the proposed regulation on affected small businesses, and (4) a description of any less intrusive or less costly alternative methods of achieving the purpose of the proposed regulation. Additionally, pursuant to § 2.2-4007.1 of the Code of Virginia, if there is a finding that a proposed regulation may have an adverse impact on small business, the Joint Commission on Administrative Rules shall be notified.
9 "Locality" can refer to either local governments or the locations in the Commonwealth where the activities relevant to the regulatory change are most likely to occur.
10 Section 2.2-4007.04 defines "particularly affected" as bearing disproportionate material impact.
Agency's Response to Economic Impact Analysis: The Department of Environmental Quality has reviewed the economic impact analysis prepared by the Department of Planning and Budget and has no comment.
Summary:
In response to a petition for rulemaking, the proposed amendments incorporate site-specific selenium criteria for the protection of freshwater aquatic life in four streams that are tributaries to Knox Creek in Buchanan County.
9VAC25-260-310. Special standards and requirements.
The special standards are shown in small letters to correspond to lettering in the basin tables. The special standards are as follows:
EDITOR'S NOTE: Subdivisions a through hh of 9VAC25-260-310 are not amended; therefore, the text of those subsections is not set out. |
ii. In the wadeable portions of the mainstem sections of the Shenandoah River, North Fork Shenandoah River, and South Fork Shenandoah River listed in the table in this subdivision, a determination of persistent nuisance filamentous algae impeding the recreation use should be made when exceedances of either of the specified benthic chlorophyll-a concentration thresholds occur in more than one recreation season (May 1 to October 31) in three years. "Wadeable" constitutes a stream that can be crossed and sampled safely during a given sampling event occurring within the recreation season.
Segment
|
Two-Month Median (mg/m2)
|
Seasonal Median (mg/m2)
|
Shenandoah River from its confluence of the North Fork and South Fork Shenandoah Rivers downstream to the Virginia-West Virginia state line
|
150
|
100
|
North Fork Shenandoah River from its confluence with Fort Run downstream to its confluence with the South Fork Shenandoah River
|
150
|
100
|
South Fork Shenandoah River from its confluence with the North and South Rivers downstream to its confluence with the North Fork Shenandoah River
|
150
|
100
|
jj. The selenium chronic criteria for the protection of freshwater aquatic life apply in the following waters:
Knox Creek watershed in Buchanan County
(1) Race Fork and tributaries.
(2) Pounding Mill Creek and tributaries.
(3) Right Fork of Lester Fork and tributaries.
(4) Abners Fork and tributaries.
Media Type
|
Fish Tissue1
|
Water Column4
|
Criterion Element
|
Egg-ovary2
|
Fish Whole-body or Muscle3
|
Monthly Average Exposure
|
Intermittent Exposure5
|
Magnitude
|
15.1 mg/kg dw
|
8.5 mg/kg dw whole-body
or
11.3 mg/kg dw muscle (skinless, boneless filet)
|
1.5 µg/L in lentic aquatic systems
3.1 µg/L in lotic aquatic systems
|
WQCint = WQC30-day - Cbkgrnd(1- f int)
fint
|
Duration
|
Instantaneous measurement6
|
Instantaneous measurement6
|
30 days
|
Number of days/month with an elevated concentration
|
Frequency
|
Not to be exceeded
|
Not to be exceeded
|
Not more than once in three years on average
|
Not more than once in three years on average
|
mg/kg dw = milligrams per kilogram dry weight
|
1. Fish tissue elements are expressed as steady state.
2. Egg-ovary supersedes any whole-body, muscle, or water column element when fish egg-ovary concentrations are measured.
3. Fish whole-body or muscle tissue supersedes water column element when both fish tissue and water concentrations are measured.
4. Water column values are based on dissolved total selenium in water and are derived from fish tissue values via bioaccumulation modeling. Water column values are the applicable criterion element in the absence of steady-state condition fish tissue data. In fishless waters, selenium concentrations in fish from the nearest downstream waters may be used to assess compliance using methods provided in Aquatic Life Ambient Water Quality Criterion for Selenium – Freshwater, EPA-822-R-16-006, Appendix K: Translation of a Selenium Fish Tissue Criterion Element to a Site-Specific Water Column Value (June 2016).
5. Where WQC30-day is the water column monthly element for either lentic (still) or lotic (flowing) waters; Cbkgrnd is the average background selenium concentration; and fint is the fraction of any 30-day period during which elevated selenium concentrations occur, with fint assigned a value ≥0.033 (corresponding to one day).
6. Fish tissue data provide instantaneous point measurements that reflect integrative accumulation of selenium over time and space in fish populations at a given site.
|
9VAC25-260-490. Tennessee and Big Sandy River Basins (Big Sandy River Subbasin).
SEC.
|
CLASS
|
SP. STDS.
|
SECTION DESCRIPTION
|
1
|
IV
|
|
All tributaries of Tug Fork in Virginia.
|
2
|
IV
|
|
All tributaries of Jacobs Fork and Dry Fork in Virginia.
|
2a
|
IV
|
PWS
|
Crockett Cove, a tributary to Jacobs Fork, from Bishop's raw water intake to its headwaters.
|
3
|
IV
|
jj
|
Levisa Fork and its tributaries and Knox Creek and its tributaries, unless otherwise designated in this chapter, from the Virginia-Kentucky state line upstream to their headwaters.
|
|
V
|
|
Stockable Trout Waters in Section 3
|
|
vi
|
|
Dismal Creek from its mouth to its headwaters.
|
4
|
IV
|
|
Russell Fork and its tributaries, unless otherwise designated in this chapter, from the Virginia-Kentucky state line upstream to their headwaters.
|
|
V
|
|
Stockable Trout Waters in Section 4
|
|
***
|
|
Caney Creek from Long Branch Creek upstream 5.5 miles.
|
|
vi
|
|
Frying Pan Creek from 1.3 miles above its confluence with Russell Fork 8.6 miles upstream (in vicinity of Bucu).
|
|
vi
|
|
North Fork Pound River from the town limits of Pound upstream to the water supply dam.
|
|
***
|
|
Russell Fork from the confluence of Pound River to the Virginia-Kentucky state line.
|
|
VI
|
|
Natural Trout Waters in Section 4
|
|
iii
|
|
Pound River from its confluence with Russell Fork upstream to the John W. Flannagan Dam.
|
4a
|
IV
|
PWS
|
Pound River and its tributaries from the John W. Flannagan Dam, including the Cranes Nest River and its tributaries to points 5 five miles above the John W. Flannagan Water Authority's raw water intake.
|
4b
|
IV
|
PWS
|
North Fork Pound River and its tributaries from North Fork Pound River Dam and the Town of Pound's raw water intake upstream to their headwaters, unless otherwise designated in this chapter.
|
4c
|
|
|
(Deleted)
|
4d
|
IV
|
|
Phillips Creek from its mouth to its headwaters and the North Fork Pound River from Wise County's swimming area around the mouth of Phillips Creek to a point 1/2 mile upstream.
|
4e
|
IV
|
PWS
|
Russell Fork River and its tributaries from the Kentucky state line 2.2 miles upstream (Elkhorn City, Kentucky raw water intake including Grassy Creek from its confluence with Russell Fork northeast to the Kentucky state line, Hunts Creek from its confluence with Grassy Creek to 1 one mile upstream, Laurel Branch to its headwaters, including Laurel Lake (Breaks Interstate Park raw water intake).
|
|
V
|
|
Stockable Trout Waters in Section 4e
|
|
***
|
PWS
|
Russell Fork from the Kentucky state line 2.2 miles upstream.
|
VA.R. Doc. No. R24-7765; Filed September 10, 2024