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REGULATIONS
Vol. 32 Iss. 5 - November 02, 2015TITLE 9. ENVIRONMENTVIRGINIA WASTE MANAGEMENT BOARDChapter 60Proposed RegulationTitle of Regulation: 9VAC20-60. Virginia Hazardous Waste Management Regulations (amending 9VAC20-60-261, 9VAC20-60-264, 9VAC20-60-265, 9VAC20-60-273, 9VAC20-60-1505).
Statutory Authority: § 10.1-1402 of the Code of Virginia; 42 USC § 6921 et seq.; 40 CFR Parts 260 through 272.
Public Hearing Information: No public hearings are scheduled.
Public Comment Deadline: January 4, 2016.
Agency Contact: Debra Miller, Policy and Planning Specialist, Department of Environmental Quality, 629 East Main Street, P.O. Box 1105, Richmond, VA 23218, telephone (804) 698-4206, FAX (804) 698-4346, TTY (804) 698-4021, or email debra.miller@deq.virginia.gov.
Basis: Section 10.1-1402 of the Code of Virginia authorizes the Virginia Waste Management Board to issue regulations as may be necessary to carry out its powers and duties under the Virginia Waste Management Act (Act). Subdivision 11 of § 10.1-1402 states that the board is authorized to "Promulgate and enforce regulations, and provide for reasonable variances and exemptions necessary to carry out its powers and duties and the intent of this chapter and the federal acts, except that a description of provisions of any proposed regulation which are more restrictive than applicable federal requirements, together with the reason why the more restrictive provisions are needed, shall be provided to the standing committee of each house of the General Assembly to which matters relating to the content of the regulation are most properly referable."
Purpose: The Virginia Hazardous Waste Management Regulations (9VAC20-60) provide requirements for the effective management of hazardous waste in the Commonwealth, including the management of mercury-containing lamps by recycling facilities or universal waste handlers. This proposed amendment is intended to revise the current management requirements for these lamps to provide for better protection of human health and the environment.
Substance: In order to obtain U.S. Environmental Protection Agency (EPA) authorization for Virginia's universal waste program for mercury-containing lamps, this regulatory action (i) revises and adds additional requirements for mercury-containing lamp recycling facilities including testing, operational, closure and recordkeeping criteria, and if applicable, financial assurance requirements and (ii) revises and adds requirements for small and large quantity handlers and destination facilities that manage mercury containing lamps.
Issues: The primary purpose of this regulatory action is to develop a set of performance standards and requirements that allow for the crushing of mercury-containing lamps (fluorescent bulbs) in a manner that is protective of human health and the environment. Crushing of mercury-containing lamps has several benefits for businesses and will help to encourage recycling by making it more economical as compared to recycling intact lamps. Recycling results in the reduction of mercury in the environment, which is important for protection of public health.
The advantages to businesses include (i) reducing storage space over that needed to accumulate intact lamps, (ii) reducing time and labor costs, (iii) reducing emissions from lamp breakage that can occur during storage as well as during transportation, (iv) reducing transportation costs, and (v) making recycling more economical. Advantages to the general public include a reduction of mercury in the environment.
Disadvantages to businesses may include additional regulatory requirements associated with lamp crushing, particularly the annual mercury monitoring requirements and associated costs and additional recordkeeping requirements. These may be offset by the cost advantages.
Advantages to the Commonwealth are the promotion and encouragement of recycling, particularly the recycling of mercury that has known public health and environmental consequences if not disposed of properly. In addition, recycling promotes the Commonwealth's stated waste management hierarchy (i.e., recycling is preferred over incineration or landfill disposal).
This regulatory action is needed in order to obtain federal authorization for lamp crushing. Under federal rules, crushing is not allowed, but states can demonstrate that they have regulatory requirements and controls in place that provide the same level of protection. Currently, businesses in Virginia that are crushing mercury containing lamps may not comply with the federal requirement and risk possible enforcement action by the EPA.
Department of Planning and Budget's Economic Impact Analysis:
Summary of the Proposed Amendments to Regulation. The Virginia Waste Management Board (Board) proposes to amend its regulation to set criteria for private businesses and governmental entities (known collectively as universal waste handlers) to safely crush mercury containing lamps (fluorescent bulbs). The Board also proposes to make the rules for entities that recycle mercury containing lamps more specific.
Result of Analysis. Benefits likely outweigh costs for all proposed changes.
Estimated Economic Impact. Currently neither the Environmental Protection Agency (EPA) nor the Virginia Department of Environmental Quality (DEQ) has rules in place that allow businesses and governmental entities (military bases, local governments or state government agencies) to crush mercury containing lamps. Currently both EPA and DEQ rules require these entities to box up spent fluorescent lamps and ship them to recycling centers. Because the EPA has been working with DEQ to formulate acceptable rules for universal waste handlers to be able to safely crush such lamps for several years, entities in the Commonwealth currently do crush this waste with the tacit approval of the EPA. Universal waste handlers are, however still currently subject to punishment (if the EPA chooses to change its non-enforcement policy) until these regulatory changes are promulgated and have become effective.
Currently, universal waste handlers crush mercury containing lamps using equipment that crushes the lamps, while filtering out any mercury vapor that is released, and then drops the crushed lamps into a drum. Costs associated with this activity include the costs of the bulb crushing unit(s) - $4,100 per unit, drums (which are reusable and are returned to the entity producing the waste after they are emptied at a recycling center) and HEPA filters - $177 per filter. The number of filters used per year will vary directly with the volume of lamps crushed by any particular universal waste handler. Costs also may include the cost of buying or renting monitoring equipment for universal waste handlers that crush large volumes of lamps. Board staff estimates that fewer than 100 entities will be required to monitor mercury vapor levels and that the costs of monitoring will likely range between $500 and $1,500 per year. Board staff also reports that effected entities that crush very large volumes of lamps may incur costs for writing a closure plan and costs associated with obtaining financial assurance. The one-time cost of preparing a closure plan will likely be less than $5,000 and obtaining financial assurance will likely be less than $500 per year. Board staff estimates that only about 10 affected universal waste handlers in the Commonwealth will crush enough lamps to meet the threshold for requiring a closure plan and financial assurance and that all of those will likely be governmental entities. Affected entities may also incur some additional bookkeeping costs that may range up to $1,000 for entities that have very large volumes of waste lamps that they crush.
If affected entities choose to crush, the costs of crushing will almost certainly be outweighed by savings universal waste handlers will experience on account of not having to box up spent bulbs whole and ship the boxes to recycling facilities. Board staff reached out to affected entities who report that crushing lamps and then sending the much less bulky drums to recycling facilities costs them 50% less (on average) when compared to conventional recycling. In particular, these entities report that crushing saves up to 20 hours of labor per 1,000 bulbs crushed and takes up 80% less space. Savings are also realized because drums are very sturdy and reusable but the boxes used to store and ship intact lamps rarely survive a trip to the recycling center and back to the universal waste handler and so, in effect are one time use storage that must be replaced at some cost.
Businesses and Entities Affected. Board staff estimates that approximately 500 entities will be affected by this proposed regulation. These entities will likely include local governments, state agencies, military facilities and medium to large businesses that would have large numbers of mercury containing lamps to dispose of. Board staff estimates that less than 10% of these entities would qualify as small businesses.
Localities Particularly Affected. No localities will likely be disproportionately affected by this proposed regulatory change.
Projected Impact on Employment. This regulatory action will likely have little impact on employment in the Commonwealth.
Effects on the Use and Value of Private Property. To the extent that these regulatory changes lower some expenses for businesses, the value of those businesses will likely increase slightly.
Small Businesses: Costs and Other Effects. Since the crushing requirements in this regulation represent an alternative to EPA and DEQ rules for recycling mercury containing lamps, no small businesses is likely to choose to crush lamps under these rules unless such a choice has more utility (is cheaper or more convenient or both) than recycling. Thus, these small businesses are unlikely to incur any net costs on account of this proposed regulation.
Small Businesses: Alternative Method that Minimizes Adverse Impact. Since the crushing requirements in this regulation represent an alternative to EPA and DEQ rules for recycling mercury containing lamps, no small businesses is likely to choose to crush lamps under these rules unless such a choice has more utility (is cheaper or more convenient or both) than recycling. Thus, these small businesses are unlikely to incur any net costs on account of this proposed regulation.
Real Estate Development Costs. This regulatory action will likely have no effect on real estate development costs in the Commonwealth.
Legal Mandate.
General: 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 Number 17 (2014). Section 2.2-4007.04 requires that such economic impact analyses determine the public benefits and costs of the proposed amendments. Further the report should include but not be limited to:
• the projected number of businesses or other entities to whom the proposed regulation would apply,
• the identity of any localities and types of businesses or other entities particularly affected,
• the projected number of persons and employment positions to be affected,
• the projected costs to affected businesses or entities to implement or comply with the regulation, and
• the impact on the use and value of private property.
Small Businesses: If the proposed regulation will have an adverse effect on small businesses, § 2.2-4007.04 requires that such economic impact analyses include:
• an identification and estimate of the number of small businesses subject to the proposed regulation,
• 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,
• a statement of the probable effect of the proposed regulation on affected small businesses, and
• 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, if there is a finding that a proposed regulation may have an adverse impact on small business, the Joint Commission on Administrative Rules is notified at the time the proposed regulation is submitted to the Virginia Register of Regulations for publication. This analysis shall represent DPB's best estimate for the purposes of public review and comment on the proposed regulation.
Agency's Response to Economic Impact Analysis: The department has reviewed the economic impact analysis prepared by the Department of Planning and Budget and has no comment.
Summary:
The proposed amendments address the management of mercury-containing lamps by recycling facilities or universal waste handlers, including (i) testing, operational, closure, and recordkeeping requirements, and if applicable, financial assurance requirements and (ii) requirements for small and large quantity handlers and destination facilities that manage mercury-containing lamps. The amendments qualify the Virginia mercury-containing lamp universal waste program as a state-equivalent program that permits the crushing of mercury-containing lamps.
9VAC20-60-261. Adoption of 40 CFR Part 261 by reference.
A. Except as otherwise provided, the regulations of the United States Environmental Protection Agency set forth in 40 CFR Part 261 are hereby incorporated as part of the Virginia Hazardous Waste Management Regulations. Except as otherwise provided, all material definitions, reference materials, and other ancillaries that are a part of 40 CFR Part 261 are also hereby incorporated as part of the Virginia Hazardous Waste Management Regulations.
B. In all locations in these regulations where 40 CFR Part 261 is incorporated by reference, the following additions, modifications, and exceptions shall amend the incorporated text for the purpose of its incorporation into these regulations:
1. Any agreements required by 40 CFR 261.4(b)(11)(ii) shall be sent to the United States Environmental Protection Agency at the address shown and to the Department of Environmental Quality, P.O. Box 1105, Richmond, Virginia 23218.
2. In 40 CFR 261.4(e)(3)(iii), the text "in the Region where the sample is collected" shall be deleted.
3. In 40 CFR 261.4(f)(1), the term "Regional Administrator" shall mean the regional administrator of Region III of the United States Environmental Protection Agency or his designee.
4. In 40 CFR 261.6(a)(2), recyclable materials shall be subject to the requirements of 9VAC20-60-270 and Part XII (9VAC20-60-1260 et seq.) of this chapter.
5. No hazardous waste from a conditionally exempt small quantity generator shall be managed as described in 40 CFR 261.5(g)(3)(iv) or 40 CFR 261.5(g)(3)(v) unless such waste management is in full compliance with all requirements of the Solid Waste Management Regulations (9VAC20-81).
6. In 40 CFR 261.9 and wherever elsewhere in Title 40 of the Code of Federal Regulations there is a listing of universal wastes or a listing of hazardous wastes that are the subject of provisions set out in 40 CFR Part 273 as universal wastes, it shall be amended by addition of the following sentence: "In addition to the hazardous wastes listed
hereinhere, the term "universal waste" and all lists of universal waste or waste subject to provisions of 40 CFR Part 273 shall include those hazardous wastes listed in Part XVI (9VAC20-60-1495 et seq.) of the Virginia Hazardous Waste Management Regulations as universal wastes,under suchin accordance with the terms and requirementsas shall therein be ascribeddescribed."7. In Subparts B and D of 40 CFR Part 261, the term "Administrator" shall mean the administrator of the United States Environmental Protection Agency, and the term "Director" shall not supplant "Administrator" throughout Subparts B and D.
8. Regardless of the provisions of 9VAC20-60-18, the revisions to 40 CFR Part 261 as promulgated by U.S. EPA on October 30, 2008, (73 FR 64757 - 64788) (definition of solid waste rule) are not adopted
herein.9. For the purpose of this chapter, any solid waste is a hazardous waste if it is defined to be hazardous waste under the laws or regulations of the state in which it first became a solid waste.
10. In 40 CFR 261.6(c)(1) and 40 CFR 261.6(c)(2) mercury-containing lamp recycling facilities must also comply with all applicable requirements of 9VAC20-60-264 B 34 and 9VAC20-60-265 B 21.
9VAC20-60-264. Adoption of 40 CFR Part 264 by reference.
A. Except as otherwise provided, the regulations of the United States Environmental Protection Agency set forth in 40 CFR Part 264 are hereby incorporated as part of the Virginia Hazardous Waste Management Regulations. Except as otherwise provided, all material definitions, reference materials and other ancillaries that are a part of 40 CFR Part 264 are also hereby incorporated as part of the Virginia Hazardous Waste Management Regulations.
B. In all locations in these regulations where 40 CFR Part 264 is incorporated by reference, the following additions, modifications, and exceptions shall amend the incorporated text for the purpose of its incorporation into these regulations:
1. Sections 40 CFR 264.1(d), 40 CFR 264.1(f), 40 CFR 264.149, 40 CFR 264.150, 40 CFR 264.301(l), and Appendix VI are not included in the incorporation of 40 CFR Part 264 by reference and are not a part of the Virginia Hazardous Waste Management Regulations.
2. In 40 CFR 264.1(g)(11) and wherever elsewhere in Title 40 of the Code of Federal Regulations there is a listing of universal wastes or a listing of hazardous wastes that are the subject of provisions set out in 40 CFR Part 273 as universal wastes, it shall be amended by addition of the following sentence: "In addition to the hazardous wastes listed
hereinhere, the term "universal waste" and all lists of universal waste or waste subject to provisions of 40 CFR Part 273 shall include those hazardous wastes listed in Part XVI (9VAC20-60-1495 et seq.) of the Virginia Hazardous Waste Management Regulations as universal wastes,under suchin accordance with the terms and requirementsas shall therein be ascribeddescribed."3. In 40 CFR 264.12(a), the term "Regional Administrator" shall mean the regional administrator of Region III of the United States Environmental Protection Agency or his designee.
4. In 40 CFR 264.33, the following sentence shall be added to the end of the paragraph: "A record of tests or inspections will be maintained on a log at that facility or other reasonably accessible and convenient location."
5. In addition to the notifications required by 40 CFR 264.56(d)(2), notification shall be made to the on-scene coordinator, the National Response Center, and the Virginia Department of Emergency Management, Emergency Operations Center. In the associated report filed under 40 CFR 264.56(j), the owner or operator shall include such other information specifically requested by the director, which is reasonably necessary and relevant to the purpose of an operating record.
6. In 40 CFR 264.93, "hazardous constituents" shall include constituents identified in 40 CFR Part 264 Appendix IX in addition to those in 40 CFR Part 261 Appendix VIII.
7. The federal text at 40 CFR 264.94(a)(2) is not incorporated by reference. The following text shall be substituted for 40 CFR 264.94(a)(2): "For any of the constituents for which the USEPA has established a Maximum Contaminant Level (MCL) under the National Primary Drinking Water Regulation, 40 CFR Part 141 (regulations under the Safe Drinking Water Act), the concentration must not exceed the value of the MCL; or if the background level of the constituent is below the MCL; or."
8. The owner or operator must submit the detailed, written closure cost estimate described in 40 CFR 264.142 upon the written request of the director.
9. In 40 CFR 264.143(b)(1), 40 CFR 264.143(c)(1), 40 CFR 264.145(b)(1), and 40 CFR 264.145(c)(1), any surety issuing surety bonds to guarantee payment or performance must be licensed pursuant to Chapter 10 (§ 38.2-1000 et seq.) of Title 38.2 of the Code of Virginia.
10. In 40 CFR 264.143(b), 40 CFR 264.143(c), 40 CFR 264.145(b) and 40 CFR 264.145(c), any owner or operator demonstrating financial assurance for closure or post-closure care using a surety bond shall submit with the surety bond a copy of the deed book page documenting that the power of attorney of the attorney-in-fact executing the bond has been recorded pursuant to § 38.2-2416 of the Code of Virginia.
11. Where in 40 CFR 264.143(c)(5) the phrase "final administrative determination pursuant to section 3008 of RCRA" appears, it shall be replaced with "final determination pursuant to Chapter 40 (§ 2.2-4000 et seq.) of Title 2.2 of the Code of Virginia."
12. The following text shall be substituted for 40 CFR 264.143(d)(8): "Following a final administrative determination pursuant to Chapter 40 (§ 2.2-4000 et seq.) of Title 2.2 of the Code of Virginia that the owner or operator has failed to perform final closure in accordance with the approved closure plan, the applicable regulations or other permit requirements when required to do so, the director may draw on the letter of credit."
13. The following text shall be substituted for 40 CFR 264.143(e)(1): "An owner or operator may satisfy the requirements of this section by obtaining closure insurance which conforms to the requirements of this paragraph and submitting a certificate of such insurance, along with a complete copy of the insurance policy, to the department. An owner or operator of a new facility must submit the certificate of insurance along with a complete copy of the insurance policy to the department at least 60 days before the date on which the hazardous waste is first received for treatment, storage or disposal. The insurance must be effective before this initial receipt of hazardous waste. At a minimum, the insurer must be licensed pursuant to Chapter 10 (§ 38.2-1000 et seq.) of Title 38.2 of the Code of Virginia."
14. The following text shall be substituted for 40 CFR 264.143(f)(3)(ii), 40 CFR 264.145(f)(3)(ii) and 40 CFR 264.147(f)(3)(ii): "A copy of the owner's or operator's audited financial statements for the latest completed fiscal year; including a copy of the independent certified public accountant's report on examination of the owner's or operator's financial statements for the latest completed fiscal year; and"
15. In addition to the other requirements in 40 CFR 264.143(f)(3), 40 CFR 264.145(f)(3) and 40 CFR 264.147(f)(3), an owner or operator must submit confirmation from the rating service that the owner or operator has a current rating for its most recent bond issuance of AAA, AA, A, or BBB as issued by Standard and Poor's or Aaa, Aa, A, or Baa as issued by Moody's if the owner or operator passes the financial test with a bond rating as provided in 40 CFR 264.143(f)(1)(ii)(A).
16. The following text shall be substituted for 40 CFR 264.143(h) and 40 CFR 264.145(h): "An owner or operator may use a financial assurance mechanism specified in this section to meet the requirements of this section for more than one facility in Virginia. Evidence of financial assurance submitted to the department must include a list showing, for each facility, the EPA Identification Number, name, address, and the amount of funds for closure or post-closure assured by the mechanism. The amount of funds available through the mechanism must be no less than the sum of funds that would be available if a separate mechanism had been established and maintained for each facility. In directing funds available through the mechanism for closure or post-closure care of any of the facilities covered by the mechanism, the director may direct only the amount of funds designated for that facility, unless the owner or operator agrees to the use of additional funds available under the mechanism."
17. In addition to the requirements of 40 CFR 264.144, "the owner or operator must submit a detailed, written post-closure cost estimate upon the written request of the director."
18. The following text shall be substituted for 40 CFR 264.144(b): "During the active life of the facility and the post-closure period, the owner or operator must adjust the post-closure cost estimate for inflation within 60 days prior to the anniversary date of the establishment of the financial instrument(s) used to comply with 40 CFR 264.145. For owners or operators using the financial test or corporate guarantee, the post-closure cost estimate must be updated for inflation within 30 days after the close of the firm's fiscal year and before the submission of updated information to the department as specified in 40 CFR 264.145(f)(5). The adjustment may be made by recalculating the post-closure cost estimate in current dollars or by using an inflation factor derived from the most recent Implicit Price Deflator for Gross National Product published by the U.S. Department of Commerce in its Survey of Current Business as specified in 40 CFR 264.142(b)(1) and (2). The inflation factor is the result of dividing the latest published annual Deflator by the Deflator for the previous year.
a. The first adjustment is made by multiplying the post-closure cost estimate by the inflation factor. The result is the adjusted post-closure cost estimate.
b. Subsequent adjustments are made by multiplying the latest adjusted post-closure cost estimate by the latest inflation factor."
19. The following text shall be substituted for 40 CFR 264.144(c): "During the active life of the facility and the post-closure period, the owner or operator must revise the post-closure cost estimate within 30 days after the director has approved the request to modify the post-closure plan, if the change in the post-closure plan increases the cost of post-closure care. The revised post-closure cost estimate must be adjusted for inflation as specified in 264.144(b)."
20. Where in 40 CFR 264.145(c)(5) the phrase "final administrative determination pursuant to section 3008 of RCRA" appears, it shall be replaced with "final determination pursuant to Chapter 40 (§ 2.2-4000 et seq.) of Title 2.2 of the Code of Virginia."
21. The following text shall be substituted for 40 CFR 264.145(d)(9): "Following a final administrative determination pursuant to Chapter 40 (§ 2.2-4000 et seq.) of Title 2.2 of the Code of Virginia that the owner or operator has failed to perform post-closure in accordance with the approved post-closure plan, the applicable regulations, or other permit requirements when required to do so, the director may draw on the letter of credit."
22. The following text shall be substituted for 40 CFR 264.145(e)(1): "An owner or operator may satisfy the requirements of this section by obtaining post-closure insurance which conforms to the requirements of this paragraph and submitting a certificate of such insurance to the department. An owner or operator of a new facility must submit the certificate of insurance along with a complete copy of the insurance policy to the department at least 60 days before the date on which the hazardous waste is first received for treatment, storage or disposal. The insurance must be effective before this initial receipt of hazardous waste. At a minimum, the insurer must be licensed pursuant to Chapter 10 (§ 38.2-1000 et seq.) of Title 38.2 of the Code of Virginia."
23. In 40 CFR 264.147(a)(1)(ii), 40 CFR 264.147(b)(1)(ii), 40 CFR 264.147(g)(2), and 40 CFR 264.147(i)(4), the term "Virginia" shall not be substituted for the term "State" or "States."
24. In 40 CFR 264.191(a), the compliance date of January 12, 1988, applies only for HSWA tanks. For non-HSWA tanks, the compliance date is November 2, 1997, instead of January 12, 1997.
25. In 40 CFR 264.191(c), the reference to July 14, 1986, applies only to HSWA tanks. For non-HSWA tanks, the applicable date is November 2, 1987, instead of July 14, 1986.
26. In 40 CFR 264.193, the federal effective dates apply only to HSWA tanks. For non-HSWA tanks, the applicable date is November 2, 1997, instead of January 12, 1997.
27. A copy of all reports made in accordance with 40 CFR 264.196(d) shall be sent to the director and to the chief administrative officer of the local government of the jurisdiction in which the event occurs. The sentence in 40 CFR 264.196(d)(1), "If the release has been reported pursuant to 40 CFR Part 302, that report will satisfy this requirement." is not incorporated by reference into these regulations and is not a part of the Virginia Hazardous Waste Management Regulations.
28. The following text shall be substituted for 40 CFR 264.570(a): "The requirements of this subpart apply to owners and operators of facilities that use new or existing drip pads to convey wood drippage, precipitation and/or surface water run-off to an associated collection system. Existing HSWA drip pads are those constructed before December 6, 1990, and those for which the owner or operator has a design and has entered into a binding financial or other agreement for construction prior to December 6, 1990. Existing non-HSWA drip pads are those constructed before January 14, 1993, and those for which the owner or operator has a design and has entered into a binding financial or other agreements for construction prior to January 14, 1993. All other drip pads are new drip pads. The requirement at 40 CFR 264.573(b)(3) to install a leak collection system applies only to those HSWA drip pads that are constructed after December 24, 1992, except for those constructed after December 24, 1992, for which the owner or operator has a design and has entered into a binding financial or other agreement for construction prior to December 24, 1992. For non-HSWA drip pads, the requirement at 40 CFR 264.573(b)(3) to install a leak collection system applies only to those non-HSWA drip pads that are constructed after September 8, 1993, except for those constructed after September 8, 1993, for which the owner or operator has a design and has entered into a binding financial or other agreement for construction prior to September 8, 1993."
29. In 40 CFR 264.1030(c), the reference to 40 CFR 124.15 shall be replaced by a reference to 40 CFR 124.5.
30. The underground injection of hazardous waste for treatment, storage or disposal shall be prohibited throughout the Commonwealth of Virginia.
31. In addition to the notices required in Subpart B and others parts of 40 CFR Part 264, the following notices are also required:
a. The owner or operator of a facility that has arranged to receive hazardous waste from a foreign source (a source located outside of the United States of America) shall notify the department and administrator in writing at least four weeks in advance of the date the waste is expected to arrive at the facility. Notice of subsequent shipments of the same waste from the same foreign source is not required.
b. The owner or operator of a facility that receives hazardous waste from an off-site source (except where the owner or operator of the facility is also the generator of this waste) shall inform the generator in writing that he has appropriate permits for, and will accept, the waste that the generator is shipping. The owner or operator shall keep a copy of this written notice as part of the operating record.
c. Before transferring ownership or operation of a facility during its operating life, or of a disposal facility during the post-closure care period, the owner or operator shall notify the new owner or operator in writing of the requirements contained in this section and 9VAC20-60-270. An owner or operator's failure to notify the new owner or operator of the above requirements in no way relieves the new owner or operator of his obligation to comply with all applicable requirements.
d. Any person responsible for the release of a hazardous substance from the facility that poses an immediate or imminent threat to public health and who is required by law to notify the National Response Center shall notify the department and the chief administrative officer of the local government of the jurisdiction in which the release occurs or their designees. In cases when the released hazardous substances are hazardous wastes or hazardous waste constituents additional requirements are prescribed by Subpart D of 40 CFR Part 264.
32. In 40 CFR 264.71, the terms "EPA" and "Environmental Protection Agency" shall mean the United States Environmental Protection Agency, and the reference to "system" means the United States Environmental Protection Agency's national electronic manifest system.
33. Regardless of the provisions of 9VAC20-60-18, the requirements of 40 CFR 264.71(j) are not incorporated into this chapter.
34. Requirements for mercury-containing lamp recycling facilities. The following requirements apply to all facilities that recover or reclaim mercury from lamps.
a. All owners and operators of mercury-containing lamp recycling facilities shall:
(1) Have established markets for the utilization of reclaimed materials and be able to identify these markets to the department;
(2) Only introduce into the processing equipment lamps or devices for which the equipment was specifically designed to process and operate and maintain processing equipment consistent with the equipment manufacturer's specifications; and
(3) Not speculatively accumulate the materials.
b. If a mercury-containing lamp recycling facility's processed materials are to be delivered to a facility other than a mercury reclamation facility, the owner or operator shall:
(1) Demonstrate proper equipment operation and efficiency by sampling and analytical testing of the processed materials. The testing shall ensure that such processed materials (i) have less than three parts per million of "average mercury" during each consecutive 12-week time period of operations ("average mercury" shall be calculated pursuant to subdivision 34 b (3) of this subsection); (ii) have less than five parts per million of total mercury as reported in the "weekly composite sample of process operations" ("weekly composite sample of process operations" shall be calculated pursuant to subdivision 34 b (3) of this subsection); (iii) are not a hazardous waste; and (iv) comply with 40 CFR Part 268, if applicable.
(2) Retest, reprocess, or deliver to a mercury reclamation facility processed materials that are in excess of the allowable levels of mercury specified in subdivision 34 b (1) of this subsection.
(3) Sample and perform analytical testing of the processed material for total mercury as follows:
(a) Facility operators shall take daily physical samples of the mercury-containing materials at the point at which they exit the processing equipment. These samples shall be representative of the materials processed during that day.
(b) At the beginning of each week, the prior week's daily samples that shall be consolidated into one weekly sample which shall be submitted for chemical analysis of total mercury content using an approved EPA methodology. At least three separate daily samples shall be taken in order to obtain a weekly sample. When a facility is not operating at least three days during a week, that week will be dropped out of the 12-week rolling average as calculated under subdivision 34 b (3) (c) of this subsection. However, all daily samples that are in a week that has been dropped out shall be counted towards the very next weekly sample that is included in a 12-week rolling average. The result of this analysis shall be considered the "weekly composite sample of process operations."
(c) The "average mercury" value calculation shall be the rolling average of weekly composite sample results from samples taken during the most recent 12-week time period with each new weekly composite sample result replacing the oldest sample result that was used in the previous 12-week period.
c. Mercury-containing lamp recycling facilities shall ensure that the separated materials that are generated from their operations are suitable and safe for their intended end use and shall bear the burden of responsibility for the safety of these materials sold or delivered from the operations. Facilities shall notify in writing receiving sources, other than mercury reclamation facilities, of the amount and type of hazardous substances present in the processed materials as demonstrated by laboratory analysis.
d. Operating requirements. Mercury-containing lamp recycling facilities shall be operated in accordance with the following requirements:
(1) Mercury-containing lamp recycling facilities shall control mercury emissions through the use of a single air handling system with redundant mercury controls and comply with the following:
(a) The owner or operator shall operate, monitor, and maintain an air handling system with redundant air pollution control equipment in order to reduce the mercury content of the air collected during the volume reduction and mercury recovery and reclamation processes.
(b) Redundant air pollution control equipment shall incorporate at least two carbon filters or equivalent technology arranged in a series so that the air passes through both filters before being released. In the event of a single filter failure, each filter shall be designed to ensure compliance with the risk-based protectiveness standards for mercury vapor provided in subdivision 34 e of this subsection.
(c) A sample of air shall be collected after the first carbon filter (or equivalent technology) and upstream of the second once each operating day while mercury-containing lamps or devices are being processed. The mercury content of the sample shall be determined for comparison with the risk-based protectiveness standards provided in subdivision 34 e of this subsection.
(d) The owner or operator shall operate, monitor, and maintain the air pollution control equipment in such a manner as not to exceed the risk-based protectiveness standards under subdivision 34 e of this subsection for mercury vapor downstream of the first carbon filter (or equivalent technology) and upstream of the second carbon filter.
(2) The area in which the processing equipment is located shall be fully enclosed and kept under negative pressure while processing mercury-containing lamps or devices.
e. Testing for mercury releases from lamp crushing units shall be performed using a mercury vapor analyzer that has been approved for the application by the U.S. Occupational Safety and Health Administration or the Virginia Department of Labor and Industry or a comparable device that has been calibrated by the manufacturer or laboratory providing the equipment. Mercury vapor monitors used for testing must be capable of detecting mercury at the applicable concentrations provided below or lower in air and must be equipped with a data recording device to provide a record of measurements taken. Mercury monitoring data shall be documented and available for inspection in accordance with subdivision 34 g of this subsection. The acute exposure protectiveness standard is 300 µg/m3 for a 10 minute exposure with the understanding that the acute exposure protectiveness standard is considered a ceiling value and at no time during bulb crushing operation will the air concentrations of mercury exceed 300 µg/m3. The following are risk based protectiveness standards at a distance of five feet from the bulb crushing unit:
Monthly Bulb Crushing Duration (X Hours/Month)*
Chronic Exposure Air Emission Limit (µg/m3)
Acute Exposure Air Emission Limit (µg/m3)
X ≥ 32
1.314skin µg/m3
300 µg/m3
8 < X < 32
6.317 skin µg/m3
300 µg /m3
X ≤ 8
27.375 skin µg/m3
300 µg/m3
*Monthly crushing duration is determined based on the maximum number of hours that bulb crushing occurred in any one month over the last 12-month period.
f. Closure. Mercury-containing lamp recycling facilities must prepare and maintain a closure plan conforming to the requirements of 40 CFR Part 264, Subpart G as adopted by reference in this section. Financial assurance shall be provided to the department in accordance with 40 CFR Part 264, Subpart H as adopted by reference in this section.
g. Recordkeeping requirements. The owner or operator of a mercury-containing lamp recycling facility shall maintain records of monitoring information that (i) specify the date, place, and time of measurement; (ii) provide the methodology used; and (iii) list the analytical results. The records maintained shall include all calibration and maintenance records of monitoring equipment. The owner or operator shall retain records of all monitoring data and supporting information available for department inspection for a period of at least three years from the date of collection.
9VAC20-60-265. Adoption of 40 CFR Part 265 by reference.
A. Except as otherwise provided, the regulations of the United States Environmental Protection Agency set forth in 40 CFR Part 265 are hereby incorporated as part of the Virginia Hazardous Waste Management Regulations. Except as otherwise provided, all material definitions, reference materials and other ancillaries that are parts of 40 CFR Part 265 are also hereby incorporated as parts of the Virginia Hazardous Waste Management Regulations.
B. In all locations in these regulations where 40 CFR Part 265 is incorporated by reference, the following additions, modifications, and exceptions shall amend the incorporated text for the purpose of its incorporation into these regulations:
1. Sections 40 CFR 265.1(c)(4), 40 CFR 265.149 and 40 CFR 265.150 and Subpart R of 40 CFR Part 265 are not included in the incorporation of 40 CFR Part 265 by reference and are not a part of the Virginia Hazardous Waste Management Regulations.
2. In 40 CFR 265.1(c)(14) and wherever elsewhere in Title 40 of the Code of Federal Regulations there is a listing of universal wastes or a listing of hazardous wastes that are the subject of provisions set out in 40 CFR Part 273 as universal wastes, it shall be amended by addition of the following sentence: "In addition to the hazardous wastes listed
hereinhere, the term "universal waste" and all lists of universal waste or waste subject to provision of 40 CFR Part 273 shall include those hazardous wastes listed in Part XVI (9VAC20-60-1495 et seq.) of the Virginia Hazardous Waste Management Regulations as universal wastes,under suchin accordance with the terms and requirementsas shall therein be ascribeddescribed."3. A copy of all reports and notices made in accordance with 40 CFR 265.12 shall be sent to the department, the administrator and the chief administrative officer of the local government of the jurisdiction in which the event occurs.
4. In 40 CFR 265.12(a), the term "Regional Administrator" shall mean the regional administrator of Region III of the United States Environmental Protection Agency or his designee.
5. In 40 CFR 265.33, the following sentence shall be added to the end of the paragraph: "A record of tests or inspections will be maintained on a log at that facility or other reasonably accessible and convenient location."
6. In addition to the notifications required by 40 CFR 265.56(d)(2), notification shall be made to the on-scene coordinator, the National Response Center, and the Virginia Department of Emergency Management, Emergency Operations Center. In the associated report filed under 40 CFR 265.56(j), the owner or operator shall include such other information specifically requested by the director, which is reasonably necessary and relevant to the purpose of an operating record.
7. In addition to the requirements of 40 CFR 265.91, a log shall be made of each ground water monitoring well describing the soils or rock encountered, the permeability of formations, and the cation exchange capacity of soils encountered. A copy of the logs with appropriate maps shall be sent to the department.
8. The following text shall be substituted for 40 CFR 265.143(g) and 40 CFR 265.145(g): "An owner or operator may use a financial assurance mechanism specified in this section to meet the requirements of this section for more than one facility in Virginia. Evidence of financial assurance submitted to the department must include a list showing, for each facility, the EPA Identification Number, name, address, and the amount of funds for closure or post-closure assured by the mechanism. The amount of funds available through the mechanism must be no less than the sum of funds that would be available if a separate mechanism had been established and maintained for each facility. In directing funds available through the mechanism for closure or post-closure care of any of the facilities covered by the mechanism, the director may direct only the amount of funds designated for that facility, unless the owner or operator agrees to the use of additional funds available under the mechanism.
9. In 40 CFR 265.147(a)(1)(ii), 40 CFR 265.147(g)(2), and 40 CFR 265.147(i)(4), the term "Virginia" shall not be substituted for the term "State" or "States."
10. In 40 CFR 265.191(a), the compliance date of January 12, 1988, applies only for HSWA tanks. For non-HSWA tanks, the compliance date is November 2, 1986.
11. In 40 CFR 265.191(c), the reference to July 14, 1986, applies only to HSWA tanks. For non-HSWA tanks, the applicable date is November 2, 1987.
12. In 40 CFR 265.193, the federal effective dates apply only to HSWA tanks. For non-HSWA tanks, the applicable date
isof January 12, 1987, is replaced with November 2, 1997.13. The following text shall be substituted for 40 CFR 265.440(a): "The requirements of this subpart apply to owners and operators of facilities that use new or existing drip pads to convey wood drippage, precipitation and/or surface water run-off to an associated collection system. Existing HSWA drip pads are those constructed before December 6, 1990, and those for which the owner or operator has a design and has entered into a binding financial or other agreement for construction prior to December 6, 1990. Existing non-HSWA drip pads are those constructed before January 14, 1993, and those for which the owner or operator has a design and has entered into a binding financial or other agreement for construction prior to January 14, 1993. All other drip pads are new drip pads. The requirement at 40 CFR 265.443(b)(3) to install a leak collection system applies only to those HSWA drip pads that are constructed after December 24, 1992, except for those constructed after December 24, 1992, for which the owner or operator has a design and has entered into a binding financial or other agreement for construction prior to December 24, 1992. For non-HSWA drip pads, the requirement at 40 CFR 264.573(b)(3) to install a leak collection system applies only to those non-HSWA drip pads that are constructed after September 8, 1993, except for those constructed after September 8, 1993, for which the owner or operator has a design and has entered into a binding financial or other agreement for construction prior to September 8, 1993."
14. In 40 CFR 265.1083(c)(4)(ii), the second occurrence of the term "EPA" shall mean the United States Environmental Protection Agency.
15. In addition to the requirements of 40 CFR 265.310, the owner or operator shall consider at least the following factors in addressing the closure and post-closure care objectives of this part:
a. Type and amount of hazardous waste and hazardous waste constituents in the landfill;
b. The mobility and the expected rate of migration of the hazardous waste and hazardous waste constituents;
c. Site location, topography, and surrounding land use, with respect to the potential effects of pollutant migration;
d. Climate, including amount, frequency and pH of precipitation;
e. Characteristics of the cover, including material, final surface contours, thickness, porosity and permeability, slope, length of run of slope, and type of vegetation on the cover; and
f. Geological and soil profiles and surface and subsurface hydrology of the site.
16. Additionally, during the post-closure care period, the owner or operator of a hazardous waste landfill shall comply with the requirements of 40 CFR 265.116 and the following items:
a. Maintain the function and integrity of the final cover as specified in the approved closure plan;
b. Maintain and monitor the leachate collection, removal, and treatment system, if present, to prevent excess accumulation of the leachate in the system;
c. Maintain and monitor the landfill gas collection and control system, if present, to control the vertical and horizontal escape of gases;
d. Protect and maintain, if present, surveyed benchmarks; and
e. Restrict access to the landfill as appropriate for its post-closure use.
17. The underground injection of hazardous waste for treatment, storage or disposal shall be prohibited throughout the Commonwealth of Virginia.
18. Regulated units of the facility are those units used for storage treatment or disposal of hazardous waste in surface impoundments, waste piles, land treatment units, or landfills that received hazardous waste after July 26, 1982. In addition to the requirements of Subpart G of 40 CFR Part 265, owners or operators of regulated units who manage hazardous wastes in regulated units shall comply with the closure and post-closure requirements contained in Subpart G of 40 CFR Part 264, Subpart H of 40 CFR Part 264, and Subpart K of 40 CFR Part 264 through Subpart N of 40 CFR Part 264, as applicable, and shall comply with the requirements in Subpart F of 40 CFR Part 264 during any post-closure care period and for the extended ground water monitoring period, rather than the equivalent requirements contained in 40 CFR Part 265. The following provisions shall also apply:
a. For owners or operators of surface impoundments or waste piles included above who intend to remove all hazardous wastes at closure in accordance with 40 CFR 264.228(a)(1) or 40 CFR 264.258(a), as applicable, submittal of contingent closure and contingent post-closure plans is not required. However, if the facility is subsequently required to close as a landfill in accordance with Subpart N of 40 CFR Part 264, a modified closure plan shall be submitted no more than 30 days after such determination. These plans will be processed as closure plan amendments. For such facilities, the corresponding post-closure plan shall be submitted within 90 days of the determination that the unit shall be closed as a landfill.
b. A permit application as required under 9VAC20-60-270 to address the post-closure care requirements of 40 CFR 264.117 and for ground water monitoring requirements of 40 CFR 264.98, 40 CFR 264.99, or 40 CFR 264.100, as applicable, shall be submitted for all regulated units that fail to satisfy the requirements of closure by removal or decontamination in 40 CFR 264.228(a)(1), 40 CFR 264.258(a), or 40 CFR 264.280(d) and 40 CFR 264.280(e), as applicable. The permit application shall be submitted at the same time as the closure plan for those units closing with wastes in place and six months following the determination that closure by removal or decontamination is unachievable for those units attempting such closure. The permit application shall address the post-closure care maintenance of both the final cover and the ground water monitoring wells as well as the implementation of the applicable ground water monitoring program whenever contaminated soils, subsoils, liners, etc., are left in place. When all contaminated soils, subsoils, liners, etc., have been removed yet ground water contamination remains, the permit application shall address the post-closure care maintenance of the ground water monitoring wells as well as the implementation of the applicable ground water monitoring program.
c. In addition to the requirements of 40 CFR 264.112(d)(2)(i) for requesting an extension to the one-year limit, the owner or operator shall demonstrate that he will continue to take all steps to prevent threats to human health and the environment.
d. In addition to the requirements of 40 CFR 264.119(c), the owner or operator shall also request a modification to the post-closure permit if he wishes to remove contaminated structures and equipment.
19. In 40 CFR 265.71, the terms "EPA" and "Environmental Protection Agency" shall mean the United States Environmental Protection Agency, and the reference to "system" means the United States Environmental Protection Agency's national electronic manifest system.
20. Regardless of the provisions of 9VAC20-60-18, the requirements of 40 CFR 265.71(j) are not incorporated into this chapter.
21. Requirements for mercury-containing lamp recycling facilities. The following requirements apply to all facilities that recover or reclaim mercury from lamps:
a. All owners and operators of mercury-containing lamp recycling facilities shall:
(1) Have established markets for the utilization of reclaimed materials and be able to identify these markets to the department;
(2) Only introduce into the processing equipment lamps or devices for which the equipment was specifically designed to process and operate and maintain processing equipment consistent with the equipment manufacturer's specifications; and
(3) Not speculatively accumulate the materials.
b. If a mercury-containing lamp recycling facility's processed materials are to be delivered to a facility other than a mercury reclamation facility, the owner or operator shall:
(1) Demonstrate proper equipment operation and efficiency by sampling and analytical testing of the processed materials. The testing shall ensure that such processed materials (i) have less than three parts per million of "average mercury" during each consecutive 12-week time period of operations ("average mercury" shall be calculated pursuant to subdivision 21 b (3) of this subsection); (ii) have less than five parts per million of total mercury as reported in the "weekly composite sample of process operations" ("weekly composite sample of process operations" shall be calculated pursuant to subdivision 21 b (3) of this subsection); (iii) are not a hazardous waste; and (iv) comply with 40 CFR Part 268, if applicable.
(2) Retest, reprocess, or deliver to a mercury reclamation facility processed materials that are in excess of the allowable levels of mercury specified in subdivision 21 b (1) of this subsection.
(3) Sample and perform analytical testing of the processed material for total mercury as follows:
(a) Facility operators shall take daily physical samples of the mercury-containing materials at the point at which they exit the processing equipment. These samples shall be representative of the materials processed during that day.
(b) At the beginning of each week, the prior week's daily samples shall be consolidated into one weekly sample that shall be submitted for chemical analysis of total mercury content using an approved EPA methodology. At least three separate daily samples shall be taken in order to obtain a weekly sample. When a facility is not operating at least three days during a week, that week will be dropped out of the 12-week rolling average as calculated under subdivision 21 b (3) (c) of this subsection. However, all daily samples that are in a week that has been dropped out shall be counted towards the very next weekly sample that is included in a 12-week rolling average. The result of this analysis shall be considered the "weekly composite sample of process operations."
(c) The "average mercury" value calculation shall be the rolling average of weekly composite sample results from samples taken during the most recent 12-week time period with each new weekly composite sample result replacing the oldest sample result that was used in the previous 12-week period.
c. Mercury-containing lamp recycling facilities shall ensure that the separated materials that are generated from their operations are suitable and safe for their intended end use and shall bear the burden of responsibility for the safety of these materials sold or delivered from the operations. Facilities shall notify in writing receiving sources, other than mercury reclamation facilities, of the amount and type of any hazardous substances present in the processed materials as demonstrated by laboratory analysis.
d. Operating requirements. Mercury-containing lamp recycling facilities shall be operated in accordance with the following requirements:
(1) Mercury-containing lamp recycling facilities shall control mercury emissions through the use of a single air handling system with redundant mercury controls and comply with the following:
(a) The owner or operator shall operate, monitor, and maintain an air handling system with redundant air pollution control equipment in order to reduce the mercury content of the air collected during the volume reduction and mercury recovery and reclamation processes.
(b) Redundant air pollution control equipment shall incorporate at least two carbon filters or equivalent technology arranged in a series so that the air passes through both filters before being released. In the event of a single filter failure, each filter shall be designed to ensure compliance with the risk-based protectiveness standards for mercury vapor provided in subdivision 21 e of this subsection.
(c) A sample of air shall be collected after the first carbon filter (or equivalent technology) and upstream of the second once each operating day while mercury-containing lamps or devices are being processed. The mercury content of the sample shall be determined for comparison with the risk based protectiveness standards provided in subdivision 21 e of this subsection.
(d) The owner or operator shall operate, monitor, and maintain the air pollution control equipment in such a manner as not to exceed the risk-based protectiveness standards under subdivision 21 e of this subsection for mercury vapor downstream of the first carbon filter (or equivalent technology) and upstream of the second carbon filter.
(2) The area in which the processing equipment is located shall be fully enclosed and kept under negative pressure while processing mercury-containing lamps or devices.
e. Testing for mercury releases from lamp crushing units shall be performed using a mercury vapor analyzer that has been approved for the application by the U.S. Occupational Safety and Health Administration or the Virginia Department of Labor and Industry or a comparable device that has been calibrated by the manufacturer or laboratory providing the equipment. Mercury vapor monitors used for testing must be capable of detecting mercury at the applicable concentrations provided below or lower in air and must be equipped with a data recording device to provide a record of measurements taken. Mercury monitoring data shall be documented and available for inspection in accordance with subdivision 21 g of this subsection. The acute exposure protectiveness standard is 300 µg/m3 for a 10 minute exposure with the understanding that the acute exposure protectiveness standard is considered a ceiling value and at no time during bulb crushing operation will the air concentrations of mercury exceed 300 µg/m3. The following are risk-based protectiveness standards at a distance of five feet from the bulb crushing unit:
Monthly Bulb Crushing Duration (X Hours/Month)*
Chronic Exposure Air Emission Limit (µg/m3)
Acute Exposure Air Emission Limit (µg/m3)
X ≥ 32
1.314skin µg/m3
300 µg/m3
8 < X < 32
6.317 skin µg/m3
300 µg /m3
X ≤ 8
27.375 skin µg/m3
300 µg/m3
*Monthly crushing duration is determined based on the maximum number of hours that bulb crushing occurred in any one month over the last 12-month period.
f. Closure. Mercury-containing lamp recycling facilities must prepare and maintain a closure plan conforming to the requirements of 40 CFR Part 265, Subpart G as adopted by reference in this section. Financial assurance shall be provided to the department in accordance with 40 CFR Part 265, Subpart H as adopted by reference in this section.
g. Recordkeeping requirements. The owner or operator of a mercury-containing lamp recycling facility shall maintain records of monitoring information that (i) specify the date, place, and time of measurement; (ii) provide the methodology used; and (iii) list the analytical results. The records maintained shall include all calibration and maintenance records of monitoring equipment. The owner or operator shall retain records of all monitoring data and supporting information available for department inspection for a period of at least three years from the date of collection.
9VAC20-60-273. Adoption of 40 CFR Part 273 by reference.
A. Except as otherwise provided, the regulations of the United States Environmental Protection Agency set forth in 40 CFR Part 273 are hereby incorporated as part of the Virginia Hazardous Waste Management Regulations. Except as otherwise provided, all material definitions, reference materials and other ancillaries that are a part of 40 CFR Part 273 are also hereby incorporated as part of the Virginia Hazardous Waste Management Regulations.
B. In all locations in these regulations where 40 CFR Part 273 is incorporated by reference, the following additions, modifications, and exceptions shall amend the incorporated text for the purpose of its incorporation into these regulations:
1. In 40 CFR 273.32(a)(3), the term "EPA" shall mean the United States Environmental Protection Agency
or his designee.2. In addition to universal wastes included in 40 CFR Part 273, other wastes are defined to be universal wastes in Part XVI (9VAC20-60-1495 et seq.) of these regulations. Part XVI also contains waste specific requirements associated with the waste defined to be universal waste therein. In 40 CFR 273.1, the definitions in 40 CFR 273.9, and wherever elsewhere in Title 40 of the Code of Federal Regulations there is a listing of universal wastes or a listing of hazardous waste that are the subject of provisions set out in 40 CFR Part 273 as universal wastes, it shall be amended by addition of the following sentence: "In addition to the hazardous wastes listed
hereinhere, the term "universal waste" and all lists of universal waste or waste subject to provisions of 40 CFR Part 273 shall include those hazardous wastes listed in Part XVI (9VAC20-60-1495 et seq.) of the Virginia Hazardous Waste Management Regulations as universal wastes,under suchin accordance with the terms and requirementsas shall therein be ascribeddescribed." Any listing of universal wastes in 40 CFR Part 273 shall incorporate the universal wastes set out in Part XVI in a manner identical to those included in the federal text; whether, for example, as in 40 CFR 273.32(b)(4), 40 CFR 273.32(b)(5), 40 CFR 273.39(b)(2), and 40 CFR 273.62(a)(20) or as items to be included in a calculation or requirement as in the definitions of "Large Quantity Handler of Universal Waste" and "Small Quantity Handler of Universal Waste."3. In addition to the requirements
for lampscontained in 40 CFR 273, the following requirements shall apply:a. A used lamp shall be considered to be discarded and a waste on the date the generator permanently removes it from its fixture. An unused lamp becomes a waste on the date the generator discards it since that is the date on which he is deemed to have decided to discard it in accordance with 40 CFR 273.5(c)(2).
b. Universal waste lamps may be crushed or intentionally broken on the site of generation to reduce their volume; however, breaking, crushing, handling, and storage must occur in a safe and controlled manner that minimizes the release of mercury to the workplace and the environment and must comply with 29 CFR 1910.1000. The procedure for breaking, crushing, handling and storing of the lamps must be documented and use a mechanical unit specifically designed for the process that incorporates the containment and filtration of process air flows to remove mercury-containing vapors and dusts.c. All handlers of universal waste (large or small quantity) who crush mercury-containing lamps under these universal waste regulations shall comply with the following provisions:(1) The handler must use a mercury-containing lamp crusher indoors with air pollution controls that capture both particulate and vapor phase mercury. At a minimum, these controls must include, or must be equivalent to the protection provided by a HEPA filter, activated charcoal, and a negative air flow (vacuum) through the crusher unit. The crusher must have documentation from the manufacturer that demonstrates that the unit:(a) Is capable of achieving the Occupational Safety and Health Administration Permissible Exposure Limit (PEL) for mercury of 0.10 milligram per cubic meter in indoor ambient air (under individual site-specific use conditions); and(b) Achieves a particle retention rate of 99.97% in the HEPA filter (at a particle diameter of 0.3 microns).(2) The handler must develop and implement a written procedure specifying how to safely crush universal waste lamps. This procedure must include: type of equipment to be used to crush the lamps safely, operation and maintenance of the unit in accordance with written procedures developed by the manufacturer of the equipment, and proper waste management practices. The handler must document maintenance activities and keep records of maintenance. In addition, the unit operator must receive training in crushing procedures, waste handling and emergency procedures (training must be documented).(3) Residues, filter media, or other solid waste generated as part of the crushing operation, which are not being reclaimed and which exhibit any characteristics of a hazardous waste, must be managed in accordance with all applicable hazardous waste management requirements.(4) The handler must ensure that spills of the contents of the universal waste lamps that may occur during crushing operations are cleaned up in accordance with 40 CFR 273.13 (d)(2) or 40 CFR 273.33 (d) (2).(5) The handler must store the crushed lamps in closed, nonleaking drums or containers that are in good condition. Transfer of the crushed lamps to other drums or containers is not permitted.(6) Drums or containers used for storage of crushed lamps must be properly sealed and labeled. The label shall bear the words "Universal Waste-Lamp(s)," "Waste Lamp(s)," or "Used Lamp(s)."4. A small quantityb. A handler having a waste subject to the requirements of 40 CFR 273.13(a)(3)(i) or 40 CFR 273.33(a)(3)(l) is also subject to 9VAC20-60-270 and Parts IV (9VAC20-60-305 et seq.), VII (9VAC20-60-420 et seq.), and XII (9VAC20-60-1260 et seq.) of this chapter.c. Small and large quantity handlers of universal waste (i) may only crush mercury-containing lamps for size reduction at the site of generation or under the control of the generator as defined in 9VAC20-60-1505 B 4 and (ii) shall comply with the applicable mercury-containing lamps crushed for size reduction requirements of 9VAC20-60-1505.
d. All large quantity handlers of universal waste lamps (i.e., generators who accumulate 5000 kilograms or more of universal waste lamps) must prepare and maintain a closure plan conforming to the requirements of 40 CFR Part 264, Subpart G as adopted by reference in 9VAC20-60-264. Financial assurance shall be provided to the department in accordance with 40 CFR Part 264, Subpart H as adopted by reference in 9VAC20-60-264.
e. The owner or operator of a destination facility that recycles mercury-containing lamps with or without storing the mercury-containing lamps before they are recycled must comply with all applicable requirements of 9VAC20-60-264 B 34 and 9VAC20-60-265 B 21 of this section for mercury-containing lamp recycling facilities.
9VAC20-60-1505. Additional universal wastes.
Note: At this time, there are no universal wastes that are not also universal wastes under 40 CFR Part 273 or 9VAC20-60-273 B.A. The Commonwealth of Virginia incorporates at 9VAC20-60-273 A all universal wastes adopted by the federal government at 40 CFR Part 273. In addition to the universal wastes listed in 40 CFR Part 273, the universal wastes listed in this section are also universal wastes in Virginia if the requirements as provided in this section for each particular universal waste are met.
B. Mercury-containing lamps may be crushed for size reduction provided the requirements of this subsection are met.
1. Mercury-containing lamps are crushed under the control of the generator as defined in subdivision 4 of this subsection, and the crushed lamps are sent off site for recycling.
2. The use of mobile crushing units is prohibited. Mobile crushing units include any device or equipment or combination of devices and equipment that is designed to be transported and operated at more than one site.
3. Mercury-containing lamps that are crushed for size reduction by a generator or under the control of the generator as defined in subdivision 4 of this subsection may be managed under the provisions for universal wastes, 9VAC20-60-273, if the owner or operator complies with all the requirements and qualifications of this section.
4. "Under the control of the generator" means:
a. That the mercury-containing lamps are generated and crushed at the generating facility (for purposes of this definition, generating facility means all contiguous property owned, leased, or otherwise controlled by the universal waste (UW) lamp generator); or
b. That the mercury-containing lamps are generated and crushed at different facilities if the crushing facility is controlled by the generator or if both the generating facility and the crushing facility are controlled by a person as defined in 40 CFR Part 260.10, and if the generator provides one of the following certifications: (i) "on behalf of [insert generator facility name], I certify that this facility will send the indicated UW lamps to [insert crushing facility name], which is controlled by [insert generator facility name] and that [insert the name of either facility] has acknowledged full responsibility for the safe management of the UW lamps" or (ii) "on behalf of [insert generator facility name] I certify that this facility will send the indicated UW lamps to [insert crushing facility name], that both facilities are under common control, and that [insert name of either facility] has acknowledged full responsibility for the safe management of the UW lamps." For purposes of this certification, "control" means the power to direct the policies of the facility, whether by the ownership of stock, voting rights, or otherwise, except that contractors who operate facilities on behalf of a different person as defined in 40 CFR Part 260.10 shall not be deemed to "control" such facilities. The certification shall be submitted to the department in accordance with subdivision 7 (h) of this subsection.
5. Mercury-containing lamp crushing operations that do not meet the definition of "under the control of the generator" in subdivision 4 of this subsection are subject to all applicable requirements for destination facilities in 40 CFR Part 273, Subpart E.
6. Safety hazards to operating personnel shall be controlled through an active safety program consistent with the requirements of 29 CFR Part 1910.
7. Crushing, handling, and storing mercury-containing lamps shall occur in a safe and controlled manner that minimizes the release of mercury to the environment. Requirements for a safe and controlled manner shall include the following:
a. Mercury-containing lamps shall be crushed in a mechanical unit specifically designed to crush mercury-containing lamps. This unit shall be hermetically sealed, except for air intakes, and under negative pressure. Air intake points must be closed when the unit is not operating.
b. Crushing operations shall occur in a space with its ambient air isolated from other work areas where persons who are not involved in the crushing operation may work. The ambient air from rooms containing crushing operations shall be discharged after filtration directly to an area outside the building where persons are unlikely to be directly exposed. If a situation exists at a particular facility in which the facility determines that discharge of ambient air from a room containing a crushing operation to the outside is technically or financially impracticable, the department may approve an alternated design that allows the discharge of ambient air from a room containing a crushing operation to another internal building space or centralized air circulation system if:
(1) The ambient air is discharged to the internal building space or centralized air circulation system through filtration system capable of capturing both particulate and vapor phase mercury.
(2) The filtration system is maintained as recommended by the manufacturer to ensure that it operates at its design mercury removal efficiency.
(3) Maintenance of the filtration system shall be documented and records of maintenance shall be kept on site.
c. Mercury-containing lamps shall be crushed with a device that is equipped with air pollution controls that capture both particulate and vapor phase mercury. At a minimum, these controls shall include a HEPA filter, a sorption column of sulfur impregnated activated carbon media, and a negative air flow (vacuum) throughout the unit. The crushing unit shall have documentation from the manufacturer that demonstrates that the unit is equipped as required and:
(1) Achieves a particle retention rate of 99.97% in the HEPA filter (at a particle diameter less than 0.3 microns); and
(2) Achieves the air emission limits specified in the risk-based protectiveness standards table of subdivision 7 n (2) of this subsection.
d. Mercury-containing lamps shall be crushed indoors.
e. The transfer of crushed mercury-containing lamps in drums or containers to other drums or containers is not permitted.
f. Crushed mercury-containing lamps shall be stored in closed and hermetically sealed, nonleaking drums or containers that are in good condition (e.g., no severe rusting, no apparent structural defects, and no leaking).
g. Drums or containers used for storage of crushed mercury-containing lamps shall be properly sealed and labeled. The label shall bear the words "universal waste-lamps," "waste lamps," or "used lamps."
h. The generator or facility under the control of the generator shall make written notification to the department of the physical location of the crushing operation no later than 30 calendar days after (insert effective date of this section) for all existing operations or 30 calendar days prior to beginning operation of a new crushing operation. The notification shall include the name of the individual or company that owns the operation; the EPA ID number if one has been issued for the facility; the location of the crushing operation; and the names, addresses, and telephone numbers of the operator and principal contact person or persons. A written notice of changes in the notification data shall be sent to the department within 15 calendar days of the change. The notification shall include the certification required under subdivision 4 (b) of this subsection if applicable.
i. A written procedure specifying how to safely crush, handle, and store mercury-containing lamps and how to minimize the release of mercury, including during drum changes and malfunctions, shall be developed, implemented, and documented. This procedure shall include (i) the type of equipment to be used to crush mercury-containing lamps safely, (ii) instructions for proper equipment operation and a schedule for maintenance of the unit in accordance with written procedures developed by the manufacturer of the equipment, (iii) proper waste management practices, and (iv) the use of personal protective equipment to include at a minimum safety glasses or full face shield and cut-proof gloves. The maintenance schedule shall identify all maintenance operations and the frequency with which they must be performed, including replacement of particle filters and the activated carbon media as recommended by the manufacturer of the crushing unit.
j. Maintenance activities shall be documented and records of maintenance shall be maintained and available for inspection per subdivision 8 of this subsection.
k. Each unit operator shall receive initial and annual training in crushing procedures, waste handling, safety, use of personal protective equipment, and emergency procedures, including proper procedures for cleaning up broken mercury-containing lamps. All training shall be documented and records of training shall be maintained and available for inspection per subdivision 8 of this subsection.
l. Residues, filter media, used equipment, other mercury-containing equipment, and other solid waste shall not be placed in the container with the crushed mercury-containing lamps. Any waste materials generated as part of the crushing operation that are determined to be hazardous waste shall be managed under this chapter, as hazardous waste or if not hazardous waste, as a solid waste under the Solid Waste Management Regulations, 9VAC20-81.
m. Any spills of the contents of the mercury-containing lamps that may occur shall be cleaned up in accordance with 40 CFR Part 273.13(d)(2) or 40 CFR Part 273.33(d)(2).
n. All generators or facilities under the control of the generator that crush mercury-containing lamps, except those generators or facilities that crush two hours or less and no more than 220 pounds/100 kilograms (CESQG equivalent) of bulbs per month, shall provide monitoring as follows:
(1) Ambient air within the lamp crushing room and exhaust air from the lamp crushing unit shall be tested for mercury during the first month of using the lamp crushing unit and whenever the unit is modified or replaced, and annually thereafter. In addition, all connection points for hoses circulating air from within the unit, the seal between the unit and the drum, and openings in the crushing unit (e.g., the lamp feed tube) shall also be tested for mercury release during the first month of lamp crushing operation and annually thereafter. Routine maintenance of the machine does not constitute modified or replaced for purposes of requiring ambient air testing. Ambient air shall be tested within five feet of the lamp crushing device. Exhaust air and other tests shall be performed within two inches of the designated testing points on the lamp crushing device. All mercury testing required by this section shall be performed at a time when the lamp crushing device is being used to crush mercury-containing lamps.
(2) Testing for mercury releases from lamp crushing units shall be performed using a mercury vapor analyzer that has been approved for the application by the U.S. Occupational Safety and Health Administration or the Virginia Department of Labor and Industry, or a comparable device that has been calibrated by the manufacturer or laboratory providing the equipment. Mercury vapor monitors used for testing must be capable of detecting mercury at the applicable concentrations provided below or lower in air and must be equipped with a data recording device to provide a record of measurements taken. Mercury monitoring data shall be documented and available for inspection per subdivision 8 of this subsection. The acute exposure protectiveness standard is 300 µg/m3 for a 10-minute exposure with the understanding that the acute exposure protectiveness standard is considered a ceiling value and at no time during bulb crushing operation will the air concentrations of mercury exceed 300 µg/m3. Alternately, compliance with the acute exposure protectiveness standard may be demonstrated by comparing the 95% upper confidence level of the mean of the individual data points to the standard. The following are risk-based protectiveness standards at a distance of five feet from the bulb crushing unit:
Monthly Bulb Crushing Duration (X Hours/Month)*
Chronic Exposure Air Emission Limit (µg/m3)
Acute Exposure Air Emission Limit (µg/m3)
X ≥ 32
1.314skin µg/m3
300 µg/m3
8 < X < 32
6.317 skin µg/m3
300 µg/m3
X ≤ 8
27.375 skin µg/m3
300µg/m3
X ≤ 2
and no more than 220 lbs/month or 100 kg/month of bulbs crushed
Monitoring not required
Monitoring not required
*Monthly crushing duration is determined based on the maximum number of hours that bulb crushing occurred in any one month over the last 12-month period.
(3) Any lamp crushing device that, when tested as described above, fails to meet the criteria specified in subdivision 7 n (2) of this subsection, must immediately be removed from service. Lamp crushing devices removed from service under this subdivision may not be returned to service until the device has been inspected and repaired, and in subsequent testing has been shown to meet the specified criteria. Test data and documentation of repairs shall be kept in the facility record and available for inspection per subdivision 8 of this subsection.
(4) The facility shall document the amount of time spent crushing lamps and this information shall be maintained in the facility record and available for inspection per subdivision 8 of this subsection.
8. A copy of all records, notifications, certifications, and reports required by this section shall be kept on site and be available for examination by the department for a period of at least three years.
9. All requirements of this section shall be immediately effective for all new facilities beginning operations on or after (insert effective date of this section). All requirements of this section shall be effective for all existing facilities no later than 90 calendar days after (insert effective date of this section).
VA.R. Doc. No. R12-3084; Filed October 9, 2015, 2:06 p.m.