Source: http://www.federalregister.com/Browse/Document/usa/na/fr/2004/2/20/04-3600
Timestamp: 2019-06-20 14:23:05
Document Index: 343060086

Matched Legal Cases: ['§ 261', '§ 261', 'art 261', '§ 261', '§ 260', '§ 260', 'art 261', '§ 260', '§ 261', '§ 261', 'art 261', '§ 260', '§ 261', 'arts 262', 'art 270', 'art 261', 'art 261', '§ 268', 'art 261', 'art 261', '§ 260']

69 FR 34 pgs. 7888-7897 - Hazardous Waste Management System; Identification and Listing of Hazardous Waste; Proposed Exclusion
Type: PRORULEVolume: 69Number: 34Pages: 7888 - 7897
Docket number: [FRL-7625-2]
FR document: [FR Doc. 04-3600 Filed 2-19-04; 8:45 am]
[FRL-7625-2]
The EPA is proposing to grant a petition submitted by Bekaert Corporation (Bekaert) to exclude (or delist) a certain solid waste generated by its Dyersburg, Tennessee, facility from the lists of hazardous wastes.
If finalized, the EPA would conclude that Bekaert's petitioned waste is nonhazardous with respect to the original listing criteria and that the generation of an F006 hazardous waste sludge from the treatment of waste waters from electroplating processes performed by the facility will not be hazardous at the point of generation because of the adequately reduced likelihood of migration of constituents from this waste. The EPA would also conclude that Bekaert's process minimizes short-term and long-term threats from the petitioned waste to human health and the environment.
The EPA will accept comments until April 5, 2004. The EPA will stamp comments received after the close of the comment period as late. These late comments may not be considered in formulating a final decision. Your requests for a hearing must reach the EPA by March 8, 2004. The request must contain the information prescribed in 40 CFR 260.20(d).
Please send three copies of your comments. You should send two copies to the Chief, North Section, RCRA Enforcement and Compliance Branch, Waste Division, U.S. Environmental Protection Agency Region 4, 61 Forsyth Street SW., Atlanta, Georgia, 30303. You should send a third copy to Mike Apple, Director, Division of Solid Waste Management, Tennessee Department of Environment and Conservation, 5th Floor, LC Tower, 401 Church Street, Nashville, Tennessee, 37243-1535. Identify your comments at the top with this regulatory docket number: R4DLP-0401-Bekaert. You may submit your comments electronically to Daryl Himes at Himes.Daryl@epa.gov .
You should address requests for a hearing to Jewell Grubbs, Chief, RCRA Enforcement and Compliance Branch, Waste Division, U.S. Environmental Protection Agency Region 4, Atlanta Federal Center, 61 Forsyth Street SW., Atlanta, Georgia 30303.
For general and technical information about this final rule, contact Daryl Himes, South Enforcement and Compliance Section (Mail Code 4WD-RCRA), RCRA Enforcement and Compliance Branch, U.S. Environmental Protection Agency, Region 4, Sam Nunn Atlanta Federal Center, 61 Forsyth Street, SW., Atlanta, Georgia 30303 or call (404) 562-8614.
C. How will Bekaert manage the waste if it is delisted?
B. Who is Bekaert and what process do they use to generate the petition waste?
C. How did Bekaert sample and analyze the data in this petition?
D. What were the results of Bekaert's analysis?
F. What did the EPA conclude about Bekaert's analysis?
B. What happens if Bekaert violates the terms and conditions?
The EPA is proposing to grant the delisting petition submitted by Bekaert to have its dewatered waste water treatment plant (WWTP) sludge (F006 listed hazardous waste) excluded, or delisted, from the definition of a hazardous waste.
Bekaert's petition requests a delisting for the dewatered wastewater treatment plant (wwtp) sludge which result from the treatment of waste waters generated as a result of its electroplating operations. Bekaert does not believe that the petitioned waste meets the criteria for which the EPA listed it. Bekaert also believes no additional constituents or factors could cause the waste to be hazardous. The EPA's review of this petition included consideration of the original listing criteria, and the additional factors required by the Hazardous and Solid Waste Amendments of 1984 (HSWA). See section 3001(f) of RCRA, 42 U.S.C. 6921(f), and 40 CFR 260.22(d)(1)-(4). In making the initial delisting determination, the EPA evaluated the petitioned waste against the listing criteria and factors cited in § 261.11(a)(2) and (a)(3). Based on this review, the EPA agrees with the petitioner that the waste is nonhazardous with respect to the original listing criteria. (If the EPA had found, based on this review, that the waste remained hazardous based on the factors for which the waste was originally listed, the EPA would have proposed to deny the petition.) The EPA evaluated the waste with respect to other factors or criteria to assess whether there is a reasonable basis to believe that such additional factors could cause the waste to be hazardous. The EPA considered whether the waste is acutely toxic, the concentration of the constituents in the waste, their tendency to migrate and to bioaccumulate, their persistence in the environment once released from the waste, plausible and specific types of management of the petitioned waste, the quantities of waste generated, and waste variability. The EPA believes that the petitioned waste does not meet the listing criteria and thus should not be a listed waste. The EPA's proposed decision to delist waste from the Bekaert facility is based on the information submitted in support of this rule, including descriptions of the wastes and analytical data from the Dyersburg, Tennessee facility.
Bekaert currently sends the petitioned waste to a hazardous waste landfill. If the delisting exclusion is finalized, Bekaert intends to dispose of the petitioned waste ( i.e. , dewatered WWTP sludge) in a subtitle D solid waste landfill in the State of Tennessee.
RCRA section 3010(b)(1) at 42 U.S.C. 6930(b)(1), allows rules to become effective in less than six months after the EPA addresses public comments when the regulated facility does not need the six-month period to come into compliance. That is the case here, because this rule, if finalized, would reduce the existing requirements for persons generating hazardous wastes.
The EPA allows the States to impose their own non-RCRA regulatory requirements that are more stringent than the EPA's, under section 3009 of RCRA, 42 U.S.C. 6929. These more stringent requirements may include a provision that prohibits a Federally issued exclusion from taking effect in the State. Because a dual system (that is, both Federal (RCRA) and State (non-RCRA) programs) may regulate a petitioner's waste, the EPA urges petitioners to contact the state regulatory authority to establish the status of their wastes under the State law. Delisting petitions approved by the EPA Administrator under 40 CFR 260.22 are effective in the State of Tennessee only after the final rule has been published in the Federal Register .
The EPA published an amended list of hazardous wastes from nonspecific and specific sources on January 16, 1981, as part of its final and interim final regulations implementing section 3001 of RCRA. The EPA has amended this list several times and published it in §§ 261.31 and 261.32. The EPA lists these wastes as hazardous because: (1) They typically and frequently exhibit one or more of the characteristics of hazardous wastes identified in subpart C of part 261 (that is, ignitability, corrosivity, reactivity, and toxicity) or (2) they meet the criteria for listing contained in § 261.11(a)(2) or (a)(3).
For this reason, §§ 260.20 and 260.22 provide an exclusion procedure, called delisting, which allows persons to prove that the EPA should not regulate a specific waste from a particular generating facility as a hazardous waste.
In addition, under § 260.22, a petitioner must prove that the waste does not exhibit any of the hazardous waste characteristics (that is, ignitability, reactivity, corrosivity, and toxicity) and present sufficient information for the EPA to decide whether factors other than those for which the waste was listed warrant retaining it as a hazardous waste. ( See part 261 and the background documents for the listed waste.)
Generators remain obligated under RCRA to confirm whether their waste remains nonhazardous based on the hazardous waste characteristics even if the EPA has "delisted" the waste.
Besides considering the criteria in § 260.22(a) and section 3001(f) of RCRA, 42 U.S.C. 6921(f), and in the background documents for the listed wastes, the EPA must consider any factors (including additional constituents) other than those for which the EPA listed the waste if a reasonable basis exists that these additional factors could cause the waste to be hazardous.
The EPA must also consider as hazardous waste mixtures containing listed hazardous wastes and wastes derived from treating, storing, or disposing of listed hazardous waste. See § 261.3(a)(2)(iii) and (iv) and (c)(2)(i), called the "mixture" and "derived-from" rules, respectively. These wastes are also eligible for exclusion and remain hazardous wastes until excluded. See 66 FR 27266 (May 16, 2001).
A. What Waste Did Bekaert Petition the EPA To Delist?
On October 28, 2002, Bekaert petitioned the EPA to exclude from the lists of hazardous waste contained in §§ 261.31 and 261.32, a dewatered WWTP sludge generated from the facility located in Dyersburg, Tennessee. The waste (EPA Hazardous Waste No. F006) is generated by treating wastewater from the copper and zinc electroplating of steel cords for the automobile tire industry. Specifically, in its petition, Bekaert requested that the EPA grant an exclusion for 1250 cubic yards per calendar year of dewatered WWTP sludge resulting from the treatment of waste waters from an electroplating operation at its facility.
Bekaert is a facility located in an industrial setting in the northeast portion of the City of Dyersburg, Tennessee.
Bekaert produces cabled wire which is a major component in the production of steel belted radial tires. The incoming "raw material" from which the wire is drawn is two (2) ton spools of high carbon steel wire rod. As part of the production process, the drawn wire is plated with copper and zinc. Treatment of the waste waters which result from the electroplating process result in the generation of sludges which are classified as F006 listed hazardous wastes pursuant to 40 CFR 261.31. The 40 CFR part 261, appendix VII hazardous constituents for which F006 hazardous wastes are listed include cadmium, hexavalent chromium, nickel, and cyanide (complexed).
To support its petition, Bekaert submitted:
(1) Results of the total constituent analysis for metals;
(2) Results of the Toxicity Characteristic Leaching Procedure (TCLP) extract for the following: volatile and semivolatile organics, pesticides, herbicides, and metals.
D. What Were the Results of Bekaert's Analyses?
The EPA believes that the descriptions of Bekaert's dewatered WWTP sludge, in addition to the data submitted in support of the petition show that the dewatered WWTP sludge is nonhazardous. Analytical data from Bekaert's dewatered WWTP sludge samples were used for evaluation in the Delisting Risk Assessment Software. The data summaries for detected constituents are presented in Table I. The EPA has reviewed the sampling procedures used by Bekaert and has determined they satisfy the EPA's criteria for collecting representative samples of the variations in constituent concentrations in the hazardous waste water treatment sludge. The data submitted in support of the petition show that constituents in Bekaert's waste are presently below health-based levels used in the delisting decision-making. The EPA believes that Bekaert has successfully demonstrated that the dewatered WWTP sludge is nonhazardous.
Antimony 7.4 ND 0.922
Arsenic 7.9 ND 0.0419
Barium 300 ND 100
Cadmium 8.4 ND 0.672
Chromium 85.3 ND 5.0
Copper 1200 ND 4710
Lead 19.6 ND 5.0
Mercury 0.04938 ND 0.2
Nickel 109 ND 127
Selenium 4.94 ND 1.0
Silver 7.9 ND 5.0
Zinc 27,700 74 1260
2,4-D ND 5.96
2,4,5-TP (Silvex) ND 1.0
Benzene ND 0.806
ND 0.560
Chlorobenzene ND 8.51
Chloroform ND 1.09
1,4-Dichlorobenzene ND 2.46
1,2-Dichloroethane ND 0.5
1,1-Dichloroethene ND 0.0982
Methyl ethyl ketone 8.71 200
Tetrachloroethene ND 0.425
Trichloroethene ND 0.5
Vinyl Chloride ND 0.0415
Cresols ND 200
m-Cresol ND 200
m-,p-Cresols ND 200
Pentachlorophenol ND 100
2,4,5-Trichlorophenol ND 400
2,4,6-Trichlorophenol ND 2.0
2,4-Dinitrotoluene ND 0.0915
Hexachlorobenzene ND 0.00295
Hexachlorobutadiene ND 0.5
Hexachloroethane ND 1.38
Nitrobenzene ND 2.0
Pyridine ND 3.19
g-BHC (Lindane) ND 0.003
Chlordane ND 0.0156
Endrin ND 0.02
Heptachlor ND 0.08
Heptachlor epoxide ND 0.08
Methoxychlor ND 10
Toxaphene ND 0.05
1 These levels represent the highest concentration of each constituent found in any one sample. These levels do not necessarily represent the specific levels found in one sample.
ND-Denotes that the constitutent was not detected.
For this delisting determination, we assumed that the waste would be disposed in a Subtitle D landfill and we considered transport of waste constituents through ground water, surface water and air. We evaluated Bekaert's petitioned waste using the Agency's Delisting Risk Assessment Software (DRAS) to predict the concentration of hazardous constituents that might be released from the petitioned waste and to determine if the waste would pose a threat. The DRAS uses EPA's Composite Model for leachate migration with Transformation Products (EPACMTP) to predict the potential for release to groundwater from landfilled wastes and subsequent routes of exposure to a receptor. From a release to ground water, we considered routes of exposure to a human receptor of ingestion of contaminated ground water, inhalation from groundwater via showering and dermal contact while bathing. The DRAS program considers the surface water pathway by erosion of waste from run-off from an open landfill. It evaluates the subsequent routes of exposure to a human receptor from such releases through exposure pathways of fish ingestion and ingestion of drinking water. DRAS also considers releases of waste particles and volatile emissions to air from the surface of an open landfill. From a release to air, we considered routes of exposures of inhalation of particulates and absorption into the lungs, ingestion of particulates eliminated from respiratory passages and subsequently swallowed, air deposition of particulates and subsequent ingestion of the soil/waste mixture, and inhalation of volatile constituents.
We used the maximum estimated waste volume and the maximum reported total and leachate concentration as inputs to estimate the constituent concentrations in the ground water, soil, surface water or air.
Assuming a cancer risk of 1 × 10-5 and a hazard quotient of one, the DRAS program back calculated a maximum allowable concentration level which would not exceed protective levels in both the waste and the leachate for each constituent at the given annual waste volume of 1,250 cubic yards.
The EPA concluded, after reviewing Bekaert's processes that no other hazardous constituents of concern, other than those for which the testing was completed, are likely to be present or formed as reaction products or by-products in Bekaert's wastes. In addition, on the basis of explanations and analytical data provided by Bekaert, pursuant to § 260.22, the EPA concludes that the petitioned wastes do not exhibit any of the characteristics of ignitability, corrosivity, or reactivity. See §§ 261.21, 261.22 and 261.23, respectively.
During the evaluation of this petition, the EPA also considered the potential impact of the petitioned waste via non-ground water routes ( i.e. , air emission and surface runoff). With regard to airborne dispersion in particular, the EPA believes that exposure to airborne contaminants from the petitioned waste is unlikely. Therefore, no appreciable air releases are likely from the dewatered WWTP sludge under any likely disposal conditions. The EPA evaluated the potential hazards resulting from the unlikely scenario of airborne exposure to hazardous constituents released from the waste water treatment sludge in an open landfill. The results of this worst-case analysis indicated that there is no substantial present or potential hazard to human health and the environment from airborne exposure to constituents from the hazardous waste water treatment sludge.
The EPA also considered the potential impact of the petitioned waste via a surface water route. The EPA believes that containment structures at municipal solid waste landfills can effectively control surface water runoff, as the Subtitle D regulations ( See 56 FR 50978, October 9, 1991) prohibit pollutant discharges into surface waters. Furthermore, the concentrations of any hazardous constituents dissolved in the runoff will tend to be lower than the levels in the TCLP leachate analyses reported in this proposal due to the aggressive acidic medium used for extraction in the TCLP. The EPA believes that, in general, leachate derived from the waste is unlikely to directly enter a surface water body without first traveling through the saturated subsurface where dilution and attenuation of hazardous constituents will also occur. Leachable concentrations provide a direct measure of solubility of a toxic constituent in water and are indicative of the fraction of the constituent that may be mobilized in surface water as well as ground water.
Based on the reasons discussed above, the EPA believes that the contamination of surface water through runoff from the waste disposal area is very unlikely. Nevertheless, the EPA evaluated the potential impacts on surface water if the dewatered WWTP sludge were released from a municipal solid waste landfill through runoff and erosion. The estimated levels of the hazardous constituents of concern in surface water would be well below health-based levels for human health, as well as below the EPA Chronic Water Quality Criteria for aquatic organisms (US EPA, OWRS, 1987). The EPA, therefore, concluded that this hazardous waste water treatment sludge is not a present or potential substantial hazard to human health and the environment via the surface water exposure pathway.
The descriptions by Bekaert of the hazardous waste process and analytical characterization, with the proposed verification testing requirements (as discussed later in this proposal), provide a reasonable basis for the EPA to grant the exclusion. The data submitted in support of the petition show that constituents in the waste are below the maximum allowable leachable concentrations (see table 1). The EPA believes that the dewatered WWTP sludge generated by Bekaert contains hazardous constituents at levels which will present minimal short-term and long-term threats from the petitioned waste to human health and the environment.
Thus, the EPA believes that it should grant to Bekaert an exclusion for the dewatered WWTP sludge. The EPA believes the data submitted in support of the petition shows the Bekaert dewatered WWTP sludge to be nonhazardous.
The EPA has reviewed the sampling procedures used by Bekaert and has determined they satisfy the EPA's criteria for collecting representative samples of variable constituent concentrations in the dewatered WWTP sludge. The data submitted in support of the petition show that constituents in Bekaert's waste are presently below the compliance point concentrations used in the delisting decision-making process and would not pose a substantial hazard to the environment. The EPA believes that Bekaert has successfully demonstrated that the dewatered WWTP sludge is nonhazardous.
The EPA therefore proposes to grant an exclusion to Bekaert, in Dyersburg, Tennessee, for the dewatered WWTP sludge described in its petition. The EPA's decision to exclude this waste is based on analysis performed on samples taken of the dewatered WWTP sludge.
If the EPA finalizes the proposed rule, the EPA will no longer regulate the dewatered WWTP sludge under parts 262 through 268 and the permitting standards of part 270.
The petitioner, Bekaert, must comply with the requirements in 40 CFR part 261, appendix IX, table 1 as amended by this proposal. The text below gives the rationale and details of those requirements.
This paragraph provides the levels of constituents for which Bekaert must test the leachate from the dewatered WWTP sludge; the leachate must conform to the standards described below to be considered nonhazardous.
The EPA selected the set of inorganic and organic constituents specified in paragraph (1) and listed in 40 CFR part 261, appendix IX, table 1, based on information in the petition. The EPA compiled the inorganic and organic constituents list from descriptions of the manufacturing process used by Bekaert, previous test data provided for the waste, and the respective health-based levels used in delisting decision-making. These delisting levels correspond to the allowable levels measured in the TCLP extract and total concentrations of the waste.
The purpose of this paragraph is to ensure that Bekaert manages and disposes of any dewatered WWTP sludge that might contain hazardous levels of inorganic and organic constituents according to Subtitle C of RCRA. Holding the dewatered WWTP sludge until characterization is complete will protect against improper handling of hazardous material.
Bekaert must complete a verification testing program on the dewatered WWTP sludge to assure that the dewatered WWTP sludge does not exceed the maximum levels specified in paragraph (1). If the EPA determines that the data collected under this paragraph does not support the data provided for in the petition, the exclusion will not cover the tested waste. This verification program operates on a quarterly basis followed by an annual basis. The first part of the verification testing program consists of testing the dewatered WWTP sludge for specified indicator parameters as per paragraph (1) on a quarterly basis. The quarter testing will be performed for four (4) quarters by taking a composite sample consisting of four (4) grab samples from an individual roll-off container once this rule is final. The first sample can be taken at any time following this rule being final. The remaining quarterly samples shall be taken at ninety (90) day intervals from the taking of the first quarterly sample. If any roll-off fails to meet the specified limits, then Bekaert must dispose of the waste as hazardous.
The second part of the verification testing program is the annual testing of one composite samples of dewatered WWTP sludge for all constituents specified in paragraph (1). The first and subsequent annual tests should coincide with the month during which the final quarterly test was performed. If the annual testing of the waste does not meet the delisting requirements in paragraph (1), Bekaert must notify the EPA according to the requirements in paragraph (6). The EPA will then take the appropriate actions necessary to protect human health and the environment per paragraph (6).
The exclusion is effective upon publication in the Federal Register but the disposal cannot begin until the first quarterly verification sampling is completed and is approved by EPA. Disposal is also not authorized if Bekaert fails to perform the quarterly and yearly testing as specified herein. Should Bekaert fail to conduct the quarterly/yearly testing as specified herein, then disposal of dewatered WWTP sludge as delisted waste may not occur in the following quarter(s)/year(s) until Bekaert obtains the written approval of the EPA.
Paragraph (4) would allow Bekaert the flexibility of modifying its processes (for example, changes in equipment or change in operating conditions) to improve its treatment processes. However, Bekaert must prove the effectiveness of the modified process and request approval from the EPA. Bekaert must manage wastes generated during the new process demonstration as hazardous waste until it has obtained written approval and paragraph (3), is satisfied.
To provide appropriate documentation that Bekaert's facility is managing the dewatered WWTP sludge, Bekaert must compile, summarize, and keep delisting records on-site for a minimum of five years. It should keep all analytical data obtained through paragraph (3) including quality control information for five years. Paragraph (5) requires that Bekaert furnish these data upon request for inspection by any employee or representative of the EPA or the State of Tennessee.
If the proposed exclusion is made final, then it will apply only to 1250 cubic yards per calendar year of dewatered WWTP sludge generated at the Bekaert facility after successful verification testing.
The EPA would require Bekaert to file a new delisting petition under any of the following circumstances:
(a) If Bekaert significantly alters the manufacturing process treatment system except as described in paragraph (4).
(b) If Bekaert uses any new manufacturing or production process(es), or significantly change from the current process(es) described in its petition; or
(c) If Bekaert makes any changes that could affect the composition or type of waste generated.
Bekaert must manage waste volumes greater than 1250 cubic yards per calendar year of dewatered WWTP sludge as hazardous waste until the EPA grants a new exclusion. When this exclusion becomes final, the management by Bekaert of the dewatered WWTP sludge covered by this petition would be relieved from Subtitle C jurisdiction. Bekaert must either (a) treat, store, or dispose of the waste in a State permitted on-site facility, or (b) Bekaert must ensure that it delivers the waste to an off-site storage, treatment, or disposal facility that has a State permit, license, or register to manage municipal or industrial solid waste consistent with the requirements of RCRA.
The purpose of paragraph (6) is to require Bekaert to disclose new or different information related to a condition at the facility or disposal of the waste if it is pertinent to the delisting. Bekaert must also use this procedure if the waste sample in the annual testing fails to meet the levels found in paragraph (1). This provision will allow the EPA to reevaluate the exclusion if a source provides new or additional information to the EPA. The EPA will evaluate the information on which it based the decision to see if it is still correct, or if circumstances have changed so that the information is no longer correct or would cause the EPA to deny the petition if presented.
This provision expressly requires Bekaert to report differing site conditions or assumptions used in the petition in addition to failure to meet the annual testing conditions within ten (10) days of discovery. If the EPA discovers such information itself or from a third party, it can act on it as appropriate. The language being proposed is similar to those provisions found in RCRA regulations governing no-migration petitions at § 268.6.
The EPA believes that it has the authority under RCRA and the Administrative Procedures Act (APA), 5 U.S.C. 551 (1978) et seq. , to reopen a delisting decision. The EPA may reopen a delisting decision when it receives new information that calls into question the assumptions underlying the delisting.
The EPA believes a clear statement of its authority in delistings is merited in light of the EPA experience. See Reynolds Metals Company at 62 FR 37694 (July 14, 1997) and 62 FR 63458 (December 1, 1997) where the delisted waste leached at greater concentrations in the environment than the concentrations predicted when conducting the TCLP, thus leading the EPA to repeal the delisting. If an immediate threat to human health and the environment presents itself, the EPA will continue to address these situations case by case. Where necessary, the EPA will make a good cause finding to justify emergency rulemaking. See APA section 553(b).
In order to adequately track wastes that have been delisted, the EPA is requiring that Bekaert provide a one-time notification to any State regulatory agency through which or to which the delisted waste is being carried. Bekaert must provide this notification within sixty (60) days of commencing this activity.
If Bekaert violates the terms and conditions established in the exclusion, the EPA will initiate procedures to withdraw the exclusion. Where there is an immediate threat to human health and the environment, the EPA will evaluate the need for enforcement activities on a case-by-case basis. The EPA expects Bekaert to conduct the appropriate waste analysis and comply with the criteria explained above in paragraph (1) of the exclusion.
The EPA is requesting public comments on this proposed decision. Please send three copies of your comments. Send two copies to the Chief, North Section, RCRA Enforcement and Compliance Branch, U. S. Environmental Protection Agency Region 4, Atlanta Federal Center, 61 Forsyth Street SW., Atlanta, Georgia 30303. Send a third copy to Mr. Mike Apple, Director, Division of Solid Waste Management, Tennessee Department of Environment and Conservation, 5th Floor, LC Tower, 401 Church Street, Nashville, Tennessee 37243-1535. You should identify your comments at the top with this regulatory docket number: R$DLP-0301-Bekaert.
You should submit requests for a hearing to Jewell Grubbs, Chief, RCRA Enforcement and Compliance Branch, Waste Division, U. S. Environmental Protection Agency Region 4, Atlanta Federal Center, 61 Forsyth Street SW., Atlanta, Georgia 30303.
You may review the RCRA regulatory docket for this proposed rule at the U.S. Environmental Protection Agency Region 4, Atlanta Federal Center, 61 Forsyth Street SW., Atlanta, Georgia 30303.
It is available for viewing in the EPA Freedom of Information Act Review Room from 9 a.m. to 4 p.m., Monday through Friday, excluding Federal holidays. Call (404) 562-8614 for appointments. The public may copy material from any regulatory docket at no cost for the first 100 pages, and at fifteen cents per page for additional copies.
Under Executive Order 12866, the EPA must conduct an "assessment of the potential costs and benefits" for all "significant" regulatory actions.
Information collection and recordkeeping requirements associated with this proposed rule have been approved by the Office of Management and Budget (OMB) under the provisions of the Paperwork Reduction Act of 1980 (Pub. L. 96-511, 44 U.S.C. 3501 et seq. ) and have been assigned OMB Control Number 2050 0053.
The Executive Order 13045 is entitled "Protection of Children from Environmental Health Risks and Safety Risks" (62 FR 19885, April 23, 1997). This order applies to any rule that the EPA determines (1) is economically significant as defined under Executive Order 12866, and (2) the environmental health or safety risk addressed by the rule has a disproportionate effect on children. If the regulatory action meets both criteria, the EPA must evaluate the environmental health or safety effects of the planned rule on children, and explain why the planned regulation is preferable to other potentially effective and reasonably feasible alternatives considered by the EPA. This proposed rule is not subject to Executive Order 13045 because this is not an economically significant regulatory action as defined by Executive Order 12866.
If the mandate is unfunded, the EPA must provide to the Office of Management and Budget, in a separately identified section of the preamble to the rule, a description of the extent of the EPA's prior consultation with representatives of affected tribal governments, a summary of the nature of their concerns, and a statement supporting the need to issue the regulation.
In addition, Executive Order 13084 requires the EPA to develop an effective process permitting elected and other representatives of Indian tribal governments to have "meaningful and timely input" in the development of regulatory policies on matters that significantly or uniquely affect their communities of Indian tribal governments. This action does not involve or impose any requirements that affect Indian Tribes. Accordingly, the requirements of section 3(b) of Executive Order 13084 do not apply to this rule.
Under section 12(d) of the National Technology Transfer and Advancement Act, the EPA is directed to use voluntary consensus standards in its regulatory activities unless to do so would be inconsistent with applicable law or otherwise impractical. Voluntary consensus standards are technical standards ( e.g. , materials specifications, test methods, sampling procedures, business practices, etc.) developed or adopted by voluntary consensus standard bodies. Where available and potentially applicable voluntary consensus standards are not used by the EPA, the Act requires that the EPA provide Congress, through the OMB, an explanation of the reasons for not using such standards.
Executive Order 13132, entitled "Federalism" (64 FR 43255, August 10, 1999) requires the EPA to develop an accountable process to ensure "meaningful and timely input by State and local officials in the development of regulatory policies that have federalism implications." "Policies that have federalism implications" are defined in the Executive Order to include regulations that have "substantial direct effects on the States, on the relationship between the national government and the States, or on the distribution of power and responsibilities among the various levels of government."
Director, Waste Management Division, Region 4.
2. In appendix IX to part 261, in table 1, revise the following waste stream, and in tables 2 and 3, add the following waste stream in alphabeticalorder by facility to read as follows:
Appendix IX to Part 261-Waste Excluded Under §§ 260.20 and 260.22
Bekaert Corp. Dyersburg, TN Dewatered wastewater treatment plant (WWTP) sludge (EPA Hazardous Waste Nos. F006) generated at a maximum rate of 1250 cubic yards per calendar year after [publication date of the final rule] and disposed in a Subtitle D landfill. For the exclusion to be valid, Bekaert must implement a verification testing program that meets the following paragraphs:
(1) Delisting Levels: All leachable concentrations for those constituents must not exceed the maximum allowable concentrations in mg/l specified in this paragraph. Bekaert must use the leaching method specified at 40 CFR 261.24 to measure constituents in the waste leachate. (A) Inorganic Constituents (from Table 1) TCLP (mg/l): Cadmium-0.672; Chromium-5.0; Nickel-127; Zinc-1260.0. (B) Organic Constituents (from Table 1) TCLP (mg/l): Methyl ethyl ketone-200.0.
(2) Waste Holding and Handling: (A) Bekaert must accumulate the hazardous waste dewatered WWTP sludge in accordance with the applicable regulations of 40 CFR 262.34 and continue to dispose of the dewatered WWTP sludge as hazardous waste. (B) Once the first quarterly sampling and analyses event described in paragraph (3) is completed and valid analyses demonstrate that no constituent is present in the sample at a level which exceeds the delisting levels set in paragraph (1), Bekaert can manage and dispose of the dewatered WWTP sludge as nonhazardous according to all applicable solid waste regulations. (C) If constituent levels in any sample taken by Bekaert exceed any of the delisting levels set in paragraph (1), Bekaert must do the following: (i) notify EPA in accordance with paragraph (6) and (ii) manage and dispose the dewatered WWTP sludge as hazardous waste generated under Subtitle C of RCRA. (D) Quarterly Verification Testing Requirements: Upon this exclusion becoming final, Bekaert may begin the quarterly testing requirements of paragraph (3) on its dewatered WWTP sludge.
(3) Quarterly Testing Requirements: Upon this exclusion becoming final, Bekaert may perform quarterly analytical testing by sampling and analyzing the dewatered WWTP sludge as follows: (A)(i) Collect four representative composite samples of the hazardous waste dewatered WWTP sludge at quarterly (ninety (90) day) intervals after EPA grants the final exclusion. The first composite sample may be taken at any time after EPA grants the final approval. (ii) Analyze the samples for all constituents listed in paragraph (1). Any roll-offs from which the composite sample is taken exceeding the delisting levels listed in paragraph (1) must be disposed as hazardous waste in a Subtitle C landfill. (iii) Within forty-five (45) days after taking its first quarterly sample, Bekaert will report its first quarterly analytical test data to EPA. If levels of constituents measured in the sample of the dewatered WWTP sludge do not exceed the levels set forth in paragraph (1) of this exclusion, Bekaert can manage and dispose the nonhazardous dewatered WWTP sludge according to all applicable solid waste regulations.
(4) Annual Testing: (A) If Bekaert completes the quarterly testing specified in paragraph (3) above and no sample contains a constituent with a level which exceeds the limits set forth in paragraph (1), Bekaert may begin annual testing as follows: Bekaert must test one representative composite sample of the dewatered WWTP sludge for all constituents listed in paragraph (1) at least once per calendar year. (B) The sample for the annual testing shall be a representative composite sample (according to SW-846 methodologies) for all constituents listed in paragraph (1). (C) The sample for the annual testing taken for the second and subsequent annual testing events shall be taken within the same calendar month as the first annual sample taken.
(6) Data Submittals: Bekaert must submit the information described below. If Bekaert fails to submit the required data within the specified time or maintain the required records on-site for the specified time, the EPA, at its discretion, will consider this sufficient basis to reopen the exclusion as described in paragraph (6). Bekaert must: (A) Submit the data obtained through paragraph (3) to the Chief, North Section, RCRA Enforcement and Compliance Branch, Waste Division, U.S. Environmental Protection Agency Region 4, 61 Forsyth Street SW., Atlanta, Georgia, 30303, within the time specified. (B) Compile records of analytical data from paragraph (3), summarized, and maintained on-site for a minimum of five years. (C) Furnish these records and data when either the EPA or the State of Tennessee request them for inspection. (D) Send along with all data a signed copy of the following certification statement, to attest to the truth and accuracy of the data submitted: "Under civil and criminal penalty of law for the making or submission of false or fraudulent statements or representations (pursuant to the applicable provisions of the Federal Code, which include, but may not be limited to, 18 U.S.C. 1001 and 42 U.S.C. 6928), I certify that the information contained in or accompanying this document is true, accurate and complete. As to the (those) identified section(s) of this document for which I cannot personally verify its (their) truth and accuracy, I certify as the company official having supervisory responsibility for the persons who, acting under my direct instructions, made the verification that this information is true, accurate and complete. If any of this information is determined by the EPA in its sole discretion to be false, inaccurate or incomplete, and upon conveyance of this fact to the company, I recognize and agree that this exclusion of waste will be void as if it never had effect or to the extent directed by the EPA and that the company will be liable for any actions taken in contravention of the company's RCRA and CERCLA obligations premised upon the company's reliance on the void exclusion."
(7) Reopener: (A) If, anytime after disposal of the delisted waste Bekaert possesses or is otherwise made aware of any environmental data (including but not limited to leachate data or ground water monitoring data) or any other data relevant to the delisted waste indicating that any constituent identified for the delisting verification testing is at level higher than the delisting level allowed by the Regional Administrator or his delegate in granting the petition, then the facility must report the data, in writing, to the Regional Administrator or his delegate within ten (10) days of first possessing or being made aware of that data. (B) If either the quarterly or annual testing of the waste does not meet the delisting requirements in paragraph (1), Bekaert must report the data, in writing, to the Regional Administrator or his delegate within ten (10) days of first possessing or being made aware of that data. (C) If Bekaert fails to submit the information described in paragraphs (5), (6)(A) or (6)(B) or if any other information is received from any source, the Regional Administrator or his delegate will make a preliminary determination as to whether the reported information requires the EPA action to protect human health or the environment. Further action may include suspending, or revoking the exclusion, or other appropriate response necessary to protect human health and the environment. (D) If the Regional Administrator or his delegate determines that the reported information requires action the EPA, the Regional Administrator or his delegate will notify the facility in writing of the actions the Regional Administrator or his delegate believes are necessary to protect human health and the environment. The notification shall include a statement of the proposed action and a statement providing the facility with an opportunity to present information as to why the proposed EPA action is not necessary. The facility shall have ten (10) days from the date of the Regional Administrator or his delegate's notice to present such information. (E) Following the receipt of information from the facility described in paragraph (6)(D) or (if no information is presented under paragraph (6)(D)) the initial receipt of information described in paragraphs (5), (6)(A) or (6)(B), the Regional Administrator or his delegate will issue a final written determination describing the EPA actions that are necessary to protect human health or the environment. Any required action described in the Regional Administrator or his delegate's determination shall become effective immediately, unless the Regional Administrator or his delegate provides otherwise.
(8) Notification Requirements: Bekaert must do the following before transporting the delisted waste: (A) Provide a one-time written notification to any State Regulatory Agency to which or through which it will transport the delisted waste described above for disposal, sixty (60) days before beginning such activities. (B) Update the one-time written notification if Bekaert ships the delisted waste into a different disposal facility. (C) Failure to provide this notification will result in a violation of the delisting variance and a possible revocation of the decision.
[FR Doc. 04-3600 Filed 2-19-04; 8:45 am]