Source: https://www.federalregister.gov/documents/2003/11/17/03-28650/hazardous-waste-management-system-identification-and-listing-of-hazardous-waste-proposed-exclusion
Timestamp: 2017-09-24 05:35:02
Document Index: 23019828

Matched Legal Cases: ['§\u2009261', '§\u2009260', 'art 261', '§\u2009260', '§\u2009261', '§\u2009261', 'art 264', 'arth1', '§\u2009260', '§\u2009261', 'art 261', 'art 261', 'art 261', '§\u2009268', 'art 261']

The EPA will accept comments until January 2, 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 December 2, 2003. The request must contain the information prescribed in 40 CFR 260.20(d).
64834-64843 (10 pages)
SW-FRL-7587-3
https://www.federalregister.gov/d/03-28650 https://www.federalregister.gov/d/03-28650
The EPA is proposing to grant a petition submitted by American Chrome & Chemicals L.P. (ACC) to exclude (or delist) certain dewatered sludge from the production of chrome oxide green pigments (K006) generated at its Corpus Christi, Texas facility from the lists of hazardous wastes.
Please send three copies of your comments. You should send two copies to the Section Chief of the Corrective Action and Waste Minimization Section, Multimedia Planning and Permitting Division, (6PD-C), Environmental Protection Agency, 1445 Ross Avenue, Dallas, Texas 75202. You should send a third Start Printed Page 64835copy to Wade Wheatley, Industrial Hazardous Waste Permits Division, Technical Evaluation Team, Texas Commission on Environmental Quality (TCEQ), P.O. Box 13087, Austin, Texas, 78711-3087. Identify your comments at the top with this regulatory docket number: “F-03-TXDEL-ACC” You may submit your comments electronically to peace.michelle@epa.gov.
ACC's petition requests a delisting for a listed hazardous waste. ACC does not believe that the petitioned waste meets the criteria of K006 for which the EPA listed it. ACC 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) (hereinafter all sectional references are to 40 CFR unless otherwise indicated). 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 petition 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 ACC's facility is based on the information submitted in support of this rule, including descriptions of the wastes and analytical data from the Corpus Christi, Texas facility.
ACC originally proposed to dispose of the dewatered sludge in an on-site surface impoundment. However, because the DRAS model cannot accommodate ACC's site specific parameters for the surface impoundment scenario, accurate estimates of potential ground water risks could not be made. Therefore, ACC has determined that the delisted waste will be disposed of in a non-hazardous waste landfill. If the delisting exclusion is finalized, ACC will dispose of the petitioned waste, dewatered sludge, at a Subtitle D solid waste landfill.
Because the EPA is issuing this exclusion under the Federal RCRA delisting program, only states subject to Federal RCRA delisting provisions would be affected. This would exclude Start Printed Page 64836two categories of states: States having a dual system that includes Federal RCRA requirements and their own requirements, and states which have received authorization from the EPA to make their own delisting decisions.
The EPA allows states to impose its 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.
The EPA has also authorized some states (for example, Louisiana, Georgia, Illinois) to administer a RCRA delisting program in place of the Federal program, that is, to make state delisting decisions. Therefore, this exclusion does not apply in those authorized states unless that state makes the rule part of its authorized program. If ACC transports the petitioned waste to or manages the waste in any state with delisting authorization, ACC must obtain delisting authorization from that state before it can manage the waste as nonhazardous in the state.
A delisting petition is a request from a facility to the EPA or an authorized state to exclude wastes from the list of hazardous wastes. The facility petitions the Agency because it does not consider the wastes hazardous under RCRA regulations.
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 we listed the waste if a reasonable basis exists that these additional factors could cause the waste to be hazardous.
On April 17, 2002, ACC petitioned the EPA to exclude from the list of hazardous waste contained in § 261.32, the dewatered sludge generated from its facility located in Corpus Christi, Texas. The waste, the EPA Hazardous Waste No. K006, falls under the classification of listed waste because of the “derived-from” rule in § 261.3. Specifically, in its petition, ACC requested that the EPA grant an exclusion for 1450 cubic yards per year of dewatered sludge resulting from its process of manufacturing chromic oxide. The resulting waste is listed, in accordance with the “derived-from” rule.
ACC's wastewater sludge contains approximately 11% solids. The petitioned waste is only the dewatered portion of the sludge, not the entire sludge (solids and wastewater) that is generated from the current wastewater treatment process. Currently, ACC discharges the wastewater sludge through Outfall 201, into an on-site storage tank. The discharge is permitted by Texas Commission on Environmental Quality (TCEQ) through a Texas Pollution Discharges Elimination System (TPDES) Permit No. 003490 (EPA NPDES Permit No. TX0004685).
The ACC facility is located in an industrial/commercial setting in the western portion of the City of Corpus Christi, Nueces County, Texas. ACC produces various grades of chromic oxide at their Corpus Christi, Texas facility. Chromic oxide is produced through the chemical reaction of sodium dichromate and ammonium sulfate. The produced chromic oxide is washed to create the desired purity of the final product. The sludge generated from this process is listed hazardous waste and identified as K006. The facility operates 24 hours per day, 7 days per week, 365 days per year with the exception of periodic planned shutdowns for routine maintenance.
(2) results of the total constituent list for 40 CFR part 264, appendix IX Start Printed Page 64837volatiles, semivolatiles, metals, pesticides, herbicides, and PCBs;
The EPA believes that the descriptions of the ACC hazardous waste process and analytical characterization in conjunction with the proposed verification testing requirements (as discussed later in this document), provide a reasonable basis to grant ACC's petition for an exclusion of the petitioned waste. The EPA believes the data submitted in support of the petition show the dewatered sludge is non-hazardous. Analytical data for the petitioned waste samples were used in the Delisting Risk Assessment Software (DRAS). The EPA has reviewed the sampling procedures used by ACC and has determined they satisfy the EPA criteria for collecting representative samples of the variations in constituent concentrations in the dewatered wastewater sludge. The data submitted in support of the petition show that constituents in ACC's waste are presently below health-based levels used in the delisting decision-making. The EPA believes that ACC has successfully demonstrated that the petitioned waste is non-hazardous.
For this delisting determination, the EPA used such information gathered to identify plausible exposure routes (i.e., ground water, surface water, air) for hazardous constituents present in the petitioned waste. The EPA determined that disposal in a Subtitle D landfill is the most reasonable, worst-case disposal scenario for ACC's petitioned waste. The EPA applied the DRAS described in 65 FR 58015 (September 27, 2000) and 65 FR 75637 (December 4, 2000), to predict the maximum allowable concentrations of hazardous constituents that may be released from the petitioned waste after disposal and determined the potential impact of the disposal of ACC's petitioned waste on human health and the environment. A copy of this software can be found on the World Wide Web at http://www.epa.gov/​earth1r6/​6pd/​rcra_​c/​pd-o/​dras.htm. In assessing potential risks to ground water, the EPA used the maximum estimated waste volumes and the maximum reported extract concentrations as inputs to the DRAS program to estimate the constituent concentrations in the ground water at a hypothetical receptor well down gradient from the disposal site. Using the risk level (carcinogenic risk of 10−5 and non-cancer hazard index of 0.1), the DRAS program can back-calculate the acceptable receptor well concentrations (referred to as compliance-point concentrations) using standard risk assessment algorithms and Agency health-based numbers. Using the maximum compliance-point concentrations and the EPA Composite Model for Leachate Migration with Transformation Products (EPACMTP) fate and transport modeling factors, the DRAS further back-calculates the maximum permissible waste constituent concentrations not expected to exceed the compliance-point concentrations in ground water.
The EPA believes that the EPACMTP fate and transport model represents a reasonable worst-case scenario for possible ground water contamination resulting from disposal of the petitioned waste in a landfill, and that a reasonable worst-case scenario is appropriate when evaluating whether a waste should be relieved of the protective management constraints of RCRA Subtitle C. The use of some reasonable worst-case scenarios results in conservative values for the compliance-point concentrations, and ensures that the waste, once removed from hazardous waste regulation, will not pose a significant threat to human health or the environment.
The DRAS also uses the maximum estimated waste volumes and the maximum reported total concentrations to predict possible risks associated with releases of waste constituents through surface pathways (e.g., volatilization or wind-blown particulate from the landfill). The DRAS uses the risk level, the health-based data and standard risk assessment and exposure algorithms to predict maximum compliance-point concentrations of waste constituents at a hypothetical point of exposure. Using fate and transport equations, the DRAS uses the maximum compliance-point concentrations and back-calculates the maximum allowable waste constituent concentrations (or “delisting levels”).
The EPA also considers the applicability of ground water monitoring data during the evaluation of delisting petitions. In this case, ACC has never directly disposed of this material in an on-site solid waste landfill, so no representative data exists. Therefore, the EPA has determined that it would be unnecessary to request ground water monitoring data.
The EPA believes that the descriptions of ACC's hazardous waste process and analytical characterization provide a reasonable basis to conclude that the likelihood of migration of hazardous constituents from the petitioned waste will be substantially reduced so that short-term and long-term threats to human health and the environment are minimized.
The DRAS results which calculate the maximum allowable concentration of chemical constituents in the waste along with the data summary of the detected constituents are presented in Table I. Based on the comparison of the DRAS results and maximum TCLP concentrations, the petitioned waste should be delisted because no constituents of concern exceed the delisting concentrations.
Table I.—Maximum Total and TCLP Constituent Concentrations of the Dewatered Wastewater Sludge 1
Maximum allowable TCLP concentration from DRAS (mg/L)
Arsenic 74.3 *0.00495 0.0377
Barium 21.8 *5 100
Chromium 113,000 0.644 5
Thallium 23 *0.05 0.355
Zinc 38.8 *0.1 1130
*Denotes that the constituent was not detected at the noted detection limit
The EPA concluded, after reviewing ACC's processes that no other hazardous constituents of concern, other than those for which ACC tested, are likely to be present or formed as reaction products or by products in ACC's waste. In addition, on the basis of explanations and analytical data provided by ACC, pursuant to § 260.22, the EPA concludes that the petitioned waste does not exhibit any of the characteristics of ignitability, corrosivity, or reactivity. See §§ 261.21, 261.22, and 261.23, respectively.
During the evaluation of ACC's petition, the EPA also considered the potential impact of ACC's 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 ACC's petitioned waste is unlikely. Therefore, no appreciable air releases are likely from the petitioned waste under any likely disposal conditions. The EPA evaluated the potential hazards resulting from the unlikely scenario of airborne exposure to hazardous constituents released from ACC's petitioned waste 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 ACC's petitioned waste. A description of the EPA's assessment of the potential impact of ACC's petitioned waste, regarding airborne dispersion of waste contaminants, is presented in the RCRA public docket for this proposed rule, F-03-TXDEL-ACC.
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 action due to the 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 ACC's petitioned waste were released from a municipal solid waste landfill through runoff and erosion. See the RCRA public docket for this proposed rule for further information on the potential surface water impacts from 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 (USEPA, OWRS, 1987). The EPA, therefore, concluded that the petitioned waste would not present potential hazard to human health and the environment via the surface water exposure pathway.
The descriptions of ACC's hazardous waste process and analytical characterization, with the proposed verification testing requirements (as discussed later in this notice), 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 I). We believe ACC's process will substantially reduce the likelihood of migration of hazardous constituents from the petitioned waste. ACC's process also minimizes short-term and long-term threats from the petitioned waste to human health and the environment.
The EPA has reviewed the sampling procedures used by ACC and has determined they satisfy the EPA criteria for collecting representative samples of variable constituent concentrations in the petitioned sludge. The data submitted in support of the petition show that constituents in ACC's petitioned waste are presently below the compliance point concentrations used in the delisting decision-making and would not pose a substantial hazard to the environment.
The EPA believes that ACC has successfully demonstrated that the petitioned waste is non-hazardous, and therefore, proposes to grant an exclusion to ACC, in Corpus Christi, Texas, for the dewatered sludge described in its petition. The EPA's decision to exclude this waste is based on descriptions of the treatment activities and characterization of the petitioned waste.
The petitioner, ACC, must comply with the requirements in 40 CFR part 261, appendix IX, Table 2 as amended by this notice. The text below gives the rationale and details of those requirements.
This paragraph provides the levels of constituents for which ACC must test the leachate from the dewatered sludge, below which the waste would be considered nonhazardous.
The EPA selected the set of constituents specified in Paragraph (1) Start Printed Page 64839of 40 CFR part 261, appendix IX, Table 2, based on information in the petition. We compiled the list from the composition of the waste, descriptions of ACC's treatment process, 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 of the waste.
The purpose of this paragraph is to ensure that any dewatered sludge which might contain hazardous levels of constituents are managed and disposed of in accordance with Subtitle C of RCRA. Holding the petitioned waste until characterization is complete will protect against improper handling of hazardous material. If the EPA determines that the data collected under this Paragraph do not support the data provided in the petition, the exclusion will not cover the petitioned waste. The exclusion is effective when we sign it, but the disposal cannot begin until the verification sampling is completed. The dewatered sludge must pass paint filter test as described in EPA SW-846, Method 9095 before it is allowed to be shipped off-site. ACC must maintain a record of the date and the actual volume of the dewatered sludge removed from the tank according to the requirements in Paragraph (5).
ACC shall conduct verification testing each time it is ready to evacuate the tank sludge for disposal. Four (4) representative composite samples for verification shall be collected from the dewatered sludge. ACC shall analyze the verification samples according to the constituent list specified in Paragraph (1) of 40 CFR part 261, appendix IX, Table 2. The results from each event should be submitted to EPA within 10 days of receiving the results.
If EPA determines that the data collected under this Paragraph do not support the data provided for the petition, the exclusion will not cover the generated wastes. The EPA will notify ACC of the decision in writing within two weeks of receiving this information.
Paragraph (4) would allow ACC the flexibility of modifying its processes (for example, changes in equipment or change in operating conditions) to improve its treatment process. ACC must prove the effectiveness of the modified process by testing and request approval from the EPA. ACC must manage wastes generated during the new process demonstration as hazardous waste until it receives a written approval from the EPA and the delisting levels specified in Paragraph (1) are satisfied.
If the proposed exclusion is made final, it will apply only to 1450 cubic yards of dewatered sludge, generated annually at the ACC's facility after successful verification testing.
ACC must manage waste volumes greater than 1450 cubic yards of petitioned waste as hazardous until the EPA grants a new exclusion.
When this new exclusion becomes final, ACC's management of the waste covered by this petition would be relieved from Subtitle C jurisdiction. ACC must ensure that it delivers the waste to an off-site storage, treatment, or disposal facility that has a state permit, license, or registration to manage municipal or industrial solid waste.
The EPA would require ACC to file a new delisting petition under any of the following circumstances:
(a) If it significantly alters the manufacturing process treatment system except as described in Paragraph (4)
(b) If it uses any new manufacturing or production process(es), or significantly changes from the current process(es) described in its petition; or
To provide appropriate documentation that ACC's facility is properly treating the waste, ACC must compile, summarize, and keep delisting records on-site for a minimum of five years. They must keep all analytical data obtained through Paragraph (3) including quality control information for five years. Paragraph (5) requires that ACC furnish these data when the EPA or the State of Texas request them for inspection.
The purpose of Paragraph (6) is to require ACC 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. ACC must also use this procedure if the verification sampling testing fails to meet the delisting 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 Agency. 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 ACC to report differing site conditions or assumptions used in the petition in addition to failure to meet the verification testing conditions within 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 we receive new information that calls into question the assumptions underlying the delisting.
The Agency believes a clear statement of its authority in delistings is merited in light of Agency 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 Agency 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 ACC provide a one-time notification to any state regulatory agency through which or to which the delisted waste is being carried. ACC must provide this notification within 60 days of commencing this activity.
If ACC violates the terms and conditions established in the exclusion, the Agency will start procedures to withdraw the exclusion. Where there is an immediate threat to human health and the environment, the Agency will evaluate the need for enforcement activities on a case-by-case basis. The Agency expects ACC to conduct the appropriate waste analysis and comply with the criteria explained above in Paragraph (1) of this exclusion. Start Printed Page 64840
The EPA is requesting public comments on this proposed decision. Please send three copies of your comments. Send two copies to Section Chief, Corrective Action and Waste Minimization Section, Multimedia Planning and Permitting Division (6PD-C), Environmental Protection Agency (EPA), 1445 Ross Avenue, Dallas, Texas 75202. Send a third copy to Industrial Hazardous Waste Permits Division, Technical Evaluation Team, Texas Commission on Environmental Quality (TCEQ), P.O. Box 13087, Austin, Texas, 78711-3087. Identify your comments at the top with this regulatory docket number: “F-03-TXDEL-ACC.” You may submit your comments electronically to peace.michelle@epa.gov.
When such a statement is required for the EPA rules, under section 205 of the UMRA EPA must identify and consider alternatives, including the least costly, most cost-effective, or least burdensome alternative that achieves the objectives of the rule. The EPA must select that alternative, unless the Administrator explains in the final rule why it was not selected or it is inconsistent with law.
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 Agency 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 Agency. 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.
Under Executive Order 13084, the EPA may not issue a regulation that is not required by statute, that significantly affects or uniquely affects the communities of Indian tribal governments, and that imposes substantial direct compliance costs on Start Printed Page 64841those communities, unless the Federal government provides the funds necessary to pay the direct compliance costs incurred by the tribal governments.
Under section 12(d) if the National Technology Transfer and Advancement Act, the Agency 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 Agency to provide Congress, through the OMB, an explanation of the reasons for not using such standards.
Under section 6 of Executive Order 13132, the EPA may not issue a regulation that has federalism implications, that impose substantial direct compliance costs, and that is not required by statute, unless the Federal government provides the funds necessary to pay the direct compliance costs incurred by state and local governments, or the EPA consults with state and local officials early in the process of developing the proposed regulation. The EPA also may not issue a regulation that has federalism implications and that preempts state law unless the Agency consults with state and local officials early in the process of developing the proposed regulation.
Authority: 42 U.S.C. 6905, 6912(a), 6921, 6922, and 6938. 2. In Table 2 of Appendix IX of Part 261 add the following waste stream in alphabetical order by facility to read as follows:
American Chrome & Chemicals Corpus Christi, Texas Dewatered sludge (the EPA Hazardous Waste No. K006) generated at a maximum generation of 1450 cubic yards per calendar year after [publication date of the final rule] and disposed in a Subtitle D landfill.
ACC must implement a verification program that meets the following Paragraphs:
(1) Delisting Levels: All leachable constituent concentrations must not exceed the following levels (mg/l). The petitioner must use the method specified in 40 CFR 261.24 to measure constituents in the waste leachate.
Dewatered wastewater sludge: Arsenic-0.0377; Barium-100.0; Chromium-5.0; Thallium-0.355; Zinc-1130.0.
(A) ACC is a 90 day facility and does not have a RCRA permit, therefore, ACC must store the dewatered sludge following the requirements specified in 40 CFR 262.34, or continue to dispose of as hazardous all dewatered sludge generated, until they have completed verification testing described in Paragraph (3), as appropriate, and valid analyses show that paragraph (1) is satisfied.
(C) If constituent levels in a sample exceed any of the delisting levels set in Paragraph (1), ACC must retreat the batches of waste used to generate the representative sample until it meets the levels. ACC must repeat the analyses of the treated waste.
(D) If the facility does not treat the waste or retreat it until it meets the delisting levels in Paragraph (1), ACC must manage and dispose the waste generated under Subtitle C of RCRA.
(E) The dewatered sludge must pass paint filter test as described in SW 846, Method 9095 before it is allowed to leave the facility. ACC must maintain a record of the actual volume of the dewatered sludge to be disposed of-site according to the requirements in Paragraph (5).
(3) Verification Testing Requirements: ACC must conduct verification testing each time it decides to evacuate the tank contents. Four (4) representative composite samples shall be collected from the dewatered sludge. ACC shall analyze the verification samples according to the constituent list specified in Paragraph (1) and submit the analytical results to EPA within 10 days of receiving the analytical results. If the EPA determines that the data collected under this Paragraph do not support the data provided for the petition, the exclusion will not cover the generated wastes. The EPA will notify ACC the decision in writing within two weeks of receiving this information.
(A) Submit the data obtained through Paragraph 3 to the Section Chief, Corrective Action and Waste Minimization Section, Environmental Protection Agency, 1445 Ross Avenue, Dallas, Texas 75202-2733, Mail Code, (6PD-C) within the time specified.
(7) Notification Requirements: ACC must do the following before transporting the delisted waste: Failure to provide this notification will result in a violation of the delisting petition and a possible revocation of the decision.
(A) Provide a one-time written notification to any State Regulatory Agency to which or through which they will transport the delisted waste described above for disposal, 60 days before beginning such activities. If ACC transports the excluded waste to or manages the waste in any state with delisting authorization, ACC must obtain delisting authorization from that state before it can manage the waste as nonhazardous in the state.
(C) Failure to provide the notification will result in a violation of the delisting variance and a possible revocation of the Exclusion.
[FR Doc. 03-28650 Filed 11-14-03; 8:45 am]