M-/A
United State*
Environmental Protection
Agency
                Solid Waste end
                Emergency Response
                (530BW)
EPA530-R-97-041
NTIS: PB97-177 621
August 1994
Background Document
for Capacity Analysis
for Land Disposal
Restrictions Phase III -
Universal Treatment
Standards, and
Treatment Standards
for Organic Toxicity
Characteristic Wastes
and Other Newly Listed
Wastes (Final Rule)
     Printed on paper that contains at tost 20 percent postconsumer fiber

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I'glled Stain
Environmental Protection
ORInoT
Solid Wule
Washington, D.C HHtO
August 1994
Background Document for
Capacity Analysis for
Land Disposal Restrictions
Phase II - Universal
Treatment Standards, and
Treatment Standards for
Organic Toxicity
Characteristic Wastes and
Other Newly Listed Wastes
(Final Rule)
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                         TABLE OF CONTENTS

CHAPTER I: INTRODUCTION	  -1
      1.1   LEGAL BACKGROUND	- -1
      1.2   CAPACITY ANALYSIS METHODOLOGY	  -1
           1.2.1  Determination of Required Commercial Treatment Capacity ..  -8
           1.2.2  Determination of Available Commercial Treatment Capacity ..  -9
      1.3   SUMMARY OF CAPACITY ANALYSIS FOR TODAY'S RULE ..1-11
      1.4   ORGANIZATION OF BACKGROUND DOCUMENT
           SUPPORTING THE CAPACITY ANALYSIS	1-13

CHAPTER 2: COMMERCIAL TREATMENT CAPACITY	 2-1
      2.1   COMMERCIAL COMBUSTION CAPACITY SUMMARY 	 2-1
           2.1.1  General Methodology	'.	 2-1
           2.1.2  Analysis of Capacity Data	 2-9
           2.1.3  Apportioning Capacity to Individual Waste Forms	2-10
      2.2   COMMERCIAL INCINERATION CAPACITY	2-13
           2.2.1  Individual Incineration Facility Capncity Analysis	2-13
           2.2.2  Other Incinerators Not Included in the Capacity Estimate .... 2-26.
           2.2.3  Future Incineration Capacity	2-27
      2.3   COMMERCIAL BIF HAZARDOUS WASTE CAPACITY	2-28
           2.3.1  Individual BIF Facility Capacity Analysis	2-28
           23.2  Commercial Bffs Not Included in the CKRC Survey	2-39
      2.4   OTHER TREATMENT SYSTEM CAPACITIES	 2-43
           2.4.1  General Approach and Assumptions	2-43
           2.4.2  Summary of Available Capncity for Biological Treatment,
                Chemical Precipitation, and Stabilization	2-44

CHAPTER 3: CAPACITY ANALYSIS FOR TOXICITY CHARACTERISTIC
      WASTES	 3-1
      3.1   BACKGROUND 	 3-2
      3.2   DATA SOURCES  	 3-5
           3.2.1  1992 Survey of Organic Toxicity Characteristic Wastes
                Managed in Land Disposal Units (TC Survey)	 3-5
           3.2.2  Comments on the ANPR.M		3-11
           3.2.3  Capacity Data Obtained  from ih£ Comments to the Proposed
                Rule	3-12
      3.3   METHODOLOGY, ASSUMPTIONS. AND PRELIMINARY
           RESULTS	3-13
           3J.1  Analysis of the TC Survey	,	3-14
           3.3.2  Quantity of Surface Dispo^d Organic TC Wastes Requiring
                Alternative Treatment Due to the LDRs	3-17

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          3.3.3  Newly Identified TC Pesticide Wastes That Were Not
               Previously Hazardous by the Old Extraction Procedure 	3-20
          3.3.4  Quantities of Used Oil Disposed in Landfills	 3-20
     3.4   CAPACITY ANALYSIS FOR TOXICITY CHARACTERISTIC
          WASTES			3-22

CHAPTER 4: CAPACITY ANALYSIS FOR NEWLY LISTED WASTES	  4-1
     4.1   DATA SOURCES AND METHODOLOGY	  4-1
     4.2   REQUIRED CAPACITY ANALYSIS FOR COKE BY-PRODUCT
          WASTES	  4-2
     4.3   REQUIRED CAPACITY ANALYSIS FOR CHLORINATED
          TOLUENE WASTES (K149-K151)	  4-5
     4.4   CAPACITY ANALYSIS FOR OTHER NEWLY LISTEP
          WASTES	  4-6

CH/-.PTER 5: CAPACITY ANALYSIS FOR SURFACE DISPOSED MIXED
     RADIOACTIVE WASTE	  5-1
     5.1   BACKGROUND  	  5-1
     5.2   DATA SOURCES 	  5-2
          5.2.1  Comments on ANPRM		  5-2"
          5.2.2  Comments on Proposed Rule	  5-3
          5.2.3  Non-DOE Mixed Waste Data Sources	,	  5-3
          5.2.4  DOE Mixed Waste Data Sources  	  5-4
     5.3   RESULTS	  5-5
          5.3.1 ' Non-DOE Generation and Storage of Mixed Low-level Waste .  5-5
          5.3.2  DOE-Generated Mixed Waste	  5-7
     .5.4   AVAILABLE CAPACITY FOR MIXED WASTE	5-10
          5.4.1  Existing and Planned Non-DOE Capacity  	5-10
  .  •     5.4.2  Existing and Planned DOE Capacity	5-11
     5.5   NATIONAL CAPACITY VARIANCE FOR MIXED
          RCRA/RADIOACTIVE WASTES	5-13

CHAPTER 6: HAZARDOUS SOIL CONTAMINATED WITH NEWLY
     LISTED AND IDENTIFIED WASTES	  6-1
     6.1   TC SOILS REQUIRING OFF-SITE TREATMENT	  6-1
     6.2   METHODOLOGY USED TO ESTIMATE TC SOILS GENERATED BY
          SURFACE IMPOUNDMENT CLOSURES REQUIRING OFF-SITE
          TREATMENT	  6-2
   .  6.3   TC SOIL GENERATION FROM ROUTINE AND SPORADIC
          ACTIVITIES  . .^.	  6-6
     6.4   TC SOIL GENERATION AND LAND DISPOSAL FROM
          FACILITIES SUBMITTING CONFIDENTIAL BUSINESS
          INFORMATION	  6-8
     6.5   CAPACITY ANALYSIS FOR HAZARDOUS SOIL	  6-8
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 CHAPTER 7: HAZARDOUS DEBRIS CONTAMINATED WITH NEWLY
      LISTED AND IDENTIFIED WASTES	 7-1
      7.1   DATASOURCES	 7-1
           7.1.1 Questionnaire for Facilities that Land Dispose Newly
               Identified Organic Wastes Exhibiting the Toxicity
               Characteristic 	 7-1
           7.1.2 Comments to the Phase I Proposed Rule	 7-2
           7.1.3 Roundtable Meetings	 7-2
           7.1.4 Other Data Sources 	7-10
      7.2   REQUIRED CAPACITY	7-10
      7.3   CAPACITY ANALYSIS FOR HAZARDOUS DEBRIS		7-11

 APPENDIX A: SAMPLE HWTC SURVEY QUESTIONNAIRE

 APPENDIX B: SAMPLE CKRC SURVEY QUESTIONNAIRE

 APPENDIX C: AVAILABLE CAPACITY ANALYSIS TELEPHONE LOGS

 APPENDIX D: SAMPLE TC SURVEY QUESTIONNAIRE

.APPENDIX E: DATA ON NEWLY  IDENTIFIED ORGANIC TC MIXED WASTES

 APPENDIX F: DATA ON DEEP-WELL INJECTED WASTES
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                                                    CHAPTKR 1
                                                  INTRODUCTION
       This document presents the capacity anulysis thnt EPA conducted to support the
 final Land Disposal Restrictions (LDRs) Phase II rule on Universal Treatment Standards
 and Treatment Standards for Organic TC Wastes and Newly Listed Wastes.  EPA
 conducts capacity analyses to evaluate the need for national capacity variances from the
 land disposal prohibitions.' The capacity analysis provides estimates of the quantities of
 wastes that will require  alternative commercial treatment prior to land disposal as a
 result of the LDRs and estimates alternative commercial treatment capacity available to
 manage  wastes restricted from  land disposal.  In this rule, EPA is finalizing LDRs.for
 certain wastes listed and identified between November 1984 and October 1992 that were
 not covered in previous LDR rulemakings as well. ;is high total organic carbon (TOC)
 D001 and TC Pesticide  wastes  injected into Chss I deep wells. The newly listed and
 identified wastes are summarized in Exhibit 1-1.

 1.1    LEGAL BACKGROUND

       The Hazardous and Solid Waste Amendments (HSWA) to the Resource
 Conservation and Recovery Act (RCRA), enacicd  on November 8, 1984, set  basic new
 priorities for hazardous  waste management. Land disposal, which  had been the most
 widely used method for managing hazardous waste, is now ihe least preferred option.
 Under HSWA, EPA must promulgate regulations restricting the land disposal2 of
 hazardous wastes according to a strict statutory schedule.  As of the effective date of
 each regulation, land disposal of untreated wasies covered by that  regulation  is prohibited
 unless  it  can be demonstrated that there  will be nu migration of hazardous constituents
 from the disposal unit for as long as the waste remains hazardous.

       Under the LDRs Program, EPA must identify levels or methods of treatment that
 substantially reduce the  toricity of a waste or the likelihood of migration of hazardous
 constituents from the waste.  Whenever possible, the Agency prefers to define treatment
 in terms  of performance (i.e., levels of treatment, expressed as a concentration of
 hazardous constituents in residuals from treatment) rather than in terms of specific
treatment methods. EPA's standards are generally based on the performance of (he best
demonstrated available technology (BOAT), as documented by treatment data collected
                  1 The LDRs are effective when promulgated unless the Administrator grants a national capacity variance from Ihe
                otherwise applicable date and establishes a different date (not in ccrccJ pro years beyond the statutory deadline) based
                on: '.. the earliest date on »hich adequate alternative treatment, rrcmery. or disposal capacity which protects human
                health and ihe environment mil be available' (RCRA section y*H.,!; dome formation, salt bed formation, or
                underground mine or cave' (RCRA section 3004(10)-
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                                                         1-6
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 at wel!-desiped and well-operated systems using that technology, or are based on data
 derived from the treatment of similar wastes that are as difficult or more difficult to
 treat.

       The LDRs are effective immediately upon promulgation unless the Agency grants
 a national capacity variance from the statutory date because of a lack of available
 treatment capacity (see RCRA section  3004{h)(2).  For every waste, EPA considers, on a
 national basis, both the capacity of commercially available treatment technologies and the
 quantify of restricted wastes currently sent to land disposal for which on-site treatment
 capacity is not available.  If EPA determines that adequate alternative commercial
 treatment capacity is available for a particular waste, the land disposal restriction goes
 into effect immediately.  If not, the Agency establishes an alternative effective date based
 on the t irliest date on which  adequate treatment capacity will be available, or two-years,
 whichever is less.  Once the variance expires, the wastes must meet the LDR treatment
 standards prior to being placed on the land.

       RCRA also allows generators to apply for extensions to the LDRs on a case-by-
case basis for specific wastes generated at a specific facility (RCRA section 3004(h)(3)).
EPA may grant case-by-case extensions to applicants who can demonstrate that: (1) no
capacity currently exists anywhere in the U.S. to treat a specific waste, and (2) a binding
contractual commitment is in  place to construct or otherwise provide alternative capacity,
but due to circumstances beyond the applicant's control, such alternative capacity cannot
reasonably be made available  by  the effective date (40 CFR 268.5).

       HSWA's schedule divided hazardous wastes into three broad categories:  solvent
and dioxin wastes: California iist wastes;3 and "scheduled" wastes.  EPA restricted
surface disposed solvents and  dioxins from land disposal on November 7, 1986 and  deep
well injected solvents and dioxins from land disposal on July 26,  1998. The final rule  for
California List wastes, which was issued on July 8, 1987, covers wastes originally listed by
the State  of California and adopted intact within HSWA.  The "scheduled" wastes consist
of alt wastes that were identified  or listed as hazardous prior to November 8, 1984 but
were not included in the first  two categories listed above.  HSWA's statutory timetable
required that EPA restrict one-third of these wastes by August 8, 198S, two-thirds by
June 8, 1989, and the remaining third by May 8, 1990.  For hazardous wastes that are
newly identified or listed after November 8, 1934, EPA is required to promulgate land
disposal prohibitions within six months of the date of identification or listing (RCRA
Section 3004(g)(4)). However, the statute does not  provide an automatic prohibition  of
land disposal of such wastes if EPA fails to meet this deadline.  Exhibit 1-2 summarizes
the previous LDR rutemakings and their respective  promulgation dates.
                  J The "Cahfoniia Isi* comprises the following classes of «-JMCS: liquid h-turdous wisies uith a pH of less iftan or
               equal to 2.0 (acidic contKxc wastes); alt liquid hazardous *aues confine; Iree cyanides, i-anous metals, and
               potycMoruvUcd bipbenvfc (PCBs) exceeding statutory concerimrioo lc«&: ,_-vJ M tnsies (liquid, sludge, or solid)
               containing halogenaied orpaic compounds (HOCs) in concentrations greater than or equal to specified statutory levels.
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                                    1-7

                                 EXHIBIT 1-2

    SUMMARY OF PREVIOUS LAND DISPOSAL RESTRICTIONS RULEMAKIXGS
Rulemaking
Solvents and Dioxins
(surface disposed )
Solvents arid Dioxins
(deep well injected)
California List
(surface disposed)
California List
(deep well injected)
First Third Rule
First Third Rule
(deep well injected)
Second Third Rule
Third Third Rule
Newly Listed and Identified
Wastes (Phase I)
Interim Final Rule for
Vacated Treatment
Standards
Federal Register Notice
5! FR 40572
53 FR 23188
52 FR 25760
53 FR 30908
53 FR 31 158
54 FR 25416
54 FR 26594 •
55 FR 22520
57 FR 37194
58 FR 29860
Promulgation Date
November 7, 1986
July 26, 1988
JulyS, 1987
July 26, 1988
August 8, 1988
June 7, 1989
June 8, 1989
May 8, 1990
June 30, 1992
May 24, 1993
1.2   CAPACITY ANALYSIS METHODOLOGY

      In evaluating the need for national capacity variances, EPA estimates the
quantities of waste requiring alternative commercial treatment as a result of the land
disposal restrictions and the capacity available ;it commercial treatment facilities to
manage the restricted wastes. By comparing the capacity demand with the available
commercial capacity, EPA can identify capacity  shortfalls and make determinations
concerning national capacity variances. This section provides an overview of EPA's
methodology in estimating required commercial  treatment capacity, briefly summarizes
the capacity analysis conducted for today's rule.  :ind highlights the national capacity
variances that EPA is granting in today's rule.
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                                        1-8

 1.2.1  Determination of Required Commercial Treatment Capacity

       Required commercial treatment capacity represents the quantity of wastes
 currently being land disposed that cannot be treated on site and, consequently, will need
 commercial treatment to meet the LDR treatment standards.  Required commercial
 capacity also includes the residuals generated by treatment of these wastes (i.e., the
 quantity of generated residuals that will need treatment prior to land disposal).

       EPA identities the waste streams potentially affected hy the LDRs by types of
 land disposal units, including surface impoundment, waste pile, land treatment unit,'
 landfill, and underground injection well. Salt dome formations, salt bed  formations, and
 underground mires and caves are additional  methods of land disposal that are affected
 by the LDRs. Since insufficient information  is available to document the quantity of
 wastes disposed of by these three methods, they are not addressed in the analysis of
 required alternative capacity.

       To determine  the type of alternative capacity required to treat the affected wastes,
 EPA conducts a "treatabiiity analysis" of each waste stream.  Based on the waste's
 physical and chemical form and information on prior management practices, EPA assigns
 the quantity of affected waste to the appropriate best demonstrated available technology
 (BOAT). Mixtures of RCRA wastes (i.e., waste streams described by more than, one
 waste code) present special treatabiiity concerns because they often contain constituents
 (e.g., organics and metals) requiring different types of treatment.  To treat these wastes,
 EPA develops a treatment train that can treat all waste types in the group (e.g.,
 incineration followed by stabilization of the incinerator ash). In these cases, the Agency
estimates the amount of residuals that would be generated by treatment of the original
quantity of waste and includes these residuals in the quantities requiring alternative
treatment capacity.

       EPA identifies the quantities of waste requiring alternative treatment on a facility
level basis; if the appropriate treatment technology is not available on site, or if
adequate available capacity is not present to  manage the waste, then the appropriate
quantity of waste requiring alternative  treatment is aggregated into a national demand for
commercial capacity.  EPA excludes from the estimates of required commercial capacity
those wastes that are managed in on-site treatment systems.

       EPA  collected generation and management  information concerning the wastes
covered in today's rule (Phase II wastes) from a number of sources. During April 1992,
EPA conducted a survey of facilities that manage newly identified TC organic wastes in
land-based units.  This survey was distributed to 139 facilities.  EPA requested waste
stream specific data on newly identified TC organic wastes and information on on-site
land disposal units and treatment systems. (See Appendix D for a sample TC Survey
questionnaire.)  Additional information was obtained from follow-up contacts  with survey
respondents.  All of the information collected was used to estimate the quantities of
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                                                 1-9
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 organic TC wastes, and contaminated soil and debris contaminated with TC wastes, that
 would need treatment as a result of the LDRs.

       This capacity analysis also incorporates data from the National Survey of
 Hazardous Waste Treatment, Storage, Disposal, and Recycling Facilities  (the TSDR
 Survey), the National Survey of Hazardous Waste Generators (the Generator Survey),
 and voluntary capacity data from several facilities in response to the Advance Notice of
 Proposed Ruiemaking (ANPRM) (56 FR 55160, October 24, 1991) and the proposed
 rule (58 FR 48092, September 14, 1993).  The analysis of coke by-product and
 chlorinated toluene wastes uses data collected by EPA between 1985 and 1987 under the
 authority of section 3007 in RCRA.  Data on RCRA wastes mixed with radioactive
 wastes was primarily obtained from DOE's comment in response to the ANPRM and
 proposed nile, from the National Profile of Commercially Generated Low-Level
 Radioactive Mixed Wastes, and from the  Department of Energy's (DOE's) report on its
 mixed waste inventory. The capacity analysis for hazardous soil and debris incorporates
 data from the 19S9 and 1991 Biennial Reporting System (BRS), information provided
 during a series of roundtable meetings held by the Agency in May and June 1991 with
 representatives of companies involved in the management and disposal of hazardous
 debris and soil and special data submissions on hazardous soil, and information from the
 TC Survey discussed above.

 1.2.2  Determination of Available Commercial Treatment Capacity

      The analysts conducted to determine available commercial treatment capacity
 focuses on treatment capacity projected to be available in August 1994, starting from the
 baseline capacity identified in the promulgated Phase I final LDR rule.   Capacity
 estimates obtained from the Phase I rule were adjusted, using two different approaches,
 to account for new treatment facilities expected to come on line. The first  approach
 used an evaluation of planned capacity for facilities in the advanced stages of the
 permitting process. The second approach. used d;ila submitted by interested parties.
These available capacity estimates then were adjusted to reflect  the utilization of
 treatment capacity by Phase II wastes.

      The determination of available capacity focuics on commercial facilities.   Conse-
quently, all estimates of capacity presented in this document represent commercially
            " EPA, Background Doc^mtnt for Capacity Anolnu for St»lr t.utrti tt'astes and Hazardous Dtbris la Support 40
         CFR 263 Land Disposal Rearictioru (Final Rule). June IWZ
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                                         1-10
 available (not private) capacity.5  In order to determine whether to grant a national
 capacity variance for newly listed and identified wastes regulated in today's rule, EPA „
 analyzed available commercial capacity for alternative treatment technologies capable of
 meeting the LDR treatment standards. This capacity unalysis generally included
 estimating the maximum or design capacity for appropriate waste management systems
 and the amount of waste currently going to these systems (utilized capacity).  Available
 capacity was estimated as the difference between maximum and utilized capacity. For
 today's rule, EPA analyzed commercial capacity for hazardous waste combustion
 (including incineration and reuse as fuel), biological treatment, chemical precipitation,
 and stabilization.

       In its analysis of incineration capacity, EPA  relied on voluntary waste quantity and
 capacity information from major commercial incineration firms. To assess incineration
 capacity, EPA analyzed the results of a 1993 survey conducted by the Hazardous Waste
 Treatment Council (HWTC), a trade association representing companies that provide
 commen ,al hazardous waste treatment.  To  assess  reuse as fuel capacity, EPA analyzed
 ihe results of a 1993 rurvey conducted by the Cement Kiln Recycling Coalition (CKRC)
 in 1991. The CKRC is a trade association representing  cement kilns that bum'wastes as
 fuel.  Additional combustion capacity information also was received from incinerators and
 cement kilns that submitted comments in response  to the Phase I proposed LDR rule (57
 FR 958, January 9, 1992).  The available combustion estimates were adjusted to
 incorporate the additional demand for capacity from routinely generated Phase I F037/8
 wastes for which the one year national capacity variance expired in June 1993.

       For the remaining treatment technologies, EPA based its capacity analysis on data
compiled and analyzed as part of the Third Third LDR rule. This analysis was based on
data from the May 1990 Commercial Capacity Report, which contains results from the
 National Survey of Hazardous Waste Treatment, Storage, Disposal and Recycling
 Facilities (the TSDR Survey). These estimates were also adjusted to reflect the
 utilization of treatment capacity by Phase I wastes.

       Regulations likely to affect the availability of capacity are currently being
developed by EPA's Office of Solid Waste (OSW) under the Hazardous Waste
 Identification Rule (HWIR).  OSW is scheduled :n  promulgate a Hazardous Waste
 Identification Rule by December 1994.  This rule will likely reclassify some contaminated
soils currently regulated under Subtitle C as Subtitle D wastes.  Specifically, the rule  •
would set constituent-specific risk-based levels ih;it  would identify "higher risk" soils, that
   ' Available treatner.t capacity can be categorized by facility M.I!U» mtu four groups: (1) commercial opacity - capacity
at facilities that manage watte from any facJir)-, (2) on-aie |prv.i:f c.»p.icnyj • capacity M facilities thai manage only
»astc generated oc-site; (3) captive capacity . capacity at tonutm t."_it nuiugc only waste from other facilities under the
same wnership; a.id (4) toted commercial capacity - capjnn jt !.>.:!.no ihtil manage »aste from a limited number of
facilities not under the ume ownership. For all opacity aiu!yKt. f.::"i,no on available capacity reflect available
commercial capacity.
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  would remain subject to Subtitle C, and "lower risk" soils, that would be exempt from
  Subtitle C.  If this rulemaking is adopted, the quantity of contaminated soil regulated as
  hazardous is likely to be reduced, resulting in an increased availability of treatment
  capacity. As a deregulatory rulemaking. however, the impact of HWIR on hazardous soil
  generation would depend on adoption of HWIR by states. The extent (o which slates
  are likely to adopt HWIR has not been evaluated.

  1 _J   SUMMARY OF CAPACITY ANALYSIS  FOR TODAVS RULE

        To estimate the  need for national capacity variances, EPA estimated the quanti-
  ties of waste requiring alternative commercial treatment as a result of the  land disposal
  restrictions and the capacity available at commercial treatment facilities to manage the
  restricted wastes.  Exhibit  1-3 indicates the total quantities of surface and deep well
  disposed wastes that will require alternative commercial treatment capacity as a result of
  the rule.

        A comparison of required and available capacity indicates that adequate ccmmer-
.  cial treatment capacity wilt be available for newly identified TC nonwastewaters (D018-
  D043), newly identified TC pesticide wastes thai were not previously hazardous by the
  old EP leaching procedure (D012-D017), coke by-product wastes (K141-K145, K147-
  K148), chloiinated toluene wastes (K149-K151), and hazardous soil and debris
  contaminated with Phase II wastes. Because sufficient capacity exists to treat these
  wastes, EPA is not granting a national capacity variance for these wastes.

        Exhibit 1-4 presents the  quantities of required and available capacity, by treatment
  technology.  As shown,  EPA has determined that there will not be adequate commercial
  capacity for mixed radioactive wastes containing newly listed and identified wastes that
  will require treatment as a result this rule. Any  new commercial capacity that becomes
  available will be needed for mixed wastes that were regulated in previous LDR
  rulemakings, and whose variances have already expired.

        Exhibit 1-5 summarizes the wastes for which EPA is granting a national capacity
 variance. EPA is granting a two-year national capacity variance for mixed
  RCRA/radioactrve wastewaters and nonwastewaters contaminated with newly listed and
  identified wastes whose standards are being finalized in this rule.  EPA is  also granting a
 one-year capacity variance for high TOC D001 nonwastewaters and D012-D017 pesticide
 wastes that are deep well injected.6
    * EPA bai very limited information on lie quantities of tixx wastes thai may be deep well injected. (See Appends
 F for EPA's data on ihese wastes.) However, several cotr.^e.-.:en 10 the proposed rale indicated that it would be
 difficult to identify, Kgepie, treat, and/or arrange (or disposal of these waste streams in a short lime frame. Therefore,
 EPA is granting a aac-year capacity variance to allow fadV-ses ;n appropriate lead lime to identify these waste streams
 and to create an infrastructure that allow their alternative rcaueemtnt consiMcnt uiiti today's rule.
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                                        1-13

                                     EXHIBIT 1-4

       QUANTITIES OF REQUIRED AND AVAILABLE TREATMENT CAPACITY,
                              BY TECHNOLOGY (TONS)
Treatment Technology
Liquid Combustion
Sludge/Solid Combustion
Stabilization
High-Lcvel Waste
Treatment
Mixed Transuranic Waste
Treatment
Low-Level Mixed Waste
Treatment
Mixed Radioactive Soil
Treatment.
Mixed Radioactive Debris
Treatment
Required Capacity
11,000
380.000
..3
l,300b
lb
400b
10b
l,000b
Available Capacity
1.267,000
438,000
1,127,000
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                           1-14

                       EXHIBIT l-S

     SUMMARY OF NATIONAL CAPACITY VARIANCES
                  FOR PHASE II WASTES
Waste
Mixed Radioactive Wastes
Deep Well Injected
High TOC D001 Wastes
Deep Well Injected
D012-D017 Pesticide Wastes
Effective Date of
Land Disposal Prohibition
August 1996
August 1995
August 1995
                                                                                               >-" 2
                                                                                               c» .- n

Chapter I: Introduction. Provides background, general methodology, and
a summary of the analysis.

Chapter 2: Commercial Treatment Capacity.  Describes the methodology
and data used to determine available commercial capacity for combustion
of liquids and solids, stabilization, biological treatment, and chemical
precipitation.

Chapter 3: Capacity Analysis for Newly Identified Toxicity Characteristic
Wastes. Discusses the methodology and data used to conduct the capacity
analysis for newly identified organic TC wastes (DOI8-D043) and newly
identified pesticide wastes (DO 12-DO 17) not previously hazardous under the
EP test

Chapter 4: Capacity Analysis for Other Newly Listed Wastes.  Describes
the capacity analysis for coke by-products (K141-K145, K147-K148) and
chlorinated toluenes (K149-K151).

Chapter Si Capacity Analysis Tor Mixed Radioactive  Wastes. Discusses the
methodology used for the capacity analysis of radioactive wastes mixed with
newly listed and identified wastes for which LDRs are being finalized  in
today's rule.

Chapter 6: Capacity Analysis for Hazardous Soil Contaminated With
Newly Listed Wastes. Discusses the methodology and data used to conduct
the capacity analysis for soil contaminated with newly listed and identified
wastes for which LDRs are being finalized in today's  rule.
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                                      1-15

       •      Chapter 7: Capacity Analysis for Hazardous Debris Contaminated With
             Newly Listed Wastes.  Discusses the methodology and data used to conduct
             the capacity analysis for hazardous debris contaminated with newly listed
             and identified wastes for which LDRs are being finalized in today's rule.

       •      Appendices: Appendix A presents a sample of the HWTC survey
             questionnaire; Appendix B presents a sample of the CKRC survey;
             Appendix C presents telephone logs;  Appendix D presents a sample of the
             TC Survey;  Appendix E presents data cm newly identified organic TC
             mixed wastes; and Appendix F presents data on deep-well injected wastes.

       In addition, EPA has prepared another background document, the Response to
Comments Received on the ft'ewfy Listed Wastes and Hazardous Soils Proposed Rule to
Support 40 CFR 268 Land Disposal Restrictions: Capacity-Related Comments, that provides
EPA's  responses to capacity-related commer:s received on the proposed rule (58 FR
48092).
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                                    CHAPTER 2
                      COMMERCIAL TREATMENT CAPACITY
       Chapter 2 presents EPA's estimates of available commercial treatment capacity
 for newly listed and identified wastes.  Section 2.1 summarizes the  results of EPA's
 analysis of commercial combustion capacity at incinerators and boilers and industrial
 furnaces (BIFs).  Section 2.2 discusses EPA's estimate of available  commercial
 incineration capacity, the methodology used to arrive at its estimate, and capacity at
 individual incineration facilities. Section 2.3 discusses EPA's estimate of available
 commercial BIF capacity, the methodology used to estimate available BIF capacity, and
 capacity at individual facilities.

 2.1    COMMERCIAL COMBUSTION CAPACITY SUMMARY
                                                  »
       This section summarizes the results of EPA's analysis of commercial  combustion
 capacity at incinerators and BIFs, as EPA expects the majority of treatment capacity for
 newly identified and newly listed wastes to come from incinerators  and BIFs.7  It
 includes a~\ analysis of incinerator and BIF combustion capacity information received
 from the Hazardous Waste Treatment Council (HWTC) and the Cement Kiln Recycling
 Coalition (CKRC) in 1993.  The HWTC and CKRC surveys are included, respectively,-as
 Appendices A arid B.  The analysis is also based on a series of data updates and
 corrections conducted by telephone with incinerator facilities.

       Exhibit 2-1 summarizes EPA's estimates of commercial  hazardous waste capacity
 by waste form for incinerators and BIFs.  Exhibit 2-2 lists (he incineration facilities
 included in the commercial combustion capacity estimate, along with the waste forms
each facility can burn.  Each of these facilities is discussed in greater detail in  section
2.2.1. Exhibit 2-3 lists the BIFs included in this capacity update, and the types of wastes
accepted at each facility.  Each of these facilities is discussed in greater detail  in section
 2.3.1. Exhibit 2-4 is a map showing the location of incinerators and BIFs considered in
EPA's estimate of commercial hazardous waste burning capacity. Specifically, the map
shows all BIFs and incinerators with available capacity that were included in the capacity
estimates.  Please note  that EPA's capacity analysis focuses primarily on capacity for
sludges and solids, and  does  not include all commercial BIFs that only accept  liquids.

2.1.1   General Methodology

      The Agency worked with the HWTC and the CKRC to process the surveys.
Subsequent to the original HWTC survey, members also received a supplemental
questionnaire regarding the burning of soils.  Survey responses received from members of
the HWTC are classified as confidential business information (CBI) and have  been
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                            Exhibit 2-2


   Incinerators Included in August 1994 Capacity Estimate
Facility Name and Localloa
Apnis. Inc.. Salt Like City. UT
Aptus. Inc. - Environmental Service*. CofTeyville. KS
CWM - Port Arthur. Port Arthur, TX
ENSCO, Inc.. El Dorado. AR
LWD, Inc., aivert City, KY
Laidlaw Environmental Services, Inc., Roebuck, SC
Norlite Corporation, Cohoes, NY
Rhooe-Pouleoc (RPBQ, Baton Rouge, LA
Rhone- Pouleoc Basic Chemicals Co., Hammond, !N
Rhonc-Poulcnc Buic ChetnicaJi Co., Hctuton, TX
Rollins Eivironmenul Sen-ices (LA) Inc., Baton
Rouge, LA
Rollins Environmental Servicea (N/) Inc.,
Bridgeport. NJ
Rollins Environmental Services (TX) IDC., Deer
Park.TX
Ross Incinentioa Services, Inc., Graftoo, OH
ThermalKEM Inc.. Rock H:ll Plant, Rock Hill. SC
Typo of Waste Burned
liquids (a^ueoui), liquids (non-aqueous), pumpable
sludges, coouinerized solids, bulk solids, soils
liquids (aqueous), liquids (non-aqueoui), pumpable
sludges. D0flpumr>iblc kludges, containerized solids.
bulk solids. comprt>ud gases, soils
liquids (iqueous), liquids (aon-aqueous), pumpable
sludges, conlaineriud solids, bulk solids
liquids (aqueous), liquids (non-aqueous), pumpibte
sludgss. coapumpable sludges, containerized solids,
bulk solids, compressed gases, soils
reported as all liquids (aqueous & non-aqueous),
pumpable sludges, containerized solids, bulk solids
reported al liquids & pumpable sludges grouped
liquids (ifcn-aqurxms), pumpable sludgca
uoreported
liquids (aqueous), liquids (noa-aqueous)
liquids (aqueous), liquids (oon-aqueoui)
liquids (aqueous), liquids (non-aqueous), pumpable
sludjes, containerized solids, soils
liquids (aqueous), liquids (aon-aqueous), pumpable
sludges, containerized solids, compressed gases, soils
liquids (aqueous), liquids (noa-aqueous), pumpabte
sludges, containerized solids, compressed gases,
x>il>. bi:lk solids
liquids (aqueous), liquids (non-aqueous), pumpable
sludges. Bonpumpable sludges, containerized solids,
bulk solids, compressed gases, soils
liquid! (aqueous), liquids (non-aqueous), pumpable
Does not include incinerators at Taciliiiei thai submitted IIWTC Surveys but that are not

currenlly operating.
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                                           Exhibit U'Continued)


                         Incinerators Included in August 1994 Capacity Estimate
FacUJty Njunc and Location

Trade Wase loctoeritioo. StugeC, IL
Types of Waste Bunted
tludgei. nonpumpable iludge*, containerized solidf ,
bulk toliili. compressed guet. toilt
coouioeriud tolidj, repotted u liquids &
punpcbl* tlodje* grouped, reported u solids &
ooopumptbte itudgej grouped
                       Doet not include incinerator] at facilities thai tubmilied HWTC Surveys but ihil are cot

                       currently operating.
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                            Exhibit 2-3


       BtFs Included in August 1994 Capacity Estimate
                                                                                                               i
F»dBty Name and Location
Ash Crave Chuute Cement Plant, Cbaoule, KS
Ash Grove Forcmui Cement Plant, Foreman, AR
Ash Grove Louisville Cement Plaot, Louisville. NE
Carolina Solile. Albemarle. NC
Citadel Cement Co.. Detnopolit, AL
Continental Cement Co., Hannibal. MO
Dixie Cement Company, Knoxville, TX
ESSROC, Loguspon, IN
Florida Solite, Green Cove Springs, FL
Giant Cement Co., Harleyville, SC
Heartland Cement Co., Independence. KS
Holaam, Inc., Arena, MS
Holoam, Inc., Holly Hill, SC
Hokum/Safety Kleen Corp.. Clarksville. MO
Kentucky Solile, Brooks, KY
Keystone Cement Company, Bain, PA
Lafarge, Alpena. Kfl
Types of Waste Burned
containerized ftolids. reported ju all liquids (aqueoui
i oon-aqiMOui)
conuiacfiud tolids, repoited as all liquids (aqueous
& ooa-aqtMout)
conuioeriml tulid,t, reported as all liquids (aqueous
& BOQ-aqucotu)
reported ai all liquids (iqueous &. non-aqueous)
pumpaMe >ludgc4, reported as all liquid) (aqueous
it oon-aqucous)
bulk foliiit. dry tolidi. reported u all liquids
(aqueous Jk non-aqueous)
contiioeriuJ solid*, reported ai liquids &
pumpable >lud(es grouped
rrportad u tolidj & Bonpuinpable iludge* grouped,
reported as til liquids (aqueous & non-aqueous)
reported u all liquids (aqueous & non-aqueous)
dry solids, reported ai all liquids (aqueous &
DOo-aqueous)
dry solids
reported u all liquids (aqueous & noo-tqueous)
reported ai all liquids (aqueous & non-aqueous)
reported u liquids & pumpable sludges grouped
reported as solids & nonpumpable sludges grouped
reported as all liquids (aqueous & non-aqueous)
reported ss all liquids (aqueous & non-aqueous)
Does ool include BtFs at fscilities that subroiltol CKRC .Surveys but that are not currently

operating.
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                              Exhibit 2-3{Cootinucd)


                 BIFs Included in August 1994 Capacity Estimate
FadCtjr Nanw and Location
Lafarge Corp., Fredonii, KS
Lafaif e Corporation, Flulding, OH
Loot Star Alternate Fuel Co. . Ope Cintdeau. MO
Lone Star I- dtutrie*. IDC,, CreeoeasUe. IN
Mcdtua Cemedt O>4» Wimpunif PA

NatiouJ Cement Cbmpuiy Lebec Plint, Lebec, CA
North Texat Cement. Midlolbiia. TX
River Ceractit. FeMui, MO
Safety Klees Eavirotyitemi Co.. Dorado, PR
Solite Corp., Catcade, VA
Solite Corp., Arvonia, VA
Soutbwe»tera Poitiuxt Cement Co., Fairbom, OH
Texas InduMrict, Inc.. Midlothian, TX
Typa of Wute Burned
dry »ltdi. reported as liquids & pumpable iludgea
grouped
pumpablc itudxea, reported u all liquids (aqueouj
ft DOA'aquccua)
coaiaineriini tolidi. reportoi u all liquids (aqueous
& DOo-aquroiu)
conlaiiwriud «olid», reported as all liquids (aqueous
& Don-aqu«Mu)
punpabte iludgei. nonpumptble tludges, reported
as ill liquid* (aqueous & non-aqueous)


reported as all liquids (aqueous & noa-aqueous)
punpablc tludgei, ooopumpable tludfet, reported
u all liquids (aqueous It Don-aqueous)
reported u all liquids (aqueous & noo-aqueou«)
reported as all liquids (aqueous & noo-aqueous)
reported as all liquids (aqueous & non-aqueous)
reported as a'l liquids (aqueous & non-aqueous)
reported u all liquids (aqueous & non-aqueous)
1)
Does not include BIFi at facilities that submitted CKXC Surveys but thai are Dot currently

operating.
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                                        2-9

 handled accordingly.  A CBI version of the applicable exhibits are available in EPA's CBI
 files. Survey responses received from members of ihe CKRC are not classified as CBf.

       Following the receipt of surveys, the Agency reviewed the data submitted by each
 facility to evaluate the completeness, consistency, and accuracy of the information.  The
 Agency identified and reconciled data gaps and anomalies by contacting the respective
 HWTC or CKRC coordinators and the individual facilities in question.

       Concurrent with the receipt of surveys received from the member groups, the
 Agency developed a data base program to track and process major data elements for (he
 capacity analysis. The data base contains facility information (e.g., location, EPA
 identification number of burner, number (if unit* currently on-line), unit specific
 information (e.g., type of incinerator/kiln unit, operating hours per year, types of
 hazardous waste feed systems, types of hazardous waste burned in 1992}, and waste-type
 specific information (e.g., tons of hazardous waste burned in 1992, average hazardous
 waste feed rate, maximum practical capacity, maximum  permit capacity).

        The Agency executed a rigorous QA.QC procedure to ensure that data
 processing was accurate and complete.  Following receipt of a survey, two staff members
 entered relevant information into the Agency's LDR capacity data base. After data entry
 was completed for all surveys, output reports were printed to summarize the data for
 each facility, A third  staff member, not involved with the original data entry, compared
 the QA/QC reports with the original surveys to ensure that all data was entered correctly.
 A detailed checklist was developed to facilitate this step of the quality control process.
 Any discrepancies were noted and changed in the data base with a subsequent re-
 examination of the particular  data element. Following these QA/QC steps, the Agency
 conducted initial combustion capacity analyses and produced database reports

2.1.2  Analysis of Capacity Data

      The data received from facilities participating in the HWTC and CKRC surveys
does not lend itself to simple summation and tabulation  of results because facilities
sometimes differed in  their approach to reporting quantities burned or burning capacity.
 Incineration systems can generally accept multiple waste forms (e.g., pumpable sludges
and aqueous liquids) and accepting larger amounts of one may reduce the capacities for
others.  In responding to the HWTC survey, facilities sometimes grouped wastes types for
their capacity-related responses.  For example, if a feed  system can accommodate both
liquids and pumpable  sludges, a facility may report a capacity for both forms grouped
together.  To address this interchangeabilily of waste forms, the Agency's LDR capacity
database accommodated the reported waste groupings (e.g., one capacity estimate for
liquids and pumpable sludges  combined).

      A second issue  also relating to the mle;ch:ingc.Mbility of waste forms required
more extensive consideration.   In responding to the HV.TC survey, some facilities
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                                                      2-10
t
 reported the maximum combustion capacity for individual waste forms that together
 exceed the reported overall capacity of the unit.  As a result, summing these individual
 capacities results in a total capacity that far exceeds what a facility may practically
 accommodate. The Agency developed an algorithm to address this complication.  The
 algorithm is discussed below in section 2.1.3.

 2.1 J  Apportioning Capacity to Individual Waste forms

       The waste apportionment algorithm focuses on three primary variables: the
 quantity of waste turned in 1992, the maximum practical capacity of the unit, and the
 available capacity for burning hazardous waste. The available capacity for a  waste form
 (e.g., aqueous liquids, dry solids) is obtained by taking the difference between the
 quantity of the form burned in 1992 (hazardous and non-hazardous waste) and the
 maximum  apacity for the waste form.  The Agency's approach assumes that a facility
 will not stop burning non-hazardous waste if it is currently burning non -hazardous waste)
 but all utilized capacity will be used for hazardous waste. Difficulties arise, though,
 because facilities report maximum capacities for each waste form without regard to
 capacity accounted for by other waste  forms.  Consequently, the sum of maximum
 capacities for all waste forms may exceed the  total capacity.

       In these cases, the Agency distributed the total maximum hazardous waste
 capacities reported by each facility to individual waste forms based on 1992 burning
 practices.  The utilization rate for each waste form was calculated by dividing the larger
 of the quantity of hazardous waste burned or total waste burned, for that waste form by
 the sum of the quantities burned for all waste  forms.  A new maximum hazardous waste
capacity for each waste, form will then  calculated by multiplying the utilization rate for
 that waste form by the maximum practical capacity for the incineration unit as a whole.

      If the calculated maximum capacity for  a waste form exceeded the reported value
for that form, EFA used the reported value. In this case, the difference between the
calculated and reported value was then redistributed to other waste forms using a
hierarchy based on the types of wastes in this rule for which capacity has historically been
most limited relative to demand.  The Agency  used the following order for redistributing
capacity:

            Soils;
      •     Bulk Solids;
      •     Containerized Solids;
      •     Nonpumpable Sludges;
      •     Pumpable Sludges;
      •     Compressed Gases;
      •     Non-aqueous liquids; and
      •     Aqueous Liquids.
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                                        2-11
       To illustrate this redistribution, assume that the c.'iltubtions resulted in a
 difference of 400 ions per year for aqueous liquids (thai j*, the calculated capacity based
 on the present utilization exceeded the reported capacity by 4CK) tons).  Exhibit 2-5
 provides an example of the calculation of available capacities given hypothetical data
 from the HWTC Survey.  In this example, the sum of the reported capacity for individual
 waste forms  (57,200 tons) exceeds the overall capacity of the units {33.000 tons) so
 adjustment is necessary.  After calculating new maximum capacity based on utilization
 (column E),  the calculated maximum for containerized solids (24,090) exceeds the
 reported maximum (15,000) so further adjustment is required. After setting the adjusted
 maximum  for containerized solids to the  reported capacity of 15,000 tons, the adjusted
 available capacity (adjusted maximum minus tons of waste burned} is calculated to be
 6.200 tons. The "excess" containerized solid capacity (2-1.WO • 15,000 = 9.090 tons) is
 added to available soils capacity since it is the highest priority category. Since the
 resulting i Ijusted capacity for soils (9,615) is  less than the reported capacity at 15,000
 tons, no further adjustments are necessary. If the adjusted available capacity for soil had
 been higher that  the reported capacity, the difference between these estimates would
 have been shifted to bulk solids, the second highest priority category.

       Once  the maximum hazardous waste capacities for each waste form have been
 calculated, the Agency calculates available capacity by Inking the difference between the
 maximum capacity for each waste form and the quantity of waste (hazardous and non-
 hazardous) burned in 1992.  In the few instances where (he calculated maximum capacity
 is less  than the amount of waste actually  burned, the two ,-irc set equal and available
 capacity is zero.

       In response to the Phase II proposed rule, a contractor with the HWTC also
 performed an analysis of the combustion  capacity data.  ThoHWTC 'calculated an "All
 Waste Available Capacity" that uses assumptions like those of the  Agency:

       •      Hazardous waste available capacity was calculated by subtracting the
           •  quantity of all waste (hazardous and non-hazardous) burned from the
             maximum reported capacity for  each waste form.

       •      All  unutilized capacity was devoted to burning  hazardous waste.

 In apportioning excess capacity among waste forms, however, HWTC used an iterative
procedure  that does not take into account the waste forms that have historically lacked
 capacity. Rather than first redistributing  excess capacity to Mills and bulk solids as
 discussed above, the  HWTC approach employs an arbitrary scheme that is rooted solely
 in mathematics.  In order to realistically represent current capacity deficiencies, the
Agency has redistributed excess capacity under the hienircliy discussed above.
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                                        2-13
 2.2    COMMERCIAL INCINERATION CAPACITY

       This section focuses on the combustion capacity of the nation's commercial
 hazardous waste incinerator facilities.  Exhibit 2-6 summarizes ihe status of incineration
 capacity at each the facilities included in the HWTC survey.  Note  that confidential
 business information is not disclosed.  Aggregated results for CBI data are provided at
 the end of Exhibit 2-6.  Section 2.2.1 profiles each of the individual facilities summarized
 in Exhibit 2-6.  Section 2.2.2 discusses  several operating facilities that were not
 considered in the capacity analysis.  Section 2.2.3 discusses planned additions to
 incineration capacity beyond August 1994.

 2.2.1  Individual Incineration Facility Capacity Analysis

       Faculty profiles are provided below for each  of the incinerators included in the
 commercial combustion capacity estimate.  These profiles have been created based on
 data provided in the HWTC survey and data received as a result of telephone contacts.
 The telephone logs for these updates are included in Appendix C.  The estimates
 included in this section do not take into account the capacity that is required for Phase I
wastes for which the capacity variance granted to routinely generated F037 and F038
expired in June 1993.

       Aptus, Cofteyville, Kansas

       Aptus, a Westinghcuse company, has both TSCA and RCRA Part B permits.  The
incinerator unit is a slagging rotary kiln with a thermal input of 61.9 MMBtu/hour. This
facility can accept liquids, pumpable sludges, nonpumpablc sludges, containerized solids,
bulk solids, and soils.  Liquids are directly injected into the rotary kiln and containerized*
solids are ram-fed.  Recycle feed and drop feed systems are used to feed bulk solids into
the incinerator unit. Aptus is seeking permit modifications to expand the facility's
treatment and storage capacity.

       Confidential capacity information provided by the facility included quantities of
waste burned in 1992 and maximum practical burning capacity.  These estimates are
included  in the aggregated estimate  in  Exhibit 2-5.   Of the Phase II wastes, this facility
accepts D01&43 wastes.

       Aptus, Tootle, Utah

       This facility has RCRA and TSCA permits and operates one slagging rotary kiln
incinerator unit.  The facility accepts liquids, pumpuhle sludges, containerized solids, bulk
solids, and  soils.  The incinerator system at this faciliiy is a slagging rotary kiln with an
afterburner. This system has a thermal input of HO MMBtu/hour.
1IWI
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    en

-------
                                                EXHIBIT 2-<


                      Summary of Commercial Incineration Capacity Through August 1994




Facility Name
Aptui, toe..
Sail Lake City. UT
UTD981SS2177




ApRli, be. - Eavironmeotal
Setviaa,
Coffiyville, KS
KSCK>8I50602S




}
CWVI - Port Arthur.
Port iVrtlnir, TX
TXO100838896



CWV Chemical Service!.
Chicago, !L
IUXM067212I

ENSCO. Inc..



Unit
Type
IF





.....
RK







*****
RK




*****
RK»


*****
RK



Waste
Type
li-pe abbreviations: FH - Fixed Hearth; LJ = Liquid Injeclion; RK = Rotary Kito; RR - Roury

Reactor; IF = Industrial Funucc; UK = Uniaouc
.
                                                                                                                          «._"
                                                                                                                        SSI
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                                                                                                                          w
                                                                                                                          Is)

                                                                                                                          71
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en



—«
                                                                                                                                 I

-------
                                    EXHIBIT 2-6 (canllnMd)
              Summary of Commercial Incineration Capacity Through August 1994





FadlilyName
B Dorado. AR
ARD06974SI92













,





LWD.bc.,
divert City. KY
KYDOS843S817







Unit
Type






RK





RK







**•**
U


RK






Wute
Type
liq(omq)
pumpil
opump jl
con! solidi
bulk solid)
compgasea
pumpil
opump >1
coal aolida
bulkaolidi
comp gases
soils
liq{aq)
liq(naq)
pumpil
npunpil
coot solids
bulk solids
comp gases
soils
TOTAL
all liqi


puopil
' Mil solids
bulk solids
•

1991
Utilized
Capacity
(Toos/Yr)






CBt





CBI







CBI
CBI


CBl



Aigutt 1994
Reported
Mwimin
C»p»d(y
CTem/Yr)






CBI





CBI







CBI
CBI


CBI



August 1994
Adjurted
Maxim tan
Capacity
CTons/Yr)






CBI





CBI







CBt
CBI


CBl


Aujustl#4
Adjurttd
Ettimtlcd
AToikblc
C«p«eity
(TonsA-r)






CBI





CBI







CBI
CBI


CBI


1)
2)
3)
CBl = CONFIDENTIAL BUSINESS INFORMATION
* = Piaaaed or Not Operating
Unit Type abbrevUtiooi: FH = Fixed Hearth; U - Liquid Injection; RK = Rotary Kilo; RR = Rotary
Reactor; IF = todusirial Furnace;  UK - Unknown
                                                                                                              o
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                                                                                                             cm
                                                                                                             CO

-------
                                 EXHIBIT 2-6 (continued)


              Summary of Commercial Incineration Capacity Through August 1994
Facility Name



Liidlia' Environment!]
Servicei, inc..
Roebuck. SC
SCD9S 1467616

N*riite Corporation.
Coboe* NY
NYD08 0469935


Rhone-l'ouleoc (RPBC),
Bnon Rouge, LA
LA0001I16I234


RhoM-1'oulene Buic
ChemJaJj Co.,
Unit
Type

RK
*****
U
***•*
RK
RK
*****
U
U
*****
IF
Waste
Type
•11 liqi
pump si
coot io!idi
bulk wlids
iUl tiqs
TOTAL
(It liq/pt
TOTAL
«<|
CBI - CONHDENTIAL BUSINESS INFORMATION

* « Plumed or Not Operating

Unit Type ibbreviuioni: FH = Fixed Heuth: U = Liquid Injection; RK = Rolvy Kiln; RR = Rotaiy

Reactor,  IF « IndustriiJ Fura»ce; UK
                                                                                                      fl> r»   J5

                                                                                                      51*-?*'
                                                                                                        USs
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                                                                                                          K)

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-------
                                     EXHIBIT 2-o (continued)


               Summary of Commercial Incineration Capacity Through August 1994
Facility Name
Hammond. IN
INDOOIIS9032

Rbone-Poulcoe Basic
Cbemieilt Co..
Ho«ilao.TX
7XOOOW99079

Rollio* Eovinomeolal
Servicei (1A) Inc..
Bdoa Rouge, LA
LAD0103951I7-P

Rollinj Environmental
Service* (NJ) lac..
Bridjeport, NJ
NJDOS3288299

Rollins EovironmeDUl
Servicet (TX) Inc..
Deef Put, TX
TXD05514137«
Unit
Type

**^*«
U

*****
RK
•*••*
RK
*****
RK
Waste
Type

TOTAL
iiq(
-------
                                                                                                                                    1
                                                                                                                                      n
                                                                                                                                      ?
                                    EXHIBIT 2-6 (continued)


               Summary of Commercial Incineration Capacity Through August 1994



•

Facility Name











ROM beiocraiioo Service!.
I»e..
Cnftcai. OH
OHDOK4S566S




1

TnenniilKEM Inc., Rock HiU
Flam,
Rock Kill, SC
SCDW4442333









Unit
Type
RK




RR




*••*#
RK








*****
FH







*•*«*




Waste
Type
liq(aq)
liq (naq)
pump >1
coot solid)
soil*
liq(aq)
liq (atq)
pumps!
bulk ulidi
soils
TOTAL
liq(«q)
liq(iuq)
pump f !
n pumps!
conl lolidi
bulkioUdi
comp jt»e»
•oilt

TOTAL
liq(aq)
liq (naq)
piunpal
opuoop s]
coal tolidi
bulk «ot;dj
compgues
toil!
TOTAL


1W2
t'tiliad
Capacity
(T«oi/Yr)
CBI




CBI




CBI
CBI.








CBI
CBI







CBI

August 1994
Reported
Max Im ua
Capacity
(Tora/Yr)
CBI




CBI




CBI
CBI








CBI
CBI







CBI

August 1994
Adjusted
Maximum
Capacity
fTons/Yr)
CBI




CBI




CBI
CBI








CBI
CBI







CBI
August 1M4
Adjusted
Estimated
ATailabte
Capacity
(Tons/Yr) .
CBI




CBI




Cfll
CBI








CBI
CBI







CBI
3>
CBI • CONFIDENTIAL BUSINESS INFORMATION

* - Plumed or Not Operating

Unit Type abbreviations: FH * Fixed He*flh; U = Liquid Injection; RK

Reactor, IF «= Industritl Furnace;  UK
                                                                    RoUiy Kiln; RR = Rotuy
                                                                                                                      •It
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-------
                                    EXHIBIT 2-6 (continued)

               Summary of Commercial Incineration Capacity Through August 1994
Facility Name
Trade Wast* Incineration.
Sauget. IL
ILD09S642424



USPQ.
Ukepoint, UT
UTD9825957M

Auregmted Results
(Openuiag Units Only)





Unit
Type
FH
FH
RK
•»*»*
UK-
• ••**







Wute
Type
coat lolidl
ill liq/p»
cent «olidl
•llliVpt
all liq/pf
all toVopl
TOTAL
liqCuj)
liq(uq)
pumptt
cpump il
cool tolid*
bulk wlidt
foils
TOTAL
liq{sq)
liqCosq)
pumps)
npumpsl
coat solids
bulk solids
diy solids
1»1
UtiHwd
Capacity
(Toos/Yr)
C8I
CBI
cat
CBI
CBI
CBI
SI.SSO
172.660
34.SIS
12.896
121.305
5S.8S3
0
August 1994
Reported
Maximum
Capacity
(Toru/Yr)
CBI
CBI
CBI
CBI
CBI
CBI
22J.M9
315.839
160.942
36,038
187.435
186.617
0
Augwtt994
Adjusted
Maxim urn
Capacity
CTons/Yr)
CBI
CBI
CBI
CBI
CBI
CBI
192.838
313.121
139.003
21.619
251.102
1 19.327
0
Aujurtl994
Adjusted
Estimated
Arailtblc
Capacity
CTom/Yr)
CBI
CBI
CBI
CBI
CBI
crt
1 10.958
140.461
104.185
8.7"23
119.797
60.444
0
I)
2)
3)
CBI - CONFIDENTIAL BUSINESS INFORMATION
• = Plumed or Not Operating
Unit Type tfabrcviuioiu: FH •* Fixed Heank; U = Liquid Injection; RK = Rolaiy Kilo; RR = Rotaiy
Re»cior, IP — Indtuuial Furnace; UK = Unknown
                                                                                                     sfs
                                                                                                     JS?
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                                                                                                                D.Q, «- "
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                                                                                                                   —J

-------
                  EXHIBIT 2-6 (cnnllnued)


Summary of Commercial Incineration Capacity through August 1994
Facility Name

Unit Wmste
Type Type
conip gues
•tl liq/ps
til tol'apt
•II t!
-------
                                        2-21

       This facility is equipped with several mechanisms for feeding waste into the
slagging rotary kiln.  Liquids are injected directly from n storage lank into the kiln and/or
afterburner chamber.  Pumpable sludges, having a viscosity lower than 10,000 centipoise,
are fed via a cement pump. Bulk solids and nunpumpable sludges arc placed into
holding tanks. From these tanks, the wastes arc moved by a clamshell to an apron
feeder where the waste is fed directly into the  kiln feed chute. Containerized solids that
do not require shredding (e.g., lab packs) are fed directly into the  kiln via an elevator
feed system.  Containerized solids and bulk solids that require shredding are processed
through a shredder prior to being placed into storage tanks.

       Confidential capacity information provided by the facility included waste quantities
burned in 1992 and maximum practical burning capacities. These estimates are included
in the aggregated CBI  estimate in Exhibit 2-5.  Regarding the Phase II wastes, Aptus,
Utah accepts D018-43  wastes.

      Trade Waste Incineration (Chemical Waste Management) Saugct, Illinois

      This RCRA Part B permitted facility operates three dry scrubber incineration
units; Two are fixed hearths and one is a rotary kiln. Each fixed hearth unit has a
maximum permitted heat release of 16 MMBtu/hour, The rotary kiln has a maximum
permitted heat release  of 50 MMBtu/hour.

      This facility can accept most physical forms of wastes.  Liquids are blended in
tanks and transferred/to atomizers for direct injection into the incinerator unit(s).
Pumpable sludges are injected into the incinerator unit(s) via a sludge lance.
Nonpumpable sludges and containerized solids are repackaged into burnable containers
and ram-fed into the incinerator units.  Bulk solids are unloaded into pits and
transported via clamshell into the rotary kiln unit.

      This facility submitted its survey independent of the set provided by HWTC. For
each unit and physical  form of waste, this facility reported waste quantities bumed during
1992 and maximum practical burning capacities. These estimates are included in the
aggregated CBI estimate in Exhibit 2-5.

      CWM  Chemical Services, Chicago, Illinois

      This RCRA interim status facility is not currently operating and is awaiting EPA
authorization for TSCA and RCRA Part B permits.   This facility is not included in EPA's
commercial combustion capacity estimate. The incinerator unit at this facility is a rotary
kiln with a thermal input of 30 MMBtu/hour.

      The feed  mechanism for the single unit  ;it CWM consists of a drum conveyor and
ram-feed for containerized solids.  In general, hulk solids and pumpable sludges are not
o
(73
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—J

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                                                  2-22
O
 accepted at (hi* facility. Nonpumpable sludges are generally accepted only when
 containerized.

       This facility submitted its survey independent of the set provided by HWTC. The
 facility reported confidential maximum current practical burning capacity for liquids and
 containerized solids. Because this facility is nut currently operating. EPA did not include
 it in the national capacity estimates.

       Chemicbi Waste Management reported that expnnsion plans will depend on the
 outcome of final permitting decisions. This facility indicated that il is seeking
 authorization to accept the Phase II waste codes DO 18-043.

       OVM-Port Arthur, Port Arthur, T«as

       This RCRA Part B permitted facility operates a rotary kiln system that has a
 thermal input of 175 MMBtu/hour.  The facility has npplied  for a TSCA permit to burn
 PCB-con laminated wastes.

       This facility accepts liquids, purnpable sludges, containerized solids, and bulk
 solids. Several feed mechanisms exist for feeding waste into the rotary kiln.  Positive
 displacement pumps are used to feed pumpnblc sludges. Containerized solids are fed
 into the unit via a ram-feed system.  Bulk solids are shredded* and charged- to the kiln by
 a chute.

       The facility reported waste quantities burned in  1992 and maximum practical
 burning capacities as CBI. These estimates are included in the  aggregated CBI estimate
 in Exhibit 2-5. This facility can accept the Phase II wastes DOI8-D043, Kl 4 1-145, and
 K147-151.  CWM indicated this facility anticipated increasing operating hours by 50
 percent in  1993-1994, and planned various process improvements for the third quarter of
 1993 that will improve on-line time and allow the  facility to accept CERCLA wastes.

       ENSCO, El Dorado, Arkansas

       ENSCO operates three rotary kiln  incinerators at this RCRA Part B permitted
facility. Each kiln can bum liquids, purnpable sludges, nonpumpable sludges,
containerized solids, bulk solids, compressed gases, and soils. Two of the kilns feed into
one secondary chamber with  a permitted combined feed rate of 29,718 pounds per hour.
The third kiln has a permitted feed rate of 12,912 pounds per hour.

       ENSCO submitted confidential business information on quantities burned in 1992
and maximum practical burning capacities. These estimates are included in the
aggregated CBI estimate in Exhibit 2-5. ENSCO accepts the Phase II waste codes D018-
043 and K149-151.
                                                                                                                       o
                                                                                                                       (/J
                                                                                                                              i
                                                                                                                        J

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                                       2-23
       L.W.D. Inc., Calvert City, Kentucky

       This facility is currently operating under interim status.  LW.D, Inc. has three
 incinerators at this facility: one liquid injection unit and two rotary kilns.  The liquid
 injection incinerator burns liquids.  The rotary kilns burn liquids, bulk solids,
 containerized solids, and pumpable sludges. The liquid injection unit has a thermal input
 of 40 MMBtu/hour.  The rotary kilns have thermal inputs of 50 MMBtu/hour and 100
 MMBtu/hour.

       This facility submitted its survey independent of the set submitted by HWTC. The
 facility provided information on quantities burned in 1992 and maximum practical
 burning capacities. These estimates are included in the aggregated CBI estimate in
 Exhibit :-5.  L.W.D. Inc. accepts the Phase II wastes D018-043. K141-145, and K147-151.

       Laidlaw Environmental Services, Inc, Roebuck, South Carolina

       This facility is fully permitted by the EPA but is under interim status with the state
 regulatory agency. Laidlaw operates one  liquid injection  unit that injects and bums
 pumpable liquids. The CBI provided included quantities of waste burned in 1992 and
 maximum current practical burning capacity.  These estimates are included in the
aggregated CBI estimate in Exhibit 2-5.         .

       Of the Phase II wastes, this  facility accepts D018-43 waste codes.  Laidlaw is
authorized to receive and bum K141-14S and K147-151 wastes. .

       Norlite Corporation, Cohoes, New York

      This RCRA Part B permitted incineration facility operates two rotary aggregate
kilns that burn liquids and pumpable sludges. The kilns are RCRA-permitted as
incinerators. Liquids are injected and sludges are  pumped into the kiln.  Each kiln has a
thermal input of 62 MMBtu/hour.  New York officials are considering a permit
modification to increase Norlite's solid feed capacity.

       Norlite submitted confidential information on quantities of waste burned in 1992
and maximum practical burning capacities. These estimates are included in the
aggregated CBI estimate in Exhibit 2-5. Of the Phase 1! wastes, the facility currently
accepts D018-043 wastes. Norlite is seeking a permit modification to accept the
remaining Phase  II wastes.
•M
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-------
                                        2-24

       Rhone-Poulenc Basic Chemicals Company, Hammond, Indiana

       This facility submitted confidential information on qunntiiies burned in 1992 and
 maximum practical burning capacity. It is operating with an interim status BIF permit.
 The industrial furnace at this facility bums liquid w.-isles only.  Rhone-Poulenc,
 Hammond, accepts all Phase If waste codes:  DIM 8-043, K141-145, and K147-151.

       Rhone-Poulenc Basic Chemicals Company, Baton Rouge, Louisiana

       This RCRA Part B permitted facility operates two liquid injection incinerators.
 These incinerators have permitted thermal inputs of 170 MMBtu/hour and 234
 MMBtu/hour. This facility can accept liquids ami pumpable sludges.  The pumpable
 sludges must either be slurried or have a sufficiently low viscosity to" be injected into the
 furnace.

       Rhone-Poulenc did not submit quantities burned or maximum practical capacity
 information for 1992. It did, however, report the amount of waste received, stored and
 processed at the facility in 1992.   Therefore, EPA tins assumed that these reported
 amounts reflect the hazardous waste burned in 1992 ;is well as the practical burning
 capacity. Of the Phase II wastes, this facility can accept D018-D043.

       Rhone-Poulenc Basic Chemicals Company, Houston, Texas

       This RCRA Part B permitted facility burns liquids in one. liquid injection
 incinerator.  The incinerator has  a thermal input of 205 MMBlu/hour.
t
       Rhone-Poulenc reported waste quantities burned in 1992 and maximum practical
 burning capacities as CBI. These estimates are included in the aggregated CBI estimate
 in Exhibit 2-5. Of the Phase II waste:, this facility accepts D018-43 waste codes.

       Rollins Environmental Services, Baton  Rouge, Louisiana

       This RCRA Part B permitted facility consists of an ashing rotary kiln, liquid
burner, and an afterburner. The thermal input to the unit is rated at 95.6 MMBtu/hour.

       Several mechanisms are used to feed waste into the incinerator system. Liquids
are atomized under  air pressure and injected into I lie liquid burner and afterburner
chamber. A positive displacement pump feeds pumpable sludges into the rotary kiln.
Containerized solids are fed into  the unit via a conveyor system.  This  facility generally
does not accept bulk solids, but it does accept  soils.

       Confidential capacity information provided by the facility included the waste
quantities burned during 1992 and the maximum pr.iLtital burning capacity. These
o
c/a
to
71
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                                       2-25

 estimaies are included in the aggregated CBI estimate in Exhibit 2-5. This facility
 indicated that it accepts the Phase II wastes D018-043. K141-145, and K147-15I.

       Rollins plans to replace its rotary kiln with two new units by 1997.  This
 modification should increase the capacity of the facility by twenty percent.  Plans also
 include installation of a free-standing drum shredder.

       Rollins Environmental Service*, Bridgeport, New Jersey

       This RCRA Part  B permitted facility operates one .-lagging rotary kiln with an
 afterburner. The thermal input to the  system is rated at  135 MMBtu/hour.

       Several mechanisms are used to feed liquids, pumpahle sludges, containerized
 solids, compressed gases, and soils into the incinerator system.  Liquids are atomized
 under air pressure and injected into the Loddby liquid burner and afterburner chamber.
 A positive displacement pump  feeds pumpable sludges into the rotary kiln. This facility
 generally does not accept bulk  solids.

      This facility reported quantities of waste burned in 1992 and maximum practical
 burning capacities as CBI. These estimates are included in  the aggregated CBI estimate
 in Exhibit 2-5.  Of the Phase It wastes, this facility accepts D018-043, K141-145, and
 K147-151 wastes.

       Rollins Environmental Services, Deer Park, Texas

      •This RCRA Pan B permitted facility has three incineration units-two rotary kilns
with afterburners, and one rotary reactor.  Each rotary  kiln  system has a thermal input of
 180 MMBtu/hour. The rotary reactor has a thermal input of 33.5 MMBtu/hour. Each
train has several feed mechanisms that utilize concrete  pumps to feed pumpable sludges
and an elevator feed for containers.  A clamshell/crane feeds bulk solids into the rotary
reactor.

      Rollins, Deer Park burns liquids', pumpable sludges, containerized solids,
compressed gases, and soils.  This facility can accept all Phase II wastes (D018-043,
K14M45,andK147-151).
                               i
      Ross Incineration Services, Graftnn, Ohio

      This incineration facility has a RCRA Part  B  permit. Ross's rotary kiln
incinerator burns liquids, nonpumpable sludges, containerized solids, bulk solids,
compressed gases, and soils.  Solids and containerized waste are fed to the kiln via four
feed mechanisms that feed into a gravity feed chute.
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-------
                                                                                                           ?fi
                                        2-26

       CBI provided in the survey included waste quantities burned during 1992 and
 maximum practical burning capacities.  These estimates arc included in the aggregated
 CBI estimate in Exhibit 2-5. Of the Phase II wastes, this facility accepts D018-43 and
 K149-151 wastes.  EPA is currently processing Ross' permit modification to accept K141-
 145 and K147-I48. Ross expects to receive authorization to burn these wastes in 1994.

       ThermalKEM, Rock Hill, South Carolina

       This RCRA Part B permitted facility uses a fixed hearth incinerator with a
 thermal input of 42 MMBtu/hour. This facility can accept liquids, pumpable sludges,
 nonpumpable sludges, containerized solids, bulk solids, compressed gases, and soils.
 Meter :d pumps feed liquid and sludge  wastes and rams feed containerized solids.
 Separate machinery feeds aerosol cans  directly to the incinerator.

       Confidential capacity data provided by the facility include waste quantities burned
 during 1992 and maximum practical burning capacities. These estimates are included in
 the aggregated CBI estimate in Exhibit 2-5. ThermalKEM indicated it can accept all
 Phase II wastes (D018-043, K141-145, and K147-151).
       In 1992, the facility indicated that it planned to increase sludge/solid capacity by
 adding an additional unit, a waste-fired boiler, and additional storage areas.  No such
 changes in capacity were reported in :he 1993 survey.

       USPCI, Clive, Utah

       This new  facility is RCRA and TSCA permitted.  The facility plans to begin 720
 hour shakedown testiitg by late 1994. This facility is not included in EPA's commercial
 combustion capacity estimate.  The unit has a permitted thermal capacity of 200
 MMBtu/hour. This facility will accept liquids, pumpable sludges, containerized solids,
 bulk solids, and soils.

       USPCI did not bum wastes in 1992. Factors assumed in estimating hazardous
waste burning capacity were provided as confidential business information, including
hourly average waste feed  rate, and maximum practical burning capacities.  These
estimates are not included in the aggregated CBI estimate.  USPCI intends to accept  all
Phase II waste codes (D01S-043,  K141-U5, and K147-151).

2.2.2   Other Incinerators Not Included in the Capacity Estimate

       In addition to facilities discussed above that are not included in the national
capacity estimate (USPCI and CWM-Chicago). three incinerators are not included in  the
analysis because  they bum a narrow  range of waste types:  Allied-Signal Tar (Fairfield,
Alabama), BDT, Inc. (Clarence, New York), and Waste Research and Reclamation Co.
(Eau Claire, Wisconsin). The Allied-Signal Tar Products incineralor is an on-site
incinerator that burns a limited amount of hazardous waste on a commercial basis.  The
  o
  71
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  o
n
 	•

-------
                                        :-27
facility is onJy permitted to burn KOOJ, K035. KOS7, UI65, and U05I. The BDT facility
burns highly specialized, difficult-to-treat matcriiils such as elemental lithium and sodium.
Finally, Waste Research and Reclamation Co. burns primarily still bottoms resulting from
the company's solvent recovery operations.

2.2 J   Future Incineration Capacity

      The incineration capacity update presented in the previous section focused on
commercial incinerators that are currently operating commercially. Several planned
commercial incinerators appear to be sufficiently advanced in the permitting and siting
process to potentially come on line by the end of 1995.  EPA contacted state regulatory
agencies for information regarding these facilities ;im! supplemented this effort with
information from the May 1993 El Digest.

      •      As discussed above, USPCI. Give, Utah plans to begin 720 hour
             shakedown testing in mid 1994. The unit  has a permitted thermal capacity
             of 200 MMBtu/hour and will jcccpt liquids, sludges, and solids including
             soil.

      •      Waste-Tech, Kimball, Nebraska. Mxm expects to receive a draft Part B '
             Permit to begin constructing a fluidizcd bed incineration facility. Pending
             successful trial burns, the facility is expected to com: on line in 1994. The
             estimated total capacity for this facility is 43,000 tons per year, of which
             5,000 tons are for sludges and solids.

      •      Waste-Tech, East Liverpool, Ohio, h;is iis RCRA Part B permit. Following
             successful trial burns in March 1992, the facility began limited commercial
             operation in  1993 with an annual capacity for sludges and solids of 52,000
             tons.  Total capacity is expected to tic 88,000 tons per year.  Due to
             ongoing negotiations regarding permit restrictions, this facility has not yet
             entered full-scale commercial Operation.

      •      Waste-Tech in Golden, CO has been siting and permitting a rotary kiln
             since  1987. Originally planned to have a capacity of 33,000 tons per year,
             the latest plans call for capacity of 45,000  ions per year. In 1989, the
             company installed the power, gat. ;ind water lines along with administrative
             buildings, laboratory, and guardhouic.  Remaining construction is expected
             to take one year.
e •»?
  *
    "Hazardous Waste Incineration 199y, E[ Digea. MJY "f(\.
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r—
                                                          2-28

                          •      Ogden has a RCRA permit to construct a facility in Texas with a thermal
                                input of 260 MMBtu/hour and a total capacity of 155,000 ions per year.
                                Construction is scheduled to begin in  1994.

                   23    COMMERCIAL BIF HAZARDOUS WASTE CAPACITY

                          This section focuses on the combustion capacity of the nation's commercial BIFs.
                   Exhibit 2-7 summarizes the  status of combustion capacity at each the facilities included in
                   the analysis. Section 2.3.1 discusses capacity at each of the individual facilities that
                   submitted CKRC surveys. Section 13.2 discusses facilities that are included in the
                   national capacity estimate but did not respond to the CKRC survey. Section 2.3.3
                   discusses combustion capacity for soils.

                   2.3.1   Individual BIF  Facility Capacity Analysis  .

                          Facility profiles are provided below for each  of the BIFs included in the
                   commercial combustion capacity estimate. These profiles have been created based on
                   data provided in the CKRC survey. The estimates included in this section do not take
                   into account the capacity that is required for Phase  I wastes for which the capacity
                   variance granted to routinely generated F037 and F038 expired in June 1993.  Also,
                   please  note that EFA's capacity analysis focussed primarily  on sludges and solids, and
                   does not include all commercial BIFs that receive only liquids.

                         Ash Grove, Chanute, Kansas

                         The Ash  Grove Chanute facility currently operates two BIFs, both of which burn
                   liquid and containerized solid hazardous wastes.  The kilns operate 7,500 hours per year.
                   Based on reported maximum practical feed rates, and  1992 utilized capacity, EPA
                   estimates the facility's available liquid waste capacity to be 17,775 tons per year and its
                   available solids capacity to be 39,499 tons  per year.  All Ash Grove facilities report that
                   their liquids contain up to 20 percent entrained solids. Of the Phase II wastes, this
                   facility accepts D018-D043 waste codes. This facility reported no plans to change its
                   hazardous waste burning practices before June 1994.

                         Ash Grove, Foreman, Arkansas

                         There are three wet process rotary  BIFs currently burning hazardous waste  at this
                   facility. They all inject liquid hazardous waste  fuel into the  hot end of the kiln, and
                   charge containerized solids to the calcining zone.  The kilns operate for 7,800 hours per
                   year. EPA estimates that  together the three kilns have 38,286 tons of liquid capacity
                   available per year and  46,737 tons of containerized solids capacity available. This
                   estimate is based on the reported maximum practical feed rates and 1992 utilized
                   capacity estimates. All Ash  Grove facilities report that as burned, their  liquids contain
3 S *

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                                        KXIllBfT 1-7


              Summary of Conimtirlal Itlfr Burning Capacity Through August 1994
Facility Nun*
Aid Grove Ciunuic Cement
Piul.
Chuute. KS
KSD03 12033 18


Adi Grov« Foreman Ct mtnl
Pluil,
Foreman. AR
ARD981SIJ270



Adi Orove Louiivilli Cement
Plant.
Louinitl*. NE
NED007260672


Caniliiu Solile.
Albemirle. NC
NCDOOOT736U
Unit
T>p.
WR
WR
*****
WR
WR
WR
*****
AC*
PC
*****
CM
Wult
T)P«
riml (otiiii
mil liqi
conl tolidi
all lii(>
TOTAL
coal wlidi
all liq>
con! tolidi
ill li<|i
coal jolid*
altliqt
TOTAL
cool »lid»
ill liqt
coat wlidi
-llliqi
TOTAL
ill liqs
1W.
L'dllac]
C.p-dly
(Tom/Yr)
5.560
19.674
4.WI
11.711
48.106
8.2.5
10.766
H.250
17.306
S.756
15.602
64.905
I.JJ7
1.181
2.945
3.892
9.355
0
August 1994
Reported
Maximum
Opacity
(ToraA'r)
24.960
28.080
24.960
28.080
106.080
22.656
25.320
22.656
, 28.320
22.656
28,320
152.928
9.360
24.960
12,4«0
24.960
71.760
22.000
Auguttim
Adjusted
Capacity
(Tc-nsAYr)
24,960
28.080
24,960
28,080
4
106.080
22.656
25,320
22.656
28.320
22.656
28.320
149,928
9.360
24.960
12,480
24,960
71,760
22.000
Autustl994
Adjusted
Estimated
Available
Capacity
(TonsA'r)
19,400
8,406
M.099
9,369
57.274
14.431
14.554
15.406
11. OH
16.900
12,718
85.023
8,023
23.779
9.535
21,068
62.405
22.000
u

2)
• • Plumed or Not Openttaf.

Unit Type ibbrtviiiioos: AC = Alli« Clulm«re - Prthe*ier. wp = Wet Process: LD = Long Diy; LW =

Long Wet;  CM » Cement; RT = Rotwy; PC = Precilcincr; TR » Tnylon WR = Wet Process Rotuy
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                                    EXHIBIT 2.7 (continued)


              Summary of Commercial BIFs Burning Capacity Through August 1994





Facility Name

Citadel Cement Co..
DecxjpolU. AL
AUXJ671 19966

Continental Cement Co.,
Hannibal. MO
MOD0540I82SS

Dixie Cement Company,
Knoxville, TN
TND106203375

ESStOC,
IJDgllBSpOftt IN
INDOOS081S42

Florida Solita.
Greta Cove Springs, FL
FLC000737312

Gi«l t Cement Co.,
Kirieyvitle. SC
SCC 003351699




Unit
Type
• **»*
AC


*•***
LW


*•***
PC


•>***#
CM


•»*«»
CM


*****
CM






Waste
TjP*
TOTAL
pump il
all liqs

TOTAL
bulk solids
dry solid*
all liqs
TOTAL
conl solid*
all liq/p)

TOTAL
•11 sol/nps
til Hqi

TOTAL
all liq>


TOTAL
dry solids
allliqs



1992
Utiliad
Capacity
(To«/Yr)
0
3.2JO
33.743

36.993
7,636
3/i03
63.0R9
73.328
10,281
8.33S

18.619
20.000
50,000

70.000
0


0
4.700
89,300


August 1994
-Reported
Maximum
Capacity
CTontfYr)
22.000
6.000
40,000

46.000
142.953
142.963
112.478
142.963
46,900
18.400

46,900
24,000
61.000

85.000
11.000


11.000
18,200
111.800


August 1994
Adjusted
Maximum
Capacity
(Tens/Yr)
22,000
6.000
40,000

46.000
25,410
5.075
112.478
142.963
28.500
18.400

46.900
24.000
61,000

85.000
11.000


11.000
I8,:00
111.800

August 1994
Adjusted
Estimated
Arailable
Capacity
fTom/Yr)
22.000
2,750
6.257

9.007
17,774
2.472
49,389
69.635
18.219
10,062

28,281
4,000
11.000

15.000
11,000


11.000
13,500
22.500

r>

2)
• = Planned or Not Operating

Unit Type abbreviations: AC = Allit Coalmen - Prtliealer; WP =» Wet Process; LD = Long Dry; LW =

Long Wei; CM = Cement; RT = Rotary; PC = Precjkiner: TR = Traylor. WR a Wei Process Rotary
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                                     EXHIBIT 2-7 (contlnurd)


               Summary of Commercial BIFs Burning Capacity Through August 1994




Facility Name

Heartland Cemeot Co..
Indcoeodeccti KS
KS09S0739999

Holnam, lac..
Aru=sU,MS
MSDOT76S3876

Holnam, Inc.,
HoUyHill. SC
SCD00336M91
'
•
Holaam/Safely KJeen Corp.,
Clarksville, MO
MOD02972968S

Kentucky Solile.
Brooks. KY
KYD0007703I3

Keystone Cemeot Company,
B»th. PA



Unit
Type
*****
CM


*****
WP


*****
TR«


AC
*****
RT


*****
CM


*****
WR




Wasle
Type
TOTAL
dry solids


TOTAL
all liq$


TOTAL
allliqt


«Uliq>
TOTAL
ill liq'pl


TOTAL
•Ksol/npt


TOTAL
all liq»


1992
Utilized
C.p.eity
CTont/Yr)
94.000
1.550


1.550
0


0
30.000


49,000
79.000
102,878


102,878
4,000


4.000
5,760

AUKUriim
Krportcd
Maximum
C.p.eHy
(ToM/Yr)
130.000
15.000


U.OOO
46.300


0
45,000


72,000
0
150.357


150.3S7
11.000


11.000
18.900

AuJiiJtlW
Adjusted
Maximum
Cipadty
(Tons/Yr)
130.000
25.000


25.000
46,300


46,300
45,000


72,000
117.000
150.357


150,357
11,000


11.000
18.900

Adjusted
Estimated
ATiilablt
Capacity
(Tons/Yr)
36,000
23.450


23.450
46.300


46.300
15.000


23.000
38.000
47.479


47,479
.7,000


7.000
13.140

2)
* - Plumed or Not Operating


Uoit Type abbtw-iitions: AC = Allij Cbalmen - Ptebeater.  WP • We» Prooas: LD = Loog Dry; LW «

Looj Wet; CM - Cemeot; RT = Rotaiy; PC = Pretilcincr; TH - Traylon WR =* Wet Process Rotaty
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                                   EXHIBIT 2-7 (contlnuttl)


              Summary of Commercial BIFs Burning Capacity Tbroufta August 1994
Facility Name
PAP002389559


Ufug;,
AIpeni.MI
M1D005379607


Lifarg: Corp.,
Fredoti*. KS
KSDO(i7I48034


Lafarg: Corporation.
Pwldiiig, OH
OHD937048733


Lone ! Ur Alternate Fuel Co.,
Cape Ciirardeau, MO
MOTS 11273 19
Unit
Type

WR
• •«««
LD
U>
*•»»*
WP
WP
%*•»**
CM
CM
**•**
PC
Waste
Type

«]| liqi
TOTAL
all liq»
all liqi
TOTAL
dry aolidi
«Hlio/pi
dry solid!
all liq/pi
TOTAL
pump ji
all liqi
pumpil
•11 liq«
TOTAL
coat solid*
all liqi
1992
Utfflied
Capacity
fToos/Yr)

29,803
35,565
41,000
43,000
96.000
788
36.503
263
48,387
85.941
1.727
27.566
1.727
27,566
58,586
354
25.543
August i9M
Reported
Maximum
Capacity
(Torn/Yr)

56.700
75,600
56.000
56.000
0
788
37,410
263
49,590
87.000
1 2.500
30,000
2.500
30,000
65.000
2,700
57.000
August 1994
Adjusted
Maximum
Capacity
(Tora/Yr)

56.700
75,600
56,000
56.000
112,000
788
36.619
263
49,322
86,992
2,500
30.000
2.500
30,000
65.000
2,700
57,000
August 1994
Adjusted
Estimated
Aral table
Capacity
(Tons/Yr)

26,895
40,035
8,000
8.000
16,000
0
116
0
935
1,051
773
2,434
773
2,434
6,414
2,346
31,457
1)
2)
* = Planned of Noi Operating

Uni( Type abbreviation!; AC - Alli> Chalmers - Prchcaier; WP =• Wet Preceu; LD = Long Dry; LW -

Long Wet; CM = Ceroeol; RT = Rotary; PC = Prccslciner; TR = Traylor; WR = Wei Process Rotary
                                                                                                           1     -B!
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                                       EXHIBIT 2-7 (continued)
                Summary of Commercial BIFs Burning Capacity Through August 1994
Facility Name

Lone Stir Induitriej. Inc..
Groeaastle, IN
IND0064192S2

Medusa Ceaeat Co..
Wunpuo, PA
PADOS3965897


UbecPlMU,
Lebec, CA
CA09S2444887

North Team Cement,
Midlothian, TX
TXtiaknown

River Cemeat.
R*tl», MO
MODOSO132S60

Safely Kleen Envinxyatenia
Co..
Dondo. PR
Unit
Type
+»*•*•
kT
*****
CM
*****
LJD

*****
CM
*****
CM
**•*•
LD
Wwte
Typ.
TOTAL
coat (Olidi
illliqi
TOTAL
purapil
apiimpd
*llliq>
TOTAL
•Uliqi

TOTAL
lUUqi
TOTAL
pumpil
npumptl
allllqi
TOTAL
aUIiqi
im
Cdltad
Ccpcdty
(T««J/Vr)
25.S97
5.332
43,556
30.S88
2.500
500
7.000
10,000
22500

22,500
1.000
1,000
16,250
3.250
45,500
65.000
4.B63
August 1994
Reported
Maximum
Capacity
(Tora/Yr)
59,700
13.000
45.556
58,556
6,400
1,200
32.400
40.000
30200

0
50,000
50,000
20,000
4.000
56.000
145.000
49,410
AugutttfcM
Adjurttd
Maxtmuro
Cmpmdly
(Tons/Yr)
59.700
13.000
45.556
58.556
6,400
1.200
32.400
40.000
30200

30,200
50.000
50,000
20.000
4,000
56.000
80.000
49,410
Ai«iBtl»94
Adjusted
F*rtni»(H
Arailable
C«p«Hy
(Tom/Yr)
33.803
7,668
0
7.668
3.900
700
25,400
30,000
7 700

7.700
49.000
49.000
3.750
750
10.500
15.000
44,547
2)
* = Plinaed or Not Openling
Unit Type abbrcviattotu: AC - Allii Chalmen - Preheatcr:  WP - Wet Pmcttr. LD = Long Ocy:  LW =
Long Wet; CM " Cement; RT = Rolacy; PC - Precalcincr; TR = Tnylor, WR » Wet Process RoUuy
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*
                                             EXHIBIT 2-7 (continued)


                      Summary of Commercial BIFs Burning Capacity Through August 1994
Facility Name
PRDC980526II5

Solita Coip.,
CuuJe. VA
VAD077942266

SotiteCorp..
Atvoda. VA
VAD09S443443

South *e»tera Portland
Cement Co.,
JFiirtora.OH
OHDW 19577$

TeJuu Industries, Ins.,
Midlothian, TX
TXDC007349327




A gjrtg»led Rcsulu
Unit
Type

*****
CM
*****
CM
*••••
CM
*•***
RT
RT
RT
RT
*****

Waste
Type

TOTAL
ill liqi
TOTAL
allliqi
TOTAL
lUUqi
TOTAL
illliqt
ill liqs
tUHqi
tllliq.
TOTAL
liq(«q)
19M
Utilized
Capacity
CTons/Vr)

4.863
15.000
15.000
15,000
15.000
630
630
19,000
19.000
19,000
19.000
76,000
0
August 1994
Reported
Muinun
Capacity
(Tom/Yr)

49.410
3J.OOO
33,000
22,000
22.000
20,000
M.OOO
60,000
60.000
60.000
60.000
0
0
August 1994
Adjusted
Maximum
Capacity
(Tons/Yr)

49,410
33.000
33.000
22,000
22,000
20,000
20,000
60.000
60.000
60,000
60,000
240,000
0
August 1994
Adjusted
Estimated
ArailaMe
Capacity
CTom/Yr)

44.547
18.000
18,000
7,000
7.000
19,370
19,370
41.000
41,000
41.000
41.000
164,000
0
       o

       2)
* = Fluxed or N'ot Operating

Unit Type ibbicviationi: AC = Allis Chiloen - Pntxiler, W? 3 Wcl Process; LD = Long Dry; LW =

Long Wei; CM = Cement; RT = Rotiry; PC = Pracilciner; TR = Traylor; WR = Wei Process Rotuy
                                                                                                          l?5


                                                                                                      '   «"E
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-------
                                EXHIBIT 2-7 (continued)


             Summary of Commercial BIFs Burninj Capacity Through August 1994
Facility Name
(Operating Uaitt Only)










foul (Opentiog Unili Only)

Unit Waste
Type Type
liq (oaq)
pumpf)
npumpit
coot folid*
tnlknUdi
dry »oli
-------
                                        2-36

 approximately 20 percent solids.  Of the Phase II wastes, the facility is authorized to
 receive D018-D040, D042, and D043 wastes.

       Ash Grove, Louisville, Nebraska

       The Ash Grove Louisville facility currently burns liquid and containerized solid  •
 waste fuel in two rotary preheater BIFs. Liquid hazardous waste fuel is injected into the
 hot end of the kiln, and containerized solids are charged to the calcining zone.  Both
 kilns operate 7,500 hours a year, slightly less than the "total operating time" of the kilns.
 Based on the reported maximum practical capacity and 1992 utilized capacity, EPA
 estimates thai the facility has 44,847 tons of liquid combustion capacity available per
 year, and 17,558 tons of containerized solids capacity available per year. Ash Grove
 reports tin: as burned, their liquids contain approximately 30 percent solids. Of the
 Phase II wastes, the facility is authorized to receive DOI8-D040, D042, and D043 wastes.

       Citadel Cement Company, Demopotis, Alabama

       This facility burns liquid and pumpable sludge hazardous waste fuels in one
 preheater kiln. Canisters are injected into the burning zone by compressed air cannons.
 This kiln is operational for 1,784  hours a year.  The facility reported that as burned, their
 liquids contain an average of 25 percent solids. Dnscd on reported maximum practical
 burning capacity and 1992 capacity utilization estimates, EPA estimates that the facility
 has 6,257 tons per year liquids capacity available, and 2,750 ions per year pumpable
 sludge capacity available.

    ,,   Continental Cement Company, Hannibal, Missouri

    '   Continental Cement currently operates one long wet BIFs, which burns liquid and
bulk solid, and dry solid hazardous wastes. The kiln operates 7,600 hours per year.
 Based on reported maximum practical capacity, and 1992 utilized capacity, EPA
estimates the facility's adjusted available liquid waste capacity 10 be 49,389 tons per year,
 its available bulk solids capacity to be 17,774 tons per year, and its available dry solids
capacity to be 3,472 tons per year. The facility reports that their liquids, as burned,
contain an average of 25  percent entrained solids.

       Dixie Cement Company, Knoxville, Tennessee

       This facility burns  liquid and containerized solid hazardous waste fuel in one four-
stage  cement kiln with preheater and precalciner. The facility reported that as burned,
their liquids contain an average of 30 lo 40 percent solids. The kiln operates 7,850 hours
per year.  Based on reported maximum  practical feed rales and 1992 waste quantities,
EPA estimates that the facility has 18,219 tons per year solids capacity available, and
 10,062 tons per year liquids capacity available.  This facility is currently not permitted to
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      03

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                                        2-37
 receive D018-D043, K141-K145, and K147-KI51 waste codes, but has submitted a permit
 modification to add these wastes.

       liolnam, Artesia, Mississippi

       This Holnam facility is new, and was not operational in 1992. It burns liquid
 hazardous wastes in one wet kiln, which is projected to operate 90 percent of the time,
 beginning 'in August of 1993.  The hazardous waste fuel is injected into the hot end of
 the kiln. There was no hazardous waste utilization during 1992. but based on the
 reported projected  maximum practical capacity, EPA estimates that the facility has
 46,300 tons per year available capacity.  The facility is authorized to accept DO 18, D019,
 D021-D036, and D038-D043 waste codes.

       Horaam, Holly Hill, South Carolina

       The Holnam facility in Holly Hill burns  liquid hazardous waste fuels in two long
wet kilns.  Liquid hazardous waste fuel is injected  into the hot end of the kiln.  The
 larger kiln operated 7,400 hours in 1992, however, operation of the smaller kiln was
discontinued during 1992 due to difficulties in meeting the hydrocarbon/carbon monoxide
standard under the  BIF rule.  EPA estimates that  the larger kiln has 23,000 tons per year
liquids capacity available.  The facility indicated that it accepts D040-D043 waste codes.

       Holnam/Safety Kleen Corp., Clarksville, Missouri

      This facility burns liquid hazardous waste fuels in one long wet rotary kiln. Liquid
hazardous waste fuel is injected into the hot end of the kiln.  The kiln operates 7,500
hours a year.  The facility reported the average solid content of liquids as burned, is 20
percent. Based on  reported maximum practical burning capacity and 1992 capacity
utilization estimates, EPA estimates that the facility has 47,479 tons per year liquids
capacity available. This facility has interim status for the following Phase II wastes:
D018, D019, D02I-D030, and D032-D043.

       Keystone Cement Company, Bath, Pennsylvania

       Keystone Cement Company bums liquid hazardous waste in two wet process
rotary BIFs.  These kilns operate 7,850 hours per year.  The  hazardous waste fuel is
injected into the hot end of the kiln. The facility reported that as burned, their liquids
contain less than IS percent solids.  EPA estimates that the  facility has 40,035 tons per
year available capacity.  This facility is authorized to receive D018-D043 wastes codes.

      Lafarge Corporation, Alpena, Michigan

      This facility operates five rotary BIFs, but only two are currently burning
hazardous waste.  These kilns burn liquids  only, and each operates 7,500 hours per year.

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CO
to
T1
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to

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                                        2-38

The facility reported that as burned, their liquids have a 15 percent solid content.  EPA
estimates that together the loins have 8,000 tons of capacity available per year. Lafarge
intends to burn hazardous waste in the three kilns that are not currently burning
hazardous waste, but must first satisfy numerous construction and regulatory
requirements. Lafarge estimates they will be on line burning liquid waste by  1994  (survey
says no changes to burning practices planned before July 1994). The facility also plans to
install a sludge handling system at some unspecified point in the future.  The facility is
authorized to receive D018, D019, D021-30, and D032-42 waste codes.

       Lafarge Corporation, Fredoaia, Kansas

      This facility operates two rotary  BIFs. Both burn liquid hazardous waste streams.
The facility reported that as burned, their liquids contain an average of 25 percent solids.
The smaller kiln operates about 7,800 hours per year, while the larger one averages 7,600
hours. EPA estimates this facility is utilizing all of its dry solids combustion capacity and
has about 1,000 tons of liquids capacity available.  The facility is authorized to burn
DOlb, D019, D021-30, and D032-42 wastes.

      Lafarje Corporation, Paulding, Ohio

      This facility burns liquid and  pumpable sludge hazardous waste fuel in two rotary
BIFs. Lafarge reports that this facility's liquids, as burned, contain approximately 10
percent solids.  One of the kilns operates approximately  8,100 hours per year, the other
7,800 hours.  EPA estimates this facility has 4,868 tons per year of available liquid
capacity and  1:546 tons of available  pumpable sludge capacity.  Lafarge has indicated  in
the past that dry solids capacity would be added. Although the 1993 survey did not
include  mention of dry solids capacity, additional containers and bulk solids capacity were
indicated for 1994-1995. The facility is  authorized to burn D018, D019, D021-30, and
D032-42 wastes.

      Lone Star Alternate Fuel Company, Cape Girardeau, Missouri

      This facility burns liquid hazardous waste fuels and containerized solids in one
precalciner kiln. Pumpable liquids are injected at the hot end,  and containerized solids
are fed via air cannon.  The kiln is operational  for 7,440 hours  per year. Lone Star
reported that as burned, this facility's liquids contain an average of 25 percent solids.
EPA estimates that the facility has 31,457 tons per year liquids  capacity available and
2,346 tons per year containerized solids capacity available.

      Lone Star Industries, Green Castle, Indiana

      This facility burns liquid and containerized solid hazardous waste fuel in one long,
wet process rotary cement kiln. The facility reported that as burned, their liquids contain
an average of 20 percent solids.  The liquid waste fuel  is injected into the hot end of the
'   ill
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                                       2-39

 kiln, and solids are reground with bulk liquid and fed as pumpable liquid at hot end (one
 gallon plastic jugs are injected at hot end). The kiln burns liquid waste fuel for 5,500
 hours a year, and burns containerized solids for 2,350 hours a year. EPA estimates that
 Lone Star has no liquid combustion capacity available, nnd 7,668 tons per year capacity
 available for containerized solids.  This facility is authorized to burn D018,  D019, D021-
 30, and D032-42 wastes.

       National Cement Company, Lebec, California

       This facility burns liquid hazardous waste in one long, dry process  cement kiln.
 Waste fuel is injected into the hot end of the kiln. The facility reported that as burned,
 their liquids contain an average of 10 percent solids. National Cement operates an
 average of 6,756 hours per year.  EPA estimates that the facility has 7,700 tons  of
 capacity available per year. This facility is authorized to burn DO 18, DO 19, D021-26,
 D028, D035, D039 and D040  wastes.

       Safety Kleen  Envfrosystems, Dorado, Puerto Rico

      This facility bums liquid hazardous waste in one dry process kiln.  Hazardous
waste feed is pumped into the hot end of the kiln. This kiln operates an average of
6,000 hours per year.  The facility has two more kilns, but did not indicate why these
other kilns are not expected to burn hazardous wastes by July 1994 EPA estimates that
the kiln has 44,547 tons per year of available capacity. This facility is  authorized to burn
D018, D019, D021-43 wastes.                                 .   ,     '

      Texas Industries, Incorporated, Midlothian, Texas

      This facility burns liquid hazardous waste fuels in four rotary kilns.  Each of these
kilns operates 8,300  hours per year.  The facility reported that as burned, their liquids
contain an average of 8 percent solids (maximum 30 percent .suspended solids).  EPA
estimates that the facility has  164,000 tons per  year liquids capacity available.  This
facility is authorized to bum DO 18, DOI9, D021-30, D032, D033, and D035-43 wastes.

23.2  Commercial BIFs Not  Included in the CKRC Survey

      EPA is aware that additional BiFs are burning hazardous waste that did not
submit 1993 CKRC surveys. These facilities include Carolina Solite (Albermarle, NC),
ESSROC (Logansport, IN), Florida Solite (Green Cove Springs,  FL), Giant Cement
(Harleyville, SC), Heartland Cement (Independence. KS),  Kentucky Solite (Brooks,
KY), Medusa (Wampum, PA), North Texas Cement (Midlothian, TX), River Cement
(Festus, MO), Solite {Arvonia, VA),  Solite (Cascade, VA), and Southdown (Fairborn,
 O
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 to
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                                         2-40

 OH}9. An additional facility, Holnam (Ada, Oklahoma), is not operating but it does
 have interim status.  It is currently negotiating with state officials for final approval. This
 facility is not included in the capacity analysis.

        To present a complete picture of available commercial combustion capacity, the
 Agency has supplemented the analysis with  information contained in the September 1993
 El Digest10. El Digest provides the quantity of hazardous waste burned in 1992 and
 the maximum practical burning capacity. The waste quantities are not allocated, though
 among waste forms (e.g., liquids and solids). To overcome  this obstacle for facilities that
 burn multiple waste forms, the Agency applied percentage utilization factors for each
 waste form at each facility based on data submitted in the 1991 CKRC Survey.
' Maximum and utilized capacities for each waste form have  been incorporated into the
 analysis.  Brief individual facility profiles are presented below based on information
 contained in the 1992 CKRC Survey and the September 1993 El Digest.

       Carolina Solite, Albemarle, North Carolina

       This lightweight aggregate facility has an interim status BIF permit. It burns liquid
 wastes in four kilns.  The facility did not bum wnslc in 1992. EPA estimates their
 current liquid waste burning capacity as 22,000 tons.

       ESSROC, Logansport, Indiana

       This facility burns liquid hazardous waste fuel in two wet process BIFs.  The
 Agency estimates that this facility has 11,000 tons per year of available capacity for
 liquids and 4,000 tons per year available for containerized solids.  Of the Phase  II wastes,
 this facility accepts D018-43, K14M45, K147-148, and K149-151.

       Florida Solite, Green Cove Springs, Florida

       This lightweight aggregate facility has an interim status BIF permit.  Florida Solite
 is currently operating one of its three kilns for burning liquid wastes.  The facility did not
 burn waste in  1992.  EPA estimates their current available capacity at 11,000 tons of
 liquid wastes.  Of the Phase II wastes, this facility is permitted to burn DO 18-043, K141-
 145 and K147-I4S.
                                                                                                                            O
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             * Marine Shale Processors (Amelia, LA) is not included in ihc iiniil^is due 10 ongoing enforcement actions.  In 1992,
          the repotted liquids capacity »as 200,000 tons and 80,000 inni i>f u:uic »crc burntd.

             * 'Industrial Furnaces 1993", El Ditesl. Stpicmbtr 19">V
                                                                                                                           UJl
                                                                                                                               j

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                                        2-41
       Giant Cement Company, Hariejviile, South Carolina

       This facility bums liquid and dry solid hazardous waste in four wet process BIFs.
 Both types of wastes are fed into the hot end of the kiln.  The facility reports that their
 liquids, as burned, contain an average of 20 percent  entrained solids.  EPA estimates that
 together the kilns have 22,500 tons per year liquid combustion capacity available, and
 13,500 tons per year available capacity for dry solids. Of the Phase II wastes. Giant
 Cement is permitted to receive DO 1 8-4 3 wastes.

       Heartland Cement Company, Independence, Kansas

       This facility bums dry solids in four dry process BIFs.  They each feed dry solid
 hazardous waste into the hot end of the kiln. EPA estimates that together the four kilns
 have 23,450 tons per year available capacity for dry solids.  Of the Phase II wastes, the
 facility is authorized to bum D018-D043 wastes.

       Kentucky Solite, Brooks, Kentucky

       Kentucky Solite has an interim status BIF permit. This facility burns solid wastes
 in three aggregate kilns.  EPA estimates  that the facility has 7,000 tons of available solid
waste bunting capacity.

       Medusa Cement, Wampum, Pennsylvania

      This facility bums liquid and sludge hazardous waste in three long dry process
BIFs. Solids are ground and mixed into the liquid sitcam, before being injected into the
kilns. The facility reported that as  burned, their liquids contain an average of 25 percent
solids. EPA estimates that the facility has 25,400 tons per year liquid capacity available,
3,900 tons per year pumpable sludge capacity, and 700 tons per year npnpumpable
sludge capacity available. The facility is authorized to burn D018, DO 19, D021-36, D03S,
D039, D042 and D043 wastes. D020, D037, D040 and D041 are acceptable in  trace
amounts.

      North Texas Cement, Midlothian, Texas

      This facility bums  liquid wastes. The facility hns an interim status BIF permit, and
has not burned commercially since April  1991.  [IPA estimates that North Texas has
49,000 tons of available liquids burning capacity.

      River Cement, Festus, Missouri

      River Cement burns liquid and sludge  h:iz:udous waste fuel in two dry process
BIFs. The facility reports that their liquids, as burned, contain an average  of 20 percent
entrained solids.  The facility filters liquid hazardous  waste and grinds sludges, before
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                                        2-42

 blending the two and pumping the hazardous waste fuel into the hut end of the kiln.
 EPA estimates that the two kilns have 10.500 tons per year liquid hazardous waste
 capacity available, 3,750 tons per year pumpable sludge capacity available, and 750 tons
 per year nonpumpable sludge capacity available.  The facility is authorized to burn D018,
 D019, D02I-36, D038, D039, D042 and D043 wastes.  D020, D037, D040 and D041 are
 acceptable in trace amounts,

       Solite-Arvonia, Arvonia, Virginia

       This Solite facility has an interim status BIF permit.  It operates four kilns that
 burn liquid wastes.  Solite-Arvonia's available liquids burning capacity is estimated by
 EPA to be 7,000 tons.  Of the Phase II wastes, this facility is permitted to bum DO 18-043.

       Solite-Cascade, Cascade, Virginia

       Sob'te-Cascade has an interim status EtF permit.  The facility burns liquid wastes
 in four kilns.  EPA estimates its available liquid burning capacity at 18,000 tons. Of the
 Phase II wastes, this  facility is permitted to burn DO 18-043.

       Southwest Portland Cement Co., Inc, Fair born, Ohio

       Southwesl's Fairbom, Ohio facility burns liquid hazardous wastes in one  dry
 process cement kiln with preheater. The  facility reported in the 1991  CKRC survey that
 their liquids, as burned, contain less than  5 percent entrained solids. The waste fuel is
 injected into the hot  end of the lain.  Based on reported maximum  practical feed  rates
 and 1991 waste quantities, EPA estimates that the facility has 19,370 tons per year of
 liquid combustion capacity available.  At present it is only permitted to burn
 characteristic metal wastes, D001, and F001,  F002, F003, and F005. It is modifying its
 RCRA permit to receive additional wastes, including the Phase II waste codes DO 18,
 D019,  D021-30, D032-40, and D043.

 23.5  Commercial BIF Capacity for Soils

       The CKRC survey did not specifically request capacity data for the combustion of
 soils. However, facilities were asked if soils could  be accepted for burning.  Of the 18
 facilities that responded to the CKRC survey, 16 explicitly indicated that they do not
 accept hazardous soils.  Two facilities, Continental Cement (Hannibal, MO) and
 Southdown (Knoxville, TN), reported that thsry could accept hazardous soils, and that this
 capacity can be considered part of their solids capacity.  The Agency believes that,
 because soil alone generally has a very low heating value, facilities are blending soils with
other hazardous wastes having high heating values, or .ire using contaminated soil as an
 ingredient rather than for energy recovery. The Agency's evaluation of heating  value
 limits provided by Continental and Southdown supports the contention that BIFs
generally cannot  accept soil as a large  peregrine of their feed (i.e., without extensive
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                                               2-43

          blending).  Exhibit 2-8 summarizes the minimum heats of combustion reported at each of
          the facilities that report accepting soils.

                                            EXHIBIT 2-8

                REPORTED MINIMUM HEATS OF COMBUSTION At CEMENT KILNS
                                THAT ACCEPT HAZARDOUS WASTES
Facility/Location
Continental Cement
Hannibal, MO
Souihdown
Knoivil!e,TN
Minimum Allowable Haling Value
(BTU/ID) As Received
Bulk
Solids
5.000
n/r
Diy
Solids
5.000
n/r
Containerized
Solids
n/f
5.000
Minimum Allowable Heating Value
(BTU/lb) As Burned
Bulk
Solids
8.000
n/r
Dry
Solids
8.000
n/r
Containerized
Solids
n/r
n/r
                 Note W radkaia UK iafonutiwi wn oat repotted
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2.4   OTHER TREATMENT SYSTEM CAPACITIES

     •This section discusses commercial treatment capacity other than combustion.
Specifically, it presents EPA's capacity analysis for stabilization, biological treatment, and
chemical precipitation. Section 2.4.1 discusses the general approach and assumptions  "
EPA used for estimating available capacity for these technologies, and Section 2.4.2
summarizes available capacity for newly listed and newly identified wastes regulated
under the Phase II LDR rule.

2.4.1  General Approach and Assumptions

      In analyzing alternative treatment capacity for stabilization, biological treatment,
and chemical precipitation for newly listed and identified wastes, the Agency built on the
capacity analyses conducted for the Third Third LDR rule. This analysis was based on
data contained in the May 1990 TSDR Capacity Data Set.11 The TSDR Capacity Data
Set contains results from the National Survey of Hazardous Waste Treatment, Storage,
Disposal and Recycling Survey (the TSDR Survey).  The TSDR Survey was administered
in 1987 to  2,500 facilities and was designed to provide comprehensive information on
current and planned hazardous waste management, and practices at RCRA-permiUed
            " US. EPA, ComawKiel Trttamuu.'Recorerji Data Sri, May I WO.
                                                                                                                  ch

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;•"*"
                                                          2-44

                   and interim status treatment, storage, recycling, and disposal facilities. The TSDR Survey
                   collected projections of capacity changes from 1986 through 1992.  The TSDR Capacity
                   Data Set includes the amount of hazardous and nonhazardous waste entering each
                   treatment system in 1936, the maximum hazardous waste capacity, and the maximum
                   total waste capacity.

                         For prior LDR rulemakings, EPA updaied  the TSDR Capacity'Data Set for
                   critical technologies based on confirmation of planned capacity changes,  and other
                   information received since the survey (e.g., comments on proposed rules).  Updaied
                   information was obtained by contacting facilities and verifying critical projected capacities
                   reported in the TSDR Survey.  Based on the information provided by facility contacts,
                   EPA determined whether planned facility capacity had come on line as projected. For a
                   more detailed explanation of the TSDR Survey and of the Third Third Rule refer to U.S.
                   EPA, Background Document for Tliird Third Wastes to Support 40 CFR Pan 268 Land
                   Disposal Restrictions, May 1990.

                   2.4.2  Summary of Available Capacity  for Biological Treatment, Chemical Precipitation,
                         and Stabilization

                         Exhibit 2-9 summarizes required and available capacities of commercial treatment
                   systems appropriate for  newly listed and identified wastes covered in the Phase II rule.
                   The 1994 baseline available capacity is the updated maximum (updated as described
                   above) net of the 1986 baseline utilized capacity.  The 1994 baseline does not reflect any
                   capacity required as a result of prior  LDR rales. To estimate the capacity available for
                   newly identified wastes, the capacity demand for previous LDR rules was subtracted from
                   the 1994 available baseline capacity.  For individual facility data refer to  the TSDR
                   Capacity Data Set.
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                                                   2-45

                                                EXHIBIT 2-9

                             AVAILABLE COMMERCIAL CAPACITY FOR PHASE II
                                  NEWLY LISTED AND IDENTIFIED WASTES"
H. ~   5 »*
Pits





Technology
Biological Treatment
Chemical Precipitation
S'abilization

1994
Baseline
Arailable
Capacity
(1000 tpy)
196
1,414
3,125
Capacity
Required
for LDR
Rules Prior
to 1992
(Tons/year)
8,000
600,000
1,921,000

Capacity
Required for
Phase I
Wastes
(Tons/year)
< 1.000
< 1,000
77,000

Capacity
Available for
Phase II
Wastes
(Tons/year)
187,000
813,000
1.127,000
                    * Toub nuy be ineuct due lo rouBdin|.
                    Source Baclyaind Documaafor JJlirrf Third Wtaa to S*ff>~t 40 CfR P<*1168 Land Cifxunf Raoiaioni. Miy 1990, ipd
                    BeJwourtDaWwferCafaciirAnatfaifvKt** LduJ M Uun «kl Haur&xu Dthrii m Support 40 CFR 26f La*
                    Kamamarieaaiu. June tin
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                                      CHAPTER 3
         CAPACITY ANALYSIS FOR TOXICITY CHARACTERISTIC WASTES
        This chapter discusses the required treatment capacity analysis (i.e., the demand
 for alternative commercially available treatmeni) conducted for the newly identified •
 tenacity characteristic (TC) pesticide wastes (D012-D017) and ihe newly identified TC
 organic wastes (D018-D043). Section 3.1 provides background information on the
 regulatory history of these wastes, the treatment standards being considered for this rule,
 and an overview of how EPA assessed the required treatment capacity for these wastes.
 Section 3.2 describes the data sources that were consulted and developed to collect the
 information required for the capacity analysis.  Section 3.3 explains the detailed method-
 ology used for the analysis of required treatmeni capacity, discusses the factors affecting
 the analysis of TC pesticide wastes (D012-D017) find TC organic wastes(D018-D043),
 and provides estimates of the quantities of these wn.stes requiring commercially available
 treatment.  Lastly, Section 3.4 presents the results'of the capacity analysis.

       Today's rule establishes treatment  standards fur all newly identified TC organic
 wastes that are managed in  units other ih.in: 1) waslcwater treatment systems which
 includ : surface impoundments and whose ultimate discharge is subject to the  Clean
 Water Act (CWA); 2) zero-dischargers who. before land disposal of the wastewater, treat
 the wastewater in a CWA equivalent system; or 3} Class I non-hazardous underground
 injection wells subject to the Safe Drinking Water Act (SOWA) Underground Injection
 Control (UIQ program. EPA is deferring regulattun of these TC wastes until the Phase
 III rulemaking, so that EPA may consistently consider these wastes with other wastes
 impacted by the D.C. Circuit Court decision issued September 25, 1992 (Chemical Waste
Management v. EPA, 976 F. 2d 2).  This court decision addressed the regulation of
 characteristically hazardous ignitable, corrosive,  and reactive wastes under the Third
Third Land Disposal Restrictions (LDRs) rule.  The court decision responded (o several
challenges to  the Third Third LDR Rule that were brought by various petitioners,12
including challenges to provisions allowing dilution ;is a treatment to remove some
   11 This court deosioa consolidated thirteen separate cases before ihc court. The coun grouped the petitioners into
several groups. The "NRDC petitioner*' »ere coropnvd of ihe )fii/:irdnus Waste Treatment Council. The
Emiranmenul Defeat Fund, the Sierra Out), and the Natural KCUUIICM Defenx Council.  The 'Industry petitioners*
were comprised of (be CScmical Manufacturers AUUIKKVI. The I ernluer Institute, Chemical Waste Management, the
American Petroleum Institute. RSR Corporation, me American Mining Congress, me American Iron and Steel Institute,
the Dow Chemkal Company, the American Paper I.iuituie. ihe Mammal Forest Products Association, the Specialty Steel
Industry of UK United States, and the Edison Elcctnc Institute. Other petitioner} included Ihe Edde Corporation,
Honetead Resource Development Company,Inc.. the Zinc Corporuimn of America, the Aluminum Association, Ihe
Secondary Lead Sachet], me Auociatioa of Battery Rrcyctcrs, the Nniunul Association of Metal Finishers, the Battery
Council tnternaliocal, the Lead Industries Association. Inc., rte Cadmium Council. El. du Pont de Nemours &
Company, Allied-Signal Corporation, the Institute of Mikcr* pf [ jrtluwei, 'Ihiafcol Corporation, and Oiin Corporation.
                                                                                                                 a » j
                                                                                                                 2~i
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                                            3-2

 hazardous characteristics13. The decision remanded ihc dilution provisions at 40 CFR
 268.1 for wastes managed in Oass I deep injection wells subject to the requirements of
 the Safe Drinking Water Act (SOWA), and at 40 CFR  268.3 for wastes managed in
 centralized wastewater treatment systems subject «> ihc Clean  Water Act (CWA).14
 Consequently, TC wastewaters and other liquid wastes 1) managed in surface impound*
 ments regulated under the Clean Water Act, 2) managed in CWA-equivalent systems15
 prior to ultimate land disposal, or 3) disposed of in Class I  underground injection wells
 regulated  under the Safe Drinking Water Act are not being addressed in this rulemaking;
 they will be addressed in the upcoming LDR rulemaking to allow the Agency sufficient
 time to address the regulatory overlap between KCKA, SDWA, and CWA.  Because
 EPA believes that most TC wastewaters will be managed in one of the three types of
 systems listed above, the analysis presented in this chapter considers only the required
 treatment capacity for TC nonwastewaters.

3.1    BACKGROUND

       Section 3001 of RCRA specifies the criteria fur identifying characteristics of
 hazardous wastes.  One such characteristic is the tnxicity of the waste.  The original test
 for toxicity was the Extraction Procedure (EP), a laboratory test that evaluated  the
 potential teachability of specific constituents from a w.-iste.  In  1980, EPA promulgated a
 set of regulatory levels for  14 constituents16 and the protocol for the EP test. The use
 of the EP test to determine whether the concentration of any of the  14 constituents in an
 extract of ihe waste exceeded the regulatory levels defined the criteria whereby a waste   .
 exhibited the hazardous waste characteristic of toxiciiy.  In the  Hazardous and Solid
 Waste Amendments of 1984 (HSWA), section 3001 was amended to direct the  EPA
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   0 In pan, UK NRDC petitioners asserted that (1) the rule's ikacirvatxm standard allowed impermissible dilution in
some cases, rather than treatment with specfic technologies; and (2) the rule allowed placemen! of untreated formerly
characteristic wastes into surface impoundments regulated under the (lean Water Act, or into Class [ non-hazardous •
underground injection «U§ regulated under the Safe Drinking V.jttr Act, thereby violating the intenl of RCRA.

   " The court deosioo vacated some parts of the Third Third rule and remanded others. Vacated rule are no longer
in effect (once the court's mandate issues), whereas remanded nilu rcrmun in force until EPA acts to replace them.
This distinction bat considerable significance witn respect to LDR treatment ctundards. II a proiously promulgated
treatment standard tor a waste is vacated, that waste is now effccioety prnhibiicd from land disposal because airy »aste
thai would IK land disposed would be land disposed without tenifli firvi hccn treated to the standard previously
established by EPA (assuming thai the »as:e is not being land disputed in a lurid disposal unit with an approved no-
migration petition). A remanded treatment staadard, on the otlxr ruoJ. remains in cdcct, and disposal of wastes treated
to the remanded treatment standard is leal until the standard is amended.

   " CWA-equivalcat treatment includes biological treatment fur nrjpnici. alltaline chlorinalkxi or ferrous sulfate
precipitation for cyanide, precipUation/scdmentaLon for metals, leductxin of hexavalcnt chromium, or other treatment
technology thai can be dernoaMrated to perform equally or greater irun ihcse technologies (see 53 Federal Register
29364. May 24. 1993).

   " These constituents were Ihe meu'j z^ftx (D004), banum (IXOI), c.idmium (D006), chromium (D007), lead
(D008), mercury (D009), selenium (D010) aad shTr (DO11).  Md me pcMicuJcs Endrin (DOi:), Lindane (DOB),
Melhorychlor (0014), Touphcne (D015X 14-0 (DO 16). and  l.H-11> (Silvex) (0017).
     '"U

     CD

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                                                      3-3
t
 Administrator to "examine the extraction procedure loxiciry characteristic... and make
 changes ... as are necessary to ensure that it accurately predicts the leaching potential of
 wastes" (RCRA section 3001 (g)). In addition, ihe Administrator was charged with the
 identification of "additional characteristics of hazardous waste, including measures or
 indicators of toricity".

       In response to HSWA, EPA proposed the Toxicity Characteristic (TC) rule on
 June 13, 1986, and promulgated the final TC rule on March  29, 1990 (55 FR 1 1798). The
 TC rule established the Toxicity Characteristic Leaching Procedure (TCLP) as a
 replacement for the HP test. In addition, the rule expanded the criteria whereby wastes
 exhibit the hazardous waste characteristic of toxicily by establishing regulatory levels for.
 25 new organic constituents (D018-D043). Generators of newly identified TC wastes
 were required to submit RCRA section 3010 notificntions to EPA, and facilities managing
 tr*ese wastes were required to submit Part A permit modifications or new permit
 applications to EPA by September 25,  1990  (or by Miirch 29, 1991  for small quantity
 generators).

       For the purposes of the LDRs, newly identified TC wastes have been divided into
 two categories.  The first category are the  newly identified TC organic wastes. This
 category consists of wastes that have been identified us hazardous because of the
 presence of one or more of the newly regulated organic constituents. The new waste
 codes and the corresponding organic constituents arc presented in Exhibit 3-1.    The
 second category, the newly identified pesticide wastes, is comprised of the TC pesticide
wastes that were determined not to be  hazardous when tested using the old EP test, but
 are now hazardous when tested using the new TCLP.  The constituents for which these
 wastes are regulated, and the appropriate codes arc presented in Exhibit 3-2.

       Nonwastewater forms of TC  organic wastes and all forms of TC pesticide wastes
 are subject to the universal treatment standards in today's rule. These universal treat-
 ment standards are based on existing treatment data, which  is based on some form of
 thermal destruction (typically incineration) as the ficsl Demonstrated Available
Technology (BOAT) for treating these  wastes.

       A regulation related to today's rule  is the fin;il listing determination for used oil
 (57 FR 21524, May 20, 1992).  Used oil may also exhibit ihe TC due to the presence of
benzene  and  other constituents.  The Agency has determined that it is unnecessary to list
 used oil that is being disposed as hazardous because the TC rule adequately defines
those used oils that should be regulated as hazardous wastes.  Therefore, under today's
                a There are 26 new wane codes and 25 new consii!ue.-,a tccmv itie regulatory level for loul ncsols (D026) a used
             if conccnuatioas for o-, m-, and p-cresol cannot be dciernuned wiwf.iirty.
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                3-4


              EXHIBIT 3-1


   NEWLY IDENTIFIED TC ORGANIC WASTES
 AND CORRESPONDING ORGANIC CONSTITUENTS
nl
III
D018 - Benzene
D019 - Carbon tetrachloride
D020 - Chtordane
D021 - Chlorobenzene
D022 - Chloroform
D023 - o-Cresol
D024 - m-Cresol
D025 - p-Cresol
D026 - Cresol
D027- 1,4-DichIorobenzene'
D028 - 1,2-Dichloroethane
D029 - 1,1 Dichloroethylene
D030 - 2,4-Dinitrotoluene
D031 • Hepiachlor and
Heptiichtor epoxidc
D032 • Hexachlorobenzene
D033 - Hexachloro-1,3-butadiene
D034 - Hexachloroelriane
D035 - Methyl ethyl ketone
D036 - Nitrobenzene
D037 - Pentachlorophenol
D038 - Pyridine
D039 - Tetrachloroethylene
D040 - Trichloroethylen?
D04I • 2,3.5'TrichIorophenol
D042 - 2,4,6-Trichlorophenol
D043 • Vinyl chloride
              EXHIBH 3-2


   NEWLY IDENTIFIED PESTICIDE WASTES
AND CORRESPONDING ORGANIC CONSTITUENTS
D012-Endrin
D013 - Ltndane
D014 • Methoxychlor
D015 - Toxaphene
DO! ft • 2.4-D
DO 17 - 2.4.5-TP (Silvex)
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 rule, used oil that is not recycled and that exhibits the TC would be subject to the land
 disposal restrictions.18

 3.2    DATA SOURCES

       This section discusses the major data sources used to perform the required
 capacity analysis for newly identified TC wastes. Section 3.2.1 discusses the 1992 Survey
 of Organic Toxicity Characteristic Wastes Managed in Land Disposal Units (TC Survey).
 This survey was the main source of data on the generation and management of newly
 identified organic TC wastes (D018-D043) used in this ;m:i lysis. Section 3.2.2 discusses
 some of the comments received in response to the Advanced Notice of Proposed Rule-
 making (56 FR 55160) regarding the newly identified TC wastes.  Section 3.2.3 discusses
 comments received in response to the  Phase II proposed rule.

 ~2.\  1992 Survey of Organic Toxicity Characteristic Wastes Managed in Land Disposal
       Units (TC Survey)

       In the spring of 1992, EPA conducted a census of 139 facilities that disposed of
 newly identified TC organic wastes in land disposal units ur underground injection wells.
 EPA identified the universe primarily based on those who had submitted RCRA permit
 modifications or received interim status for managing these wastes.  For each facility,
 EPA requested waste stream-specific data on newly identified TC organic wastes and
 information about on-site land disposal units and treatment and recovery systems.

      The purpose of the TC Survey was to obtain estimates of the quantities of newly
 identified organic TC wastes (D018-D043) that are currently being managed, and that
 would be managed, in land disposal units (i.e., landfills, Iqnd treatment units, surface
 impoundments, waste piles and underground injection wells) from 1991  to  1995.  These
 waste quantities will require alternative commercially available treatment capacity prior
 to land disposal upon promulgation of the LDRs for these wastes. The data reported in
 the TC Survey were 1991 data.  EPA used this baseline  data to project demand for
 alternative treatment from 1992 to 1995, taking into account such  factors as planned
 waste minimization activities, construction of on-site treatment capacity, and anticipated
 changes in waste management practices at individual facilities, as reported  by the
 respondents to the TC Survey. EPA also requested estimates on quantities of newly
 identified TC organic wastes that are not currently land disposed, yet would require
 alternative treatment prior to land disposal (e.g., tank clean out sludges that will be
 generated in the future from tanks that replace surface impoundments).  EPA used the
 results of the survey to support the required capacity analysis conducted for today's rule.
The TC Survey also collected data on hazardous soil and debris contaminated with TC
 organic wastes.  Appendix D contains a sample of the TC Survey questionnaire.
            " Used oil itoa a recycled is noi subject 10 ihe land dapsvii rx-K.Tcm.w (JO CFR »l.6(a) and {b)).
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                                       3-6
      3.2.1.1 Identification of Population

        This section describes the data sources EPA used to identify the facility
population for the TC Survey. It includes a brief description of the data sources and how
EPA used the information to determine the final list of facilities.
Survey:
      EPA used three primary data sources to identify the target population for the TC
            National Survey or Hazardous Waste Treatment, Storage, Disposal, and
            Recycling Facilities (TSDR Survey).  EPA mailed the TSDR Survey in the
            fall of 1987 to approximately 2,500 facilities (hat managed hazardous waste
            on site.  These facilities included all of the 2,400 RCRA-permitt?d or
            interim status treatment, disposal, or recycling facilities, plus about 100 of
            the 700  RCRA permitted storage facilities.  The TSDR Survey requested
            information on hazardous waste quantities and management practices for
            the calendar year 1986, as well as any projected changes in hazardous waste
            management capacity prior to 1992.

            Because the TSDR Survey reflects 1986 hazardous waste management
            practices, it does not directly provide information on facilities managing
            newly identified TC organic wastes; these wastes were not identified as
            hazardous until  1990. For identifying (he target population to receive the
            TC Survey, EPA used the TSDR Survey for information on the type of
            land disposal units at a facility.

            Hazardous Waste Data Management System (HWDMS).  HWDMS was
            developed in the early 1980's to track (he activities of the RCRA-regulated
            community. EPA regional offices entered data on facilities generating and
            managing hazardous waste into ten regional data bases.

            EPA used HWDMS to gather information on facilities operating land
            disposal units that had submitted applications to modify their RCRA
            permits, on the assumption that some of these modifications were to
            manage  TC organic wastes.

            Resource Conservation and Recovery Information System (RCRIS). As the
            RCRA program changed (particularly as a result of HSWA), greater
           'authority was increasingly being given to the states for administration of the
            RCRA program. Fitting the additional data requirements into  the existing
            HWDMS data base structure became increasingly difficult, and OSWER
            designed RCRIS as a replacement data base for HWDMS.  RCRIS con-
            tains information on hazardous waste handling facilities, including the
            facility name, location, mailing addrcvi. owner name and address, types of
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                                                     3-7
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             activity (generator, transporter, burner/blender), and the types of hazardous
             waste handled.  A facility that treats, stores, or disposes of hazardous waste,
             roust obtain a RCRA permit, which consists of two parts, referred to as
             Part A and Part B.  EPA enters all of the Part A information into RCRIS,
             as welt as the process codes and design capabilities for the hazardous waste
             treatment units  from Part B. If a facility is required to undertake correc-
             tive action activities, EPA enters into RCRIS information on these activities
             including the type of contamination, the remedial activities planned, and
             the instrument (permit or order) by which corrective action is required.

             For identifying the TC Survey population, RCRIS provided information on
             whether the owner or operator of a hazardous waste TSDR facility had
             submitted an application to modify Part A or Part B of their RCRA permit
             to manage newly identified TC organic wastes.

       EPA verified the information in the above data sources in several ways.  EPA's
Office of Solid Waste, Permits and State Programs Division, obtained from each EPA
region a list of facilities that had submitted Part  A applications or Part B modifications
for the generation or management of TC organic wastes.  Using this information, EPA
verified the data provided by the TSDR Survey,  HWDMS, and RCRIS, and also
identified an additional fifty potential survey participants.  EPA's Office of Water,  Under-
ground Injection Control (UIC) Branch, obtained, from each region, information on
facilities  that operated Class I injection wells and were believed to inject TC wastes.  The
Chemical Manufacturers Association also provided (to UIC Branch) information on
facilities  it believed to be injecting TC wastes. EPA also contacted the Regional Offices
to inquire about additional facilities. When EPA found inconsistencies in the data
sources, the Agency contacted the Regional Offices to verify the information obtained
regarding these facilities; when the Regional Offices did not  have the necessary informa-
tion, EPA contacted the State agencies.

       EPA assumed that commercial facilities would manage some of the newly
identified TC organic wastes after the LDRs became effective, as hazardous waste
generators chose not to treat the waste themselves.  Consequently, all commercial
landfills and surface impoundments were included as potential survey participants.

       As a result of these data base searches and telephone calls to regions and states
described above, EPA initially identified -100 facilities as potential survey participants.
EPA called each facility to verify that the facility was managing newly identified TC
organic wastes in land disposal units.  Based upon this screening, EPA  identified 139
facilities that manage newly identified organic TC wastes in land disposal units.
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       3.2.1.2 Population Not Included in the TC Surrey

       Because the TC Survey was sent only to those sites that land disposed TC organic
wastes, the TC Survey estimates the quantity of newly identified TC organic wastes being
land disposed that would require alternative commercially available treatment as a result
of the LDRs. Not all of the sources of newly identified TC organic waste generation
potentially requiring alternative commercial treatment, however, were captured by the
TC Survey.  The two most obvious sources of potential additional TC organic waste
generation are corrective action activities and Superfund site clean-ups.

       EPA did not capture all of the generation due to  corrective action activities
* ecause the data bases used do not in themselves give complete information on the
corrective action activities at a particular  facility. In the  HWDMS data base, the
permitting and enforcement data are stored in two separate pans of the  data base.
General information on corrective action  events are  stored with the permitting data.  The
RCRIS data base contains all the information from the Part A application and only
minimal information from Pan B.  Detailed technical information about the construction,
operation, maintenance, and closure of all the unite  handling hazardous waste at a
particular facility is not available from RCRIS. In addition, although corrective action
requirements would be included  in Part B of a facility's RCRA permit, most facilities, at
the time the permit is granted, would not be far into the corrective action process and
could not estimate the quantity of corrective action wastes that might be  subject to the
LDRs.  For example, it is  not unusual for facilities to begin corrective action procedures
several years after Part B of the  permit is approved.

       Another complicating factor is that when the  survey was conducted (1992), the •
Corrective Action program was relatively  new. Facility investigations and corrective
measure studies are still being conducted  today.  Therefore, it is relatively difficult to
estimate the quantity of waste affected  by corrective actions.

       How a corrective action is to be performed would also affect whether a particular
facility was included in the TC Survey.  Wastes to be treated in situ or left in place would
not trigger the LDRs; consequently, EPA did not request that these quantities be
reported in the TC Survey.

       In spite of these limitations, EPA believes that the TC Survey captured most of
the TC organic waste generation due to corrective action and requiring alternative
treatment due to the LDRs. EPA believes these wastes would be included in the
quantity of TC organic wastes reported as land disposed  by the commercial facilities.
The commercial facilities would be the  ultimate  receivers for most of these wastes,
because if the corrective action wastes are subject to the LDRs, generators of these
wastes would need to obtain a RCRA permit to treat these wastes on-site.  These
permitting requirements could discourage generators from treating their wastes on-site
unless their corrective action would span several years.
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                                        3-9

       Using the TC Survey, EPA collected data on waste generation resulting from the
 clean-up of Superfund sites only where wastes were removed from the site and sent off
 site for treatment or disposal.  For example, organic TC wastes from Superfund clean
 ups that are sent to commercial landfills would be accounted for in EPA's analysis of TC
 organic wastes land disposed at commercial landfills.

       3.2.1-3  Formal of the TC Survey Questionnaire

       The TC Survey questionnaire was divided into five sections: (I) General Facility
 Information; (II) Land Disposal Units; (HI) Newly-identified Organic TC Waste Streams
 Managed in Land Disposal Units; (IV) Treatment or Recovery Systems for  Managing
 Newly-identified Organic TC Wastes; and (V) Additional Information. A sample
 questionnaire  is  provided in Appendix D. Each of these sections is described below.

       Section I: General Facility Information. Section I requested information on the
 facility, including the name, EPA ID number, mailing address, location, and the name
 and phone number of the person to contact regarding responses to the survey. Section I
 also requested a simple block diagram of units managing newly identified organic TC
 wastes.

       Section II: Land Disposal Units. Section [I requested information on the land
 disposal units at  the facility that are used to treat, store, or dispose newly identified
 organic TC wastes.  Specifically, this section requested information on the type of land
 disposal unit (landfill, land treatment  unit, surface impoundment, underground injection
•well or waste pile), management practices (storage, treatment,/ or disposal), the commer-
 cial status (on-site, captive, or commercial), and the no-migration petition status of the
 waste piles, [and treatment units, and underground injection wells.  Information on the
 no-migration petition status of land disposal units was requested since the LDRs are not
 applicable to wastes managed in land disposal units with an approved no-migration
 petition.  (See Section 3.3.1 for  a more detailed discussion on the use of this information
 for analyzing the survey responses.)

       Section II also requested information an the closure plans for surface impound-
 ments along with the estimated  quantities of wastes to he removed at closure. This
 information was used to identify those facilities that planned  to switch to tanks rather
 than comply with the minimum  technological requirements for surface impoundments by
 the March 25,  1994, deadline (55 FR  11835. March 29, 1990).

      Section  IIT; Newlv-identificd Organic TC Wnste Streams Managed in Land
Disposal Units. This section requested information on organic TC waste streams that are
managed on site  in land disposal units.  Because the primary goal of the TC Survey is to
estimate the quantities of organic TC  wastes that will require alternative treatment due
to the LDRs, the survey focused on identifying the quantities of organic TC wastes being
managed in land  disposal units rather than the quantity of TC organic wastes generated.

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                                       3-10

 Consequently, this section did not request information on wastes being shipped off site
 for treatment, recycling, or disposal.  If the waste w;is shipped off site and managed in a
 land disposal unit, EPA identified this quantity from (he receiving facility rather than the
 generator.

       Section III is divided into three sub-sections. The first subsection (Pan A)
 requested a description of the waste stream, including the origin of the waste stream (i.e.,
 on-site or off-site); the EPA ID of the generator; the form of wasie stream received from
 off-site locations (e.g., drums); the EPA hazardous waste code; the waste stream's
 physical form and chemical composition, underlying hiiznrtlous constituents, and concen-
 trations; the type of generation (i.e., routine, sporadic, or remedial); and the quantity
 managed in on-site land disposal units.

       Pan B requested information on the type of waste management (storage, disposal,
 treatment, etc.), the .type of land disposal unit  managing the waste stream, and  the
 quantity of the waste stream managed in the land disposal unit.   Part C requested
 information on  planned waste minimization activities that could  potentially reduce or
 eliminate the TC waste stream, including the type  
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                                      3-11
       3.2.1.4  Administering the TC Surrey

       To assist facilities in responding to the questionnmrcs, six chemical engineers were
 each given responsibility for a unique subset of the 139 fiidlities to facilitate the collec-
 tion of information from the respondents. The cngirigcrs I'irM contacted the facilities to
 inform them that their facility had been identified :ts  m:in:iging newly identified TC
 wastes in land disposal units and that they would be receiving a questionnaire.  These
 same individuals made follow-up telephone calls to verily receipt of the questionnaire, to
 answer questions and to  provide assistance in completing I lie questionnaire.

       When the questionnaires were completed and  returned by the facilities, the
 engineers responsible for these facilities examined the questionnaires for. completeness
 and technical accuracy, verified and validated the infonnniion, and made follow-up
 tele; hone calls when necessary to clarify information.

       Of the f 39 questionnaires mailed, three facilities did not return the questionnaire,
 and 39 responded that they do not  manage newly identified TC wastes in land disposal
 units. Exhibit 3-3 presents an overview of the 97 facilities who confirmed that they
 manage newly identified organic TC wastes in land Ji%[)i«;il units.

                                   EXHIBIT 3-3

        TC SURVEY RESPONDENTS WHO REPORTED MANAGING NEWLY
          IDENTIFIED TC ORGANIC WASTES IN LAND DISPOSAL UNITS
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Respondent
Commercial
Non-Commercial
TOTAL
•Surface
Disposal
17
66
83
Underground
Injection
5
13
IS
Both
0
4
4
3.2.2  Comments on the AN'PRM

      In the October 24, 1991, ANPRM (56 FR 55K.O). 1IPA requested data on the
quantity of TC organic waste that would require alternative treatment.  E. I. Dupont de
Nemours & Company, Inc. (Dupont) and Lawrence l.ivcrmore National Laboratories
(LLNL) provided waste quantity estimates for some nf ilicii facilities.  Many of the
commenters (Chemical Manufacturers Association fC'MA), American Petroleum Institute
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                                                    3-12
|
 (API), Dupont, Utility Solid Waste Activity Group (USWAG), and American Indepen-
 dent Refiners Association (AIRA)), however, felt that the collection of TC data requires
 more time than the 45-day comment period allowed by the ANPRM, and consequently,
 were not able to submit complete data.

       Commenters discussed the various sources of data and the methods that may be
 used to estimate the quantities of wastes requiring alternative treatment due to the
 LDRs.  Dupont agreed with the Agency's acknowledgement that EPA's existing data
 bases do not provide a clear or comprehensive view of the quantity of TC organic wastes
 that will be generated and that may require alternative treatment due to the LDRs.
 Three commenters, CMA, Synthetic Organic Chemical Manufacturers Association
 (SOCMA), and LLNL encouraged EPA to conduct a comprehensive survey of the
 industry before proceeding with the LDR rulemalcing. SOCMA recommended that EPA
 develop and use information from facilities that have been complying with the new TCLP
 characteristic.

      Three commenters (API, CMA, and SOCMA) warned against using the Toxic
 Release Inventory (TRI) as a basis for quantity estimates because the TRI data reflect
 the quantity of the listed toxic chemical in a waste stream rather than the quantity of the
 whole waste stream which would be subject to alternative treatment.

      API believes that EPA should not use data on the quantity of TC wastes generat-
 ed prior to the implementation of the TC Rule  because this quantity does not reflect the
 substantial changes in the regulatory climate in light of the National Emission Standards
 for Hazardous Air Pollutants (NESHAP) rules for primary sludge (F037 and F038) and
benzene. API also noted that in the past EPA has estimated quantities using best-case
examples which are not representative of the petroleum refining industry. Consequently,
API  recommended that EPA incorporate data which considered all elements of a
 required capacity analysis.

      The ANPRM also requested comments and data on the development of treatment
standards and quantities of wastes requiring alternative commercial capacity due to the
LDRs for the newly identified TC pesticide wastes.  EPA did not receive any estimates
for additional D012-D017 wastes due to the use of TCLP rather than the EP.

3.2J  Capacity Data Obtained from the Comments to the Proposed Rule

      In the background document to the Phase II proposed rule, EPA presented  its
estimates of the quantities of TC nonwastewaters that would require alternative, commer-
cially-available treatment due to the LDRs for the time period 1991 to 1995.  EPA did
 not receive any comments to the Phase  II proposed rule that disputed  EPA's estimates of
the quantities of newly identified TC nonwastewatcrs that would require alternative
commercially-available  treatment due to the LDRs.  Consequently, EPA has not changed
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                                       3-13

 its estimates of the quantities of TC nonwastewaicrs i)i;it will require alternative
 treatment due to the LDRs.

       In the Phase II proposed rule, EPA solicited comnuTiis on the quantities of newly
 identified organic TC wastewaters and nonwasiewatcn ihfit were impacted by this rule
 (i.e., wastewaters and olher liquid wastes not 1) m.inayccl in surface impoundments
 regulated under the Clean Water Act, 2) managed in CWA-cquivalent systems prior to
 ultimate land disposal, or 3) disposed of in Gass I  urulcground injection wells regulated
 under the Safe Drinking Water Act). EPA did not receive siny comments on this issue;
 therefore, the Agency has concluded that sites managing organic TC wastewaters will not
 be impacted by this rule..

33   METHODOLOGY, ASSUMPTIONS, AND PRELIMINARY RESULTS

      In conducting the capacity analysis for Phase II wastes, EPA estimated the
amounts and characteristics of the wastes that will require iiliernative, commercially-
available treatment or recovery as a result of :he LDRs,  These estimaies were revised
between the proposed and final  rules as EPA evaluntcit ;idciiiional data. This section
presents only the estimates obtained for the final rule. The basic methodology did not
change between the two rulemaltings, and the analysis  (if required capacity for TC wastes
consisted of four tasks:

      '*     Collect information on waste generation, chemical/physical characteristics,
            type and concentration of constituents, waste (reliability, and current and
            potential management practices (treatment, Murage, disposal, ond recycling)
            of newly identified organic TC hazardous wiiMcs (DOI8-D043) that will be
            restricted from land disposal.  EPA collected  this information using the  '
             1992 Survey of Organic Toxicity CharacicriMic Wastes  Managed in Land
            Disposal Units (TC Survey), and the comments EPA received to the Phase
            II proposed rule.

      •     Quantify the demand for alternative jrciitiiicni or recycling (i.e., national
            demand for on-site and commercial capacity) that will be created  by the
            shift of untreated D018-D043 TC WJMCS  away from land disposal  at the
            expected promulgation date of the LDR  (August,  1994), and for the two
            year capacity variance "window" following ilic final rule  (August 1996).

      •      Collect information on the generation, ni;in;i£cmcnt, and demand for
            alternative treatment or recycling capacity for the newly identified D012-
            DO 17  pesticide wastes.

      •      Collect information on the generation, m;in<'i£cment, and demand  for
            alternative treatment capacity for used oil exhibiting the TC.
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                                       3-14
 Each of these tasks is discussed below. Section 3.3.1 describes how EPA analyzed and
 interpreted the TC questionnaire responses.  Section 3.3.2 presents EPA's estimates for
 the quantity of newly identified surface disposed TC nonwastewaters that will require
 alternative commercial treatment due  to the LDRs. Section 3.3.3 presents a discussion of
 the required capacity analysis for newly identified TC pesticide wastes that were not
 previously hazardous by the old'EP leaching procedure. Section 3.3.4 concludes with a
 discussion of EPA's estimates for the quantity nl uvd oil disposed in landfills.

 3-3.1   Analysis of the TC Survey

       Fur each questionnaire. EPA analyzed the waMe stream specific information and
 categorized the quantities by year of generation, organic TC waste code {i.e., D018-
 D043), the type of generation (routine, sporadic, tank clean out,  treatment surface
 impoundment closure, storage surface  impoundment closure, or disposal surface im-
 poundment closure), waste form (wastewater, noitwastewater, liquid nonwnstewater,
 mixed radioactive, soil or debris), whether the tircam  was mixed with any RCRA listed
wastes containing other organic constituents, and whether the waste stream would be
treated on-site or off-site when the LDRs become effective.  EPA estimated the quanti-
 ties of newly identified TC wastes that would be subject to the LDRs and that could also
be treated on-site using available or anticipated alternative treatment capacity.  These
quantities are  not part of EPA's estimate of waiict requiring alternative commercially
available treatment due to the LDRs.

       Routinely and Sporadically Generated Wanes.  EPA estimated the quantities of
newly identified organic TC wastes requiring alternative treatment as a result of the
 LDRs. For wastes identified in the questionnaire as routinely or sporadically generated,
the quantities reported for 1991 were used as the baseline quantities for estimating the
annual waste generation for 1992 through 1995.  EPA assumed that any waste reported
as routinely or sporadically generated an an annual basis (i.e., irregularly generated over
the course of a year) would continue to be generated at the same. rate through 1995,
 unless the questionnaire respondent specifically indicated otherwise. If a routinely
generated waste was not generated for an entire year, the amount of waste estimated for
that year was the  annual amount prorated for the portion of the  year that the waste was
being generated.  This steady state assumption ;ibo was used to project the annual
quantity of wastes, from 1992 to 199S,  associated with management of TC wastes in land-
based units and potentially requiring alternative commercial treatment due to the LDRs.

       One-Time  Generated Wastes.  Waste quantities reported  as one-time generations
(e.g., quantities resulting from a remediation activity) were only included in the estimates
of wastes requiring alternate treatment for the year «>r years in which these wastes were
generated or planned to be generated. Waste quantities generated from remedial actions
or corrective action activities were treated as one-time generations and reported only for
their year of generation.  EPA believes that theic unites wo>itd not be generated at a
constant rate over the time frame of the  analviiv
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                                         3-15

        No-Migration Petitions.  Restricted wastes may continue to be land disposed
 without treatment to the LDR treatment standards if a facility c:in demonstrate that
 hazardous constituents will not migrate from the disposal unit for ns long as the waste
 lemains hazardous. The demonstration must include the components specified in 40
 CFR 268.6(a) and meet the sampling, testing and analysis criteria required in 40 CFR
 268.6(b).  An approved no-migration petition allows wastes to be land disposed  at a
 specific site.  If wastes were managed in land disposal units hfivjng nn approved no-
 inigration petition for the TC constituents in the wastes, then these wastes would not be
 subject to the LDRs pursuant to RCRA section 3004(h)(4).  If i!ie no-migration petition
 for a land disposal unit was not yet approved at the time of the questionnaire, and no
 i.pproximate  date for approval was given, then EPA assumed iliat the land disposal unit
 would not have an approved no-migration petition for the entire period from 1991
 through 1995, and that the quantities of wastes handled in such units would be subject to
 the LDRs.

       Waste Forth  \flxtures.  Some survey respondents indicated more than one waste
 form (i.e., wastewater, nonwastewater, soil, dtbr:s) for an individual waste stream. Waste
 form mixtures were  apportioned based on the specific waste forms in the  mixture.
 Mixtures of soil and debris or nonwastewater and debris were ;i.ssumed to be 75 weight
 percent soil or nonwastewater, and 25 weight percent debris.1''  The quantities of all
 cither waste form mixtures were apportioned equally between the individual waste forms.
 (Question 27  of Section III indicated the waste forms of each W.MMC stream managed by
 the facility.)

       Organic TC Wastes Mixed with Organic F. K. U. or_P_ Wastes. Many individual
 waste streams were reported as bearing more than one RCRA waste code. EPA
 examined each mixture to determine whether the mixture would require alternative
 treatment. LDR treatment standards have existed for  all  F, K, U, and P wastes  since
 1990.   Treatment standards for these wastes are incineration, wet air oxidation, carbon
 adsorption, or air/steam stripping.  Consequently, treatment of these wastes by these
 methods would likely result in the waste no longer  exhibiting  T.I'A »nn representatives of companies
i -KU manage hazardous debris. See Background Dxumia f>* r^^-Li Jmkiu l<* Xnfy Land H'asies ami Hazardous
Iktris 10 Support 40 CFR 263 Land Disposal Ktsirictions (Fir-! R-'ei. Jcnc W2, Volume 1, p. 6-6.

   * With ihe ocepiion of say and debris contaminated w:!; I>..:J 1>,;rJ V.-MC-, .mJ mulu-source leactuie, which
r:«iw!(J variances in the Third Third Rgk until Nfay 1991
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                                       3-16

 longer characteristic, and EPA assumed that these wastes would not require additional
 treatment as a result of the LDRs for TC wastes.

       Mixtures of Organic TC Wastes.  If all the RCRA waste codes of the waste
 stream were newly-identified TC codes (i.e., D018-D043), the waste quantity was
 apponioned equally among the organic TC codes.

       Mixtures of Metal and Organic TC Wastes. If the waste stream carried organic
 and metal TC waste codes, the appropriate LOR treatment to meet the metal standards
 (e.g., stabilization) would not necessarily meet the TC LDR standards. Because the total
 mixture would likely require treatment for the organics, the total waste quantity was
 apportioned among the organic TC codes.

      Waste Minimization. Waste minimization was declared a national policy by
 RCRA section 2003(b).  In this analysis the reported quantities of generated waste were
 noi reduced to account for waste minimization that was begun on or before  1991,  as
 EPA assumed the quantities reported in 1991  reflected the effects of this waste
 minimization activity.  EPA did not adjust these  quantities unless additional waste
 minimization efforts were reported to be  planned for the future.  For waste minimization
 reported to  begin after 1991, EPA reduced the waste quantities by the amount of  the
 reductions the facilities expected as a result of waste minimization.  EPA used the effects
 of anticipated waste minimization activities to adjust estimates of wastes requiring
 treatment between 1992 and 1995.

      Wastes Managed in Landfills. Land Treatment  Units, or Waste Piles.  EPA
 assumed that the entire quantity of newly identified TC wastes reported as being
 managed in  landfills, land treatment units, or waste piles would require alternative
 treatment as a result of the LDRs, unless the facility reported having an approved no-
 migratiqn petition for management of the newly  identified TC wastes.

      Wastes Generated in Surface Impoundments.  Sites that were managing newly
 identified TC wastes in surface impoundments wece required to upgrade these impound-
 ments to meet the Minimum Technological-Requirements (MTRs) if the sites wished to
continue to manage hazardous wastes  in these impoundments.  If sites chose not to
 upgrade their impoundments, the sites were required to close the impoundments or
convert them into Subtitle D impoundments to manage non-hazardous wastes within four
years from the date of promulgation of the TC Rule (March 25, 1994).  EPA assumed
that any waste stream reported as being managed in a treatment impoundment that
complied with the MTRs would continue to be managed in the treatment impoundment
after March, 1994.

      Surface impoundment closures would likely generate  nonwastewater sludges, soil,
and debris.  EPA assumed that any sludge, debris, or soil, leaving" or removed from a
surface impoundment that managed newly identified TC wastes would exhibit the TC and
    ^?5
•-   -rs?
  0.0.5-1
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      71
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                                        3-17

 would require alternative treatment due to the LDRs.  The only exception to this rule
 occurred when the facility reported that the surface impoundment would be closed with
 the wastes in place.  Because no wastes were retrieved from the  unit, the wastes would
 not be subject to the LDRs.

       Wastes Managed in Tanks.  Most of those facilities that reported managing newly
 identified TC waste streams in surface impoundments that did not meet the MTRs, also
 reported that these waste streams would be managed in tanks on or before the effective
 date of the MTRs (March 25, 1994). Wastes managed in tanks would not be subject to
 the LDR treatment standards. However, nonwastewater sluJge (lank clean out wastes)
 would be generated and would likely require alternative treatment.  EPA assumed these
 wastes would exhibit the same organic TC as the wastes managed in tanks, and that these
 tank clean-out wastes would require alternative treatment due to the LDRs.

 3-3.2   Quantity of Surface Disposed Organic TC Wastes Requiring Alternative
       Treatment Due to the LDRs

       Exhibit 3-4 shows EPA's estimates for the quantities of newly identified TC wastes
 that will require alternative commercially available treatment  as a result of the LDRs.
 Exhibit 3-4 projects the estimated demand for alternative treatment through 1995.
 These estimates of future demand for alternative treatment were based on survey
 respondents' answers about anticipated waste generation activities, planned waste
 minimization efforts, planned construction of alternative, non land-based treatment
 systems, and actions taken because of other regulatory requirements (i.e., NESHAPs and
 the minimum technology requirements (MTRs)).

       N'omvastewater Sludges/Solids.  The survey results indicate a more or less steady
generation, through 1995, of nonwastewater sludges that wftuld require  alternative,
commercially available treatment as a result of the LDRs. Many facilities reported plans
to replace their surface impoundments with tanks.  Although  these tanks were expected
to be ready to meet the March, 1994, deadline, approximately half of the facilities that
would be replacing their surface impoundments with tanks could not estimate  the amount
of nonwastewater sludges they would be removing from their  tanks as a result of tank
clean-outs.  If a facility did not estimate their tank clean-out quantities,  EPA assumed
they generated none. Consequently, the results most likely underestimate the  actual
quantity of waste generation from tank clean outs.

      The preliminary analysis of the survey responses revealed  a number of trends in
the quantities of wastes requiring alternative treatment.  Virtually nil of the survey
respondents indicated they would be shipping their newly identified TC  waste quantities
off-site for treatment once  the LDRs become effective.  Only one facility reported having
alternative treatment capacity already in place to treat all of their newly identified TC
wastes currently managed in  land disposal units.  EPA believes that there are two reasons
for this limited development  of on-site capability. First, the treatment standards for the
o
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                                        3-13

                                     EXHIBIT 3-4

        SURFACE DISPOSED ORGANIC TC NONWASTEWATERS REQUIRING
             ALTERNATIVE COMMERCIALLY-AVAILABLE TREATMENT
                                                                                                        '   *":
Physical Form
Nonwastewaters-
Sludges/Solids
Nonwastewaters-
Liquid
Annual Totals
Surface Disposed Nonwastewatcrs (Tons)
1991
263,518
11,450
274,968
1992
305,213
11.447
316.660
1993
252,347
11.447
263,794
1994
220.262
. H.170
231.432
1995
256,200
1 1,447
267,647
                                                                                                            ia»

                                                                                                            3 rt 2.
                                                                                                            *°R
                                                                                                               o
newly identified TC wastes have not been promulgated.  In follow up conversations, a
number of facility contacts said they had several potential plans for constructing alterna-
tive treatment systems, and are waiting for the treatment standards  to be published
before they decide how to proceed. A second reason, is that the TC Survey was directed
to facilities that land disposed newly identified TC wastes.  EPA did not send the survey
to those facilities that generated and managed newly identified TC wastes in non land-
based units, or those facilities that generated newly identified TC waste, yet shipped it
off-site for treatment or disposal as a matter of routine practice."   No information was
collected on whether these facilities have plans for constructing on-site treatment systems
to manage their newly identified TC waste.  Because some generators may construct on-
site treatment rather than transfer the waste off-site, the  future demand for commercial
treatment may shift to on-site treatment.

      Exhibit 3-5 presents the estimates of newly identified surface-disposed TC
nonwastewater sludges/solids that will require alternative  commercially available treat-
ment in 1994, broken down by waste code.  For each  type of waste  tracked in the survey,
Exhibit 3-5 reports the quantities exhibiting  the TC for DO 18 and D019-D043.  The
apportionment assumptions discussed in Section 3.3.1  for wastes exhibiting the TC for
several waste codes were used to generate these results.  Of the 220,262 tons of newly
identified TC organic  nonwastewater sludges/solids anticipated to require alternative
treatment in 1994 as a result cf the LDRs, the TC Survey data indicated that 122,525
   :| For ihe group of generators of TC organic uauea irui routinely shipju'd ihcir wtnlci of! site for treatment or
disposal. EPA assumed that the required capacity for these fencrjiora WM eipiured in the TC Survey responses of
commercial facilities that land disposed TC wastes.
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                                                   3-19

                tons (56 percent) will consist of D018, and 97.737 Ions (44 percent) will consist of D019-
                D043.
/
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                                                EXHIBIT 3-5

                                    1994 ESTIMATED SURFACE DISPOSED
                            ORGANIC TC NONWASTEWATER SLUDGES REQUIRING
                           ALTERNATIVE COMMERCIALLY-AVAILABLE TREATMENT
c e S
Is"
H
       O
Waste
Code
D018
D019
D020 .
D021
D022
D023
D024
D025
D026
D027
D028
D029
D030
Quantity
(Tons)
120,000
8,700
6,300
8,500
8,400
3,900
520
310
1,500
1,200
11,000
3,800
510
TOTAL*
Waste
Code
D031
D032
D033
D034
D035
D036
D037
D038
D039
D040
D041
D042
D043
Quantity
(Tons)
200
3,300
450
410
4,200
260
600
3,600
6,900
6,600
110
120
16,000
220,000
                             'Note: Tout auy not 41103 due lo rounding.
                                                                                                                 n
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                                                                                                               a
                     Liquid Npnwastewaters.  Exhibit 3-4 also shows the projected demand for alterna-
                tive commercial treatment for surface-disposed liquid nonwastewaters. (Liquid nonwaste-

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                                         3-20

 waters are liquid wastes not meeting the definition of a wnstewater.  )  EPA anticipates
 a steady generation of liquid nonwastewaters requiring alternative commercially available
 treatment through 1995.  These 11,000 tons of liquid ntmwnstewaters tend to contain a
 high organic content, and were reported in the TC Survey us being managed in landfills.
 For the purposes  of the capacity analysis, these wastes were assigned to liquid combus-
 tion.

 333  Newly Identified TC Pesticide Wastes That Were  Not Previously Hazardous by the
       Old Extraction Procedure

       In response to the October 24, 1991 ANPRM. EPA did not receive any estimates
 for additional D012-D017 waste quantities or newly identified D012-D017 wastes due to
 the use of TCLP rather than the EP.  Because of the lack of comments to this issue,
 EPA continues to believe that the quantities of the newly-identified D012-D017 pesticide
 wastes due to the  use of the TCLP rather than the EP arc small, if any, and expects little
 or no additional demand for commercial treatment capacity us a result of the LDRs.

 3.3.4  Quantities  of Used Oil  Disposed in Landfills

       Several EPA programs  regulate used oil generators, transporters, collectors and
 recyclers. In addition, used oil that exhibits the TC may be subject to the LDR, if it is
 not recycled.23  In a previous analysis, EPA estimated thnt the majority of used oil
 (approximately 800  million gallons per year) is being recycled by burning for energy
 recovery and refining, and that a small portion of the total quantity of used oil generated
 each year (approximately 80 million gallons) is disposed.

       EPA extracted data from the 199! Biennial Reporting System and reviewed
 preliminary data from the State of New Jersey in order 10 estimate the quantities of used
oil that are managed in landfills.  Exhibit 3-6 shows the total quantities of waste types
 that may contain used oil and  indicate the quantities managed on-site and off-site and the
 quantities of these wastes reportedly landfilled on-site and off-site.  The quantity of
 landfilled wastes that may contain used oil is a small percentage of the total quantity of
 used oil generated and managed by other means  than disposal (i.e., treatment or
•Ml
   22 A wastewater a deBacd in 40 CFR 263.2 as a liquid wane having leu than I1* by weight total organic carbon
(TOC) and leu than 1% by weight total suspended solids (TSS). with The following exceptions: (1) FOOI, FOOI F003,
F004, and FOOS wasiewaten are solvent-water menu res that eiimain leu than If by weight TOC or less than 1% by
might total FOOI, FOB, FOOS, F004, and FOOS solvent consmucnts listed in S26H.41, Table CCWE; (2) KOI 1. KOI3, and
KOI4 wastewaten contain leu Ihao S% by Might TOC and tea than 1% by weight TSS, at generated; and (3) K103 and
KI04 wasiewaten contain less than 4% by Might TOC and leu ihun l"3> by weight TSS.

   a Used oil thai  is recycled and exhibits the TC is not subject 10 inc I.UKs. m accordance with §261.6{aX4).

   :* EPA, Haiardota Watte Management Syvim; Central lArM'icuruai anil I Ming of Hazardous tt'oiK; Hud Oil
(Final Rule),W CFR Part 361, May 1992.
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                                                        3-21

                  recycling). Overall, the BRS data show that approximately one percent of all reported
                  waste oil is landfiiJed.  For example in the "Oil Changes" category of the 1991 BRS,
                  approximately 1,400 tons was reported as landfilled. Furthermore, most of the wastes
                  from oil changes are reported as state codes (primarily from California and New Jersey)
                  and may not be subject to this rule.
                                                     EXHIBIT 3-6

                                              USED OIL'MANAGEMENT
srPi
    •••. H
  3   ™
  Ifff
      ft
.
Source/Form Code
Possibly Containing
Used Oil
Source Code A54
Oil Changes
Font Code B205
Oil-Water Emulsion
Mixture
Form Code B205
Waste Oil
Form Code B603
Oily Sludge
Total Used Oil*
Total All Wastes*
Quantity
Managed On
Site (Tons)
5.500
10,000.000
SS.OOO
470.000
1.600,000
-
Quantity
Managed Off
Site (Tons)
80,000
230.000
290,000
: 10,000
710,000
--
Quantity
Landfilicd
On Site (Tons)
30
0
30
2,900
2,900
530.000
Quantity
Landfilicd •
Off Site (Tons)
1.400
3.600
UOO
.17,000
43.000
2,000,000
                     • Totab nay 001 MUD due lo rouQdin{.
                     Source: 1991 Biennial Reporting S}i(cm
                       The State of New Jersey treats used oil as state hazardous waste and maintains
                 waste management data from State manifests. Preliminary data from New Jersey on
                 used oil management are shown in Exhibit 3-7 and indicate that approximately one
                 percent of all used oil generated in the state is landfilled.  This one percent includes both
                 used oil hazardous for TC organics and nonhazardous used oil (i.e., used oil that is
                 considered hazardous under New Jersey regulations, but not under federal regulations).

                       EPA's analysis of used oil has determined that the quantities of used oil that are
                 land disposed and are also hazardous for TC organics are  small  and that sufficient reuse-
                 as fuel, energy recovery, and or incineration  capacity exists. Thus, EPA has determined
                 that a capacity variance is not warranted for these wastes.
                                                                                                                              o
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                                                3-22

                                             EXHIBIT 3.7

                              NEW JERSEY'S USED OIL MANAGEMENT
Year
19SS
1989
1990
1991
1992
Quaniity of Used Oil Managed in
Landfills (Tons)
2,200
660
2,000
3.700
650
Total Quaniity of Used Oil
Generated (Tons)
120.000
160,000
210,000
170.000
130,000
             Source SuieofSt* Jtre«y Hazardous Waste Coatus™

         3.4   CAPACITY ANALYSIS FOR TOX1CITY CHARACTERISTIC WASTES

               To determine the need for national capacity variances, EPA estimated the
         quantities of TC waste requiring alternative commercially available treatment as a result
i, ~)     of the LDRs and the available capacity at commercial treatment facilities to treat these
 ~"      restricted wastes.  As discussed in this chapter. EPA expects little if any additional
         demand for treatment capacity for newly identified pesticide wastes (D012-D017).
         Exhibit 3-8 summarizes the quantities of organic TC minwastewaters that will require
         alternative, commercially available treatment capacity ;>s a result of today's rule and
         compares then to the commercial treatment capacity that is projected to be available in
         August 1994 for each alternative treatment  technology required for newly identified TC
         wastes, as discussed in  Chapter 2.  A comparison of the required and available capacity
         indicates that sufficient capacity exists to treat surface disposed nonwastewater sludges/-
         solids exhibiting the TC for D018-D043.  EPA also believes that sufficient commercial
         treatment capacity is currently available tb treat surface disposed organic TC
         nonwastewater liquids.  For the purposes of this analysis, EPA has assigned the entire
         quantity of organic TC liquid nonwastewaters to liquid combustion.

               As previously mentioned in this chapter, the TC Survey was the main  source of
         data on the quantities of newly identified TC wastes that will require alternative
         commercially available treatment due to the LDRs. Although the TC Survey question-
         naire asked respondents to provide data on the piociicc of other hazardous  constituents
         in their wastes, very few respondents provided this d;ii;i.  Consequently, EPA was not
         able to determine (1) whether the  newly identified TC wastes covered by today's rule
         also contained other hazardous constituents th.it would he subject to the Universal Treat-
         ment Standards; (2) the other hazardous constituents  in the wastes; and (3) how the
                                                                                                                     5-

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                                       3-23

                                    EXHIBIT 3-8

                        COMPARISON OF REQUIRED AND
                   COMMERCIALLY AVAII.AIU.K CAPACITY FOR
    SURFACE-DISPOSED NEWLY IDENTIFIED ORGANIC TC NONWASTEWATERS
Waste Type
D018-D043
Sludges/Solids
D018-D043
Liquid Nonwaste-
waters
D018-D043 Wastes
(Treatment
Residuals)
Treatment
Technology
Sludges/Solids
Combustion
Liquids
Combustion
Stabilization
Available Capacity
(Tons/year)
334,000
541,000
1.127,000
Required Capacity
(Tons/year)
253,000
1 1,000
NAa
     ' Stabilization ma* be required to m»t underNiD| hutrdcu* ncul crmuilurmi in organic TC *^»ica 1j
O
o
presence of these constituents would affect the waste's trcutubility or the choice of
technologies that could be used to treat these wastes. Therefore, EPA assumed that no
additional treatment of the TC wastes or their residuals wilt be required due to the
presence of organic underlying hazardous constituents. EPA believes that any metal
underlying hazardous constituents in these Basics can bu treated to universal treatment
standards using stabilization.  As shown in Exhibit 3-8, there is sufficient stabilization
capacity to treat these wastes, if necessary.
                                                                                                             J

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                                    CHAPTER 4
               CAPACITY ANALYSIS FOR NEWLY LISTED WASTES

       This chapter presents EPA's analysis of required alternative commercial treatment
 capacity for several newly listed wastes that are currently being land disposed.  This
 chapter specifically addresses coke by-product wastes (KS4I-K145, K147-K148) and
 chlorinated toluene wastes (K149-K151).  The purpose of the required capacity analysis is
 to estimate the quantity of these wastes requiring alternative commercial treatment
 capacity as a result of the LDRs.

 4.1  DATA SOURCES AND METHODOLOGY

       EPA used several data sources for conducting the required capacity analysis for
 these newly listed organic wastes. The Agency collected generation and management
 information on coke by-product wastes (K141-K145, K147-K14S) during 19S5 and 1987
 under the authority of section 3007 of RCRA. Additional capacity information on coke-
 by product wastes was obtained from the Regulatory Impact Analysis25 and the
 Economic Impact Analysis (ELY)26 for the listing of these wastes, along with comments
 submitted in response to the proposed rule for the identification and listing of coke, by-
 product wastes (56 FR 35758, July 26, 1991).  Generation and management information
 on chlorinated toluene wastes was collected by EPA during  1987 under the authority of
 section  3007 of RCRA.  Several companies involved in the data collection effort for both
 chlorinated toluene and  coke by-product wastes requested that their information be
 classified as Confidential Business Information.

      EPA's assessment of required alternative commercial capacity was based on an
 analysis of the most current generation and management of these wastes. To determine
 how each individual waste stream will  be affected by the final rule, EPA first considered
 whether a waste stream  is currently land-disposed. If a waste is not currently land-
 disposed or is land-disposed in a unit that has received a no-migration petition, or is
 managed in a RCRA-exempt unit, it would not be subject to the LDRs. For the
 required capacity analysis, EPA assumed that all land-disposed wastes will require
commercial alternative treatment.

      These land-disposed waste quantities were assigned the technology on which the
Agency based the final LDR treatment standards. EPA compared the required capacity
 for a particular treatment process to the available commercial capacity to determine
whether a capacity variance would be warranted.
   -Midwat Reward! Imtiluie, Background Doewrunt Supponinf tht Propoitd Lilting of Wasus From the Production,
Rtcovtry, end Refining of Cvk* By-ProJuett Produced From Cooi rtfort prepared tor EPA, 1991.

   ^DPRA Incorporated, Con and Economic tmfaa XiuAiit Of Luring Additional Wailti From iht Coke By-Pmduea
(Coking and Tar Riffling) Indian, nport prepared for EPA. !V».
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                                        4-2

 4.2    REQUIRED CAPACITY ANALYSIS FOR COKE BY-PRODUCT WASTES

       K141-K145 wastes are generated by the coking industry. Two types of plants exist
 within this industry: captive and merchant plants. Captive coke plants are operated by •
 major iron and steel companies and produce blast furnace coke that is generally used  on
 site or within the company at integrated iron and steel plants to produce steel.  Captive
 plants are owned by the iron and steelmaking firms.  Merchant plants are  smaller,
 independent plants that sell coke on a commercial basis. Foundries (hat use coke to
 melt iron prior to casting are the major consumers of coke produced by merchant plants.
 Between  1985 and 1989, the number of coking plants in operation declined from forty to
 thirty-four.27 Updated information provided by an industry trade organization indicates
 that there are currently thirty-two active plants.2* Twenty-two of the thirty-two plants
 are classified as captive and ten are considered merchant.  A list of active  plants is
 provided  in the Background Document for the final listing of these wastes.

       K147 and K148 wastes are generated by tar refining plants. Tar  refining plants
 purchase  coal tar from coking plants for use in production and use distillation processes
 that separate the various products (e.g., coal tar  pitch, creosote oil, naphthalene, solvent
 naphtha, and refined tar).  There are fourteen active tar refining facilities. Eleven of  the
 fourteen tar refining facilities generate K147 and KJ48 wastes.2'

       Coke by-product and tar refining wastes contain hazardous constituents such as
 benzene and polynuclear aromatic hydrocarbons.  The definition of coke by-product
 wastes are:
  •Q _ M,
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     71
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   K141      Process residues from the recover)' of coal tar, including but not limited to
             tar collecting sump residues from the production of coke from coal or the
             recovery of coke by-products produced from coal.  This listing does not
             include  K087, decanter tank tar Sludge from coking operations.

   K142      Tar storage tank residues from the production of coke from coal or the
             recovery of coke by-products produced from coal.

   K143      Process residues from the recovery of light oil, including but not limited to
             those generated in stills, decanters, and wash oil recovery units from the
             recovery of coke by-products produced from coal.
   "op. tit., DPRA Incorporated. 19)0.
          EPA, final Rutt: Idtroipftoion and LJsanf of /tii-rfotu U'aile; CERCLA Hazardous Subiianct
Dcsipwion; Reponotlt Quantity Adjusonz/u:  Coke Bi-Pmiuc-j U'astti. July 31, i992.
      "U
                                                                                                               LU

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o
            K144



            K145


            K147

            KI48
                                       4-3

             Wastcwater treatment sludges from light oil refining, including but not
             limited to intercepting or contamination sump sludges from the recovery of
             coke by-products produced from coal.

             Residues from naphthalene collection and recovery operations from the •
             recovery of coke by-products produced from coal.

             Tar storage tank residues from coal tar refining.

             Residues from coal tar distillation, including but not limited to still bottoms.

       The coke by-products listing was proposed on July 26, 1991 (56 FR 35758) and
 finalized on July 31, 1992. For all coke by-product anil tar  refining nonwastewaters, EPA
 is promulgating concentration standards (consistent with UTS) based on incineration
 performance data. For coke by-product wastewaters, EPA  is promulgating concentration
 standards based on the performance of industrial wasicwater systems.  The primary
 source of data on waste management practices was the EIA for the listing of these
 wastes.30 For the EIA, waste management practices were determined on a plant-
 specific basis for each waste stream. If a facility did not report a management practice
 for a specific waste, the Agency used best engineering judgement to determine the
 management practice. EPA believes that the quantities of coke by-product wastes land-
 disposed may be lower than those documented in the EIA for two reasons. First, the
 number of coking plants decreased between 1985 and  19S9. Second, commenters noted
 an increase in recycling of coke by-product wastes in response to the proposed rule for
 the listing of these wastes.'

      According to information submitted by coking plants in the 1985 RCRA 3007
questionnaires for the proposed listing, the  majority of coking plants used biological
treatment for wastewaters in RCRA-exempt tanks before discharging them to a POTW
or through a NPDES permitted outfall.  Tank bottoms may be removed from these units
periodically and potentially be subject to the LDRs. EPA solicited comments or
information  on tank bottoms that may require alternative treatment, but received no
responses. In 1985, six coking plants managed wastewaters  in surface  impoundments.31
Presently, all facilities in the coking industry have closed  their surface  impoundments and
lagoons.   Those facilities currently manage wastewaters generated from coking
operations in wastewater treatment plants that arc regulated under the Qean Water Act
and other EPA regulatory programs.
            "ibid.

            "ibid
            "op. til., DPRA Incorporated, 199O.
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                                        4-4

       Management practices and estimates for each newly-listed K141-K145
 nonwastcwater, obtained from 1987 data, are discussed below.33

       •     Only one facility land disposed process residues from coal tar recovery
             (K141) in an on-site landfill.  The remaining facilities recycled the wastes
             back to coke ovens or decanters.  The total amount of K141
             nonwastewaters managed in the on-site landfill was 49 tons.

       •     Seven facilities reported that  they land disposed tar storage lank residues
             from coking operations (K142) in on-site or off-site land-based units. The
             total amount of K142 nonwastewaters kind disposed was 2,750 tons. The
             remaining facilities recycled watte back to the coke oven.

       •     The majority of residues from light oil plant processing units (K143) were
             recycled to coke ovens, decanters or to tar sumps.  Several facilities used
             the wastes as fuel in boilers   Several facilities shipped waste off-site for
             reclamation.  One facility disposed 10 tons of K143 nonwastewaters in an
             off-site landfill.

       •     The majority of wastewater treatment sludges from light  oil refining (K144)
             were recycled to coke ovens, sumps or decanters.  Four facilities managed
             these wastes in landfills. The total amount of K144 nonwastewaters land-
             disposed during 1987 was 304 tons.

       •     Facilities that generated residues from (he production of naphthalene
 ,.            collection and recovery (K145) recycled the residues back to decanters,
             ovens, or to tar tanks. No K145 nonwastewaters were land-disposed in
             1987.

       According to information submitted by tar-refining plants in response to 1985
RCRA 3007 questionnaires for the listing of these wastes, all tar-refining plants managed
their waste waters in RCRA-exempt tanks or in surface impoundments already regulated
under Subtitle C because they managed K035 wastes (i.e., wastewater treatment sludges
generated from creosote production).  Presently, all facilities in the tar refining industry
have closed their surface impoundments and currenlly manage wastewaters generated
from tar refining operations in wastewater treatment plants.   These wastewater
treatment plants are regulated under the Clean  Water Act and other EPA regulatory
programs.
Q, O. r> <*
•  o " >-
   "ibid.

   "Source: EPA, ratal Rule:  Umttficeaon and Loom of H^aniaur Ua\u: C.tRCLA liazvioiu Substance
Designation; Rtponatlc Quantity Adjustment: Cola By-rnxlu?x lliii/rt, Jul> 31. 1992.
     O
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                                                                                                               un

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                                       4-5

       Management practices and estimates for K147 ;md K148 nonwastewaters,
 obtained from 1987 data, are discussed below.'1

       •     Tar storage tank residues (K147) were recycled hack to coke ovens,
             recycled back to the production using circulation pumps, or landfilled.  The
             total amount of K147 nonwastewaters land-disposed was 1,403 tons.

       •     Still bottoms and residues from coal tar distillation (K148) were recycled
             back to coke ovens and landfilled.  The tola! amount of K148
             nonwastewaters land-disposed was less than 1(K) tons.

       In total, EPA estimates that about 4.600 tons of coke by-product nonwastewaters
 (K14M45, KI47-148) will require alternative commercial treatment as a result of today's
 final rule.

 43    REQUIRED CAPACITY ANALYSIS FOR CHLORINATED TOLUENE WASTES
       (K149-K1S1)

       KI49-K15I wastes are generated from the manufacturing of chlorinated toluenes.
The chlorinated toluene industry is composed of four facilities thai manufacture ten
chemical products. Chlorinated toluenes are used as intermediates and raw materials for
manufacturing chemical products such as pesticides, herbicides,  Pharmaceuticals, and
solvents. The manufacture of chlorinated toluenes includes four .chemical processes:
(1) Thermal chain (alpha) chlorination. (2)  ultraviolet light-catalyzed chain chlorination,
(3) Lewis acid-catalyzed ring chlorination, and (4) catalyiic steam hydrolysis.  These
wastes typically contain various hazardous halogenaicd orgimic compounds.  The
definitions of newly listed chlorinated toluene wastes (K149-K1S1) are:

      K149  Distillation bottoms from the production  of alpha- (or methyl) chlorinated
             toluenes, ring-chlorinated toluenes, bcnzoyl chlorides, and compounds with
             mixtures of these functional'groups.  (This waste does not include still
             bottoms -from the distillation tJf benzyl chloride.)

      K150  Organic residuals, excluding spent carbon adsorbent, from the spent
             chlorine gas and hydrochloric  acid recovery processes associated with the
             production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated
             toluenes, benzoyl chlorides, and compounds with mixtures of these
             functional groups.

      K1S1  Wastewater treatment sludges, excluding  neutralization and biological
             sludges, generated during the treatment (if wastewaters from the production
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                                       4-6

             of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes,
             benzoyl chlorides, and compounds with mixtures of these functional groups.

       The chlorinated toluene wastes listing was  proposed on October  11, 1991 (56 FR
 51593) and finalized on September 30, 1992 (57 FR 44999). For chlorinated toluene
 nonwastewaters, EPA is promulgating concentration standards based on incineration
 performance data.  For chlorinated toluene waste-waters, EPA is promulgating
 concentration standards based on the performance of industrial wastewater systems.

       EPA collected generation and management information on wastes generated from
 the production of chlorinated toluenes (KI49-K151) under the authority of section 3007
 in RCRA and during site visits in 1983. Additional information was obtained from the
 Background Documents for the listing of these wastes.36 EPA identified no K149
 nonwastewaters, no K150 nonwastewaters, and less than 100 tons of K151
 nonwastewaters that are currently being land disposed.  EPA identified  no quantities, of
 chlorinated toluene wastewaters that would require alternative commercial treatment as a
 result of the LDRs.
o
4,4    CAPACITY ANALYSIS FOR OTHER NEWLY LISTED WASTES

       EPA estimates that 4,600 tons of coke-by-product nonwastewaters and less than
100 tons of chlorinated toluene nonwastewaters require off-site commercial capacity as a
result of this rule.  EPA has determined that these waste can be treated to meet LDR
standards by using combustion technologies.  EPA also as determined that there is
adequate sludge/solid combustion capacity to accommodate these wastes. Therefore, the
Agency is not granting a capacity variance for these other newly listed wastes.
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   **Thc Background Documcnls consist of an Enjjneenflj Analyst and ;i Health Assessment Document.  The
Engineering Analysts ta been classified as Conlidcmial Buuress Information (CGI) and a not available [o ine public.
The Healti) Assessment Document is not CBI anJ is avaits&ie in ihc UCHA Docket.
                                                                                                            Oi

                                                                                                            Oj

                                                                                                            —I

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                                    CHAPTER S
   CAPACITY ANALYSIS FOR SURFACE DISPOSED MIXED RADIOACTIVE WASTE
        This chapter presents EPA's estimates of the quantities of mixed RCRA/
  radioactive wastes (mixed wastes) contaminated with newly listed and identified wastes
  (D012-D017; D018-D043; K141-K145; and KZ47-KI51) that will require alternative
  commercial treatment as a result of the proposed Phase II LDRs. The chapter also
  discusses the available alternative treatment capacity for mixed wastes. The chapter is
  organized into four sections: Section 5.1 provides background on EPA's findings for
  previous analyses of required capacity concerning mixed wastes; Section 5.2 examines  the
  data sources used to conduct the analysis of required capacity for Phase II mixed waste;
  Section 5.3 presents the results of EPA's review of the available data sources on DOE
  and non-DOE mixed waste generation; Section 5.4 discusses the alternative treatment
  capacity that will be available to treat mixed wastes; and Section 5.5 discusses the
  national capacity variance for mixed wastes.

  5.1    BACKGROUND

        EPA has defined a mixed waste as any matrix containing a RCRA  hazardous
' waste and a radioactive waste subject to the Atomic Energy Act (53 FR 37045, 37046,
 September 23, 1988).  Regardless of the t>pe of radioactive constituents that  mixed
 wastes contain or the radiological classification of the wastes (i.e., high-level, low-level, or
 transuranic), thess wastes are currently subject to RCRA hazardous  waste regulations. In
 general, the treatment standards for mixed waste are the same treatment standards in
 effect for non-radioactive RCRA hazardous waste.

        Mixed wastes that contain spent solvents, dioxins, or California list wastes, First
 Third, Second Third, or Third Third scheduled wastes,  or Phase I scheduled wastes, are
 subject to the land disposal restrictions already promulgated for those hazardous wastes.
 In the Third Third rulemakmg,  EPA granted a two-year national capacity variance  for
 mixed waste contaminated with First Third, Second Third, and Third Third waste because
 of a lack of available alternative treatment capacity. This variance expired on May 8,
  1992.  In addition, EPA granted a generic,  one-year extension of the LDR effective date
 applicable to all facilities managing hazardous debris (with several exceptions), including
 mixed waste classified as debris. This extension was renewed  for one additional year and
 expired on May 8, 1994.

       In the Phase I nilemaking (57 FR 37194. August 18, 1992), EPA granted a two-
 year national capacity variance for mixed waste contaminated with Phase I waste because
 of insufficient alternative treatment capacity.  The wnsies  regulated under  the Phase I
 LDRs include F037, F038, K107, K108, K109. KI10. Kill, KI12, K117, K118, K123,
 KI24, K125, K126, K131, K132, K136, U328. U353,  and U359. This variance expired  on
 June 30, 1994.
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                                      5-2

       The Department of Energy (DOE) submitted a case-by-case (CBC) extension
 application for certain Third Third mixed waste generated and stored at 31 of its sites.
 DOE requested a one-year extension of the Third Third capacity variance for the mixed
 waste addressed in the application. EPA reviewed DOE's application and issued a
 proposed finding that DOE had made all hut one of the demonstrations required by 40
 CFR 268.5 for a case-by-case extension (57 FR 22024. May 6. 1992).  The remaining
 demonstration would have required DOE to enter into a binding contractual commitment
 to construct or otherwise provide alternative treatment, recovery, or disposal capacity for
 the wastes included in the application. As a result of the passage of the Federal
 Facilities Compliance Act and the belief expressed by Congress that DOE no longer
 needs a CBC ixtension, EPA suspended further processing of ihe CBC.

       The Federal Facilities Compliance Act (FFCA) was enacted into law (Public Law
 102-386) on October 6,  1992. FFCA amends the Solid Waste Disposal Act (1965) which
 was itself previously  amended by the Resource Conservation and Recovery Act (RCRA,
 1976) and the Hazardous and Solid Waste Amendments (HSWA, 1934).  Section 102 of
 the FFCA waives sovereign immunity for executive branch departments and agencies,
 and allows states to impose fines and penalties ;ig;iinst federal facilities for violations of  .
 RCRA. However, the FFCA delays the effective date of the waiver for mixed waste
 storage violations for three years to allow DOE time to prepare plans for the develop-
 ment of treatment capacities and technologies for facilities at which DOE generates or
 stores mixed waste.  Consequently, the FFCA dclnys the effective date of the LDRs until
 October, 1995 for surface disposed mixed waste.

 5.2     DATA SOURCES

      Section 5.2.1 discusses the types of comments that were  received in response to '
 the October 24, 1991 ANPRM.  Section 5.2.2 discusses comments received in response to
 the proposed rule. Sections 5.2.3 and 5.2.4 discuss the sources  of information on non-
 DOE and DOE mixed waste, respectively, that were used to prepare this analysis of
 required capacity.

 5.2.1  Comments on ANPRM

      The Advance  Notice of Proposed Rulcmaking (AN'PRM) for Phase H (56 FR
 55160,  October 24, 1991) requested data and comments on the generation and
 management of certain newly listed and identified wastes. Treatment standards for these
wastes  are included in today's final rule.  In response to Ihe ANPRM, eight commenters
discussed issues relating to the capacity available for the treatment of mixed waste. The
commenters addressed the following major issues:
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                                        50

       »     The tack of commercial treatment capacity for mixed waste streams;

       •     The need for a national capacity variance for mixed waste contaminated
             with the newly listed and identified waste; nnd

       •     The treatment of mixed waste to remove the hazardous portion, thus
             allowing the waste to be reclassified and managed as radioactive waste.

       Only two commenters provided quantitative information on mixed waste. The
 quantitative information consisted mostly of mixed waste generation and characterization
 data.  Where appropriate, EPA incorporated this information into the analysis of
 required capacity (information received from DOE in response to the ANPRM is
 discussed in Section 5.2.4).  Following its review  of the information, EPA believes that
 there are little or no additional quantities of mixed waste contaminated with D012
 through D017 wastes that are newly identified due to the change in the leaching
 procedure.  EPA received no data on mixed waste .streams containing coke by-products
 (K141-K145, K147-K148) or chlorinated toluenes (K149-K151), and the Agency believes
 that few, if any, mixed waste streams exist th;it arc contaminated with K141-K14S and
 K147-K151.

 5.2.2  Comments on Proposed Rule

       In response to the Phase II proposed rule* EPA received six comments concerning
 the proposal to grant a two-year national capacity variance for non-soil, non-debris TC
 organic mixed radioactive wastes.  All six commenters, including DOE, were in favor of
 the two-year capacity variance. Furthermore, none of the commenters identified any
 additional treatment capacity for the wastes.  EPA's responses to these comments may be
 found in the Response to Comments Received on  the Ncwty Listed Wastes and Hazardous
Soils Proposed Rule to Support 40 CFR 268 Land Disposal Restrictions: Capacity-Related
 Comments, which is part of the public docket for this rulemaking.

 5.2.3  Non-DOE Mixed Waste Data Sources

       For previous LDR rukmakings, EPA has received comments and data concerning
 the generation and treatment of mixed waste.  Based on these comments, EPA believes
 that DOE facilities generate the vast majority of mixed waste.  According to the
 Background Document for the Third Third LDRs, nun-DOE mixed waste is believed to
 account for less than one percent of all mixed waste gent-rated nationwide.37
   " EPA. Background Docvmerufor Hunt Third Wautt to \upfaa -tli( IK Part 268 Land Disposal Rumriioni. Final
Rult, Third Third H'osu Vctumt*. Charaacnstici. and Required ami AvutluHr '[rratimru Capacity, Volume III. Apptrutix
B, May 1990.
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                                        5-4

       In the process of conducting the analysis of required capacity that appears in
 Section S.3, EPA evaluated available data on the generation and treatment of non-DOE
 mixed waste contaminated with Phase  II wastes. The amount of comprehensive
 information available to EPA on these wastes is limited at this time. EPA and the
 Nuclear Regulatory Commission  (NRC), however, recently published the results of a
 survey designed to "collect information to  develop ;i national profile on the volumes,
 characteristics, and ireatability of commercially generated mixed wasie." The published
 results of the survey are known as the  "National Profile on Commercially Generated
 Low-Level Radioactive Mixed Waste" (National Profile).  The National Profile contains
 information on 'ow-ltvel mixed waste generated hy commercial (non-DOE) facilities in
 1990 and in storage at these facilities at the end i>l 1990.  Data from the National Profile
 are discussed further in Section 5.3.

 5.2.4  DOE Mixed Waste Data Sources

       In response to the ANPRM, DOE submitted comments that contained
 information on mixed waste streams affected  by the proposed rule. In developing its
 comments, DOE focused largely on collecting dala 
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                                        5-5
 stream data were often omitted because many Held sites did not consider TRU waste
 streams relevant to the data call.

       Section 105 (a) of FFCA required DOE to prepare a mixed waste inventory
 report within  ISO days of the enactment of FFCA (i.e., by April, 1993).  This Interim
 Mixed Waste  Inventory Report was prepared on time, and included a national inventory
 of all mixed wastes that are currently stored or will he generated over the next five years,
 and a national inventory of mixed waste treatment capacities and technologies.  This
 report is currently being updated; however, the Final Mixed Waste Inventory Report
 (MWIR) Data Case that will be used to develop the Final MWIR was made public in
 May, 1994.  This data base provides waste-stream specific information for each DOE site.
 Because the data in the MWIR Data Base are more recent and more comprehensive
 that those provided in DOE's comment to the ANPRM and the CBC. we  have relied on
 these data in conducting our  capacity analysis for mixed wastes, as discussed below.

 S3    RESULTS

      This  section presents the results of EPA's review of available data on DOE and
 non-DOE mixed waste streams contaminated  with newly identified hazardous wastes
 being restricted in today's rulemaking.  Mixed waste containing newly identified TC
 pesticide waste, coke by-products, or chlorinated toluenes arc not discussed, as EPA does
 not believe  that any of these waste currently are being generated.40 This section
 presents estimates of the quantities of TC organic mixed waste that will  be generated
 annually and that are expected to be in storage at both DOE and non-DOE sites.
 Section 5.3.1 discusses non-DOE generation and storage of mixed low-level waste and
 Section 5.3.2 addresses the  quantity of DOE mixed waste  generated annually and in
 storage.

 5-3.1  Non-DOE Generation and Storage of Mixed Low-level Waste

      Information collected on individual hazardous constituents present in the mixed
 waste streams identified in  the National Profile was generally incomplete.  As a result,
 estimating the quantities of non-DOE low-level mixed waste that contain newly identified1
 TC organic  wastes is not possible and is not specifically addressed in this subsection.
 However the results from the National  Profile do provide the most recent overall picture
 of non-DOE low-level mixed waste generation.

      Results from the National Profile presented in Exhibits 5-1 and 5-2 include
 estimates of the types and quantities of non-DOE low-level mixed wastes that were
 generated in 1990, as well as the total quantities of non-DOE low-level mixed wastes in
storage at the  end of 1990.  The National Profile identifies five non-DOE sectors that are
  »" According to the MWIR Daia Bait, none of these wastes j:c currently hemg generated or scored ai any DOE site.
In addition. EPA has not received any indication from o&et vurccv ihjl these wastes are hem j generated.
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                                        5-6
 sources of mixed waste:  academic, government, industrial, medical, and nuclear power
 plants. The quantities of mixed waste generated by each of these sectors in  1990 and the
 quantities of mixed waste stored by each of these sectors at the end of 1990  are listed
 and identified below in Exhibit 5-1.  The National  Profile's estimate of annual non-DOE
 low-level mixed waste generation is greater than the estimate developed in the Third
 Third capacity analysis.  EPA believes, however, thai ihe newer data are more complete
 and therefore more reliable.
» 5
                                    EXHIBIT 5.1

                      SOURCES OF NON-DOE MIXED WASTE
                       GENERATED OR IN STORAGE IN 1990
Sector
Academic
Government
Industrial
Medical
Nuclear Power Plants
TOTAL
1990 Generation
fmV)
X21
750
I.4M
564
J86
3.949
Amount Stored 
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                                               5-7

                                           EXHIBIT 5-2

                                TYPES OF NON-DOE MIXED WASTE
                               GENERATED OR IN STORAGE IN 1990
Wwte Tyft
Organic;
Liquid Scintillation Fluids (LSFi)"
Waste Oil'
Chlorinated Organics*
Fluorinaied Organic*
Chlorinated Fluorocarbons (CFCs)
Other Organics
Corrosive Liquids
LewlWulcs
Mercury Wtstes
Chromium Wtstcs
Cadmium W«ste*
Other H*zardous MMertaU
TOTAL
1990 CrnrnMlnn
(mjl

:.«37
W
71
1)
IB
275
HO
X2
13
28
0.25
.VII
3.949
Amount Stored «s of
12/31/90 (m*)

363
178
27
4
255
US
12
139
81
S3
745
141
2,116
              M*y contain Be»ly idtaufied TC orpaic wute.
             Source Oik Ridft Natioul Laboratory, ffaaaaal Ffofk en C<
                  NUREO/CR.5»3«. ORNL-4731. Deccralxr 1992.
•uOlf C.watd Lou-Lrvcl OalioocA* Matd Want,
         may contain newly regulated TC organic wastes.  Hie RODs did not identify any mixed
         debris.

         53.2  DOE-Generated Mixed Waste

               This section summarizes and evaluates DOE data on the quantities of newly
         identiGed TC organic DOE mixed waste generated annually and in storage. The data are
         organized by each of the newly identified TC organic waste codes. Although the
         proposed rule  addresses treatment standards for newly identified TC pesticide wastes
         (D012-D017) that were not previously hazardous by I he old EP test, none of the data
         identified any DOE mixed waste contaminated with newly identified pesticide wastes.
                                                        pill
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                                        5-8

 Consequently, EPA believes that very small quantities (if any) of mixed waste containing
 newly identified TC pesticide wastes exist at DOE facilities. Therefore, the analysis of
 Phase I! DOE mixed wastes presented in this chapter focuses on mixed wastes containing
 newly identified TC organic wastes.

       Exhibit 5-3 presents EPA's estimates of the quantities of newly identified TC
 organic high-level waste (HLW), mixed transuranic wastes (MTRU), and mixed low-level
 wastes (MLLW) that are generated annually and that currently are in  storage at all DOE
 sites.41 These estimates include only waste streams that carry at least one of the TC
 organic waste codes and do not carry any other RCRA listed waste codes. Many cf the
 waste streams in the data submitted by DOE contained more than one newly identified
 TC oiganic waste code; therefore, this exhibit shows the total quantity of all mixed
 organic TC wastes, as well as the quantity carrying each wnste code.  Please note that
 summing across waste codes may result in double-counting.

       Of the mixed  TC organic wastes currently in storage, approximately 45 percent are
 MTRU, 35 percent are MLLW and 20 percent are HLW.  The total quantity of waste
 currently in storage is 51,000 m .  In contrast, the projected annual generation rate for   .
 1994 is a total of 2,700 m3, with almost 50 percent HLW, 40 percent MLLW, and 10
 percent MTRU. As  can be seen in the exhibit, much of the mixed waste carries more
 than one TC organic waste code.

       Exhibit 5-4 breaks out both the current inventory and the annual generation of
 newly identified  mixed organic TC wastes by waste type.  As shown, the majority of the
 MTRU and MLLW is considered to be hazardous debris, while most of the HLW is
aqueous liquid or slurry. The quantity of hazardous soil in  storage or projected to be
generated in  1994 is very small. This can be attributed to the fact that the MWTR Data
Base generally does not include DOE environmental restoration wastes.  When these
wastes are generated they will increase the quantity of newly identified mixed wastes,
 particularly soil,  that  require treatment. Although these wastes are not included in the
Final  MWIR  Data Base, the IMWIR estimates that DOE will generate approximately
600,000 m  of mixed  environmental restoration wastes over the period from 1993 to
 1997.42
                  "The estimate of ihe quantity generated annually is based on KIC projections of the quantity that will (x generated in
                1994.

                  '• Some of these wastes may be organic TC mixed radioactnc soils.
                                                                                                                             "
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                           5-9



                       EXHIBIT 5-3



  QUANTITY OF DOE TC ORGANIC MIXED RADIOACTIVE WASTE

                GENERATED OR IN STORAGE
Waste Code
D018
D019
D020
D021
D022
DOB
DOZ4
D025
DQ26
D027
D028
D029
0030
DQ31
D032
D033
D034
DOSS
D036
D037
D038
D039
D040
D04I
D042
D043
ToUl
Current Inventory (nr*)
HLW
10,452
10,727
0
10,452
10.452
0
0
0
10.452
0
10.452
0
0
0
10.452
0
10.452
10.452
0
0
0
0
10.452
0
0
0
10.727
MTRU
5.044
5,043
0
20
17302
5.022
5,022
5,022
5.043
0
103%
11,882
0
0
20
0
20
20
0
0
0
0
22
0
0
0
23,001
MLLW
4,914
3.088
36
179
8,189
2,856
2,839
2,895
2.9SS
132
W77
11.090
79
91
131
46
111
914
0
0
0
0
879
35
.W
134
17.427
Annum! Generation (m3/jr)
1ILW
1,165
1.282
0
1.165
1.165
0
0
0
1.165
0
1,165
0
0
0
1.165
0
1,165
1.165
0
0
0
0
1.165
0
0
0
1.282
MTRU
378
378
0
7
378
371
371
37!
378
0
7
0
0
0
7
0
7
7
0
0
0
0
7
0
0
0
379
MLLW
732
496
3
409
590
44
44
44
450
28
502
109
3
2
409
3
409
649
0
0
0
0
529
3
3
0
1.061
Source Rui Mixed Wuu [AVCQKXJI Report Dan B*K. May. rw.

Note Rows do eoc MIB bediae ioae *wic iiraai carry m-*r ih-in «nc
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                                      5-10

                                  EXHIBIT S-4

           TYPES Ofr DOE TC ORGANIC MIXED RADIOACTIVE WASTE
                         GENERATED OR IN STORAGE
Waste Tjpc
Aqueous Liquids/Slurries
Organic Liquids
Solid Process Residues
Soils
Debris
Lab Packs
Compressed Gases
Other
Total*
Current Inventory (mj)
HLW
6.998
0
3.729
0
0
0
0
0
10,727
MTRU
0
2
4.461
0
18.339
0
0
200
23.001
M1J.W
206
1,276
I. Ml
24
1X054
7f>
2
242
17,427
Annual Generation Rate
(mV)
1ILW
h!7
0
465
0
0
0
0
0
1,282
MTRU
0
0
0
0
378
1
0
0
379
MLLW
16S
130
76
10
645
24
0
8
1.061
c "£
o y
KM g
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     Source Final Mind Waob* fovratwy Report Data Bise. Mty IVM,
     •TouJ nay not vtm 4we to rouadiag.
5.4   AVAILABLE CAPACITY FOR MIXED WASTE

5.4.1  Existing and Planned Non-DOE Capacity

      Currently, only five commercial facilities nationwide hold or are in the process of
obtaining RCRA permits to treat mixed RCRA/radkwietive waste, including waste
scintillation fluids. Two facilities, one each in Florida and Texas, currently  hold RCRA
Pan B Permits for the storage and processing of mixed waste. A third facility, located in
Tennessee, holds a Pan B Permit  for the storage of mixed waste and is operating a waste
fuel boiler under RCRA interim status.  A founh facility, Incited in Colorado, stores and
processes mixed wastes under interim status, and h;is submitted an application for a Pan
B Permit.  A second facility in Tennessee currently (rents low-level radioactive waste  and
has submitted an application for a Pan B Permit in order to process mixed RCRA/radio-
active waste. Only one facility, located in Utah, is permitted to land dispose mixed
RCRA/radioactive wastes. The types of waste disposed ;il this facility are constrained by
the facility's RCRA permit and NRC license. Other th;m these facilities, EPA is aware

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                                        5-11

 of no other non-DOE facilities that are permitted to irc;it, store, or dispose of mixed
 RCRA/radioactive wastes.

       According to the National Profile, a total of 41,000 nvVyr of capacity is available
 for treatment of commercially-generated low-level mixed wastes at the four facilities
 currently accepting these wastes.  This treatment capacity is spread over various technol-
 ogies, including bulking/vial shredding followed by storage (for liquid scintillation fluids,
 LSFs); incineration; stabilization; chemical oxidation and reduction; neutralization;
 cleaning, decontamination, and macroencapsulation (for lend materials); and solidifica-
 tion. Approximately 33,000 m3fyr of this treatment capacity is available for the bulking
 and storage of liquiu mixed wastes,  mainly LSFs. for radioactive decay prior to incinera-
 tion. However, EPA docs not consider storage for radioactive decay in determining
 available treatment capacity, and therefore these facilities dn not provide any treatment
 capacity for incinerable mixed wastes.  The remaining 8,000 m3/yr of capacity appears
 sufficient to manage the more than  6,000 mj of non-DOE mixed waste that required
 treatment in 1990 (the annual generation + amount in storage), but no capacity currently
 exists for 300 m3 of the total amount.43

 5.4.2 Existing and Planned DOE Capacity

      As part of its CBC extension application, DOE performed a comprehensive search
 for commercial facilities capable of treating mixed RCRA/radioactive waste. DOE
 concluded that only very limited commercial treatment capacity exists nationwide to treat
 its mixed RCRA/radioactive waste.  The existing capacity  that was identified was limited
 to the treatment of liquid scintillation fluids.

      As part of its comments on the ANPRM, DOE submitied a series of appendices
from its CBC application that provide information on 45 mixed RCRA/radioactive waste
 treatment facilities at  13 DOE sites.  Subsequently, DOE modified its CBC application by
withdrawing certain treatment facilities and adding another; reducing the total number of
 mixed waste treatment facilities to 36 (57 FR 22024, May 26, 1992).  EPA evaluated this
 information in order to determine the amount of available mixed waste treatment
capacity at DOE facilities.

      In addition, as part of the data call described earlier, DOE requested its field sites
to indicate whether their treatment units were capable (if accepting mixed RCRA/radio-
active wastes contaminated with newly identified TC organic wastes.  Not all of the DOE
field sites responded by the internal deadline;  DOE received responses concerning  only
 15 of the 45 existing or planned mixed RCRA/radioactive  waste  treatment units originally
included in the CBC.  All 15 of these units, however, were unable to accept mixed
RCRA/radioactive wastes contaminated with newly identified TC organic wastes. The
   "This 300 ions includes CFCs and lead shielding for »Ri-l there a nor .idri)uJic treatment capacity.
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                                       5-12

 units are either not technically capable of accepting TC organic*, or are not allowed to
 do so by their permit or permit application.  Some units face both of these difficulties.

       EPA'j review of the IMWIR indicates that  4,000 m* of treatment capacity are
 available annually for HLW at three DOE treatment systems. The available capacity
 appears sufficient to treat the estimated average annuaH generation.  However, the
 IMWIR indicates that the current national inventory of HLW is greater than 280,000 m3.
 This quantity dwarfs DOE's annual available treatment capacity for HLW. Consequently,
 DOE faces a treatment capacity shortfall for high-level mixed radioactive wastes.

       DOE is developing the Waste Isolation Pilot Project (WIPP) in New Mexico as a.
 permanent repository for DOE TRU wastes, including MTRU wastes. However, EPA
 has not yet authorized DOE to begin the placement of TRU wastes in the WIPP.  In
 addition, wastes received at the WIPP must meet DOE's WIPP Waste Acceptance
 Criteria (WIPP-WAC). DOE is still in the planning stages for facilities designed to
 prepare MTRU wastes for shipment to the WIPP. As a result, DOE faces a capacity
 shortfall for treatment of MTRU wastes.

       EPA's review of the IMWIR indicates that 300 rrrVyr of currently available
 capacity exists at four DOE treatment systems for  the treatment of alpha MLLW.
 (MLLW may be categorized as either alpha or non-alpha depending on the transuranic
 alpha content.)  However, the available capacity is greatly exceeded by the estimated
 quantity of alpha MLLW requiring treatment annually  over the next five years, 3,700 m3.
 Consequently, DOE faces a treatment capacity shortfall for non-soil, non-debris alpha
 MLLW.

      According to'IMWIR, 1,000,000 m3/yr of treatment capacity among 26 systems are
 currently available to treat non-alpha (i.e., less than 10 nCi/g transuranic alpha content)
 MLLW.  However, LMWIR states that most of DOE's  currently available treatment
 capacity for MLLW is represented by facilities limited to the treatment of wastewaters
 (defined by DOE as less than  1 percent total suspended solids (TSS)). While these
 treatment facilities provide excess capacity for MLLW wastewaters, they cannot process
wastes with high TSS and are not readily adaptable for other waste forms.  Thus,
 although the quantity of MLLW treatment capacity is greater than the total quantity of
 mixed wastes, DOE faces a treatment capacity shortfall for minwastewater MLLW, and
 thus non-alpha MLLW.

      The  IMWtR indicates that no available treatment capacity exists at DOE facilities
for mixed radioactive soils. In addition, EPA's review of IMWIR data indicates that 16
m fyr of currently available capacity exists at  one DOE facility for the treatment of high-
level mixed radioactive debris, an amount that exceeds  the estimated annual generation.
As noted above, EPA has not  authorized DOE to begin placement of MTRU wastes into
the WIPP.  As a result, DOE faces a treatment capacity shortfall for mixed transuranic
debris. Finally, review of IMWIR reveals that less  than 2 m3/yr of treatment capacity is
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         available that can accept mixed low-level debris. Thus, DOE faces a treatment capacity
         shortfall for both alpha and non-alpha mixed law-level debris.

                While DOE has provided its best available data on mixed waste generation,
         uncertainty remains about mixed waste generation at DOE (and non-DOE) facilities.
         For example, as discussed above, the MW1R data generally did not include DOE
         environmental  restoration wastes which, when generated, will increase the quantity of
         newly identified mixed wastes that require treatment. The IMWIR estimates that DOE
         will generate 600,000 m3 of mixed environmental restoration wastes (primarily MLLW)
         over the period from 1993 to 1997.  Although the IMWIR notes that the estimates of
         DOE environmental restoration wastes arc preliminary, any quantity of this magnitude
         will place additional strains on DOE's limited available mixed waste treatment capacity.
         In addition, although uncertainty exists as the total quantities of TC organic mixed wastes
         generated at DOE and non-DOE facilities that are affected by today's rule, EPA believes
         that insufficient treatment capacity exists for these wastes at both DOE and commercial
         sites.

         5.5   NATIONAL CAPACITY VARIANCE FOR MIXED RCRA/RADIOACTIYE
               WASTES

               Based on the analysis presented above, EPA believes that DOE generates a large
         majority oC mixed RCRA/radioactive wastes affected by this rulemaking and previous
.' ~}     LDR rulemakings, and that major treatment capacity shortfalls currently exist for
^•^     previously regulated mixed RCRA/radioactK-c wastes generated at both DOE and non-
         DOE facilities.  As a result, EPA has determined that there is currently no BOAT or
         equivalent available treatment capacity for any newly listed mixed RCRA/radioactive
         wastes at DOE or non-DOE facilities.  Because a treatment capacity shortfall was
         identified for every mixed RCRA/radioactive waste treatability group, EPA is today
         granting a two-year national capacity variance for all mixed RCRA/radioactive wastes
         contaminated with newly listed and identified wastes  for which treatment standards are
         included in this rulemaking.
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                                   CHAPTER 6
                   HAZARDOUS SOIL CONTAMINATED WITH
                   NEWLY LISTED AND IDENTIFIED WASTES
       This capacity analysis focuses on hazardous soil contaminated with wastes whose  ••
 treatment standards are promulgated by the Phase I! LDRs. The hazardous soil covered
 by this rule includes soi! contaminated with D018-D043 organic TC wastes, and soils
 contaminated with coke-by product wastes and chlorinated toluene wastes.  This chapter
 first discusses the estimated quantity of TC soils that would require off-site treatment,
 approximately 70,000 to 120,000 tons.  The next three sections describe the methodology
 and information used to determine the quantity of soil requiring alternative commercial
 treatment from surface impoundment closures, routine and sporadic activities, and CBI
 facilities, respectively.  The final section summarizes the results of the capacity analysis
 for Phase II hazardous soils.

      To estimate the total quantity of land-disposed  TC soil, EPA used several data
 sources:

      •      Responses to the Advance Notice to the Proposed Rule'making (ANPRM)
             for the newly identified wastes (56 FR 55160, October 24, 1991);

      •     The newly developed TC data set discussed earlier in Chapter 3;

      •      Information provided during a series of roundtable meetings held by
             the Agency in May and June of  1991 with representatives of
            companies involved in the management and disposal of hazardous
            soil; and

      *     Telephone contacts with  individual generators.

 S.I   TC SOILS REQUIRING OFF-SITE TREATMENT

      When the Phase II LDRs were  proposed, the Agency estimated that
approximately 233,000 tons per year of TC soils would require off-site commercial
i reatment and the majority of these TC soils would be generated from  surface
impoundment closures. Based on new data received from owners/operators concerning
: urface impoundment closure practices, the Agency misestimates that the annual
quantities of TC soil that is land disposed and  subject  to the LDRs ranges from 70,000 to
 :20,000 tons.  Because TC soil generation from surface impoundment closures  is
somewhat discretionary, decisions by owners/operators of facilities concerning closure
methods resulted in significant changes in the generation rates previously estimated in the
TC Survey.
      The Agency confirmed generation and land disposal rates with those facilities that
the Agency expected to generate TC soils from surface impoundment closures in 1993,
1994, and 1995. Nearly all of the owners/operators revised their estimates for TC soil
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                                      •6-2
 generation downward.  Most owners/operators revised their closure practices to minimize
 or eliminate TC soil generation.  Some facilities closed impoundments prior to today's
 rulemaking and other facilities are closing their impoundments as landfills. In closing as
 a landfill, a facility closes the impoundment with the waste in place. The facility
 owners/operators remove all free liquid, stabilize the sludges, cap the impoundment, and
 establish a ground water monitoring system. Therefore, for these facilities, no alternative
 commercial treatment capacity would be necessary for TC soils.  The Agency also
 reviewed the TC Survey and public information on specific facilities to assess the TC soil
 generation rate from routine and sporadic activities th.it might require off-site disposal.

 6.2    METHODOLOGY USED TO ESTIMATE TC SOILS GENERATED BY
       SURFACE IMPOUNDMENT CLOSURES  REQUIRING  OFF-SITE
       TREATMENT

       Promulgation of the TC rule created a series of deadlines for owners and
 operators of surface impoundments managing waste that is newly identified as hazardous.
 Surface impoundment closures create the greatest  concern because of the large quantities
 of TC soils that may need off-site treatment. On Ihe  other hand, retrofitting surface
 impoundments to meet the MTRs should not affect the capacity analysis because any off-
 site disposal of soils occurred by the end of March 1994.  Alternatively, owners can close
 their surface impoundments as landfills.  In closing as a landfill, (he facility closes the
 impoundment with the waste in place.  The facility owners or operators will remove all
 free liquid, stabilize the sludges,  cap the impoundment, and establish a ground water
 monitoring system. Similarly, the conversion of surface impoundments to Subtitle D units
 should not present capacity difficulties because little TC soils will be generated during
 conversion activities.

    '   Because of the possibility of extensions to the MTR requirement deadlines,
 uncertainty existed regarding the following issues:.

       •      The number of owners or operators  who will seek extensions;
       •      Whether EPA or authorized states will grant extensions;
       »      Definition of criteria for obtaining an extension;
       *      Time allowed for on-site TC soil management (i.e., when must the material
             be shipped off-site); and
       •      The number of surface impoundments that will close as landfills.

 6.2.1   Resolving Capacity Issues

       In order to resolve the issues of capacity and the potential impacts of deadline
extensions, EPA reviewed the TC Survey results :md contacted generators of TC soils
 requiring off-site treatment in 1993 and 1994. In 1993, about 28  facilities without LDR
treatment units were projected to transfer TC soils off-site because of surface
impoundment closures.  However, EPA's review of the quantity of TC soils actually
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                                        6-3

 generated in 1993 by some of ihese facilities appears to he over 115,000 tons lower than
 expected (see Exhibit 6-1).  EPA confirmed wfth the generators whether closures took
 place, the reasons for discrepancies in projected and actual generation rates, and the
 expected timing of future TC soil removal (e.g., prior to mid-August 1994).

       Based on EPA's discussions with facilities, a number of delays occurred that
 prevented the closure of many surface impoundments scheduled lo close in 1993.
 Consequently, the actual generation rates for 1993 were much lower than originally
 estimated. The actual closure of these remaining impoundments could impact the
 demand for alternative treatment due to the LDRs. If the TC soils expected to have
 been generated by surface impoundment closure in 1993 is deferred until after the
 promulgation of the  Phase II LDRs, these additional quantities may affect the national
 capacity for LDR treatment.

       For some of the facilities originally scheduled to generate TC soils in  1993, the
 delay should not affect LDR treatment capacity.  Two of the facilities, BASF Corp. and
 BP Oil - Alliance, do not expect  to generate  TC soils because they plan to close their
 surface impoundments as landfills in 1994. In addition, while Phillips - Sweeney expects
 to generate almost 32,000 tons of TC soils, it plans in complete closure prior to the
 expected LDR promulgation date of mid-August.  No LDR treatment capacity will be
 necessary for these TC soils.

       However, for  the other two facilities, Fina Oil and Total Petroleum, some
 uncertainty exists concerning the ability of these facilities to ship al! of their TC soils off-
 site prior to the effective date of the LDRs; their combined estimates for TC soils are
 approximately 5,400  tons. These facilities would not confirm whether they might seek
 deadline extensions.  Even if these facilities generate all their TC soils after mid-August,
 the impact on LDR treatment capacity will be minimal.  In addition, the 5,400 ton TC
 soil estimate may be  loo high because most of the wastes disposed in the surface
 impoundment were F037-F038.  These surface impoundment may never have managed
 wastes identified as TC by the TCLP, but soils under the liners may fail TC because of
 the accumulation of benzene over the years.  On the other hand, the possibility exists
 that little or no TC soil will be found during closure. Total Petroleum is currently
 conducting tests on its surface impoundment  soils to determine if the soils are considered
 TC wastes.

       The TC Survey also predicted generation of TC soils in 1994  and 1995 and follow-
 up telephone conversations with facilities updated expected generation rates (see Exhibit
 6-2).  Based on these estimates, approximately 25,000 tons of TC soils from surface
 impoundments will be land-disposed off-site in IV94. However, according to the facilities,
 all of this TC soil should have undergone final disposal prior to the mid-August deadline
 and will not require LDR treatment capacity. Of the other facilities contacted, one
 facility plans to close as landfills and bioremediate  its surface  impoundments without
generating TC soils.  The last facility, Lyondell Petroleum - Houston, does not expect to
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 generate any TC soils thai wit] require off-site treatment. No facility contacted
 anticipated seeking an extension to the MTR requirement deadlines.

       AM the owners or operators of surface impoundments that originally predicted TC
 soil generation in 1995 changed their estimate to indicate (hat no TC soil would be
 generated after 1994 (see Exhibit 6-2). Of those facilities thai originally predicted TC
 soil generation in 1993, only Fina Oil mentioned that a surface impoundment would be
 closed in 199S. Fina Oil stated that an aeration impoundment would be closed but could
 not estimate TC soil generation rates.

 63    TC SOIL GENERATION FROM ROUTINE AND SPORADIC ACTIVITIES

       The Agency also assessed the TC soil generation rate from routine and sporadic
 activities that might require off-site disposal.  For this analysis, the Agency assumed that
 routine activities, and the quantity of soil generated, should  be considered constant over
 time when analyzing the generator population as a whole.  However, for sporadic
 activities (e.g., surface impoundment closures), which by their nature occur infrequently,
 the year in which they occur is critically important in determining the required capacity
 for soil following the effective date of the Phase II  rule.

       To perform the analysis, EPA used information from the TC Surveys, phone logs,
and summaries (since the surveys provided data only through 1992, EPA derived 1993
TC data using the phone logs).  EPA reviewed the surveys  first, and then used the
phone logs and summaries to verify the results derived from the surveys.  EPA used the
following methodology to complete the analysis:

       •      EPA reviewed each survey to determine if soil was a waste
             component and, if so, whether soil was  the physical form of waste in
             the waste stream, the quantity of TC  soil in the waste stream, and
             the disposal method of the TC soil.

       •      Once EPA determined that TC soil existed at  a particular facility,
             EPA entered the following information into a  database:  EPA
             identification number, facility name, type of waste generation
             (routine, sporadic, remedial), origin of waste (on or off site),
             quantity of TC soil, quantity of mixtures contaminated with TC soil,
             and comments.

       *      EPA resolved conflicting responses as best as possible, given
             information available, and explained how it did so (if applicable) in
             the comment section of the data bnse.

       •      When the TC soil was reported  to be combined with debris, and no
             percentage of soil was provided. EPA assumed a 50/50 percentage
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                                        6-7
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             of soil and debris.  When a survey report provided a range of soil
             for a particular waste stream. EPA used ihe mid-point of the range
             to calculate the amount of soil in the waste Mrcam. Once it selected
             a mid-point, EPA created a second d:\tn base  to indicate the  new
             TC soil quantities.

       •     When survey forms were incomplete but some form of hazardous
             waste generation reports44 were provided, EPA converted monthly
             volumes to annual volumes.  EPA also used these reports to
             determine the type of waste generated and the origin of the waste.

       •     Where surveys reported soil quantity as pounds or cubic yards, EPA
             used conversion factors of 2,000 pounds/ton, or 1.2 tons/cubic yard.

       •     In the final phase of the analysis, on a ffidlity-by-facility basis, EPA
             compared the new TC  soil and soil/debris mixture quantities with the
             phone logs and summaries in order to identify any errors. EPA also
             compared the quantities to quantities extracted from the TC Survey
             data base described in Chapter 3.  EPA corrected inconsistencies or
             explained them by reviewing the data sources  and by using
             professional judgment.

       For the lower bound estimate (70,000 tons), as mentioned above, the Agency used
the 50-50 ratio of soil and debris in mixtures characterized as soil and debris.  Using this
assumption, EPA estimates that  approximately 70,000 tons cf TC soils generated by
routine and sporadic activities will require additional treatment annually. In addition, for
this lower bound estimate, the Agency assumed that all facilities were able  to manage the
TCsoils generated from surface impoundment closures prior to the effective date of
today's rule.  Therefore, for the lower bound estimate, no TC soils from surface
impoundment closures are expected to require additional treatment capacity.  Based on
these assumptions, the Agency calculates that the lower bound  estimate is 70,000 tons of
TC soils per year.

       For the upper bound estimate, the Agency assigned the  entire quantity of mixtures
of soil and debris reported in the TC Survey as TC soils. As a  result, the TC soil
generation rate for routine and sporadic activities increased  by  about 20,000 tons to
approximately 90,000 tons of TC soils per year.

       To verify the accuracy of  the upper bound estimate, the Agency contacted
individual facilities to determine  actual TC soil generation rates.  Based on  these
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   " To reduce the burden on chc facilities required to compteie ihc 1C Survey. liPA allowed respondents 10 submit
hazardous waste generation rcpora prepared for other purpwci anJ rnnuinmg the same information as required by the
survey.
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                                       6-8
 contacts, the TC data base overestimated TC soil generation from routine and sporadic
 activities by approximately 8,000 tons.  Many facilities Mined thai actual generation rates
 were lower or thai the estimate included one-time wastes from surface impoundment
 closures that already occurred. Therefore, the  Agency revised the upper bound estimates
 for TC soil generation rates for routine and sporadic activities at ihese facilities to
 approximately 82,000 tons per year.

       After adding the 5,300 tons of TC soils generated by surface impoundment
 closures, the estimated upper bound quantity of TC soil requiring additional treatment is
 approximately 90,000 tons per year.

 6A    TC SOIL GENERATION AND  LAND DISPOSAL FROM FACILITIES
       SUBMITTING CONFIDENTIAL BUSINESS INFORMATION

       The Agency conducted a similar review of facilities that submitted confidential
 business information (CBI) concerning  TC soil generation rales.  In developing the lower
 bound estimate for TC soil generation,  EPA assumed no generation from the CBI
 facilities. In establishing the upper bound, EPA assumed that 100 percent of the
 mixtures were TC soils. These facilities were estimated to generate an additional 53,000
 tons of TC soils.

       EPA contacted some of the CBI facilities to determine actual soil generation
 rates.  Based on these contacts, the TC data base overestimated TC soil generation from
 routine and sporadic activities by approximately 23,000 tons.  As with the non-CBI
 facilities, many CBI facilities stated that actual generation rates were lower or that the
 estimate included one-time wastes  from surface impoundment closures  that already
 occurred. Therefore, the revised estimate for TC soil generation for routine and sporadic
 activities from CBI facilities is approximately 30,000 tons per year.

 63    CAPACITY ANALYSIS FOR HAZARDOUS SOIL

       Due to reduced generation of TC soils from surface impoundment closures in
 1994 and 1995, and overestimates of TC soil generation rates from routine and sporadic
 activities, the Agency estimates that between 70,000 and 120,000 tons per year of TC
 soils will require off-site commercial treatment.  EPA considers the lower bound estimate
 to be more probable  than the  upper bound estimate of 120,000 tons. Nevertheless, for
 decision-making purposes, the Agency used the  more conservative, upper bound estimate
 of 120,000 tons of TC soils that will require off-site commercial treatment. EPA does not
 believe that there are significant quantities of soil contaminated with the other newly
 listed wastes covered  in this rule that will require off-site commercial treatment capacity.

       EPA believes the TC soils can be treated to meet LDR standards by using
combustion technologies. EPA has determined  that there is adequate sludge/solid
combustion capacity to accommodate these wastes. Therefore, the Agency is not
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                                           6-9



            granting a capacity variance for soil contaminated with newly listed and identified wastes'

            covered under this ruling.
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                                     CHAPTER 7
                       HAZARDOUS DEBRIS CONTAMINATED
                  WITH NEWLY LISTED AND IDENTIFIED WASTES
        This chapter presents the data and methodology used to support the capacity
  analysis for hazardous debris contaminated with newly listed and identified wastes.
  Specifically, this chapter presents the estimates of the quantities of hazardous debris that
  will require alternative treatment prior to land disposal as a result of this rule.  This
  analysis uses data from several sources: the  Questionnaire for Facilities that Land
  Dispose Newly Identified Organic Wastes Exhibiting the Toxicity Characteristic (TC
  Survey); comments and data received in response to the recently promulgated rule on the
  Land Disposal Restrictions of Newly Listed  Wastes and Hazardous Debris (57 FR
  37193), also known as the Phase I rule; industry roundiable meetings; and several other
  data sources.

        This chapter is organized into three sections.  Section 7.1 summarizes the available
  information sources on hazardous debris, Section 7.2 presents the methodology and
  results of the analysis of required capacity, and Section 7.3 presents the results of the
  capacity analysis.                    .

  7.1    DATA SOURCES

  7.1.1  Questionnaire for Facilities that Land Dispose Newly Identified Organic Wastes
        Exhibiting the Toxicity Characteristic

        In April and May 1992, EPA conducted the TC Survey by sending a questionnaire
  to land disposal facilities that manage newly identified TC organic wastes  in land-based
,  units or depose of these wastes  using underground injection wells.  The effort covered
  139 facilities that had submitted permit modifications or received interim status for
  managing the newly identified TC organic waste codes (D01.8-D043).  EPA did not
 specifically target RCRA corrective action sites and Superfund cleanup sites as sources of
 newly identified TC organic wastes.4*

        For  each facility targeted by the survey, EPA requested waste stream-specific data
 on newly identified TC organic wastes, including the waste code of the waste stream, the
 physical form of the waste stream (including hazardous debris), and the type of
 generation  (including routine generation, remediation-derived waste, and waste derived
 from closure of surface impoundments).  EPA also requested information on cm-site land
 disposal units and treatment systems.
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    ** Some of the debrii from remedial actions managed in o-mrarra.il landfills are captured by (he TC Survey.
 However, there are likely to be additional quantities of remedu:>c
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                                        7-2

       EPA has prepared a data set from the results of the data collection.  This data set
 contains information on the quantities of newly identified organic TC wastes that will
 require commercial treatment capacity as a result of the LDRs. Based on the data
 collected, EPA projected waste quantities for 1992 through 1995 by adjusting 1991
 routinely generated quantities for future waste minimization and regulatory actions
 expected by the respondents.

 7.1.2  Comments to the Phase I Proposed Rule

       The January 9, 1992 Proposed Phase I Rule (57 FR 958) presented the
 methodology for and the results of EPA's preliminary capacity analysis for hazardous
 debris. In the proposed rule, the Agency solicited comments on its approach as well as
 estimates of available treatment capacity.

       EPA received over  100 debris-related comments in response to the proposed rule.
 Of these, 45 comments discussed issues relating to capacity available for contaminated
 debris.  Many of the comments dealt with issues concerning hazardous debris in general,
 while other comments focused on debris contaminated with specific types of waste.  In
 addition to commenting on debris contaminated with previously listed and identified
 waste and the newly listed  and identified wastes covered in the Phase I rule, several
 commenters also-discussed debris contaminated with newly listed and identified Phase II
wastes, such as  the newly identified TC organic wastes.  The commenters raised the
 following major issues:

       •      Underestimation of the quantity of contaminated debris generated;

       *      Total volume of debris generated;

       •      Capacity variances for  hazardous debris contaminated with
             newly  listed and identified wastes;

       •      Materials handling problems with hazardous debris;

       •      Concerns about treatment capacity for hazardous debris; and

       •      Concerns about storage capacity  for contaminated debris.

7.1 J   Roundtable Meetings

       As part of the Agency's efforts to gain a more complete understanding of capacity
issues associated with the LDRs for hazardous  debris. EPA held three roundtable
meetings, in May and June of 1991, with representatives of companies that generate or
manage these wastes. The roundtable meetings covered a broad range of topics.
                                                                                                                         --
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                                        7-3
 including generation and management of hazardous debris, composition of hazardous
 debris, and capacity issues. The following summarizes the three meetings:

       •     The first roundtable meeting included representatives from seven waste
             management companies who operate commercial landfills, and a
             representative from the National Solid Waste Management Association;

       •     The second roundtable meeting was attended by representatives from 13
             companies that generate and primarily miinage hazardous debris in on-site
             landfills; and

       •     The third roundtable meeting included waste treaters and brokers from
             sevc.t firms.

       7. U.I  Quantities and Composition of Hazardous Debris

       In these roundtable discussions, industry participants provided information on the
 quantity and composition of hazardous debris generated ;md/or managed by their
 companies. Most participants provided quantity estimates of the proportion of the total
 waste volumes they manage that could be classified as debris.  Of the 1 1 generators that
 estimated the volume of debris waste managed on-site, four estimated that  debris
 comprised 10 percent or less of the total waste volume they manage; three  estimated that
 debris accounted for between 10 and 25 percent of the loial, three reported that debris
 contributed to about SO percent of the waste managed on-site, and one generator
 estimated that debris comprised almost 80 percent of the loial waste landfilled.

       One representative  of a commercial  landfill estimated that 75 to 80 percent  of all
 deliveries to landfills contain some type of debris.  Pr.ictically all deliveries of wastes from
 remedial actions are believed to contain at least some debris. A second landfill operator
 estimated that approximately 30 percent of the waste stream volume received could be
 classified as debris.

       Waste generators noted that debris comprises a lurge diversity of materials, often
 generated on an irregular basis. Some of the most common types of debris include
 construction debris, wood,  rocks, bottles, and miscellaneous equipment ranging from
 laboratory gloves to empty containers, filters, and pipes.  Participants also noted that
 filters come in all  sizes and shapes and that, although they are typically made of some
 type of metal, they also can be made of such materials as polypropylene, dacron, and
 nylon.  In addition, there are also activated  carbon filters, caustic filters, and clay filters.

       Representatives from commercial landfill companies noted that some types of
 debris such as personal protective equipment, spill cleanup materials, and contaminated
scrap metal and equipment are universally generated, whereas the generation of some
 other types of debris may vary among the different region of the United States.
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                                        7-4

 Participants also remarked that some debris waste streams are recurrent, including
 asphalt from oil change businesses, oil wax and wicks from train maintenance, and filters
 from all types of industrial processes.

       Overall, the roundtable participants agreed th;it quantifying debris volumes is
 difficult because debris is often generated with soil or mixed with other contaminants and
 separation is not usually possible. Furthermore, TSD facilities have historically classified
 wastes according to waste  code rather than by waste type (i.e., debris).  Accordingly, the
 quantity data on debris wastes are less precise than Jala for must other hazardous waste
 streams.

       7.1J.2  Sources of Hazardous Debris

       The universe of hazardous debris can be divided into three primary sources: (1)
 routinely generated debris, (2) demolition/construction  debris, and (3) remediation debris.
 Each of these sources has  characteristics that affect the type, quantity, variety, and timing
 of debris generation.  Exhibits 7-1 through 7-3 depict the various sources of hazardous
 debris and subsequent management  options.

       Routinely generated debris includes waste items that are generated regularly or
 continuously from a given "source" or industrial activity. -Examples of routinely generated
 debris include:

             Filters;
      •      Off-spec manufactured items;
      •      Spent batteries;
      •      Lamps and electronic components; and
      •      Personal protective equipment (PPE).

      Debris from demolition and construction activities are generated sporadically
 because construction and demolition tend to be seasonal and non-continuous.
 Furthermore, the quantities of debris generated vary from  site to site. Debris resulting
 from private party remedial actions that are relatively small in scale are included in the
 demolition/construction category.  The types of materials^ generated in this category
 include:

      •      Concrete and metal construction materials;
      •      Geologic materials; and
      •      Durable manufacturing and process equipment.

      Remediation debris are primarily generated through Superfund, State CERCLA,
;md RCRA corrective  action  activities. This source category is characterized by large
quantities of hazardous debris being  generated from single locations over a potentially
long period of time.
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                                          7-8
        The quantity of debris generated through demolition/construction and remediation
  related activities is estimated to exceed the amount (if routinely generated debris by up
  to a factor of ten. Debris from large remedial actions tend 10 be managed on-site and
  therefore do no: require off-site commercial treatment capacity.  However, debris from
•  demolition or construction and from routine operations ;irc usually sent off-site for
  management and constitute the most important sources nf debris requiring commercial
  off-site treatment. Exhibit 7-4  presents the relative volumes of hazardous debris
  currently going to commercial landfills.

        The volumes of debris that are generated also vary depending on (he region, the
  time of year, and economic conditions. For example, more debris is generated in the
  summer than in the winter due to increased construction activities.  In aging industrial
  areas, a greater quantity of debris is generated from the demolition of older plants,
  whereas in other areas, a greater proportion of the generated debris may originate  from
  road construction or the cleanup of federal facilities.  In many southern sites,
  approximately 25 percent of the tonnage generated at remediation sites is reported to be
  wood. Finally,  in a depressed economy, industrial waste streams are reduced and plant
  retrofitting is delayed or cancelled, resulting in smaller quantities of debris generated.

        7.1 JJ  Current Management of Hazardous Dchris

        The management of hazardous debris is often  made 'difficult because of material
 size and because debris waste streams are often mixed with other contaminated wastes.
 Management options currently  employed include landfilling debris without treatment,
 incineration, stabilization, and decontamination through washing and steaming. (Exhibits
 7-1 through 7-3 show the variety of management options for each major debris source.)
 Approximately 80 percent of the hazardous debris  land  disposed off-site is landfilled
 without treatment. Data received by EPA indicate that, t>f the land-disposed hazardous
 debris, approximately 90 percent is contaminated with metals, while the remaining 10
 percent contain organics, and are often also contaminated with metals. "**

        Participants in the roundtable meetings estimated that incineration  is the
 predominant treatment  method employed far the hazardous debris that is now treated.
 While stabilization of hazardous debris is also practiced, one constraint to stabilization  is
 the availability of sizing equipment required for pre- treatment.  Also, debris
 contaminated with asbestos is not usually stabilized because of the potential health  risks
 to workers.

        A large proportion of hazardous debris could be  managed using decontamination
 processes.  Many facilities and treaters are currently performing what they consider to be
    * This estimate is skewed to»aidj debns eontanu3a:cd »".1 in^uma because ihe national capacity variance
 graned in ihe Third Third rule 10 inorganic solids debris »» --. c!!c« .u the lime these data wtre collected.
 Fimhermore, the impact of the relatively new TC rule a juw ^f.vunj: H> he reflected in the data available to EPA.
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                        EXHIBIT 7-4
                  Sources of Hazardous Debris
               Received By Commercial Landfills
         Construction/
        Demolition Debris
Q
            50%
  Routinely
  Generated
   Debris
Remedial
 Debris
20%
 30%
                    Commercial Landfill
                                                                      • §*8
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                                                        7-10
  /,
 decontamination of materials cm-site, a process whereby the hazardous waste is separated
 from the debris material, thereby decontaminating the debris material. Roundtable
 participants argued that EPA needs to recognize these procedures.  Commenters also
 argued that if treatment permits were required for practices currently considered to be
 decontamination, this would cause severe disruptions in treatment.  EPA has taken these
 comments into consideration in updating its treatment standards.  Nevertheless, EPA
 recognizes that the currently available RCRA permitted capacity (off-site)  for many
 extraction technologies is very limited.

 7.1.4  Other Data Sources

       In addition to the information sources described above, the Agency also used
 other data sources in its analysis of required capacity.  These data sources  are described
 below.
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       7.1.4.1  Envirosafe Data

       The Envirosafe landfill facility in Ohio voluntarily submitted information on all the
waste streams it received in 1990. The data contain a description of each waste stream
including waste form and waste codes, as well as the volume received.  According to this
data, the Envirosafe landfill received 47,000 torn of hazardous debris during 1990.47
Of this volume, 470 tons (approximately 1%) was contaminated with the newly identified
TC organic wastes (D018-D043). The remaining volume of debris was contaminated with
wastes that have been previously regulated under earlier LDR rules.

       7.1.4.2  LaidlawData
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                       The Laidlaw landfill facility in South Carolina voluntarily submitted information on
                all the soil and debris waste streams it received in 1991.  The data contain a description
                of each waste stream including waste form and waste codes, as well as the volume
                received.  According to this data, the Laidlaw landfill received 7,100 tons of hazardous
                debris during 1991. Of this volume, 950 tons (13 percent) was contaminated with the
                newly identified TC organic wastes (D018-D043).  The remaining volume of debris was
                contaminated with wastes that have been previously regulated under earlier LDR rules.

                7.2    REQUIRED CAPACITY

                       EPA conducted the TC Survey specifically to address the effects of the LDRs on
                waste streams containing newly identified TC organic wastes. The results of this survey
                predict erratic generation of contaminated debris requiring off-site treatment between
                   " Some waste streams included IxnO soil and debra. Relief ifuri attempt 10 estimate the relative proportions of
                soil and debris, the entire volume was assumed to be soil Therefore, f-a euimaie may unoenuic the tnie volume of
                hazardous debris received at the facility.
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                                       7-11
 1991 and 1995; this reflects ihe ways in which contaminated debris is generated.  Some is
 generated through spills and other routine causes, but some results from one-time events,
 such as remediation efforts and surface impoundment closures.  Exhibit 7-5 presents the
 quantities of newly identified TC organic debris requiring off-site commercial treatment
 capacity by waste code for 1993.

       EPA is finalizing treatment standards for two other groups of newly-listed wastes
 in this rule, coke by-product wastes (KI41-KU5 and K147-K148) and chlorinated
 toluenes (K149-K151).  Under the  authority of section 3007 of RCRA, EPA collected
 generation and management information concerning coke by-product wastes and
 chlorinated toluenes. However, during these data collection efforts, EPA did not
 investigate hazardous debris.  Since EPA has not  received information indicating that
 there is hazardous debris contaminated with these wastes, the Agency assumes that there
 will not be significant volumes of hazardous debris contaminated with coke by-products
 and chlorinated toluenes.

 73    CAPACITY ANALYSIS FOR HAZARDOUS DEBRIS

       EPA estimates that approximately 34,000 tons of debris contaminated with newly-
 identified organic TC wastes are currently land disposed and require off-site commercial
 treatment capacity. EPA believes this debris can  be treated to meet LDR standards by
using combustion technologies.  EPA has determined that there  is adequate sludge/solid
combustion capacity to accommodate these wastes. Therefore, the Agency is not
granting a capacity variance for debris contaminated with newty  listed and  identified
wastes covered under this ruling.

       EPA recognizes that generators of debris contaminated by wastes covered under
this rule may be faced with logistical issues in complying with the new regulations.
However, EPA has granted a three-month  national capacity variance for all wastes
covered by this rule. The Agency believes  that this is a reasonable time period for
addressing logistical issues related to compliance.
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                                    7-J2



                                 EXHIBIT 7-S




          QUANTmES OF NEWLY-IDENTIFIED TC ORGANIC DEBRIS BY SOURCE
O
Waste Code
DOIS
D019
D020
D021
D022
D023
D024
D025
D026
D027
D028
D029
D030
D031
D032
D033
D034
D035
D036
D037
D038
D039
D040
O041
D042
D043
Totals'
Tons of Surface Disposed Waste
26,400
220
20
210
80
60
60
60
700
290
280
330
90
10
70
110
40
300
70
130
570
970
890
20
20
1,700
34,000
                     * Toul may IMM SUB due to r

                     Source: TC Survey
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           APPENDIX A


SAMPLE HWTC SURVEY QUESTIONNAIRE
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           HAZARDOUS WASTE TREATMENT COUNCIL J993 SURVEY
       OF COMMERCIAL HAZARDOUS WASTE INCINERATION CAPACITY

        The Hazardous Waste Treatment Council (HWTC) is conducting a voluntary survey
 of commercial incineration companies to determine their capacity to burn RCRA hazardous
 wastes. The responses to this survey will be submitted to the U.S. Environmental Protection
 Agency's Office of Solid Waste.  This information-will be lued in EPA's  capacity analysis
 for "newly identified* RCRA hazardous wastes. This capacity analysis is  used to establish
 the effective  date of treatment standards under the Land Disposal Restrictions (LOR)
 program.  In the LDR process, standards are established for individual waste codes, based
 on the performance of the Best Demonstrated Available Technology (BOAT) for the waste.
 Once enacted by rule, these standards must be met before a waste may be disposed of on
 the tsnd.  EPA analyzes the availability of alternative treatment capacity  when setting the
 effective date at which BDAT standards must be met.

        HWTC requested  that EPA indicate what types of information EPA uses to
 conduct the capacity analysis.  This questionnaire incorporates the information provided by
 EPA. It focuses on the types and quantities of hazardous wastes that are typically managed
 in incinerator units.  It requests information on current (as of March 1993) and planned
 practices (anticipated before  July 1994) liat  affect hazardous waste capacity.  EPA is
 interested in future plans that affect capacity because the regulatory agenda for LDR rules
 spans several years.

      To arrive at accurate capacity estimates, EPA requires facility and unit-specific data.
 Questions 7,8,9 acd 10 pertain to individual units. If a facility burns hazardous wastes in
 more tbaa one unit, these questions should be completed for each thermal destruction unit.
A supplemental question set is included for additional units.

      Submission of information requested in this questionnaire is voluntary.  It  is not an
EPA survey, nor is* it required under any EPA authority. Where possible, multiple choice
questions hive been provided to simplify responses. Separate pages may be used to provide
clarifying information or explain specific  responses.   Other materials, (e.g., company
brochures, permit applications, or trial burn report dm  that  provide the requested
information may be attached to your response.   Any facility that  wishes to have  their
information submitted to EPA as  Confidential Business Information (CBI) may  do so by
marking specific information as CBI. Information that is available from publicly available
sources should not be marked as CBI.

      We anticipate that completing this form may require information  from marketing.
operations, and environmental personnel.  Once source materials and inputs from various
individuals art-compiled, we expect completing the form to require two to three hours per
facility.
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                                                                                                                     «.•.!=-.]•
      In. order to provide  this information to EPA io time for the  capacity analysis,

completed forms must be received by HWTC  by MfL 14- 19?3-  H you  have general

questions regarding this data collection effort, please contact A.E. Lovett or Eli EiJbott at

the HWTC at 202-783-0870. If you have technical questions, please contact Gary Light of

ICF (SPA'S Capacity Analysis Contractor) at 703-934.3928.                         '

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A.    Facility Information
Iff
1.    Respondent Name and Tide:
      Company:
      Phone number:
2.     Name and address of company that owns the thermal destruction device at this
      facility:
      Facility name, location, and address:
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      EPA ID of burner
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     EPA   ID   of  on-iite  proceisor   (if   different   from   above):
     EPA ID of other on-sitc hazardous waste tramporten
                                         martaeten
                                      •  storcn
     Number of incinerator unia currently burning hazardous wastes at this facility:
     Additional incinerator units opected to bum hazardous wastes by July 1994:
     Incinerator unfa at this facility not expected to burn hazardous wastes by July 1994:
     Total Number of incinerator units a: this facility (should be total of above):
                                       •1-
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4.     Please indicate the fonn(s) in which you receive hazardous wastes by checking all
      that apply:

            	Roll-Off Bin
            	End Dump Tracks
            	Hopper Trucks
            	Steel Drum, specify sizes:	\	
            	Poly Drum, Specify sizes:	_
            	Fiber Drum, specify sizes:	
            	Bag or other flexible container, specify sizes:	
            	Rigid Tote
            	Tanker Trucks (transferred to tank)
            	Tanker Trucks (direct feed to incinerator)
            	Rai! car
            	C-.boy
            	Pallet
            	Gaylords
            	Hoppers
            	Compressed gases
            	Lab Packs
            	Other, specify: 	     •	
5a.   Please indicate your current and planned qn-site and company owned off-site storage
      capacity for hazardous wastes. Indicate any requested specifications below the table.
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Maximum RCRA Hazardous Waste Storage Capacity
Storage
Type
Containers
Liquid
Tanks
Contain-
ment Bldg
Bulk Solids
Waste Piles
Other
(specify)
Current Capacity
(gallons)
On-site





Off-site





Total





Planned Capacity
Additions
(gallons)
On-site





Off-site





Total





Expected Date for
Planned Additions
On-site





Off-site





Total





                                                                                                     GHi

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                 5b.    What processing operations do you perform oo-siie for liquid wastes?
  F«
    1



1
Process
Blending
Filtration
Decanting
Ceatrifugation 	
Other (spenfy)
Description





Incinerator Rate Limiting (Y or N)





      Are any of these processes rate limiting to the  totaJ iacineratioa  process	?  if so.
      describe.

Sc.   What processing operations do you perform on-site for solid wastes?
      For each, please describe size and configuration limitations for waste feed materials. Also.
      explain the throughput rate and any rate limiting steps. '
Process
Size Reduction
Grindjng
Shredding
Sorting
Repackaging
Other (specify)



Description



-





Size Limitations
..








Incinerator Rate Limiting
(YorN)









                1 For purposes of tail form, 'processing" includes all blending, repackaging, or other physical
                processing  required to prepare  the waste  to be  fed  to  the  incinerator unit  Attach Part B
                application pages or other narrative description if it is helpful.
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6.     Please complete the Mowing table indicating this facility's capacity to receive and process
       wastes on-rite priorto buminf. Maximum practical processing capacity estimates should
       be based on the most limiting technical or permitting constraint oa receiving, storage, and
       processing  operations that  occur in sequence.   Please estimate  maximum practical
       processing in terms of waste quantities as received.  In the "Limiting Factor" column.
       indicate whether the limit is a permit limit (P), another regulatory limit (R), or some other
       technical limit (I).  If regulatory limits contain overall facility capacity below the sum of
       individual incinerator unit capacity limits, please distribute the facility capacity limit such
       that individual incinerator unit limits  do not exceed total facility limits.
\

 T
 ;



 f;
 •I

 3
On-site Hazardous Waste Receiving and Processing Capacity
Waste Type
Liquids
(aqueous)
Liquids
(non-aqueous)
Pumpible
Sludges
Nonpumpable
Sludges-
Containerized
Solids
Bulk Solids
Compressed -
Gases
Total
Tons Received
During 1992





.
.-

Tons Processed
During 1992


•
•





Current Maximum
Practical Processing
Capacity
(toat/yr u received)








Capacity
Limiting
Factor





•


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                                                     Unit Number
of

Questions 7,8,9 and 10 should be completed for each incinerator unit currentlyj»uming hazar^m
waste or that you Qg&£LtQJ2UIXI hazardous waste by July, 1994. A .-upplementaj question    is
inducted for additional units.
7.     Unit Number.
      Tjpe of incineration unic
      Thermal input (Bm/hour):

      Total hours operating per year on average:
     Type(s) of hazardous waste feed sywem(s) currently used with this kiln:

           fumpablc liquict tnjeaed:            	
           Bulk solids Injected;                  	
           Containerized solids charged          	
           Sludge Pump:                       	
           Non-Pumpabtc Sludge feed:           	
           Compressed gases:                   ;	._
           Other (specify)	
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                                                                             Oi
g.
       ?|ease indicate the amount of hazardous wastes you actually buraed in this kiin during 1592
       and  the  maximum practical  amount you  could burn in one  year, taJaag into  account
       operational down time,  residual management capacity limits, Interim  Status, and permit
       limit*. In the 'Capacity  Limiting Factor" coluein. indicate whether it is a permit lirru IP}.
       another type of regulatory limit (R), a beat release limit (H) or some other technical Icni
       (T). If permits limit overall facility capacity and not icdividuaJ incinerator capacity, please
       make sure that the sum of individual thermal destruction unit capacities does not exceed
       overall facility limits.  Explain any exceptions on a separate page as necessary.  (Total
       capacity may norrqual the sum of the waste specific capacities if there is a permit limit OB
       total capacity, or if one form of waste capacity may be traded off for another.)
. Kiln Number
Liquids
(aqueous)
Liquids
(con-aqueous)
Pumpable
Sludges
Noopumpable
Sludges
Containerized
Solids
Bulk Solids
Compressed
gases
Total
Tons of Hfyrdouf
Waste Burned During
1992



•'




Total toos of
Waste Burned
during 1992







-
Maximum
Current Practical
Burning Capacity
(Tons/Year)








Capacity
Limiting
Factor








                                                                                                          3 S01
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8a.    EPA is rwsfc that hazardous wastes thit are teperated »s solids are often blended is to
       liquids for injection to the incinerator ucit.  What is the average solid content in the liquids
       fed to this unit (on a tonnage basis), and what fraction of the solids entrained in  these
       liquids were originally generated as solids.
      Average total solid content in liquids (a burned):
      Percent of above solids originally generated as lolids:
                                            -6-
                                                                 (%)
                                                                                                           —V

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                                                             Unii Number	of
 9.     Please indicate the values you assumed for each of the following factors in estimating th<

       hazardous waste burning capacity of each incinerator unit  Fill in those that do not appl

       with N/A.
Waste Type
Liquids
(aqueous)
Liquids
(non-aqueous)
Pumpable
Sludges
Nonpumpable
Sludges
Containerized
Solids
Bulk Soli*
Compressed
gases
Average Haz.
Waste Feed
Rate (Ib/hr)







Average Ifliat
Waste Feed
Rate (Ibs/hr)






•
Days Feeding
Haz. Waste per
Year(davs/yr)






•
Average Heating
Value of Haz.*
Waste (Btu/lb)

•
(




                                                                                                      » 5
                                                                                                         O
                                                                                                         C/3
                                                                                                         to

                                                                                                         71
                                                                                                         o
                                                                                                         O
Please list any other critical parameter! on which capacity estimates are based and  include

additional operating assumptions that further clarify your capacity estimate for this incineratior

unit.
                                           -7-
                                                                                                        —I

-------
                                                          Unit Number
of
10.    If thh unit is not currently burning hazardous wastes (as of March 1993), please indicate

      when you expect it to begin burning hazardous waste, and any physical changes or regulatory

      (eg, permit or Interim Suns) modification that must occur and or be authorized before

      this bin will begin burning hazardous wastes.
      lOa) When (year and month or quarter):
                   :»   III
      lOb) Physical changes (include planned schedule):
                                                                                                   8   sr

                                                                                                   iM
                                                                                                     o
     lOe) Regulatory modifications (include planned schedule):
                                                                                                     71
                                                                                                     o
                                                                                                     o
                                        -8-

-------
i
                Please fill in the following table for aJl authorizations you are seeking in order to burn RCRA
                hazardous wastes. Consider all permits that limit your ability to burn hazardous wastes. Also
                indicate when you expect final authorizations.  Please use the following permit status codes
                in the current status column:

                NR-  Pennh Mot Required (explain in notej
                FP -   fully permitted to receive RCRA hazardous wastes
                PM •  Preparing Permit Modification for Additional Wastes
                SA -   Submitted Complete Application and Awaiting Response from Issuing Agency
                MA -  Modifying Permit Application for Additional RCRA Wastes
                IS -   Interim Status
                ND -  Currently Responding to fcjotkes of Deficiency in Application
                PH-   Awaiting £ubue Hearing on Permit
                OT-   Other  (please specify):
I

Authorization Required
Federal
Blf
RCRA Storage
RCRA Treatment
dean Air Act
Other (specify)
State
Hazardous Waste
Air Emission
Land Use/Siting
Other (specify)
lineal
Hazardous Waste
Air Emission
Land Use/SUag
Other (specify) -
Authorizing Agency Name •
and Phone Number

„


*








Current
Status













Expected Date
of Authorization.





• •







                                                                                                                     o
                                                                                                                     O
                                                                                                                     O

-------
lla.  Please indicate the acceptable ranges of all physical and chemical waste properties that you
      consider before agreeing to receive a waste. Fill in only those that apply, and add properties
      as necessary. In the "Limiting Factor* column, indicate whether the limit is a permit limit (P).
      another regulatory limit (R). or some other technical limit (1). If you have a total specified
      metals limit and not individual metal limits, indicate the total specified metals limit and check
      off which metals are included in this limit.  Explain any exceptions on a' separate-sheet as
      necessary.                                  _
"As Received" Liquid Aqueous Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Particle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other (Specify)
Other (Specify)
Total Halogen Content
Chlorine Content
Fluorine Content
Bromine Content
Othen Specify
Othen Specify
Minimum
Allowable
(specify units)








•


-





Maximum
Allowable
(specify units)

















Limiting
Factor











-





                                                                                                            i * s" w

                                                                                                                 o
                                                                                                                 o
                                                                                                                 o
                                           •10-
                                                                                                                 —I

-------
Property
Total Specified Metals Content
Antimony Concent
Arsenic Content
Barium Content
Beryllium Concent
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
:>clenium Content
Silver Content
Thallium Content
Vanadium Content
7Jnc Content
Other Specify
Other Specify
Minimum
Allowable
(specify units)



•










•"


•-
Maximum
Allowable
(specify units)
















-

Limiting
Factor


















 ??5
> ^§ *
  S M
  O
  o
  O
  —i

  un

-------
lib.   Are your liquid waste limitations 'as burned* the same as waste limitations 'as received"?

      (Y/N)	


      If yes, skip to 12a, If no, please indicate the limitations on ail physical and chemical waste

      properties as burned.  Fill in only those that apply, and add properties as necessary-  In the

      •Limiting Factor* column, indicate whether the limit is a permit limi: (P), another regulatory

      limit (R), a heat release limit (H) or some other technical limit (T). If you have a total

   •   specified metals limit and not individual metal limits, indicate the total specified metals limit

      and check off which metals are included in this limit. Explain any exceptions on a separate

      sheet as necessary.
'As Burned* Liquid Aqueous Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Particle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other Specify
Other: Specify
Total Halogen Content
Chlorine Content
Fluorine Content
Bromine Content
Other Specify "'
Other. Specify
Minimum
Allowable
(specify units)






*










Maximum -
Allowable
(specify units)

.




*










Limiting
Factor ,


















                                                                                                              O
                                                                                                              en
                                                                                                              to
                                                                                                              >n

                                                                                                              o
                                                                                                              o
                                          •12-
                                                                                                             cn

-------
Property
Totaj Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other: Specify
Other Specify
Minimum
Allowable
(specify units)














•



Maximum
Allowable
(specify units)


•











.



Limiting
Factor



















                                                      ft *
                                                          n
                                                          71
                                                          o
                                                          o
•13-

-------
I2a.  Please indicate the acceptable ranges of all physical and chemical waste properties  that you
      consider before agreeing to receive a waste. Fill in only those that apply, and add properties
      as necessary. In the 'Limiting Factor* column, indicate whether the limit is a permit limit (P).
      another regulatory limit (R), or some other technical limit (T).  If you have a total specified
      i.-.etaJs limit and not individual meuJ limits, indicate the total specified metals limit and check
      off which  metals are included in this limit  Explain any exceptions on a separate  sheet as
off which
necessary.
*As Received" Liquid Non-Aqueous Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
TotaJ Inorganics Content
Particle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other (Specify)
Other (Specify)
Tool Halogen Content
Chlorine Content
Fluorine Content
Bromine Content
Other: Specify
Other Specify- "
Minimum
Allowable
(specify units)







/









Maximum
Allowable
(specify units)















""

Limiting
Factor

















                                                                                                             «r ™

                                                                                                              O
                                                                                                              00
                                                                                                              O
                                                                                                              O
                                          -14-
                                                                                                              co

-------
•As Receiver Liquid Non*Aqueoui Waste Limitations
Property
Total Specified MetaJs Content
Antimony Content
Anenic Content

Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Memuy Content
Nickel Content
Selenium Content
Silver Content
Thallium "Content
Vanadium Content
Zinc Content
Other Specify
Other Specify
Minimum
Allowable
(specify units)













*




Maximum
Allowable
(specify units)


















Limiting
Factor






•"











                                                       H
                                                         O
                                                         71
                                                         o
                                                         o
-15-

-------
      Liquid Non-Aqueous Waste Acceptance Limits As Burned

I2b.   Are your liquid waste limitations "as burned* the same 3$ waste limitations 'as received"*
      (Y/N)	

      If yes, skip to !3au If no, please indicate the limitations on all physical and chemical waste
      properties as burned.  Fill in only those (hat apply, and add properties as necessary. In (he
      •Limiting Factor- column, indicate whether the limit is a permit limit (P), another regulatory
      limit (R), a heat release limit (H) or some other technical limit (T).  If you have a total
      specified metals limit and not individual metal limits, indicate the total specified metals limit
      and check off which metals are included in this limit. Explain any exceptions on a separate
      sheet as necessary.                                                        ^^
*As BurnecT Liquid Non-Aqueous Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Particle/Object She
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Othen Specify
Other: Specify
Total Halogen Content .
Chlorine Content
Fluorine Content '
Bromine Content
Other Specify
Other: Specify
Minimum
Allowable
(specify units)




4












Maximum
AJIowable
(specify units)

















Limiting
Factor








•









                                                                                                          o
                                                                                                          O9
                                                                                                          10
                                                                                                           o
                                                                                                           o
                                        •16-
                                                                                                          Oj

                                                                                                          COS
                                                                                                              J

-------
•As Bunted* Liquid Non-Aqueous Waste Limitations
Property
Total Specified Metats Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Othen Specify
Other Specify
Minimum
Allowable
(specify units)












t





Maximum
Allowable
(specify units)
•

















Limiting •
Factor





-












                             m
                             V _ a
                              Sg-S
                               O
                               o
                               o
-17-
                              Oi


                              CD

-------
Ua.
Pumpabte Sludges Waste Acceptance Limits As Received

An your pumpable sludge waste limitations  'as received" (he same as waste limitations
specified in questions 12a or b? If so, specify which table applies (e*. 12a or 12b) and skip
to 13b:

If no. please indicate the acceptable ranges of all physical and chemical waste properties that
you consider before agreeing to receive a waste.  Fill  in only those that apply, and add
properties as necessary. In the "Limiting Factor* column, indicate whether the limit is a
permit limit (P), another regulatory limit (R), or some other technical limit (T). If you have
a total specified meals limit and not individual metal  limits, indicate  the total specified
metals limit and check off which metals are included in this limit. Explain any exceptions on
a "FT*""* sheet as necessary.
                                                                                                        SSS

                                                                                                          s
                                                                                                         Is"
"As Received* Puinpable Sludfes Waste Limitations
Propei ly
Heat of Combustion
Water Content
Total Solkh Content
Total Inorganics Content
Panicle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other Specify
Other. Specify
Total Halogen Content
Chlorine Content . .
Fluorine Content
Bromine Content
Other Specify
Other Specify
Minimum
Allowable
(specify units)

















Maximum
Allowable
(specify units)












•




Limiting
Factor

















                                                                                                           o
                                                                                                           
                                                                                                           10
                                                                                                          "rt
                                                                                                            i
                                                                                                           O
                                                                                                           O
                                         -18-
                                                                                                           CQ

                                                                                                           ru
                                                                                                                  i

-------
•As Received* Pumptble Sludfes Waste Limitations
Property
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Cooper Content
Lead Content
Mercury Content
Ifickel Content
!>eteniuffl Content
Silver Content
'.rhallium Content .
Vanadium Content
21inc Content
Other Specify
Other Specify
Minimum
Allowable
(specify unto)












•
•





Maximum
Allowable
(specify units)
•

















Limiting .
Factor


















-19-
                              5S 0-Z

                              o 8 So
                             fili
                             ?•§•*»

                              I
                               o
                               00
                               to
                               o
                               g
                              03


                              Uj

-------
      Pumpable Sludges Waste Acceptance Umlts As Burned

13b.   Are your  pumpabfe sludge waste limitations "as burned* the same as waste limitations
      specified in earlier questions?  if so, specify which table applies (e£, 12b) and skip to Ua:


      If no, please indicate the limitations on all physical and chemical waste properties as burned.
      Fill in only those that apply, and add properties as necessary.  In the 'Limiting Factor*
      column, indicate whether the limit is a permit limit (P), another regulatory limit (R), a heat
      release limit (H) or some other technical limit (T). If you have a total specified metals limit
      and not  individual metal limits, indicate the total specified meals limit and check off which
      metals are included In this limit  Explain any exceptions on a separate sheet as necessary.
>   ?If
•As Burned* Pompabte Studces Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Particle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other: Specify
Other Specify
Total Halogen Content
Chlorine Content
Fluorine Content- ••
Bromine Content
Other Specify
Other Specify
Minimum
Allowable
(specify unto)




„•












Maximum
Allowable
(specify units)












-




Limiting
Factor


,








•





                                                                                                         a » *
                                                                                                         If!-
                                                                                                           o
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                                                                                                           to
                                                                                                           71
                                                                                                           o
                                                                                                           o
                                         -20-
                                                                                                          CO
                                                                                                            .J

-------
"As Burned" Punpable Sludges Waste Limitations
Property
Total Specified Metals Qmtent
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Stiver Content
Thallium Content
Vanadium Content
Zinc Content
Other Specify
Other. Specify
Minimum
Allowable
(specify unit)












4





Maximum
Allowable
(specify units)


















Limiting
Factor


















                                  o
                                  C/3
                                  K>

                                  71
                                  o
                                  o
-21-
                                  Oj


                                  C30
                                     !

                                  un

-------
14a,
Nonpuznpable Sludges Waste Acceptance Limits As Received

Are jour nonpumpable sludge waste limitations 'as receiver the same as waste limitations
specified in earlier questions?  If so. specify which  table applies (eg, 12a) and skip to 14b:
If no, please indicate the acceptable ranges or attphysical and chemical waste properties that
you consider before agreeing to receive a waste.  Fill in only those that apply, and add
properties as necessary.  In the "Limiting Factor* column, indicate whether the limit is a
permit limit (P), another regulatory limit (R), or some other technical limit (T). If you have
a total specified metals limit and not individual metal limits, indicate the total specified
metals limit and check off which metals are included in this limit  Explain any exceptions on
a separate sheet as necessary.
'As Received" Noapumpable Sludfes Waste Limitations
Property
Heat of Combustion
Water Content
total Solids Content
Total Inorganics Content
Particle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other Specify
Other Specify
Total Halogen Content
Chlorine Content . .
Fluorine Content
Bromine Content
Other: Specify
Other Specify
Minimum
Allowable
(specify units)







-









Maximum
Allowable
(specify units)

















Limiting
Factor


*









1




                                                                                                     •a o Sg o
                                                                                                     68*3
                                                                                                    o
                                                                                                    to
                                                                                                    71
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                                                                                                   COi
                                                                                                   on
                                   -22-
                                                                                                          t

-------
'As Received' Nonpunpable Sludges Waste Limitations
Property
Total Specified Meals Content
Antimony Content
Arsenic Contest
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
' Selenium Content
Sliver Content
Thallium Content
Vanadium Content
Zinc Content
3then Specify
Othen Specify
Minimum
Allowable
(specify units)












•





Manmura
Allowable
(specify units)


















Limiting
Factor
















•

                                  ?  - •*

                                     •§5g
                                      ;?" w
                                   0.0.
                                     ss
                                      O
                                      c/a
                                      to
                                      O
                                      O
                                      nj

                                      CQ


                                      —i
-23-

-------
      Noopumpabie Sludges Waste Acceptance Limits As Burned

14b.  Arc your nonpumpabte sludge waste limitations 'as burned" the same as waste [imitations
      specified in earlier questions? If so. specify which table applies (e^, 125) and skip to 15a:


      If no, please indicate the limitations on all physical and chemical waste properties as burned.
      Fill in only  those that apply, and add properties as necessary. In the 'Limiting Factor*
      column, indicate whether the limit is a permit limit (P), another regulatory limit (R), a neat
      release limit (H>t>rsome other technical limit (T). IF you have a tool specified metals limit
      and not individual metal limits, indicate the total specified metals limit and check off which
      metals are included in this limit. Explain any exceptions on a separate sheet as necessary.
*As Burned* Nonpumpable Sludges Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total inorganics Content
Panicle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other Specify
Other Specify
Total Halogen Content
Chlorine Content
Fluorine Content ~
Bromine Content
Other Specify
Other Specify
Minimum
Allowable
(specify units)



,
* P












Maximum
Allowable
(specify units)

















Limiting
Factor

















                                                                                                           o
                                                                                                           TJ

                                                                                                           O
                                                                                                           O
                                          -24-
                                                                                                          CO

                                                                                                          CQ

-------
"As Burned" Noopumpable Sludges Waste Limitations
Piupcrty
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other: Specify
Other Specify
Minimum
Allowable
(specify units)












*





Maximum
Allowable
(specify units)
'

















Limiting
Factor


















                                *zs
                              \  ?§»
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                               3 « —
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                                e O-
                                 o
                                 71
                                 o
                                 o
-25-
                                 CO


                                 uo

-------
      Containerized Solids Waste Acceptance Limits As Received

ISa.   Are your containerized solids waste limitations *as received* the same as waste limitations
      specified in earlier questions? If so, specify which table applies (tg, 12a) and skip to I5b:
      If no. please indicate the acceptable ranges of all physical and chemical waste properties that
      you consider before agreeing to receive a waste.  Fill in only those that apply, and add
      properties as necessary. In the 'Limiting Factor* column, indicate whether the limit is a
      permit limit (P), another regulatory limit (R). or some other technical limit (T). If you have
      a total specified  metals limit and  not individual metal limits, indicate die total specified
      metals limit and check off which metals are included in this limit.  Explain any exceptions on
      a separate sheet as necessary.
iHl
  37   A 1
  A ***   I
n " *» *. I
O.O.JT »
•  O <" •-
•As Received* Containerized Solids Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Panicle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other Specify
Other. Specify
Total Halogen Content*
Chlorine Content
Fluorine Content
Bromine Content
Other Specify
Other Specify
Minimum
Allowable
{specify units)

















Maximum
Allowable
(specify units)











*





Limiting
Factor

















                                                                                                             o
                                                                                                             CO
                                                                                                             to
                                                                                                             ^n-
                                                                                                             o
                                                                                                             o
                                          -26-
                                                                                                            UQ

-------
f
•As Received" Cantaiaeriztd Solids Waste Limitations
Property
Total Specified Metals Content
Antimony Content
Arsenic Content "
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
1 Nickel Content
Selenium Content
Stiver Content
Thallium Content
Vanadium Content
Zinc Content
Othen Specify
Othen Specify
Minimum
Allowable
(specify units)












/





Maximum
Allowable
(specify units)


















Limiting
Factor


















                                                                       *!?


                                                                     »ig|
                                                                     g-«< 55 &z
                                                                     ji _ o ** >^
                                                                      rt " '
                                                                      a o..
                                                                        °s
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                                                                        to
o
o
                                  •27-
                                                                        LO

-------
      Containerized Solids Waste Acceptance limits As Burned


ISb.  Are your containerized solids waste limitations 'as burned" the same as waste limitations

      specified in earlier questions? If so, specify which table applies (eg-, 13b) and skip to 16a:
      If no, please indicate the limitations on all physical and chemical waste properties as burned.

      Fill in only those that apply, and add properties  as necessary.  In the "Limiting Factor
      column, indicate whether the limit ts a permit limit (P), another regulatory limit (R), a heat

      release limit (H) or some other technical limit (T).  If you have a total specified metals limit
      and not individual metal limits, indicate the total specified metals limit and check off which
      metals are included in this limit.  Explain any exceptions on a separate sheet as necessary.
, .... tn

    •
"As Burned* Containerized Solids Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Particle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Othen Specify
Other: Specify
Total Halogen <"v*"»«t
Chlorine Content
Fluorine Conceit
Bromine Content
Other Specify
Other Specify
Minimum
Allowable
(specify units)




i












Maximum
Allowable
(specify units)

















Limiting
Factor















•

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                                                                                                               co
                                                                                                               K)

                                                                                                               71
                                                                                                               0
                                                                                                               O
                                           •23-

-------
*As Burned* Containerized Solids Waste Limitations
Property
Total Specified Metals Content
Antimony Content
Arsenic Content
1 Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other: Specify
Other Specify
Minimum
Allowable
(specify units)


















Maximum
Allowable
(specify units)


















Limiting
Factor


















                                     O
                                     00
                                     K)

                                     71
                                     O
                                     O
-29-
                                     u

                                     uu
                                             * : Eli

-------
      Bulk Solids Waste Acceptance Units AJ Received
16a.  Are your bulk solids waste limitations 'as received* the same as waste limitations specified
      in earlier questions? If so, specify which table applies (e>g, 12a) and skip to 16b:	

      If no, please indicate the acceptable ranges of all physical and chemical waste properties that
      you consider before agreeing to receive a waste,   Fill -in only those that apply, and add
      properties as necessary.  In the "Limiting Factor* column, indicate whether the limit is a
      permit limit (P), another regulatory limit (R), or some other technical  limit (T). If you have
      a total specified meals limit and not individual metal limits, indicate the total specified
      metals limit and check off which metals are included in this limit. Explain any exceptions on
      a separate sheet as necessary.
a ? "<»
        «
•As Received* Bulk Solids Waste Limitations •
Property
Heat of Combustion
Water Content
Total Solids Content
Tool Inorganics Content
Particle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other Specify
Other Specify
Total Halogen Content
Chlorine Content
Fluorine Content '"
Bromine Content
Other Specify
Othen Specify
Minimum
Allowable
(specify units)




*
•











Maximum
Allowable
(specify unisj

















Limiting
Factor

















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                                                                                                            C/3
                                                                                                            to
                                                                                                            71
                                                                                                            o
                                                                                                            o
                                                                                                             -pi.
                                          -30-
                                                                                                             -C!

-------
•41
•As Receiver Bulk Solids Waste Limitations
Property
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Sliver Content
Thallium Content
Vanadium Content
Zinc Content
Other Specify
Other Spedfy
Minimum
Allowable
(specify units)












•.





Maximum
Allowable
(specify units)


















Limiting
Factor


















                                                               Is
                                                                o
                                                                C/3
                                                                K)

                                                                71
                                                                o
                                                                o
                             -31-
                                                                uo


                                                                tn

-------
      Bulk Solids Waste Acceptance Limits As Burned
16b.  Are your bulk solids waste limitations 'as burned" the same as wane limitations specified in
      earlier questions?  If so, specify which table applies (tg* 13b) and skip to 17a:	

      If no, please indicate the limitations on all physical and chemicaJ waste properties as burned.
      Fill in only those that apply, and add properties as necessary.  In the "Limiting Factor
      column, indicate whether the limit is a permit limit (P), another regulatory limit (R), a heat
      release limit (H) or some other technical limit (T).  If you have a total specified metals limit
      and not individual metaJ limits, indicate the total specified metals limit and check off which
      metals are included in this limit. • Explain any exceptions on a separate sheet as necessary.
.*
•As Burned* Bulk Solids Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Particle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium'Content
Other: Specify
Other Specify
Total Halogen Content
Chlorine Content
Fluorine Content
Bromine Content
Other: Specify
Other Specify
Minimum
Allowable
(specify units)





;



•


"




Maximum
Allowable
(specify units)

















Limiting
Factor

















                                                                                                             o
                                                                                                             
-------
"As Burned" Bulk Solids Waste Limitations
Piu|jcjiy
Total Specified Metals Content
Antimony Content
Anenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other Specify
Other Specify
Minimum
Allowable
(specify units)












.,





Maximum
Allowable
(specify units)


















Limiting
Factor



















                                     ,61
«5"g.
=•< ?aS!
                                      Q.&
                                        -."
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                                        to

                                        71
                                        o
                                        o
-33-
                                         UQ
                                             i

-------
      Compressed Gas Waste Acceptance Ltmlti AJ Received

17a.   Please indicate the acceptable ranges of all physical and chemical waste properties  that you
      consider before agreeing to receive compressed gas waste. Fill in only those that apply, and
      add properties as necessary.  In the "Limiting Factor* column, indicate whether the limit is
      a permit limit (P). another regulatory limit (R^or some other technical limit (T). If you
      have a total specified metals limit and not individual metal limits, indicate the total specified
      metals limit and check off which metals are Included in this limit.  Explain any exceptions on
      a separate sheet as necessary.
•As Received* Compressed Gas Waste Limitations
Piopcfty
Heat of Combustion
Water Content
Total Inorganics Content
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other Specify
Other Specify
Total Halogen Content
Chlorine Content
Fluorine Content
Bromine Content
Other Specify
Other Specify
Minimum
Allowable
(specify units)






•


•





Maximum
Allowable
(specify units)















Limiting
Factor















                                                                                                           S"
                                                                                                            O
                                                                                                            a>
                                                                                                            to
                                                                                                            o
                                                                                                            o
                                                                                                            CQ

-------
•As Received" Compressed Cu Wane Limitations
Property
Tool Specified Metals Content
Antimony Content
Arsenic Concent
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
• Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zone Content
Ottten Specify
Other Specify
Minimum
AJtowablc
(specify units)












..

.



Maximum
Allowable
(specify units)
-

















Limiting
Factor
















•

                                g«
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                                   o
                                   71
                                   o
                                   o
-35-
                                  UD

-------
      Compressed Gas Waste Acceptance Limits As Burned

ITb.  Are jour compressed gas waste limitations 'as burned" the same as waste limitations specified
      in earlier questions?  If so, specify which table applies (eg, 17a) and skip to 18:	

      If no, please indicate the limitations on all physical and chemical waste properties as burned
      Fill in only those that apply, and add properties as necessary.  In  the limiting Factor*
      column, indicate whether the limit b a permit limit (P), another regulatory limit (R). a heat
      release limit (H) or some other technical limit (T). If you have a total specified metals limit
      and not individuaTmetal limits, indicate the total specified metals limit and check off which
      metals are included in this limit.  Explain any exceptions on a separate sheet as necessary.
"As Burned* Compressed Gu Waste Umiutions
Property
Heat of Combustion
Water Content
Total Inorganics Content
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other: Specify
Othen Specify
Total Halogen Content
Chlorine Content
Fluorine Content
Bromine Content
Other Specify
Other Specify
Minimum
Allowable
(specify units)




•
•









Maximum
Allowable
(specify units)















Limiting
Factor















                                                                                                             O
                                                                                                             (/)
                                                                                                             Is)
                                                                                                             71
                                                                                                             o
                                                                                                             O
                                          -36-
                                                                                                             CD

-------

'As Burned" Compressed Gas Waste Limitations
Property
Total Specified Metafs Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content -
Other Specify
Othen Specify
Minimum
Allowable
(specify units)












•





Maximum
Allowable
(specify units)











,
.



-

Limiting
Factor


















                                                      5
                                                       o
                                                       00
                                                       to
                                                       (-n

                                                       o
                                                       o
-37-
                                                      UJ

-------
                                                               CVDCS 01
      contaminated debns at this facility, and any physical or chemicaj conditions  t*
restrictions or limitations) in addition to ihnv tperified above which would be required for
you to do so. Note any important acceptance conditions io the table and explain them on the
page following the table. If one of the types of debris may be included in wastes you receive.
but you are uncertain, please check off the 'Don't Know* column:
Hnsrd0u Vittu OnwnUniUd DcMs Acecptiaec
TjpcofDdufe
Common Clotfi M*ieriil» (cj, rajs, mop
heads, blankets, or dodiinc)
Penocul Pnteedoo Exjuipmeni (&(. Tyvoc
AbS)
Paper or CarAxxril Materials
FdierCanridtes
WoodMaterUs
Rubber Objeeo (tf. (ires, hoses)
PVCP|K
Other Plasdc Debris
Class Debris
Ceramic Debrb (e«. semiooodueion)
Meal Objecis (e«, pipes, vtlves. pumm. oua
wdbolB)
Asbestos Materials (e*, ihiiujJes. tasulitioo)
Non-Soa Oeotojie Material (e*, rocks)
-oncncte Debris
Refnoory Brick
Other Brida
SU|
jmct BaRerics
Battery Cases
EJeoroofc Compooeia (64, printed drcuit
boards)
Electrical Wires. Swttdtes. etc.
Other
Accept
Now
OT/N)









;












Plan B> Accept
Dy June 94
fY/N)


,














_
.



Aecepance
Cofldidons
(to addition to abow)






















Don't
Know
{/)
^ '















"





                                                                                                *
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               19.   Please explain uy debra aceqxancc oondidons noted on the previous page
                                                                                             :   s-JS

                                                                                             1  s-l
                                                                                                S v E
                                                                                                  *
                                                                                                              "1.
4
              19a.  Do you accept soils? If jo, under what conditions or limitations?
                                                                                                  O
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                                            -39-
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                                                                                                  CD


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-------
                     Permit Conditions
               20.   Please listall JOU waste codes you are oimmbf authorized to receive and burn
                     as of March 1993 fre, you have received full permit or interim sums approval
                     Attach a separate sheet as necessary.                               w

                                                                                                                   512
                                                                                                                  ;*!
                                                                                                                   zo-z
                                                                                                                 *t*s
                                                                                                                   2£ w
;pVi
• ^;i
 '•X
 "J

 I
                                                                                                                 8 "

              21.   Pte»e list all additional RCRA waste codes you are seeking permit or interim status
                    modifications to receive and bum. When do you expect authorization wburn thfe
                    waste?
                                                                                                 O
                                                                                                 oo
                                                                                                 to
                                                                                                                    o
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             22.
Are you authorized to receive and burn 'newly identified" wastes F037, FQ38, F039,
FQ32, F034, F035, K1414CI45, K147-K151 or D018-D043? If not, what would you
have to do to be authorized for those codes?
                                                 -40-
                                                                                                                   UJ

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23.
Please fill in the following table for all authorizations you require in order to burn
RCRA hazardous wanes.  Consider all permits trot limit your ability to burn
hazardous wastes. Please use the following permit status codes in the current status
column:

NR •  Permit Hot Required (explain in note)
FP -  E«Hy Eermined to receive RCRA hazardous -wastes
PM •  Ereparing Permit Modification for Additional Wastes
SA -  Submitted Complete Application and Awaiting Response from Issuing Agency
MA -  Codifying Permit Application for Additional RCRA Wastes
IS -   Interim Status
ND •  Currently Responding to tJocices of Deficiency in Application
PH -  Awaiting Eublic Hearing on Permit
OT-  Other (please specify):                             _
                                                                                              £ "P
                                                                                             rM!
                                                                                             i^:.«
Authorization Required
Efi&caj
BIF
RCRA Storage
RCRA Treatment
Clean Air Act
Other (specify)
Sfatq
Hazardous Waste
Air Emission
Land Use/Siting
Other (specify)
L&ai
Hazardous Wtste
AirErawkxi
' Land Use/Siting
Other (speclry)
Authorizing Agency Name
and Phane Number



_.
•'








Current
Status













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 r
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               24.
                                                                               ni
                    baarfow **« is a: proem or to begin burning hazardous wise in any ofiheunta
                    included in this form.  Abo indteue *fco you «pea the du^« to be m«t ^^5
                    when UK) bow }ou would haw to change jour curant practices If these dutun are
                    not approved.
                                                                                                II!
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                                                                                                  71
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 25.
                                          "*
                                                                                 thi,
                                       Yes

                                       No
26.
 [f you do plan to make changes to this facility, please describe the nature of cad]

 modification (including incinerator unit number for specific changes),  when you

 expect it to be completed and fully operational, and the effect it will have on this

 facility's hazardous waste capacity.  Include modifications to waste receiving facilities,

 fuel processing systems, waste feed systems, analytical equipment and facilities, and

 air pollution control devices.  You may attach appropriate sections of jour permit'

 modification application that describe these changes if convenient



a) When (month or quarter, and year):
                                                                                                       iQ-o s a °

                                                                                                       **" n a •*
                                                                                                       caSS "
                                                                                                       a -*   A **

                                                                                                       I «» P" M
     b) Effect on hazardous waste capacity:
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                                                                                                      to

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                                                                                                      o
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    c) Modifications:
                                                                                                          n
                                     -43-
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                                                                                            1
                                                                             I  Hi
                                                                              II
                                                              SB °-x
                                                              a S-Q
                                                                               s <*
                                                                               Q.O.trS"

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           APPENDIX B



SAMPLE CKRC SURVEY QUESTIONNAIRE
                                                                                  O
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                                                                                               ns«s
                                                                                               a a. •- t»
 1
4
                       CEMENT KILN RECYCLING COALITION 1993 SURVEY
                        OF CEMENT KILN HAZARDOUS WASTE CAPACITY
JVLY
                                                                                                  O
                                                          O
                                                          O
             Completed forms must be received by CKRC at the following address by July 23. 1993:

                                Cement Kiln Recycling Coalition
                                1212 New York Avenue, N.W.
                                Suite 500
                                Washington, D.C. :0005
                                Ann: Craig Campbell
                                                         ULJ

                                                         CD

                                                         UQ

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               CEMENT KILN RECYCLING COALITION 1993 SURVEY
                 OF CEMENT KILN BAZARJDOL'S WASTE CAPACITY

          The Cement Kiln Recycling Coaliucn (CKRO is conducting a voluntary survev i>t
  cement  companies to determine  their  capacity  10  burn  RCRA hazardous wastes,  the
  responses to ihis survey will be submitted ic the L'.S. Environmental Protection Agency's
  Office of Solid Waste.  This information will be used in EPA's capaciry analysis tor" n«wl\
  identified" RCRA hazardous wastes. This capacity analysis is used to establish the eirccme
  date of treatment standards under the Land Disposal Restrictions (LDR)  program.  In the
  LDR  process, standards  are  established  for  individual waste  codes, based  on  the
  performance of the Best Demonstrated Available Technology (BOAT) for  the waste. Once
  enacted  by rule, these standards must be met before a waste may be disposed of on the
  land.  EPA  analyzes the  availability of alternative treatment capaciry when setting the
  effective date at which BOAT standards must be met.

         CKRC requested that EPA indicate what' types of information EPA uses to conduct
  the capacity analysis. This questionnaire incorporates the information provided by EPA.
  It focuses on  the types and quantities of  hazardous wastes that cement kilns are authorized
  and technically able to bum.  It requests information on current (as of July 23. 1993) and
  planned practices (anticipated before July !994) that affect hazardous waste capaciry. EPA
  is interested in future plans that affect capacity because the regulatory agenda for LOR rules
  spans several yean. EPA is particularly interested in the effects of Clean Air Act (CAA)
.  permits, and  the Boiler and Industrial Furnace (BfF) Rule (Federal Register Volume 56
  Number  35, February 21, 1991) on cement bin capaciry for hazardous wastes.

       To arrive at accurate capacity estimates. EPA requires facility and unit-specific data.
  Questions 8.9.10.11. and 12 pertain to individual kilns. If a facility bums hazardous wastes
  in more than  one kiln, these questions should be completed for each kiln.  A supplemental
 question set is included for additional kilns.

       Submission of information requested in this questionnaire is voluntary.  It is not an
 EPA survey, nor is it required under any EPA authority.  Where possible, multiple choice
 questions have been provided to simplify  responses. Separate pages may be used to provide
 clarifying information  or explain specific  responses.  Other materials  (e.g., company
 brochures, permit applications, or BIF precompliance certification forms)  that  provide the
 requested information may be attached to your response.  Any facility that wishes to have
 their information submitted to EPA as Confidential Business Information (CBI) may do so
 by marking specific information as CBI. Information that is available from publicly available
 sources should not be_marked as CBI.

       We anticipate that completing this form may require information from marketing.
 operations, and environmental personnel. Once source materials and inputs from various
 individuals are compiled, we expect completing ihe form to require two 10  ihree hours per
 facility.
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      In order to provide this  information to  EPA in ume  for the capacity ar.aivsis
completed forms must be received by CKRC by Iulv^23. 1993. If you have eenerai questions
regarding this data collection effort, please contact Craig Campbell at the CKRC at :o:-'S
-------
•'«!
;!
               A.     Facility lofornutioa
                I.     Respondent Name and Title:
                      Company:
                      Phone number:
               2.    Name and address or company that owns (he cement kilns at this facility:
                     Facility name, location, and address:
                     EPA ID of burner:
                     Name of the company who manages the hazardous waste fuel program at this facility
                     (if not the cement company):
o
GO
to
  1
                     EPA ID of on-site processor
                     EPA (D of other on-site hazardous waste transporter:
                                                           marketer:
                                                           storer:
                     Number of loins currently burning hazardous wastes at this facility:
                     Additional kilns"expected to bum hazardous wastes by July 1994:
                     Kilns at this facility not expected to burn hazardous wastes by Juty 1994:
                     Total Number.of kilns at this facility (should be total of above):
                                                      -I-
                                                                                                                              •"6

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  4.
Please provide the name, location. ind phone number or the erf-sue interme_';j:

processor« (excluding onainal gene;a:orsi who provide ihe largest amount ot w

you receive,  [n  the  'Waste Type  :oiurnn. pleaie use the following waste n
                                                                              nr:
                  ,                            .                               nr:

        Liquids. Pumpable Sl-dges. Nonpumpatle Sludge*. Containcnred Solids. Bulk Shims

        and Dry Soiids'.
Off-Site Processor*
Processor S'ame






Location
Phone Number
' 1 ' J 	
Waste Tvue Receiwu !
•
1 i




i





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                                                                                                             to
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    lThroughout this survey,  dry solids are soi.ds that, like coal dust, can be  conveyed

pneumatically.

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B.

5.
Potential Capacity and Waste Acceptance Limitatio.ns

Please indicate the form(s) in which you receive hazardous wastes by checkine all that
apply:

      	Roll-Off Bin
      	Steel Drum, specify sacs:	
      	Poly Drum, specify sizes:	          	
      	Fiber Drum, specify sizes:_
                                                                                                   Sun
            	Bag or other flexible container, specify sues:_
            	Rigid Tote
            	Tanker Trucks (transferred 10 tank)
            	Tanker Trucks (direct feed to kiln)
            __t Rail car .
            	Carboy
            	Pallet
            	Other, specify:  	
                                                                                                     3g
     Please indicate your current and planned on-site storage capacity for hazardous
     wastes.  Indicate any requested specifications below the table.
                                                                                                  n
                                                                                                  71
                                                                                                  o
                                                                                                  o
Maximum RCRA Hazardous Waste Storage Capacity
Storage
Type
<•
Containers
Liquid
Tanks
Bulk Solids
Other
(specify)
Current Capacity
(Specify Units)



fc
Planned Capacity
Additions
(Specify Units)



•
Expected Date for
Planned Additions




                                                                                                        ULJ

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?a.   Please complete the fc '-wing table  indicating the quantity ot waste recent  :.

                                                                                                             71
                                                                                                             o
                                                                                                             UJ
                                                                                                                     I

                                                                                                                 J

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 7b.   What processing operations do you perform on-site for wastes'-  In the  'W3»ie
       Type" column,  please use the following wasie rypes:  Liquids.  Pumpable Slud«».
       Nonpumpable Sludges. Containenzed  Solids. Bulk Solids, and  Dry Solids.  In 'the
       "Capacity" column. EPA is especially interested in knowing if the capacity tor the
       processing system is less than the overall unit capacity for rypes of waste processed.
       In (he "Limiting Factor" column, indicate whether the- limit is  a permit limit |P).
       another regulatory limit (R). or some technical limit (T).  Use more than one copy
       or this table for the different waste rypes processed.
On-site Hazardous Waste Processing Capacity
Process
Blending
Filtration
Decanting
Centrifugation
Size Reduction
Grinding
Shredding
Sorting
Repackaging
Other (Specify)



Waste Type(s)
Processed









.



Annual
Capacity








/




Size/Material
Limitations






.



.


Capacity
Limiting Factor









.



m
?•§•*"
  g-3
                                                                                                             o
                                                                                                              O
                                                                                                              O
Are any of these processes rate limiting to the total thermal destruction process
If so. describe.
    2 For purposes of this form, "processing1 includes all blending, repackaging, or other
physical processing required  to prepare the waste to be fed to the kiln.
     on

-------
                                                       Kjln Number
Questions 8. 9. 10. 1 1 and 12 should be completed for each kiln currently burning
waste or that you expect to burn hazardous wane by July. 1994.  A supplemental question
set is deluded for additional kilns.  (Question  12 focuses on loins thai are not burmne a» >>t
Julv  23. 1993).
                                                                                                  US
8.
Kiln Number:

Type of Kiln:
      Ginker capacity (tons/lir):

      Thermal input (Btu/ton clinker):

      Type of cement product(s) produced in this kiln:

      Total hours operating per year on average:
      Type(s) of hazardous waste feed systems) currently used with this kiln:
            Pumpable liquids injected at "hot" end:
            Dry solids injected at "hot" end:
            Containerized solids charged to calcining zone:
            Sludge Pump:
            Other, (specify)	
                                                                                                     o
                                                                                                     00
                                                                                                     o
                                                                                                     o
      Please describe the sludge and solid feed systems indicated above (e.g.. containers are
      conveyed to a platform where  they are  manually placed into a gravity teed chute
      connected to the kiln).
                                                                                                          Uj

-------
                                                        Kilo Number:
 9.     Please indicate the amount of hazardous wastes you actually burned  m ;hi$ kiln
       during 1992. and the maximum practical amount you could burn in one vear ukinu
       into account operational down time, residual management capacity limits  interim
       Status precompliance limits, and permit limits.  In the "Capacity Limiting Facior
       column, indicate whether it is a permit limit (P). another' type of regulatory limit f'Rl
       a product quality limit (Q). or some other technical limit 
-------
                                                         Kiln Number;
 10.    Please indicate (he values you assumed for each of ine following factors in estimating
       the hazardous waste burning capacity of each kiln.  Fill in those that do not jppiy
       withX/A.
Wasie Type
LJ quids
Pumpable
Sludges
Nonpumpable
Sludges
Containerized
Solids
Bulk Solids
Dry Solids
Average
Haz. Waste
Feed Rate
(Ib/hr)






Daily Hours
of Operation
Feeding
Haz. Waste
(hr/day)






Days
Feeding Haz.
Wane per
Year
(days/yr)





•
Average
Heating
Value of
Haz. Waste
(Btalb)






Percent of
Fuel Value
provided by
Haz. Wastes
(Biu basis)






                                                                                                            * **
                                                                                                               O
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                                                                                                               K>

                                                                                                               71
                                                                                                               O
                                                                                                               O
Please list any other critical parameters on which capacity estimates are based and include
additional operating assumptions that further clarify your capacity estimate for this kiln:

-------
                                                       Kiln Number:
11.
 When (e.g.. calendar month) and for how  long is (his bin usually shut  down
 scheduled maintenance?
                                                                                                          SSE
12.
      When?

      How lone.'
If (his kiln L. not currently burning hazardous wastes (as of July 23.  199 J). please
indicate when you expect it to begin burning hazardous waste, and any  physicat
changes or regulatory (e.g.. permit or Interim Status) modification that must occur
and or be authorized before this kiln will begin burning hazardous wastes.

      a) When (year and month or quarter):
      b) Physical changes (include planned schedule):
                                                                                                      o
                                                                                                      GO
                                                                                                      K)
                                                                                                      71
                                                                                                      o
                                                                                                      o
     c) Regulatory modifications (include planned schedule):
                                                                                                            UJ
                                                                                                                   |

-------
      Liquid Waste Acceptance Limits As Received
13a.   Please indicate the acceptable ranges of all physical and chemical waste properties  that >.»-
      consider before agreeing to receive a waste. Fill in only those that apply, and jdd pro'per:ie»
      as necessary. In the "Limiting Facto;' column, indicate whether the limii is a permit limit i p. -
      another regulatory limit (R). a product quality  limit (Q.). or some other technical limn iT>
      If you have a  total specified metals limit and not individual metal limits, indicate the
      specified metals limit and check off which  metals  arc included in this limn.  Explain
      exceptions on  a separate sheet as necessary.
'As Received" Liquid Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Panicle/Object Size
Cvanide Content
Sulfur Content
Sodium Content
Potassium Content
Other (Specify)
Other (Specify)
Total Halogen Content
'Chlorine Content
irluorine Content
Bromine Content
Other: Specify
Other Specify
Minimum
Allowable
(specify units)













•

1

Maximum
Allowable
(specify units)

















Limiting
Factor

















                                                                                                            1=5*
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'As Received" Liquid Wane Limitaiions
Propeny
Pesticides
Fungicides
Herbicides
Insecticides
Rodeniicides
Other: Specify
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other: Specify
Other: Specify
Minimum
Allowable
Cspeory units I
























Maximum
AJIowable
f specify units)




.






•



•








Limiting
Factor
























                                      !*!
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                                       to
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                                       o
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                                       uu

-------
      Liquid Waste Acceptance Limits As Burned

13b.   Are your liquid waste limitations  'as turned" the same as waste limitations  js :t^ei\e^  '
      (YN>	

      If yes. skip 10 Ma. If no. please indicate the limitations on all physical and chemical »J»TC
      properties as burned. 'Fill in only these that apply, and add properties as necessary.  In she
      "Limning Factor' column, indicate whether ihe limit is a permit limit (P). another regulator)
      limit (R). a product quality limit (Q). or some other technical limit (TV  If you have a total
      specified metals limit and not individual metal limits, indicate  the total specified metals limit
      and check off which metals are included in this limit.  Explain any exceptions on a separate
      sheet as necessary.
8 0-8
I £ "
"As Bumed" Liquid W»ite Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Panicle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other: Specify
Other: Specify
Total Halogen Content
Chlorine Content
Fluorine Content
Bromine Content
Other: Specify
Other: Specify
Minimum
Allowable
(specify units)

















Maximum
Allowable
(specify units)

















Limiting
Factor

















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                                                                                                               oo
                                                                                                               to
                                                                                                               71
                                                                                                               o
                                                                                                               o
                                          -12-
                                                                                                               Oj

                                                                                                               UJ

-------
"As Burned" Liquid W»iie Limitationi •
Property
Pesticides
Fungicides
Herbicides
Insecticides
Rodenticides
Other: Specify
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nicker Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other: Specify " '
Other Specify
Minimum
Allowable
(specify units)
























Maximum
Allowable
(specify units)






•








-




-
.


Limiting
Factor
























                                                          o
                                                          (73
                                                          N)
                                                          o
                                                          o
-13-
                                                          Uj

-------
Pumpable Sludges Waste Acceptance Limits As  Received
Are your  pumpabie  sludge waste limitations 'as received" the same as wasw !im:ut;or>
specified in questions 13a or b? If so. specify which table applies (e.t- >3a or L-hi jnd >k:r
to Ub: _
If no. please indicate  the acceptable ranges of all physical and chemicai waste properties that
you consider before  agreeing to receive a waste.   Fill in .only those that apply,  and acJ
properties as necessary,  in the "Limiting Factor" column, indicate whether the limit is j
permit limit I Pi. another regulatory limn (R),  a product quality limit (Q). or  some mrter
technical limit (T). If you have a total specified metals limit and not individual metal limits.
indicate the total specified metals limit and check off which metals are included  in (hi* limn.
Explain any exceptions on a separate sheet as necessary.
_CT
"As Received" Pumpable Sludces Waste Limitations
Property
H:at of Combustion
Water Content
Tc tal Solids Content
Tctal Inorganics Content
Particle/Object Size
Cyanide Content
Su fur Content
Sodium Content
Potassium Content
Ot!ier: Specify
Other: Specify
To:al Halogen Content
Chlorine Content
Fluorine Content
Bromine Content
Other: Specify
Other: Specify
Minimum
Allowable
(specify units)

















Maximum
Allowable
(specify units)













•



Limiting
Factor

















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                                    -14-
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                                                                                                                 I

-------
'A> Received" Pumpable Sludfes Waste Limitations
Property
Pesticides
Funeicides
Herbicides
Insecticides
Rodeniicides
Other: Specify
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
fhallium Content
Vanadium Content
Zinc Content
Other: Specify "'
Other Specify
Minimum
Allowable
(specify units)
























Maximum
Allowable
(specify units)
























Limiting
Factor

























                                 O
                                 GO
                                  O
                                  o
• 15-
                                 LU
                                 cn

-------
      Putnpable Sludges Waste Acceptance Limits As Burned
Mb.   Are  your pumpable sludge waste limitations  as hurncd" ihe same as waste
      specified in earlier questions.'  If so. specify which table applies (e.g.. Ua) anil skip to ::j
      If no. please indicate the limitations on 2!! physical and chemical waste properties as t
      Fill in  only those that apply, and add properiiej  as necessary.   In the  'Limiting Factor
      column, indicate whether the  limit  is a permit limn (P). another regulatory limit (R;. j
      product quality limit (Q). or some other technical limn (T).  If you have a total specified
      metals limit and not individual metal limits, indicate ihe iota! specified metals limit and check
      otf which metals are included in this limit.  Explain any exceptions on a separate sheet j>
      necessary.
"As Burned" Pumpable Sludjts Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Particle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
• Potassium Content
Other: Specify
Other Specify
Total Halogen Content
Chlorine Content
Fluorine Content
Bromine Content
Other: Specify
Other: Specify
Minimum
Allowable
(specify units)

















Maximum
Allowable
(specify units)













•



Limiting
Factor

















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                                                                                                                HTJ
                                                                                                                O
                                                                                                                O
                                          •16-
                                                                                                                UJ
                                                                                                                — i

-------
As Burned" Pumpable Sludftj Waste Limitations
Property
Pesticides
Fungicides
Herbicides
Insecticides
Rodenticides
Other: Specify
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other: Specify
Other: Specify
Minimum
.Allowable
(specify units)
























Maximum
Allowable
(specify units)












•



•







Limiting
Factor ]
























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aa .- «
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-------
      Vonpumpible Sludges Waste \ccepunce Limits As Received
I5a.
Are your nonpumpable sludge waste limitations 'as received" the same as waste
specified in earlier questions'  If so. specify which table applies (e.g.. I3a) and jktp u> !:
      If no. please indicate (he acceptable ranees of all physical and chemical waste properres that
      you consider before agreeing to receive a  wasie.  Fill in only those that apply. jnJ jJJ
      properties as necessary.  In the "Limning Factor' column, indicate whether the limit is j
      permit limit (P). another regulatory lirmt (R). a product quality ttmit (0).  or some other
      technical limit (T).  If you have a total specified metals limn and not individual metal limns.
      indicate the total specified metals limit and check off which metals are included in this limit.
      Explain any exceptions on a separate sheet as necessary.
                                                                                                   -ii!
"As Received" Nonpumpable Sludges Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Panicle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other: Specify
Other: Specify
Total Halogen Content
Chlorine Content
Fli orine Content— -
Bromine Content
Other: Specify
Other: Specify
Minimum
Allowable
(specify units)

















Maximum
Allowable
(specify units)

















Limiting
Factor

















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                                         -18-
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'As Received" Nonpump»ble Sludges Waste Limitations
Propeny
Pesticides
fungicides
Herbicides
Insecticides
Rodemicides
Other Specify
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other: Specify *"' "
Other Specify
Minimum
.Allowable
(specify unitsl
























Maximum
.Allowable
( specify units)







•













- .


Limning
Factor
























                                       o-&£a
                                       * •» S.


                                      pill


                                       *£?*
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                                        o
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NoopumpabI* Sludges Waste Accepuoce Limiii \t Rumtd
I5b.
Are your nonpumpable sludge waste limitations  ,u hurned' the  i.ime .is *a\te
specified in earlier questions?  If so. specify which t.iMc jpphes ic$ .  l.'a i and  skip M |n.i
                                                                                                            ffs
                                                                                                        ^   *="•
If no. please indicate the limitations on all physical anJ chemical waste properties .is
Fill in  only those that apply, and add properties as  necessary   In (he  Limmniz F.Ki»>r
column, indicate whether the limit is a permit limn  (Pi. .inoiher  regulatory limit iRi.  j
product quality limit (Q), or some other technical limit  iT)   II you hnve ,1 tdt.il  spcrcineJ
metals  limit and not individual metal limns, indicate the mial tpecitied metals limit jml check
off which metals are included in this  limit.  Explain any exceptions on 3 separate sheet j>
necessary.
"As Burned" Nonpumpabk Sludfes Waste Limn.itioni
Property
Heat of Com buition
Water Content
Total Solids Content
Total Inorganics Content
Panicle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other: Specify
Other: Specify
Total Halogen Content
Cilorine Content
Fluorine Content
Bromine Content
Oi hen Specify
Other: Specify
Minimum
Allowable
(specify uniu)

















Maximum
Allowable
(specify units)




•












Limning
Factor

















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                                                                                                         oo
                                                                                                         O
                                                                                                         o
                                                                                                         LU

-------
".As Burned" Nonputnpablc Sludges Wane Limitations
Property
Pesticides
Fungicides
Herbicides
Insecticides
Rodenticides
Other: Specify
Total Specified Metals Content
Antimony Content
Arsenic Concent
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercuiy Content
Nickel Content
Selenium Content
Silver Content
rhalliutn Content
Vanadium Content
Zinc Content
Other: Specify
Other: Specify
Minimum
Allowable
upecily units)
























Maximum
Allowable
1 specify units)
























Limiting
Factor
























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                                         O
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                                         to
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      Containerized Solids Watte Acctpuoct Limui Xi Rrcnted

toa.   Are your containerized solids waste limitations 'jj received" the  same js « ute II.T.JJ:. r>
      soecified in earlier questions?  If so. specify which lablc applies (e.g..  IJa(  id ixip t.' .*"

      It no. please indicate the acceptable ranges ot all physical and chemical waste properties. :(ij:
      you consider before agreeing to receive  a waste.  Fill m  only those that  apply, and jjj
      properties as necessary.  In the  'Limning Factor  column, indicate whether  the Itmn ,» j
      permit limit (P). another regulatory limit (R). a  product quality  limit (0). or sorrw oiher
      technical limit iT). If you have a total specified metals limit and not individual metal limns.
      indicate the total specified metals limit and check off which  metals are  included in this limit..
      Explain any exceptions on a separate sheet as necessary.
"As Received" Contaiaerlzed Solids Wasie Limitations
Properly
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Panicle/Object Size
Cyanide Content
Sulfur Content •
Sodium Content
Potassium Content
Other: Specify
Other: Specify
Total Halogen Ccntent
Chlorine Content
Fluorine Content
Bromine Content
Other: Specify
Other: Specify
Minimum
Allowable
(specify units)

















Maximum
Allowable
(specify units)













.



Limiting
Facior

•















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                                                                                                                 to
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                                                                                                                 ULJ

                                                                                                                 UU

                                                                                                                 UU

-------
Ai Received" Containerized Solids Waste Limitations
Property
Pesticides
Fungicides
Herbicides
Insecticides
Rodenricides
Other Specify
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other: Specify
Other: Specify
Minimum
Allowable
(specify units)
























Maximum
.Allowable
< specify units)





















•


Limiting
Factor
























  5|s

•  i'-S
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   O

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-------
Containerized Solids Waste \ccepunce Limits \t Burned
16b.
Are your containerized solids waste limitations 'as turned" the same as »aiie !im:ij:i."-.>
specified in earlier questions,' If so. specify which table applies (e.g.. I3aj and skip to  !"..•
It' no. please indicate the limitations on all physical and chemical waste properties as
Fill in  only those that apply, and add properties as necessary.  In (he 'Limiting Factor
column, indicate whether the limn is a permit limn tP). another  regulatory limit ,Ri,  j
product quality limit (Q}.  or some oiher  technical limit ("H.  If you have a total specitied
metals  limit and net individual metal limits, indicate the iota! specified metals limit and check
oft" which metals  are included in this limit.  Explain  any exceptions on a separate sheet as
necessary.
                                                                                                           •9 «•
                                                                                                           - •< z
                                                                                                          o. a ,- «
                                                                                                          -  o « —
                                                                                                            2 ft 8
"As Burned" Containerized Solids Waste Limitations
Property
Heat of Combustion
Waier Content
Total Solids Content
Total Inorganics Content
Particle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Otter: Specify
Otiier: Specify
To:al Halogen Content
Ch orine Content
Fluorine Content
Bromine Content
Other: Specify
Other: Specify
Minimum
Allowable
(specify units)

















Maximum
Allowable
(specify units)

















Limiting
Factor

















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AJ Burned" Containerized Solid! Waste Limitations
Property
Pesticides
Fungicides
Herbicides .
Insecticides
Rodenticides
Other: Specify
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other Specify
Other Specify
Minimum
Allowable
(specify units)
























Maximum
Allowable
(specify units)




















^



Limiting
Factor
























C £



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-------
                Bulk Solids Waste Acceptance Limits As Received
i
          I7a.   Are your bulk solids waste limitations "as received" the same as waste limitations spec;t:eu .-
                earlier questions? If so. specify which .table applies (e.g.. Ua) and skip to  l~b:
                If no. please indicate the acceptable ranges ot all physical and chemical waste prop~ertie» thj-
                you consider before agreeing to receive  a waste.  Fill  in only  those  that apply,  and joJ'
                properties as necessary.  In the 'Limiting Factor' column, indicate  whether the limit is j
                permit limit {P}. another regulatory limit (R). a product quality limit (0). or some othc'
                technical limit (T).  If you have a total specified  metals limit and not individual metal l.miii
                indicate  the total specified metals limit and check off which metals are included in this limit
                Explain any exceptions on a separate sheet as necessary.
"As Received" Bulk Solids Waste Limitations
Property
H:at of Combustion
Water Content
Tc'tal Solids Content
Total Inorganics Content
Particle/Object Size
Cyjnide Content
Sulfur Content
Sodium Content
Potassium Content
Otter: Specify
Other: Specify
Tot il Halogen Content
Chlorine Content
Fluorine Content
Bromine Content
Othur: Specify
Other: Specify
Minimum
Allowable
(specify units)

















Maximum
Allowable
(specify units)






•


•







Limiting
Factor


















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                                                                                                                            O
                                                                                                                            O
                                                     •26-
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-------
'As Received" Bulk Solids Waste Limitations
Property
1 Pesticides
Fungicides
Herbicides
Insecticides
Rodemicides
Other: Specify
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
1 Nickel Content
Selenium Content
Stiver Content
Thallium Content
Vanadium Content
Zinc Content
Other: Specify
Other: Specify
Mininium
Allowable
(specify units)
























Maximum
Allowable
(specify units)
























Limiting
Factor

























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n
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-------
                  Bulk Solids Waste Acceptance Limits A* Bumed
/I
            l?b.   Are your bulk solids wasie limitations 'as burned" ihe same as waste limitations specie.! .*
                  earlier questions?  If so. specify which table applies (e.g., I3a) and skip to  ISa;	
                  If no. please indicate (he limitations on all physical and chemical waste properties us nurnei.*
                  Fill in only those  that  apply, and add properties  as necessary.   In the 'Limiting Footer
                  column, indicate whether the limit is a permit  limit (P). another regulatory limit iRi. j
                  product quality limit (0). or some other technical limit (T).  If you have a total specaied
                  metals limit and not individual metal limits, indicate the total specified metals limit and check
                  ot'f which metals are included in this limit.  Explain any exceptions on a separate sheet 3*
                  necessary.
"As Burned" Bulk Solids Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total Inorganics Content
Panicle/Object Size
Cyanide Content
Sulfur Content
Sodium Comem
Potassium Content
O:her: Specify
Other: Specify
Total Halogen Content
Chlorine Content
Fluorine Content
Bromine Content- •
Oner: Specify
Other: Specify
Minimum
Allowable
(specify units)

















Maximum
Allowable
(specify units)

















Limiting
Factor

















                                                                                                                         3   "
                                                                                                                              .
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{"As Burned" Bulk Solids Watte Limitations i|
Property
Pesticides
Fungicides
1 Herbicides
I insecticides
f Rodenticides
Other Specify
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
_ Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other: Specify
Other Specify
Minimum
Allowable
f specify units)
























Maximum
Allowable
(specify units)









•


1











Limiting |
Factor J




I



























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                                                            71
                                                            o
                                                            o
•29-
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-------
      Dry Solids Waste Acceptance Limits As Received
IS:.   .Are your dry solids waste limitations "as received" the same as waste limitations »pei:ir:eu' .n
      earlier questions?  If so. specify which lable applies (e.g.. 13a) and skip :o 135:
      If no. please indicate the acceptable ranees of all physical and chemical waste property that.
      you consider before agreeing 10 receive a waste.  Fill in only those that apply. jnJ jdj
      properties as necessary.  In the "Limning  Factor" column, indicate  whether the limit is j
      permit limit (P). another regulatory limn (R). a product quality limit (Q). or some other
      technical limn (T).  tf you have a total specified metalj limit and'not individual metal limits
      indicate the total specified metals limit and check off which metals are included in this limn
      Explain  any exceptions on a separate sheet as necessary.
ff&Sf j
|S a!
*aai
BgSJ
*•»:
0.0. ;-
".As Received" Dry Solids Waste Limitations
Property
He at of Combustion
Water Content
To:al Solids Content
Total Inorganics Content
Particle/Object Size
Cyanide Content
SuHur Content
Sodium Content
Potiusiutn Content
Other Specify
Oth :r Specify
Totiit Halogen Content
Chlorine Content
Fluorine Content
Bromine Content.. . . -
Other: Specify
Other: Specify
Minimum
Allowable
(specify units)

















Maximum
Allowable
(specify units)

















Limiting
Factor

















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t".)
'As Received" Dry Solids Waste Limitations
Property
Pesticides
Funeicides
Herbicides
Insecticides
Rodenticides
Other: Specify
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other: Specify
Other: Specify
Minimum
Allowable
fsoecifv units)










,













Maximum
Allowable
'specify units)












•








•


Limiting
Factor

-






















                                                                   5S;

                                                                   .|||

                                                                   •5a<
                                                                   'I;'

                                                                   .0."- I
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                                                                   2 tt M
                                                                   c ^ 52

                                                                   Is"

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      Dry Solids Waste \ccepuoce Limits As Burned
iSb.   Axe your dry solids waste limitations "as burned" the same as waste limitations jpecitiej ;n
      earlier questions?  If so. specify wrich table applies (e.g.. 1 ja) and skip to I* __ _
      If no. please indicate the limitations en all physical and chemical waste properties J> hurneJ'
      Fill in only those  that a^ply. and add  properties  as  necessary.  In the  "Limiting Faeirr
      column, indicate whether  the limit is a permit limit  (P). another  regulatory  limit iRi. .1
      product quality limit (Q), or some other technical Itmti  (T).  If you have a  total specified
      metals limit and not individual metal limns, indicate the total specified metals limn and check
      off which metals are included in this limit.  Explain any exceptions on 'a  separate  sheet j»
      necessarv.
                                                                                                              *
:~0 § 2
'As Burned" Dry Solidi Waste Limitations
Property
Heat of Combustion
Water Content
Total Solids Content
Total inorganics Content
Panicle/Object Size
Cyanide Content
Sulfur Content
Sodium Content
Potassium Content
Other: Specify
Other. Specify
Total Halogen Content
Chlorine Content
Fluorine Content
Bromine Content
Other: Specify
Other: Specify
Minimum
Allowable
(specify units)




»












Maximum
Allowable
(specify units)

















Limiting
Factor

















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                                         -32-
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'As Burned" Dty SoIWi Wasie Limitations
Property
Pesticides
Fungicides
Herbicides
Insecticides
Rodenitcidei
Other: Specify
Total Specified Metals Content
Antimony Content
Arsenic Content
Barium Content
Beryllium Content
Cadmium Content
Chromium Content
Copper Content
[Lead Content
Mercury Content
Nickel Content
Selenium Content
Silver Content
Thallium Content
Vanadium Content
Zinc Content
Other: Specify
Other: Specify
Nfimmum
.Allowable
(specify units)
























Maximum
Allowable
(specify units)





















.


Limiting i
Factor i
























                                       a a g-
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IV.    EPA has identified several types of debns thai may be contaminated with hazardous »j>tc»
      Please indicate whether you accept or plan to accept any of the tallowing types oi ruraf^u-.
      waste contaminated debris at ihis facility,  and any  physical  or chemical conditions ,?.»!..
      restncnons or limitations J in addition to those specified above which would be required UT
      you to do so. .Vote any important acceptance conditions in the table and explain them on the
      page following the table. If one of the types of debris  may be included in wastes you recent.
      but you are uncertain, please check off the  Don't Know' column.
(Uwdous Wuu Coausmtud Dtbrij Acetpunce '
T>peo(Oebns
Common Cloth Materials (e.g.. rigs, mop
heads, blankets, or cloihinj)
Personal PrOiectiOB Equipment (e.g.. Tyvec
suits)
Paper or Cardboard Material!
: Filter Cartridges
Wood Materials
Rubtxr Objects (e.g., tires, boses)
PVC Pipe
Oiber Plastic Debris
Class Debris
Ceramic Debris te.f.. semiconductors)
Metal Objects (e.g., pipes. vtNet. pumps. BUI*
and bolts)
Asbestos Maiertals {«.&.. sbifigles. iasulatios)
Non-Soil Oeolopc Material (e.g., rods)
Concrete Debris
Refractory Brick
Other Bricks
Slag
Intact Batteries
Batterv Cases
Electronic Components (e.g.. printed circuit
(wards)
1 Electrical Wires. Switches, etc.
Accept
Now
(YN)





















Plan to Accept
Bv Julv 94
'(YN)





















Acceptance
Conditions
(In addition to abovei





















Done •
KJIO*
(/i i







-

I

I

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1
1



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                                          -34-

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                 20.    Please explain any debns acceptance conditions noied on the prexious
1
                                                                                                                         •z
                                                                                                                         'O
                                                                                                                          •4
                                                                                                                  P-S-sr
               20a.  Do you accepi hazardous waste soils?  [f so. under what conditions or limitations?

                     How are (hey processed and burned?
                                                                                                                      o
                                                                                                                      C/3
                                                                                                                      10
o
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                                                    -35-
                                                                                                                      cn

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                   C.    Permit Conditions



                   21.    Please lilt all RCRA waste codes you are currently auihorized and willing to

                         and bum as of 7/23/93 (i.e.. you have received full permit or interim status approval i

                         Attach a separate sheet as necessary.
.-?.'


:::'j»
3 S


l»
                   21    Please list all additional RCRA waste codes you are seeking permit or interim status

                         modifications to receive and burn by 7/23/93 (i.e.. Pan A will have been submitted

                         by 7/23/93).
  o
  C/2
  to

  71
  o
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                   23.    If you are not authorized to receive and bum "newly identified" wastes F037, F038,

                         F039, F032, F034. F035. K088, K14MC145. K147-K131, or D018-D043, what would

                         you have to do to be authorized for those codes?
                                                        -35-
                                                                                                                              Uj


                                                                                                                              -c


                                                                                                                              —I

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24.    Please till m the following table tor all auihonranons you require in order :o rum
      RCRA hazardous  wastes.   Consider all  permits that  limit your ability to ?urn
      hazardous wastes. Also indicate when you expect final authorizations.  Please use :he
      following permit status codes in the current status column:

      NR -  Permit ^ot Required (explain in note)
      FP -   £utly Eermitted to receive RCRA hazardous wanes
      PM -  £reparing Permit Modification for Additional Wastes
      SA -   Submitted Complete Applicaiion and Awaiting Response from Issuing Agency
      .VIA -  Modifying Permit Application for Additional RCRA Wastes
      IS -   Interim Status
      ND -  Currently Responding to Donees of Deficiency in Application
      PH •   Awaiting £ublic Hearing on Permit
      OT •   Qjher (please specify):
    * S f
'   irB
  a o, •- »
  • rt W ^
Authorization Required
Federal
BIF
RCRA Storage
RCRA Treatment
Clean Air Act
Other (specify)
$tttf
Hazardous Waste
Air Emission
Land Uw/Siring
Other (specify)
Local
Hazardous Waste
Air Emission
Land Use/Siting
Other (specify)
Authorizing Agency Name
and Phone Number













Current
Status













Expected Date
of Authorization













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                                                                                                                                                 ••a
                                                                                                                                                  i

f
                        Please describe any permit changes other than R^rfTnrTmrnn tnal wl!, he      ^
                        for you to continue to burn hazardous waste as at present or  to begm burning
                        hazardous waste in any of the kilns mcluded in this form.  Also indicate when v™
                        expea the changes to be made, and when and how you would have to charge vour
                        current practices if these changes are not approved.                     "  '
                                                                                                                               O
                                                                                                                               GO
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                 26.    When do you plan to submit a Pan B Application {month and year)?
                                                      -38-
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                         Do you plan to make any changes 10 the hazardous waste burning practices
                         facility before July 1994?
                                                  	Yes
                                                  	No
•.•
:S.    If you do plan 10 make changes to this facility, please describe the nature of each
      modification (including lain number for specific changes), when you expect it to be
      completed and fully operational, and the effect it wilt have on this facility's hazardous
      waste capacity.  Include modifications to waste receiving facilities, fuel processing
      systems, waste feed systems, analytical equipment and facilities,  and air pollution
      control devices.  You may attach appropriate  sections  of  your  precompliance
      certification that describe these changes if convenient.

      a) When (month or quarter, and year):
                         b) Effect on hazardous waste capacity:
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                        c) Modifications:
                                                        -39-
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                                                                                                                                                   I

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             APPENDIX C


AVAILABLE CAPACITY ANALYSIS TELEPHONE LOGS
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                TRANSMISSION  REPORT
THIS DOCUMENT  WAS  CONFIRMED

(REDUCED SAMPLE ABOVE  - SEE DETAILS BELOW)



   ** COUNT **

TOTAL  PAGES SCANNED    :   2

TOTAL  PAGES CONFIRMED  :   2


**» SEND ***
No.

KE2MOTE STATION
ay i e ia+uas M uos ia* 13
START TIME l»K\lli>S>C.\CillS
+ -.20-94 1:34in| | i ...i-j L'/ 2
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No.: OfLKATION M MBi;R 48 : 4HUO8PS SEUECTI.O l.l   I KKOK fl HUM-XT  Ca : C2 OAtMl NlfATUlN

TO : COLt.tD BY KEMOTE SF = STORI: * FOR»AkU XI   Kl l.\> IMTIATK  KS : KI-ll-AV .STATION

Ml) : SEND TO MAILBOX  I>C : Pt>U.I\G A REMOTE Ml-   ill 1.1 I -llit.l.tNC  KM : KI-XIUU- Id MI-AHiKY

-------
                                                              PBl    cfR 20 '94  12:13










                                                                   s*rt--.-l» 3««M|«. V» M(W
       A>TUS
           FAX TRANSMtTTAL SHEET
4
                     (Including Cover Sheet)
a^-x^r    >^y
  s**<»;£4'
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C0rvC**it  t*~tvt
                    If there are any problems with this transralttaJ, please call

                    459-3475, extension:   grj-/f   . Thank You!
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4-20-94 :
                                                             u. ru_    it-K <)}  *

                                              JCF 1«c«rp«med-9l«a469514005I24l35;» 2/ 2
      Aptes C«lfcy*ine, ICiuHUti

      Apttu. a Wettbihouw eompuy, ha both TSCA «nd R.CRA P«n 0 penuib. The
Iniueator uoit ii • «l«atDj rouiy lula with * Ittennil mpui oC 61.9 MMBtmlxiur. TTw fadliiy
an «acpt ligutdi; purap*M« tfudja, ixmpvKpibie tludfa, ouauloeraod Mi)illd« into the tocuortlM unit.

                 capacity InfonaAtloo proyMed by Ui« (Kilily indudod qualities at wwie
                *"*"''••••" pnctkcl buraiac 
-------

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{REDI'CHD SAMPLE-  AliOVII  -  SI-:!-:  UI{TAILS !iKLO\V

   **  C(;LAT  **
T07AL PAGES SCAXXHl)    . :   2   .
TOTAL PAGES CONt;IRMf{l)  :   12
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BPR-22-19S4  a-IK   FROM
                                                 TO
                                                            91"e392497acitjfbiclf-i'ttadty uujpb fa»
     U aewtj Iklcd ind ac«V ifc*UScd waca bdwftnj wtn Utai extfA ibe tnriciij
cfc.r««e*dE(53PR4W6a.T.K»teySqiUwl>er>*J
     bctnuadvcoedUeetid. Onnfid«i«d daaew* •• 0>c proQe wOJ bo htakcd out In UK oou
-------
 'I
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      This fwiitj tu« * RCRA hit-B ptmrlt-'Bd operate me tlaatag rctuy kiln inainentnr
      he fiatta M»qio> Ikiiri, pumpsiJe sludges. cbottuKiixd sali^, bulk JOlid», sad jofc.
                     mil The fiatta M»qio>
                              '    '
                                                          13CA
                     Hity^aPCtoivrti, iquJcfbc >atu> tf lidt noiAK-thc-4W>>3u »ey: The bdotntor ijstaa
                     M Cbfe faeilily a 4 sfog|faf rotty kin wilh en sHrfaunft. Thit ijKien ha a tbimntl Input of ytS' rfO
      Tkis btaity ii equipped wilh icven! meekninnt frw footing v»lr nrtn tbc lUofog rutary
frfr*  Uqotdf ire mjcded dircctiy lion • tUnge oak law ibo tOi ind.'ur afiabuimx dunibcr.
Fu«f>Ii«na|iw^tT to*w Ono 10,000 ocnlipohc, ire fed vu i cement pump.
Bulk .vXid» tat wovmuyttik tludga «re pUocd bto bohlhig tonia. Froai lb«w tmb, the »»te»
me wovol ty • dRtvbe> to M ap«oo tccda vbae :tc WOK b t&LQjgf-r °"" '^ Ula fc«J
thubs. Omtaineriiod «olid« tbti do not require tfuaWtet (c.^. SaiMJvv; fed djnxiljr into the kih
via 13 etevuor fe-1 tyttm. Cooutoentod KAb Md bulk toll* tbti require ihreckfinj tre
pwoesxrf t&rough * ifaceddn pnot to teiaf pi*c«d bto iionec tanta.
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          FACSIMILE
                                               ICJF INCORPORATED
                                            P-**ll.t{*« 0whf**ltfcJna MWTTO Survey*
                                            cm v*«h
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V» tcw««*«aa«t^«k or »l4*rn*i«iy. m«rk •pwetfla inftorBtmJoD th*t aHowt<5
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    KJ*Uk «C C7O>> 21»-343« or fma* rojpofia** •<» b^cn •• C'OI) fr»«-l#T4O by rVlvvy. April 33ad.
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                         TRANSMISSION   REPORT
       THIS  DOCUMENT   (REDUCED   SAMPLE  ABOVE)
       WAS  SENT

           #*  COUNT  *#
           #    4
«*« SENS *»»
KO| SEMOTE STATION I. 0.
1 Toa 572 teai
START T:ME i
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       Chemical Waste Management, Saitget, Illinois

       This RCRA Part B permit led facility operates three dry scrubber incineration units. Two
are fixed hearths and one is a rotary kiln.  Each fixed hearth unit has a maximum permitted heat
release of 16 MMBtu/hour. The rotary kiln has a maximum  permitted heat release of 50
MMBtu/hour.

       This facility can accept most physical  forms of wastes. Liquids are blended in tanks and
transferred to atomizers for direct injection inio the incinerator unit(s). Purnpable sludges arc
injected into the incinerator unit(s) via a sludge  lance.  Nonpumpable sludges and containerized
solids are repackaged into burnable containers and ram-fed into the incinerator units.  Bulk solids
are unloaded into pits and transported via clamshell into (he roiary kiln unit.

       This facility submitted its survey independent of the set provided by HWTC. For each
unit and physical form of waste, this facility reported waste quantities burned during 1942 and
maximum practical burning capacities.  These estimates .ire included in the aggregated CBI
estimate in Exhibit X.
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       CWM Chemical Services, Chicago, Illinois

       This RCRA interim status facility is not currently operating and is awaiting EPA
authorization for TSCA and RCRA Part B permits.  The incinerator unit at this facility is a rotary
kiln with a thermal input of 30 MMBiahour.

       The feed mechanism for the single unit at CWM consists of a drum conveyor and ram-
feed for containerized solids,  tn general, bulk solids and pumpable sludges  are not accepted at
this facility. Nonpumpable sludges are generally accepted only when containerized.

       This facility submitted its survey independent of the set provided by HWTC.  The facility
reported confidential maximum current practical burning capacity for liquids and containerized
solids.  Because this facility is not currently operating. EPA did not include  it in the  national
capacity estimates.

       Chemical Waste Management reported that expansion plans will depend on the outcome
of Gnai permitting decisions. This facility indicated that it is seeking authorization to accept the
Phase II waste codes DO 18-043.
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       CWM-Port Arthur, Port Arthur, Texas

     '  This RCRA Part B permitted facility operjlc* a rolary kiln system (hat has a thermal '
input of 175 MMBtu/hour. The facility has applied fur ;i TSCA permit to burn PCB-
contaminated wastes.

       This facility accepts liquids, pumpablc slopes, containerized solids, nnd bulk solids.
Several feed mechanisms exist for feeding waste iaio the rotary kiln. Positive displacement pumps
are used to feed pumpable sludges. Containerized solids arc fed into the unit via a ram-i'ucd
system. Bulk solids arc shredded and charged to the kiln hy a chute.

       The facility reported waste quantities burned in IW2 and maximum practical burning
capacities as CB1. These estimates arc included i.i the aggregated CBI estimate in Exhibit X.
This facility can accept the Phase 11 wastes DOIS-D043. KI41-145. and KU7-151.  CWM
indicated this facility anticipated increasing operating hours hy 50 percent in 1993-1994. and
planned various process improvements for the third quarter of 1993 that will improve on-line lime
and allow the facility to accept CERCLA wastes.
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       VACTSSIIVIIL.E:
        ANSMirr
        RECORD
                                       HWIX: Sfvr*«y*
Contractor for |h« Fhu.o U L4.1U /
                                   fttvn^nf for l*m 1-
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THIS DOCUMENT  WAS CONFIRMED
(REDUCED SAMPLE ABOVE - SEE  DETAILS  BELOW)
   **  COUNT **
TOTAL PAGES SCANNED    :
TOTAL PAGES CONFIRMED :
                                2
                                2
 *** SEND ***
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BUI 8G* 232U
START TIMU
4--JU-'.M |:U
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                 ENSCO, El Dorado, Arkansas
                 ENSCO operates three rotary kiln incinerators at this RCRA Part B permitted facility.
           Each kiln can burn liquids, pumpable sludges. nonpumpaMc sludges, containerized solids, bulk
           solids, compressed gases, and soils.  Thermal inputs of Iho three incinerators arc 70 MMBlu/hour,
           140 MMBiu&our. and 64 MMBlu/hour.

                 ENSCO submitted confidential business information on quantities burned in 1992 and
           maximum practical burning capacities. These estimates arc included in the aggregated CBI
           estimate in Eihibit X ENSCO accepts the Phase II waste codes, D018-043rK}44-US_and K147-
.- "
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   **  COUNT  **
TOTAL PAGES SCANNED
TOTAL PAGES CONFIRMED
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                                                                                                                                          SP .l^tf""!
                  Laidlaw Environmental Services, IDC, Roebuck, Siiulh Carolina

                  This facility is fully permitted but the permit is under appeal. Laidlaw operates one liquid
           injection unit that injects and burns pumpablc liquids. The confidential business informalion
           provided included quantities of waste burned in 1992 and maximum current praciical burning
           capacity. These estimates are included in the aggregated CBI estimate in Exhibit X.

                  Of the Phase II wastes, this facility accepts DOlX-43  waste codes. Laidlaw is seeking—
                         receive and burn K141-U5 and KI47-I5I waxlcs.
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          RECORD
                          • M** I »* ni**—r  	gWUfka. viriMnaiji aaucM i*M*r

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                  nt 1*11* «3*»n«Pf»»i«»«J*»n«»* to •«»
                  €*» *!»• r*«jii*y fi**«nU;*. To (h
                        C.'UI t
                                  »w.vfn«n». \Va mu»1 cn*|MiM»U« thm Ifrta Agency bi not
                             en Afl**rw4»* wJ« MT rewrite tlirlj n«-t:IKm«. I*|CM«C cntl Kcter
                            BM« «»» hln% »t
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THIS  DOCUMENT WAS CONFIRMED
{REDUCED  SAMPLE ABOVE -  SEE DETAILS BELOW)
   **  COUNT  *#
TOTAL PAGES SCANNED
TOTAL PAGES CONFIRMED
2
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So.
1
REMOTE STATIOV
SO23U58aiU
START T MB: |w KM ION , »I'AGI-S
1 I
\K)Dli j KI3( l.TS
KC 'coMflJ-TKD
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                          TOTAI.   <|.IMI r,7~  a
 VJTK:
 v». = OPERATION; \IMBER  4» =  •taixiui-s si:i.r;fri;i) i.t ; i KKOK COKKI-CI   ca :  c	  	
 PD : i>OLLKD BY REMOTE  SF :  STORIi « I-'MK»AKU  Kl • KH.AY IMTIATE  KS :  KI3.AY STATIiiS
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       L.W.D. Inc., Calvert City, Kentucky

                                                      nil"r>y ifte Male regulatory agency.
                                                      rale under interim status while the
appeal is under consideration.  L.W.D. has three incinerators al this facility:  one liquid injection-
unit and two rotary kilns. The liquid injection incinerator burns liquids.  The ruiary kilns burn
liquids, bulk solids, containerized solids, and purr.pahle sludges.  The liquid injection unit has a
thermal input of 40 MMBtu/hour. The rotary kilns have thermal inputs of 50 MMBtu/hour and
100 MMBtu/hour.
P-g-sr!
                                                                                                .

       This facility submitted its survey independent of the set submitted by HWTC. The facility   .l
provided information on quantities bumcd in 1992 and nuximum practical burning capacities.
These estimates arc included in the aggregated CBI estimate in L\lnbit X.  LW.D. Inc. accepts
the Phase II wastes DO 18-043, K141-1-45. and K147-I5I.
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       FACTS IMILE
     TRA1M S iVI rXTTAL.
        RKCO&D
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                    .         .  ,
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THIS  DOCUMENT WAS  CONFIRMED
(REDUCED  SAMPLE ABOVE  - SEE  DETAILS BELOW)
   **  COUNT ##
TOTAL PAGES  SCANNED    :    2
TOTAL PAGES  CONFIRMED  :    2
 **« yi-:\D ***
 Vn. i  KI-IMUII-: sr.vi'KA   i
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-------
FACSIMILE
TRANSMITTAL
RECORD
ICF INCORPORATED
9300 1« Hrtm* l*rf«, Vtjjnn 220J1-IW l:a Minuter. (703) i;ii.2«»
TOi
FROM:
sufuwrr-
Date:
FaciliUct SubmilUng HWTC .Surveys
EdBcrjicr FAX: 31»-Z35-rttM
ICF Incorporated. EPA Coaimctor for the Phase IT LDR
Cap/uaty ADft)y*u
CBI Iwue* Attnciatcd with Data Gmtainol in Ihe 1992
HWTC Survey

Pftjps I of 2
                                                                      a c. tr
                                                                        3   "
                                                                        5 "a
                                                                        ^° 5
                                                                            R
       EPA it current)? writing the capacity backpuund document I'nr its LOR capacity analysis Air
Phase n  acwly  bled and  newly identified »•*.<(«* including wuio  ll>«  uchihil  the  tnxicity
chiratdcriitic (5ft PR 4MI92, Tuesday September 14,1V93). As in Ihe past (e-g., the Phew I Capacity
Background DuvuuttHt), EPApUtu 10 include hrief profile* efcsch amc of (hi* informttlinn
n in (be public dumaio. the cotirc 1993 HWTC' Surey rcjpomci have nevertheless hcun tuhmillcd
at CBJ.

       The purpose of thi> corrt»pondcnco  is to conSna the non-confidentiality of ipecUJc diita
Clc-m^nU contdineJ in the f»cC!ity proillet.   To this  cod, please  review the attached  profile and
wnfirm that ic dooi nnt waiaia CBI iarorm*tit>o, nr alicroately. raark specific in fdrmatinn ihachould
be trcauxJ ».< ccinfidcniiiy.  CoofuJcnlial dwncnu m the profile will he blflnlced out in Ihe non-CBS
vcrsfcm nf Use l>haic il Capacity Background Document We mutt emphwizc ihtl  the Agency'» not
providing no opportunity ftir fecililtci to otherwise edit or rewrite ihctr sectkinx Please call Pclcr
Klein ai (7IQ) 218-26.^ or f« rvapooses in niro V. (70?) «4-97-in by FfitUy. April 22nd.
>*«r
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-------
                                                                516 235 O233   =.C2/B2
       Nortlt» Gvporatlm, Coho**, .Vtw Vork^-
       Tb» rcccaUy permiucd Incinwaiion laciljty operatci two toUry aggregate bins that burn
liquid* and pumpcMe dudgca. The fa'hw »« RCRA-permitted •» incinerator*.  Uquidi are
mjec!«sd and tlodja arc pumped into Use kiln. Each kilo hoi 4 thermal loput of 62 MMStu/hour.
New York officUh arc considering a permit moJiCaUon to incrcaw Kortite'i tolkl Teed capacity.

      Noriiu (ubmiilcd cnnfidentiil ta/orm*Jioo oa quantititt uf uujto burned Co 1992 aod
nndmum practical b'jrninj capacities. These «timaies are included la the aMrcttCed CBT
eiiiinjce in Exhibit X. Of tie Pbwc II w«te», ike facility currently acecpb DO 18-043 waste*.
Norlhe a (eckiaj a peraut midiCcalioo tu accept die remaining Phase II wanes.
lifl
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-------
         FACSIMILE
          APtfSMITT
          RECORD
                                      ICF* INCORPORATED
                            •»OQ L~ Hl»»-»y
                                    Y*»cllt«fM 9ubinJiri»c KWTC fti
t«»eorpcar« I «•*!. X3PA. Contractor for ib« f*h*«* n L_DJl.
                          D»ta: <4'15>94
    aanflra tfe*« It do** ool ooalmin. Out tziform»ili«*ly. murk «p«cijr)c feA>rm*tJou lh*t *hould:
    bn trwMftt*d] *» ooikCIdMuatt*!. CooAd«nxjl*4 n|«fncnu tn thA pronl* **ill IMW bl*o)r*d out iti Lh«» Don^CBl
    v*r*Ioa ef tfe* Fb«*« U C«p»ett> llmckground Docuaiant. >V* rnu*t «mph*«1t* tb»t the /\g«;ncy !• not

    Klcta mi (7O.*> 21H*2A3* or f*» r*«pozuo* to him •« (7OJ) ».i4-*7-*O by FrldMy, April X£n«l.
                                                                                         ?SJJ
                                                                                          c ,- 2
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                    TRANSMISSION  REPORT
      THIS  DOCUMENT   (REDUCED  SAMPLE  ABOVE)
      WAS  SENT

         **  COUNT **
         n    2
**« SEND ***
NO REMOTE STATION I. 0. |
1 213 932 
-------
«=R-ia-19S4  UJ29
                         Nwwra
                                                  TO
                                                                             P.Ot
           Xtei«-Poik» Bulc Ctadab Comffsj, Hmmn»< toilwu


           Tkk bdlhy nfeeittcd coafldeetU iafotnitioa on qumlitioi boraei ID 1992. tod xMlmun

      ertedet] bundsi ctfidqr. It b gpewtag »iih ta btttim tuttut EJT penniu Tbs bduttiW

      fttfManttluifatfiiiytruraillquiJwBMtoaly. Rhae«-Poul«c, tknmond, Kcepu *U Phue 0

      wv«u)da: D01WMJ, K14M45. ttd K147.JS1.
            Port-tt" b.-uid lax Iran tmi-ita! me-no 76711
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KA.CSIMILK
1-RAisrsMrrrA.i.
FHTCORI3



IOK INCORPORATED,
K*t,:^«'»«»1",%K7TA^,r
""""• i^Jisj;!!1:::^- CI'A ••-"••«"" '••'  to liltn *>t
                                                                         I
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                 TRANSMISSIOX'  REPORT
THIS  DOCUMENT WAS  CONFIRMED

(SEDUCED  SAMPLE ABOVE  - SEE  DETAILS BELOW)



   **  COUNT **

TOTAL PAGES  SCANNED    :   2

TOTAL PAGES  CONFIRMED  :   2


*** SEND ***

•>.
1
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a«W7W
START TIME
•1 -ao-!H 1 1 : KiAM
{» K \TlDNUl
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No.: OPKRATION NIMBK8 -18 : KilJUliCS SKLKCTIJ) 1C : I KKuK COKRI-XT  C^ : CL> OWH \ IC'ATH'N

I'D : rULLkD BY REMOTE SI' : STllkK « I-'ORHAKD  Ki  KII.\V INITIATI:  KS : kM.O STATION

W : SEND TO MMI.BOX  I-G : HH.I.ING A KHMUTh «••  Mil I I I'OU.I \G  KM : RI-XT'UI: Id MliMilK^
                                                                          UJ


                                                                          —I

-------
(fP RHdNE-POULENC
     RHONE-POULENC BASIC CHEMICALS COMPANY
     Baton Rouge Plant
     P.O. Box 628
     Baton Rouca. LA 70821
     (504)356-7111
                                   Q.QDGEDI]  £
*!*!
                                                                               » S
                                                                             P-^tr^
   ° g
    M
                                                TIME:
      FAX NUMBER ................. (504) 359-3705
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      IF TRANSMISSION PROBLEMS OCCUR, PLEASE CONTACT:

      PHONE NUMBER	(£04) 359-3772	Dochla Speor
            J
                    &n-1»r?f ;/> Pttfowiet rr-tlt M /.'./i.i
                                                                                uui

                                                                                --J

-------
                                  ^   ifo  ;     Uf Uetrp.rr.td-
8S93?03:
FACSIMILE
TRANSMITTAL
RECORD
ICF INCORPORATED
MOO L.-C H!*mny FKiriM, Virginia 20,'l-ia;7 KM ^ui)1^.•r f?oj) VMV740
TO:
FROMi
SLRIEtTi
FKili:i«« Submitliuf HWTC Survey*
Ds»n SuKwlor FAX: J04-35«M705

ICF ln:orpin»U:d. EHA Qmlracipr f»r Ihc Phnse 11 LOR
C»pac;(y Anatoli*
CBI luue* Aiuxi.itcd >iih Dxl.1 Conixinc J In
HWTC! Survey

Dite: April 20, IV94
the 1UB2

Pfl£C I of 2
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                                                                                                                      n
                                                                                                                      C/3
       EPA B turrcnllji writing the c»p*city'h»ckjroand iIcKumc:il tor it* LOR capHcily »nhl)i« for
       II  newly titled  HIM! newly identified waitu including WMIM lh«l cxbfhil ihc ton'cily
ch«ricterh(ic (38 PR 48092, Tuctdty September 14, l'W3). Ai io the put (c.j., the Fhiuc! Opacity
B«ckjfojnJ Document), EPA plaai lo intrude brief profile, of cacli eommcrciAl comhwiiun laciiity
ia iu ttipucily  bnvkyround documeol. Tbo«e fpcJIly pmfllta totildin infornatloo nn «xch Facility
tnclmJinft Ihc unit type*, waitex ncctpled, nnd hem nslcttc rytinp. Alihrnifih vimc ot thlt infnrritlion
i» in ihc public itouutin, ibr entire 1993 HWTC Survey reiponxc* h«ve nevenhdcx keen nuhmitir.il
uCBI.

       The purpose oCthii coires{nmdcncc  ii in Biafirm (he rton-confideiiiiiiUly of specific data
otcmcnlt contained ia the hdlity proGJti.   Tn  ittis  end. pleuc icview tin: utuchcj pntfitc  nnd
omfinn that it dtw* mil cum dill CSt inKirci»lidQ, nrultcinalely. murk kpccitie Iftfotminion that shuulJ
ho irculc'U w ennfidenitoL <^n(1dential ctanenti ji (he profile will he hlxnlced uul in Uie non-CBl
ventun of the Phaw n Opacity Hnck^rouod Dot-j.-ncr-L We mtut ctnphuize ihut  Ihc Aj(tncy in not
pnnridiai ui nppiirli.nily Tor fatililia lo  otberv^w edit or rewrllc  Lheir ict-Uimt.  Plcs.ic oil! Pclcr
Klein Hi. (705) 218-2636 or fm raprtntci  to him ct (7p3) 934-7740 hy Friday,  April 22ad.
                                     o
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-------
  25 '3*
FCF  JMJOWORATE)
                    R-Cr-C ». Thac
iacioenion h«w^benn«l input mttap of 170 MMBtu/ht.ur «nd 234 MMBtu.'hout. 'I hb (aciliiy
cm accept U({ut(I( nod pump«ble uludgti. The punpahlc dudge* m»K either be »luuiul IT hive a
*u/fideotly knv viiavity lo be injected liiui the furo*.v.

      Rbuoc-Pcmtenc did not tufcaic quuelstiet binned nr miu;«um prucUcel capacity
Informttkn for 1V92. It did, hnwcver. report (he iinowot of wutc received, itored and prixxutd
at the futility in 1991  Therefore, EPA htl tttuntcd ihni IhcK fep.irttd amount! reflect :he
hcuniuui wttto burned in 1992 11 mil m (h*  iif.icM huniiiU'iujntitf  Of the Phwie H Mtt'.e
ihii facility can accept DCI8-DWJ
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      ElH^ltj£fi^»>i3 I^Ov«a4«ril). iLl'.'X. |»l w

      in ii« vi.Ht.'».^.«tv !"•*. W«iv«*fntl tjw.-iy>n

      trwlt*

TOTAL  PAGES CONFIRMED   :    li
                            !.;•; M.
 ••.on;:

 \-. • Of'C-KAf l'>\ '.! v; ! ,;  iii   !",.•• >!•.'•; -,' I ! i I.

 IT) : I'ui.i.Kl) iiv X!-:\i-'ii-:   r   :;ii-M; ••• t- -;«•!;
 ^!!i • r;t-:\u iu VMI.H.-.X  i-w   i'
-------
rP RH&NS'POULENC
  . Sf • ~-S -.— •
   "> lE-POULENC BASIC CHEMICALS CO.
   f o'»« »'i
            PACSIMTLg    COVR B
             rot
        Coapanyi
           PDona:
            FOX:


            rroai
         coapany:  RHdWt-POOLOfC, HOOSTOW
           Fiion.:
                              - 5V J/
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      tnel cover:
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-------
FACSIMILE
TRANSMETTAL
RECORD
ICF INCORPORATED
9?0n 1 ce Hieft-^J FtMn. Vipai* ZZOJM3R fk* Humber (TO) m-W4fl
TO:
FROM!
SUBJECT:
Ftciljtit* Submitting HWTC Surveys
7;ooy Ibmillon FAX: 7I3-9W->*31
l^F Tneorporated, EPA Gnicrtetor for ibc Fhast H LOR
Ctpcciiy Anatysa
C3I [rfvxa Avocialcd with D*U> Cnnuimcd in the 1992 t
HWTC Survey

Due: 415/94.. _ Page 1 of 2
       EPA is currently writing tbc cipaciljr beettittuod docupeni for id LDR cipscity anaJjio for
Phuc  0 newly listed and  ncwfy ideatiGed;.wi«ui Including wttla  that cahjtril  (he ifixJcitf
chamuiriKfc (58 Eg 46092, Tu«diySef>lcml»« t«. 1993). AJ fn the paw (e-t, U>e Fbaws I Capacity
Backjniund Document), EPA pl todude^ricf pnjfilc* nf e«cb comtaercial ujmHtutinn ftcitfty
ir. iu cepicity baoicground document. Tknc-twility pniGlu contain iofctnnjtion no each facility
indudia| the unit $pcs. wanes acecpled, and boti relewm rxliegt. Allhougtf toox: of Ait ioformatind
is in the pahlic dottioto. ibc emit* 1993 HWTCJSurvcy rurpooici htv« aeviprrbelen bcco lubmitted
                                                                '
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Tbe purpoic of thti eotrcjpoodcncc is to uinErro ibe w'rv-eouOdeoti'aliiy uf ipedfic d«t«
  conUtncd la die ftcOJty piofita.  To (bis «iJ, please rcvi'cwjbe attached profile and
    l it doc* not mnlaip CHTjnfrxTB.li^gf »ltcTnaUdy. tnark ip«iCcTnfprp«lioo that »hi)ii3
                                                 aUy. tn
t* cctitd ti QjnSdeaUtl.  COnCdcodil efemchu inihe prolJc wift be blaQicd uul in (he Don-C81
venibo Of We PhMC U QlfUury Bsckpouod Document. We mat emphasiic Ibat the Agenq* is not
piwidraf tuj oppornioity for facilitia to DtherwiK edit or rewrite ibeir icctlom. PIc»se caU
Klein at (703) 21R-2656 or fsx iwpomej 10 him it (703) 9J4-97« by Friday, Appi 22nd.
               if
               S:
               •*'•
                                                                                                         Uj

                                                                                                         —i

                                                                                                         UQ

-------
                                          t.,.  .3 ;- .:-:ii.;.". .O.eJ/iNw. ;;;U;i.4; r  3
                                         , H«uira, T«M»
              V            '          "•                     ':
      Thk RCRA fan B permitted Mlity bntra b'i CBLfTbac cftimatet are includdl in ibc «(|r«(A(ed CB1 estimate in Edubit X. Of
(be Phnic O wuiui; diii facilitr mxepu DCIifejft VMM cudai.    '      !^
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KACSHV1ILE
, RKCTOKI*

;

ICF
!55iH!KcK
KM«»*li 1OF tnvorita*
(.•»•»•** i«V A'*
HWI C * Surv

D»4«: */!*-•*
ItStXmi'ORAXED
swilMIng IIWTTX: .S«*iv.tyM
l«i O/i* P<»1 Pl"itt »--*X: M»a.'y7H- «>!«*
• M|«H!, 1- 1*^ C%nit**«t«'r fi»r »hf PhiH«c II L.OK
*I^M
wv

•""*« * «' a
                                                                            \  . 3 •
            es. *Hc unit typ*1** WMJI
                    unify
                                                                                o
i
                      TRANSMISSI0\ REPORT
                                                                                 O
                                                                                 O
     THIS DOCUMENT WAS CONFIRMED
     (REDUCED SAMPLE  ABOVE  - SEE  DETAILS BELOW)

       ** COUNT **
     TOTAL  PAGES SCANNED    :   2
     TOTAL  PAGES CONFIRMED  :   2

     *** SE\D ***
\...
1
RiiMOTE STAT 1 O\ ' ST ART T IVt- U K \ 1 1 < A ; * 1 ' 4GMS

»-I«-S>l 3:a«-M ; I U.-I-
a/ -2
\H)Di; { kcsi i.is
ir |coMri.i-:Ti;u
jOGOO
                            TOTAL   o:i>ri':r  :>
     VJTE:
     So.: OII-RATION \IWJU« 4U ! 48UOHI-S SKLKCTl-W  If : CkKoH UHCKt-CT  GU :  ca OAWl MCATIO\
     111  : I-OLIJ-D BY Rh-MOTE SF : STOKK S K»K»AKD  Kl  ttl.l..\\ IMTIATI:  RS :  RI-I.AV STATKA
     MB  : SK\D TO UMI.BOX  PC : |1)|J.ING A Kli\XlTI-  Ml' : Ml 1.1 I If H.I. I NO  KM ;  KliCEIM! TO MI.MdkV

-------
                                                     917335349748   P.01
             •OLtXM KXVIKOXMIXT10.

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                 »e»t Offie* »oz
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                                                    ro
       RolUw JtafaoBAmtal SMV{OW, Bttoa Rout*,

       Thi« RCRA Pan B pcrmitlcd facility consists o(t-*iiOT»^A>U[y kiln, liquid burner, and
 IP iftertunicr. The thermal input to tbc unit a rated at ».o MMBtu/hour..

       Seven] ffiocbsutanu are used tc feed waste Into the incinerator sjxtem. Liquiib are
 atomized under lir procure ud iqjected into the liquid burner «nd afierhurner dumber. A
 positive displacement pump feeds puiapabte ttodce* Into the rotary b'ln.  Containerized tolidk are
 fed into tbe unit via a conveyor tyitem. This beiSty gew:r4ly doe* not auccpt hulk sclidi. but it
 doc* Mcept «rHU.

       GmCdeotiol copvcity Infongaiiou proved by the lacility included the waste quantities
bumcd during 1992 nod the mmiauin pnciiei] burolof capacity. Thise etUowtes are included in
the aj|rcj»tod CK cituoatc in Exhibit X Thj [tcllity iadicftted that it accepb the Phua fl y
waste* D018-043. K14M45, nod KI47-151.
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      TKAJSSMITTAX.
         RECORD
                                P'*tiiitlc>4i Nult mil tins ifWTC atwrwy*
                                Mitt- fiitc** l-AXi .10?     «
                       FRO Mi    nrp tnuorp«.ir»u-tl
                                OK tnc*»rp*.ir«n«-it
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                   TRAiNSMISSION  REPORT
THIS DOCUMENT  WAS CONFIRMED
 {REDUCED SAMPLE ABOVE  -  SEE  DETAILS  BELOW)

   ** COUNT **
TOTAL  PAGES  SCANNED     :    2
TOTAL  PAGES  CONFIRMED  :    2

 *** SI£\D ***
Vu.
1
NEMOTE STATION
47S»S!53
START TI«E IX RATIOS
4-18-94 1-OOPSl | t Oil~
»I^CI-.S
a/ a
MODE | WLStl.TS j
•Ccrtlt'LirrKD |
1 '.KiOO j
                         TOTAL   0:ni ()!)-   a
NOTE:
\o. : OI'ERATION MWBKR  48 :  48(Mllit>S SKI.L'CTi:0  I-XT •• l-KKOK CORRIXT   GS : O2 CiiMWAICATKiN
I'D : KJI-IAT) BV R»WTE  Sl; :  STORK « FORWARD  Rl : kll.XI INITIATE  R5 : KI-J.AY STATION
Mil : SK.NU TO M.\ILBOX  fG :  fOLI.ING A RUMnTI-.  Ml' • Ml l.f I fol.l.INC   KV| : RKCT-IM-: TO MIARlKV
                                                                                   uu
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       Rollins Environmental Sen-Ices, Bridgeport, No* Jrr>ey

       This RCRA Part B pcrmilted Tacility operates one .sl;i|>i;ing rtitary kiln wilh an aftcrhurncr.
The thermal input to the system is rated artjS-MMBiu.liour.
                                     i  "i
       Several mechanisms arc used to feed liquids, punipuhlu sludges, com.iincrizcd solids.
cotnprcsseiJ gases, and soils into  the incinerator swtem. Liquids are atomized under air pressure
and injected into the Luddby liquid burner and aOeiburner ch.imbcr. A  positive displacement
pump feeds pumpable sludges into the rotary kiln.  This facility generally does not accept hulk
solids.

       This facility reported quantities of waste burned in IW2 and maximum practical  burning
capacities as CBI.  These estimates are included in the aggregated CBI estimate in  Exhibit X. Of
the Phase II wastes, this facility accepts D018-(H3 waste*.4ml dki-nor indicate whether it accepts
KI41-14Sor K147-I5I.
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FACSIMILE
T¥*AIMS1V«ITTAI .
KKOORIY
IC^F IrMc:oMi»OKA.Ti«;r»
»>MJ !i» v^4.***O
TO* r*wt ilftlw* Vt»t»MtlitU»ti IIWTC" 3urwy»
fttOfVff 1C ^* |t»i»t| IWlVMllHl, *--!•>% < tn»t«l«»I».^»U. Oom«l«~J in i»i* J-vj
nxv-rcr surwv
DW«M: 4/IM^^ »*M« J
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         KP-vVU
     t"h«*«* IX t»v-wly
        v*vrh»iiw |34
      In (Ha nu««l*c
     » cm.
          mvInr t»«vltBr«»wi*(« «Ui».-*jirt*-f>i. In*** r*c-l»y prnfll** *-«»n«*lf
          ih« unit >yyi«n. ««^>*t*:i> t-c~ ; I-RRI* C-OMKIXT  ca : ca ownsiCATios
TO = 1-<»IJ.H> Bt REMOTE  St: :  STORE A I OR»ARO  KI  : RI.I.N IS1TIATK  RS = RKI.AV STATION
MB : SUND TO MAILBOX  I«G ••  P(H.LING A RKMori; \U- i Ml I.I I • I'DI.I.I\CJ  KM : RI-CIMXK TO Ml-MORV
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                           Kolilas Environmental Services, Deer Park, Texas

                           This RCRA Part B permitted facility has three incineration units-two rolary kilns with
                    afterburners, and one rotary reactor.  Each rotary kiln system has a thermal input of 180
                    MMBtu/hour. The rotary reactor has a thermal input of XVS MMBtu.fiour.  Each train has
                    several feed mechanisms that utilize concrete pumps to feed pumpable sludges and an vtuvaior
                    feed for containers. A clamshelL'crane feeds bulk solids into the rotary reactor.

                           Rollins, Deer Park burns liquids, pumpable sludge*, containerized solids, compressed
                    gases, and soils.  For each incineration unit.  I he facility provided confidential business information
                    on waste quantities burned during 1992 and  maximum current practical burning capacity. These
                    estimates arc included in the aggregated CBI estimate in Exhibit X.  This facility can accept all
                    Phase U wastes (DO18-043. KU1-145. and KN7-131).
.
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      TMA.NSIVI ITTAL,
          KCGORD
                                  IOF
                         VMM t«t »•••

•ItN      l*tfMillltlw* SttfevuIllBB HW^fC:
        CrV Polum TAX? Z1*-T*H-      . .. T_ . ...  .... ..

KKOMi    Iff lr»«H»v|taiv«iod, KI*A C.'«*ntf«viitr for Ihu Pb**e U UOW/**
                        O*it-: Ai.rlJ ,
                                                             Pn»c. 1 of 3
                             MrvU l*v«i
         TV»» 7*;*rpti*ai *»l" ttala fiairg»t»«jn*i «•>»»«» •• i
     *|*n*fil» «i»n(*f*Mi«l !«• tbo fnvlliry pMtffth** fi*
     confirm cn«i W UHMP «*«rt «r«tniHtnd9I ltilvn»i»*ik»«i. ••• •»•**
                                       ii«« «M'int«ln'
                                                      •
                                                    ol thi* i«it< »rn*«ik»i
           t**«tl««m IK* ni>n^.*t>nn«J«nt1u1iiy v«t* •pau-illu «lntf«
           •- nOfMl. pl«««i* i«viww tttv »4i4i«;tai.xl prul'llw M<»«I
                        ~  * '   itU>n i UMI ohou'Ul
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                   TRANSMISSION  REPORT
THIS DOCUMENT WAS  CONFIRMED
 (REDUCED SAMPLE  ABOVE  -  SEE  DETAILS BELOW)

   ** COUNT  **
TOTAL  PAGES SCANNED     :    2
TOTAL  PAGES CONFIRMED  :    2

 *»* SEND ***
So.
1
REMOTE STATION
2.0748 i:«IU
START TIMI-:
4 -*>-!» I^KII-M
Ut RATION
., ro-
»{• \CiES
J/ -2
\K)l)K
L-C
KtCSU.TS
amit-iiTED
!K>UU
ToT.M. ii -mi !",:;- -j
NOTE:
So.: OPKRATIO\ MMBEK -«8 : 4HOOWS Sia>XTKD IX' : I'KKuK CHKRIXT Ca : 02 CtWIMl \l CATION
TO = rW-U-B BY RBKITI: S^ : STORE * KORHAKD Kl r Kl LAY IMTIATh RS : BI:l.AY STATION
MB : SHXD TO MAILBOX I*G : COLLING f. KCMO1K Ml* • Ml I. T 1 ItlLL 1 \C KM '• KtiCtiiM-: Id MI^KJk'H ^*
                                                                                 CO

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                                                                =-001.002 fK 25 '34 IS:27
                                                                                                                 *»
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                                  MESSAGE
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?




R.O.S.S. Corporation
Ross Analytical Services, Inc.
Ross Consolidated Corp.
Ross Consulting Services. Inc.
Ross Environmental Services, Inc. - Giles Hd.
Ross Environmental Services, Inc. - Royalon Rd.
Ross Environmental Services, Inc.- Tech. Dopt.
Ross Foundation. Inc.
Ross Incineration Services, Inc.
Ross Service Corporations
Ross Transportation Services, Inc.
FasNq.
216-748-1399
216-572-7620
216-748-1399
216-748-1399
216-748-1267
216-748-1399
216-748-3956
216-748-1399
216-748-1267
216-748-1399
216-748-1135
Confirmation
No,
216-748-2282
216-572-3200
216-748-2200
216-748-2200
216-748-2171
216-748-2200
216-748-2200
216-743-2200
216-748-2171
216-748-2200
216-746-2171
                                                                                                                      UJ
A.-FAXOOQK3AUS
                                                                                 so-Kta
                                                                                                                           J

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              2167-01399
                                   ROSS CO*»fiNl£S
r-lSJB P-flB2--302 ff* 25
.. -.
                                                                                               15:38
                                            ,Crmfb>a>OU»
                      Thl» jaanenlfaa bcitily ha I RCRA Fyt 8 pemJL Rna'i routy kiln ladoetMar
                UK! Kotunettcd WMta an fed to tto Ua vta ftntf feed mecbtalm that feed lotu a |tav(ty feed
'•if!
                      ConfidcnlW buriacai toJormitten pcnrided to the turvCy locludod watte quantities tetncd
                during 1992 aod nanmi practical buraiof capadljca.  Th««c cslhzuiUa ate induJed in tbo
                tjCgr^Ued C8I eitiBuae to Ekbibil X. Of *e FbMe d WMtct, Chb fteillly accqiU D01M3w«tc
                code* but did not Jmficalc its ahflsly to aeaapl K14M4S of JCK7-I51.

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     RECORD
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                         I'MOJMU
                             r»«4HtJ«— ftiilvinirDnn IfWTC Surwy*

                             ;..*)<>. «t«,^». I'/\K- HOI r\2J 4*37*4
                                  IfH l«*w»l«mnwilor fcur iti* f'HuiH» 1C LOR



                                  Cut l»«u«« A«iHHilMr^.tJ with [>*«• C*
                    r*k**l«B-  April
       A. In 4M*rrwaily vtrrlluic rhi* u*t|»*cily bAcKcnvuntI UIM UMTICH* '••• ''• C OH. cnpivvfty ^»*n1yiM U*»

       »w^ly JUtuU *i»** «i*™rly MU^nLifMO MT,^«M ln«.lvklln|K  **«*<*•*» thM« •KtilHit Ihtr tw«t«.-iiv

<-.H«r«ct*rt»ilc CSS n». 4HOTZ. T«*«-N4l»y »cptc«ntwr I*. IW3). A* 4n ilwi )•**• (•-)(.. <

UA^kvound TJ«KU|tnc;Di>, CPA |*l««fw tit tnctw4a f«ilW pruCilvN ^a'««*^1» b4*nuncrcml U4*mtfua

in it* c*p»cliy K»ek||n»\iaU O*>vw(i(rni. Th«*« r«.*«Hty ^*ulit«« t>*«i»i«lM Uit**rnioiion I.I.I\O A RI-WTK
>l If
• I'M,
•Ji
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1!
!C 1 kkoK
Kl - Kl LAY
Ml> : VII !.| |
MODI:
1
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ICtJMI'LKTKU

OiKKtXT
i M TI AI r-:
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Kl-1.A> STAI10X
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       TbcmilKEM, Rock HIIL South Cirollaa

       This RCRA Part B permiiied facility uses a fixed hearth incinerator with » thermal input
of 42 MMBtuAour. This facility can accept liquids, pumpable sludges, nonpumpabie sludges.
containerized solids, bulk solids. compresse.d gases. »od.*oil».  Metered pumps feed liquid and
sludge wastes and rams feed containerized solids. Separate machinery feeds aerosol cans directly
to the incinerator.

       Confidential capacity data provided by the facility include waste quantities burned during
1992 and  maximum practical burning capacities.  These estimates are included in the aggregated
CBI estimate in Exhibit X. ThermalKEM indicated it can accept all Phase II wastes {D01R-O43.
KUt-I43.andKM7.151).

       Ic 1992. the facility indicated that it planned to increase sludge/solid capacity by adding an
additional unit, a waste-fired boiler, and additional storage areas.  No such change* in capacity
were reported in the 15*93 survey.
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                       TbcruclKEM, Rock Hill. South Ciroliu

                       This RCRA Part B permilied facility uses J fixed hearth incinerator with a thcrtn.il input
                of 42 MNfBlu/bour. This facility can accept liquid*, pumpable sludges, nonpumpablc sludges.
                containerized solids, bulk solids, compressed gases, and soils. Meiered pumps feed liquid and
                sludge wastes and rams feed containerized solids. Separate  machinery feeds aerosol cans directly
                w the incinerator.

                        Confidential capacity data provided by the facility include waste quantities burned during
                1992 and  maximum practical burning capacities.  These estimates are included in  the aggregated
                CBI estimate in Exhibit X. ThermalKEM indicated it can accept all Phase II wastes (DfllR-iU.V
                KI41-14J. and KI47-151).

                       In !992. the facility indicated that it planned in increase sludge/solid capacity by adding an'
                additional unit, a waste-fired boiler, and additional storage areas. Nonsuch changes in capacity
                were reported in tbe 1993 survey.
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         KACSIMH.K
                    *rAJL,
                                      ICF
RC>*4>    li'f Incntpofowa. t*P<\ Com rut tin lor tho flln.n II I.IJK '
                                    VTC' .HmvNiy
                                                                      r-i>« t .*rigf prvftUM ol *iwh «.«*fn*i*ii«>inl «*H«HM»*|«U« *«»i-«l*tx
      U,Thi uup-^ly b^-kvniina dr.Ai«ui«i. Tl~^u CxrU.tr r-n-niu <-»n.. bit.••.•».!.«.«, .>- tf«j,-l. l«M.l.ly
      tocludhwOM! iinll «re~. <••.«!<>• AuucplcU. «o«l H««I f»l«.-«»» i-n-li.. Alihuu*h ~>.n« «.f ihto u.1... .r..i.»n
      taintlw nubile (Jumlllii. Itw entire IVVA IIWIX.: itunnsy r~1«>iuu> h«vo a:»u I"   1!
 NOTK:
 Xo. :  WEKATUK M.M8KR  4B :  -taOUHCS Slil.lCCnOJ 1C : I KKOR CMKKI-ZT
 ID =  t-OUJai BY ROIOTIC  ST :  STOK<£ « I okHAKU  Kl : kl-J.^V INITIATE
 »IB :  SEND TO MAILBOX   K :  1HX.I.INC A KI-MOH:' *«•  Ml l.TI-I"<)I.LI\G
                               : Ga CiiMW MCATION
                               : Rftl.AV STATION
                               -. Kt:ci:m: TO

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 PPR 20
                      PROM USPCt CIC UBTS34
 uspa
 0:v« Inenettioa Rally
 TO. Sex 2228)
 Our
 Mission:
quaOty waste and uy-

producl management

services that consis-

tently meet or exceed

customer needs and

regulatory require-

ments *t competitrVe>

eoet whila enhancing

shareholder v»1u«.
           X     C   0  V  E'R   :S;"H   E  ET
                          Executive
                   Cllve Incineration Facility, UT
                                                Fix
To
Company:
Date:


From:
                                     •/.'? «,-*y
Number of sheets (uKlu&ng this one).

Comments:	_..  _
                     If Cue is incomplete or OSepble. please conuct.
                                       NOTICE:
   THE INFORMATION CONTAINED IN THIS FAX MESSAGE IS 1NTEMOEO ONLY FOR THE PERSONAL AND
               CONFIDENTIAL USE OF THE DESIGNATED RECIPIENTS IIAMCO ABOVE.
 This messaga may be an ailomcy-cfenl eofnmur.ictVxi. t--xl a> such is pfWegtd and confidential, if tha reader o(
 this rrwtsagt » not lha intended recipiant or an aj*.-* r»ipc-^iWo {« dorivering it to the intended teeipienl. you sue
 hereby notified that you have recevad iKs dococnerj in *rrr. aid lhal any ravitw, disssminatkxi. distribution, or
 copying of this message is strictly prohbied.« you htv« r*c«ke(J tWs communietton in *m*. please not*/ the s«nd«r
 immediately by lefephona and return the original men.*;* 13 ttw serx'tf by US Mat!at cur expense Thankyou.
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«* 28 •«  HISS
SBff BV'KF I.VCCKtfOMTO
                             Clr M

                         3-20-94 MP
ICF ImrojritH-
                                                                     801 59J *46J:* I.' 2
                                                                                                                   <•
FACSIMILE
TRANSM1TTAL
RECORD
ICF INCORPORATED f
WBIteUeni PW«w.V' fix-
  Pb»e  II oewiy liuod tod oc«(f ideodAd *Ma  ioduding WBI«I «hai  ethibit rhe ttneity
  -Sep£eohtf!«,!»?). At la tte pat (feg, tbe Muse I Cipadiy
  BlctfroaDd tknuaeni), EPA pUo» Id ioctodo btiaf ptuffla of cich ocxnmcreuj ancbultion facility
  (a it* e»p«city bickgnxmd ducvmcsL Tbew bcAqr profiles oooMin infonnatixi oo oKfa ftdfoy
  iodudiof theunir lyptx, wuic* toocpied. «nd tieu idciMC ruiagL Altboofb wme ufthn inTortuuioa
  is JA the public domain, ihcctuire 1W3 HVrTC Survey rccpooac* twve nevenheka been tubmittol
  »CB1

        llw porpotc of this ooneipondenee it to oMtGrm the  noo-touCdcocULcy vt ipeafK dau
  deoena cuouioul ia ibe bcdiiy profle*.  To Ail cad. pteuc review the tuMfacd ptofde and
  onafirm dial Jt °
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ffK 20 '94  14:56     F

SCSI B»;i€F INOOWOfcrtH)
                    USPCI Clc

                     : 4-Sfl-*
                             TO 9-9--TJ3934sT40

                          ! wepc all fhu* H wvte coda DO 18-043, Xt 41-
1M  Jn/( fT1J7-1
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         APPENDIX D


SAMPLE TC SURVEY QUESTIONNAIRE
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        QUESTIONNAIRE FOR FACILITIES THAT UNO DISPOSE NEWLY-IDENTIFIED
              ORGANIC WASTES EXHIBITING THE TOXICITY CHARACTERISTIC
                                      INTRODUCTION
  Purpose of Iht Survey
    The U.S. Environmental Protection Agency's
  Ofliet of Solid Waste (OSW) is currently
  developing regulations mat wfll restrict the land
  disposal of certain wastes exhibiting the
  Toxicfty Characteristic (TC)  fie., newy.
  identified organic TC wastes: RCRA codes
  DOi 8 through 0043).  In preparation fofthe
  land disposal restrictions (LDRs) at these
  wastes. OSW is conducting a capacity analysis
  to Identify 1) tne volume of newiy-Wentfied
  organic TC wastes that win require treatment
  as a result of me LDRs, and 2) the availability
  of treatment/recovery systems to manage
  newly-identified organic TC wastes to meet
  treatment standards. The results of this
  analysis wil be useti to support EPA's
  determination on whether to grant a national
  capacty variance from the statutory date of the
  LDRs for newly-identified organic TC wastes.1

   To estimate the quantity of nawfy-tdenffied
  organic TC wastes that are currently land
  disposed and* tsiereforv. may requro treatment
  upon promulgation of the LDRs, OSW is
  conducting  a focused data collection effort.
 This effort consists of a quesfjonnaini for
 facBfties with land disposal units that are
* permitted or have interim status to land
  dispose the newly-identified organic TC
 wastes.  [NOTE: LUND DISPOSAL UNITS REFER
 TO UMTS USED TO TREAT. STORE. OR DISPOSE
 HAZARDOUS WASTES M OR ON THE LAND.
  LAND DISPOSAL UMTS INCLUDE LANDFILLS.
  SURFACE IMPOUNDMENTS. LAND TREATMENT
  UNTO, WASTE PILES, AND UNDERGROUND
 INJECTION WELLS.]  Under Section 3007 of the
  Resource Conservation and Recovery Act
  (RCRA). 42 USC 6927, you are required to
 provide EPA wkti the information requested in
 this qitf itiofmaire..
                                                  The purpose of this data collection effort is
                                                to determine 1) the volumes ol newly-identified
                                                organic TC wastes that will require treatment
                                               . as a result ol the LDRs. and 2) the availability
                                                of on-stte treatment and recovery systems to
                                                manage newly-identified organic TC wastes.
                                                (EPA is undertaking a separate effort to
                                                evaluate tne commercial availability of
                                                treatment and recovery systems to manage
                                                newty-idemtfied organic TC wastes.)

                                                How We Pl*n to Collect thl* Information

                                                  We have prepared this questionnaire as a
                                                guide for data collection. The questions in
                                                each section of the questionnaire suggest a
                                                format to present the answers. We expect
                                                respondents to provide the data in the  most
                                                convenient means available. Examples of
                                                alternative ways to answer the questionnaire
                                                include sending computer printouts or copies
                                                of Internal records and downloading electronic
                                                data,

                                                  We are providing contractor support to
                                                assist ladities in responding to me
                                                questionnaire and we ptan to work closely with
                                                you. Prakasn Ramaswamy of 1CF Incorporated
                                                has already contacted your facility and  wiB
                                                serve as your primary contact. After you have
                                                read through the questionnaire, but before you
                                                begin to assemble the information, we
                                                encourage you to contact Prakash
                                                Ramaswamy at (703) 934-3426. Also, please
                                                feel free to can Bengie Carrol or Pan Lee, U.S.
                                                EPA. Capacity Programs Branch at (70?) 308-
  w 5.
*"
 -
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                                                Who Should Respond

                                                  Only facilities that have managed the newly-
                                                identrfied organic TC wastes in land disposal
    'Th» LDRs ere MectM
                           t pmmutgalKJ meil in* Aamrt
                                                       r gnra a netionit capacity vwiance Bom
tnt omemtte (ppicabletiM and ttaaattn » oMnnt dan (not to noted two yHrs beyond ir» statutory
OMtttnt) btMO on...the earieit date on wNcn adtquci tummrtt trtcmtnt, lecovwy, or SapoMl c*p*c«y wtiicri
prewca hunan ntairt and the environment WB be eviiibii~(RCRA Section 3004{h)(2)).  Cet»«/-c
-------
 units in 1991. including TC-eomaminated soil
 and debris, should complete this
 questionnaire. Newty-identified organic TC
 wastes are defined as those wastes thai have
 an EPA hazardous waste code of 0018
 through 00*3 in 40 CFR 261.24.  Each waste
 cod* corresponds to an organic constituent
 determined by a* Toxfcity Characteristic
 Leaching Procedure (TCLP) to exceed the
 promulgated regulatory level  The codes and
 corresponding consttueras are listed in
 Appendix A.

   Facilities that flans land dispose newly-
 identified organic TC wastes fie., do not
 dispose, store, or treat newly-Identified organ*
 TC wastes  in landlSkt, surface impoundments,
 land treatment units, waste pies,  or
 underground injection wetts) only need to
 complete Section I of this questionnaire.

 When to Return thi» Questionnaire

   Please plan to complete the questionnaire
 within three weeks of receipt and maS ft back
in the enclosed postage-paid envelope.

Where te Return this Questionnaire

  In the event One the enclosed envelope is
misplaced, the address you should return the
questionnaire to ic

    ICF Incorporated, Room 815
    3300 Lee Highway
    Fairfax. Wgtta 22031-1207
    Fax: (703) 034-9740
    Anre Prakash Ramaswamy

Organization et the Questionnaire

    This questionnaire is organized into live '
sections and tour appendtees:
Section!
          General information on yourfacSty;.
Section B  Land Disposal Units: Information
          on existing land (fit posa! units used
          in 1991 to manage newly-identified
          orgarttc TC wastes*

Section m NawMdentBed Oroante TC Waste
          Uoitsi information on wastes
          exhibiting a newly-identified organic
          TC that are managed in ort-sne
        .  land disposal units;

Section IV Treatment or Recovery Systems For
          Managing Newly-Identified Organic
          TC Wastes:  Information on
          treatment or recovery systems that
          are used or could be used to
          manage newly-identified organic TC
          wastes, including soil and debris;

Section V Additional Information: Information
          on future changes in the generation
          and management at newty-
          identified organic TC wastes;

Appendix A    NewMdentified Organic TC
              Ha^ydnus Waste Codes and
              Their Constituents:

Appendix B    Potential Organic TC Treatment
              or Recovery Systems:

Appendn C    Debris Tvoes: and .

Appendix 0    Sample Block Diaaramj.

Confidentiany

   The Information that you provide in this
questionnaire w* be harxfled In accordance
wkh RCftA Section 3007(b), 40 CFR Part 2.
and 40 CFR Part 260.2 which establish EPA's
general poBcy regarding public disclosure of
information.  Information may be submitted as
Confidential Business Information (CBI) in
accordance with 40 CFR Pan Z203(b).
Information covered by * claim of CBI wffl be
treated in accordance with the procedures set
forth in 40 CFR Part 2, Subpan B. However.
information not covered  by a CBI claim may be
made available to the pubBc without prior •
notice 10 the business.

   If you wwh to submit information as CBI,
please send your response to at the following
address:

  • U.S. Environmental Protection Agency
   401  M Street. S.W.. Man Code OS-312
   Washington. D.C.  20460
   Ann.: Margaret tee.  Room SE-264
   Thank you for your help.
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 U.S. ENVIRONMENTAL PROTECTION AGENCY
Font) Approved
OMB No. 2050-0119
Expires 12/31/92
ID* 0121
 OUCSHONKURE FOR FACILITIES THAT LAND DISPOSE NEWLY-IDENTIFIED ORGANIC TC WASTES
 Section L     GENERAL FACILITY INFORMATION
    1. Facility Name

    2. Facility EPA ID Number

    3. Facffity MaiSng Address
      City, town, etc.
      Stale
      Zip Code
    :  County

    4. Facility Location (if 
-------

  U.S. ENVIRONMENTAL PROTECTION AGENCY
                                                                    Form Approved
                                                                    OMB NO. 20504119
                                                                    Expires 12/31/92
                                                                    10* 0121
  QUESTIONNAIRE FOR FACILITIES THAT LAND DISPOSE NEWLY-IDENTIFIED ORGANIC TC WASTES
 Section I.     GENERAL FACILITY INFORMATION (continued)
    7. Provide simple Mock diagrams fte.. schematics) ot relevant systems relating to the
       generation anoVor management of wastes exhibiting an organic toxicfty characteristic (TC).
       Indicate any operations or processes that invoke newly-Identified' organic TC wastes (e.g.,
       generation, handling, treatment, and disposal)- The block diagrams are a tool to organize
       data collection and allow us to understand,« a glance, your facility's operations.  (Ptease
       refer ID Appmtf* O lor sample Week diagrams.)
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*.
                 VS. ENVIRONMENTAL PROTECTION AGENCY
                                                                    Form Approved
                                                                    OMB No. 2050-0119
                                                                    Expires 12/31/92
                                                                    10* 0121
                 QUESTIONNAIRE FOR FACILITIES THAT LAND DISPOSE NEWUMDENTIFJED ORGANIC TC WASTES
 Section)!.    UNO DISPOSAL UNITS  .

    This section requests Information on the land disposal units at your facility. For the capacity
 analysis, we compare the total volume ol wastes that are placed m or on the land prior to the effective
 date of the standard with the total national capacity capable of meeting the LDft treatment standards.
 The data you provide wO be used to determine the volumes of wastes that are placed in or on the
 land. We will use your responses on specific unfts to determine whether the volumes managed in the
 units vi* be included in the demand for needed treatment as a result of the LDRs.  For example.
 volumes of wastes disposed in units with approved no-migration petitions can continue to be
 managed in the land disposal unit and will not require treatment as a result of the LDRs. Whereas,
 the volumes of TC wastes disposed untreated in iandfffls will require treatment


 Coat and complete the relevant pan of Section It tat fact) land disposal unit that was used in  1991 to
 manage organic 1C wastes: A) Landfills; 8) Land Tremnertt Units; C) Surface Impoundments; D) Waste
Piles; and £) Underground Injection Wells.  Assign « unique number to each unit and indicate the
number on each page.  Plane note thtt ihrwotout thft tectlon. the tfim TC wattet refer* to the  ,
newhr-idtnttfied organic TC wastet.
                                                                                                                                     o
                    8.  Type of land disposal units at your facfty used to manage wastes exhibiting the newly-
                       identified organic TC: (Check all mat apply and compfere the relevant sections}

                    Q Landfi (Complete Section A lor each tencrtJQ


                    O Land Treatment Unit (Complete Section B for each lend treatment unit)


                    Q Surface Impoundment (Complete Section C tar each surface impoundment)


                    LJ Waste Pile (Complete Section O (or each »*sre pile)


                    LJ Underground Injection WeH (Complete Section E lor each underground injection well)
                                                                                                                     o
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                Pages

-------
  U.S. ENVIRONMENTAL PROTECTION AGENCY
Form Approved
OMB No. 2050-0119
Expires 12/31/92
ID* 0121
. QUESTIONNAIRE FOR FACILITIES THAT LANS DISPOSE NEWLYJOENTIFIED ORGANIC TC WASTES


  Section n.    UNO DISPOSAL UNITS {continual)

  A.  Landfills
                  .   .                                        |  Landfill Unit No.

    Answer the following questions for etch jctVa fiewntous wasi» tonqtilt at to«si» that received
                      c TC waste* during
    9. Commercial status" of tha landSt (Cftec* «0 rut «ppfy)

      D The landfi is only avaflaM* lor tnaragemont ol hazardous waste generated an she.


      D Tha larxjfffl is avaBabte only .to frms owned by trte tarns company.


      D The landfiB is available to a Emfced group ol cstablishmeres (or commercial hazardous
          waste management.

      LJ llwlandflisavala&ietoanyGrmorestablishinortforcoi^^
          managemenL

    I0.a)   Total quarttyofnazardous wastes disposed In 1091:
          Quantity: _  torts gaJora   (circle 'one)
      b)   Permined capacity remaining after Ooeembof 31. t09l :
          Quantity: _  tons gaSons   (c/rcfeone)
                                           c-
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U.S. ENVIRONMENTAL PROTECTION AGENCY
                                                          Form Approved
                                                          OMB No. 2050-0119
                                                          Expires 12/31/92
                                                          IDll* 0121
QUESTIONNAIRE FOR FACILITIES THAT LAND DISPOSE NEWLY-IDENTIFIED ORGANIC TC WASTES


Section a.    LAND DISPOSAL UNITS (continued)

B. Land Treatment Unit*
                                                       I Land Treatment Unit No._

  Answer the following questions tor each tenrf vrtment unit at the site that received newrV-
  identitled orcwifc TC wastes Outing 1991.   '

  11.    Commercial status of the land treatment untt: (Crtcc* a//tfwr appjy)

     O The land treatment unit is only available lor management of hazardous waste generated
         on site.
     D
The land treatment unit ts available on'/ 
-------
  U.S. ENVIRONMENTAL PROTECTION AGENCY
Form Approved
OMB NO. 2050-0119
Expires 12/31/92
ID* 0121
  QUESTIONNAIRE FOR FACBJT1ES THAT LAND DISPOSE NEWUMDENTIF1EO ORGANIC 1C WASTES


  Section tl.    LAND DISPOSAL UNITS (continued)

  C. Surface Impoundment*   '	
                                                  | Surface Impoundment No.

    Anaw tf» feHomaa questions tor each surface imooyndmcnt »f tt>o sin ttef received nevvV-
    itlentmca oratn.'e TC waste? during 1991.


    13.    Type of surface Impoundment: (OMd[«ffiri«4ppjy)

       Dstorage

       LjTreatment (spec/iy tfw                                 .                   .


   14.    Cocnmcrcjal status of the surface impoundment: (Owe* off tfw: apply)

       LJThe surtacs impoundment is only available tor management o< hazardous waste
          generated on sKe.          •

       Lithe surtace impoundment is available only to firms owned by the same company.

       DTTW surface impoundment is available to a tatted group d estabfisnments lor
          commercial hazardous waste managemenL

       LjThe surface impoundment is available to any firm or establishment lor commercial
          hazardous waste managemenL

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                                                                                                          C]T»



                                                                                                           J

-------
 U.S. ENVIRONMENTAL PROTECTION AGENCY
                                                                 Form Approved
                                                                 OMB NO. 20504119
                                                                 Expires 12/31/92
                                                                 ID* 0121
 auEsnONNAflje FOB fActunes THAT UNO DISPOSE NEwuMDeNTmeo ORGANIC TC WASTES


 Section II.     LAND DISPOSAL UNITS (continued)

 C.  Surface Impoundment* (continued) 	
I                                                     Surface Impoundment No.
                                                    ^m^^^mfm^f^^m^^^-^-^^m^^^^_^^^_l^^^

   15. Status of st«face impoundment w«n respect to minimum technological requirements:
      LJ Meets minimum technological requirements. (Proceed to next /and disposal i/n/i)
(provide date).
      dRevorined to meet mnimum technological requirements on
          (Proceed to next (and oVsposa/'un/l)

      LjWil be ratrofiaed to meet minimum technological requirements. '
          Date when retrofinlna wfll be compteted _ (Proceed to next land disposal
         HasappSed for a waiver from retrofining. What is the status of the application?
         _ Pending
         _ Rejected
         (Proceed to next bnd disposal unit)

      LJKas received a waiver from retrofitting. Provide basis for waiver .
          (Proceed to next tend disposal unit)

      LjPta to dose prior to effective date of minimum technological requirements fue.. March
          25,1994). (Proceed to nea land disposal unrf)

      [Dwas closed by end of 1991.
          What was the date of closure?      	
          (Continue » question 16)

      Ow> be closed by 1995.
          What is the expected date of closure?	
          (Continue to question 76}

      Owa be dosed after 1995.
          What is the expected date of closure?	
          (Continue to question 76)
                                                 .
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-------
 US. ENVIRONMENTAL PROTECTION AGENCY
                                                                Form Approved
                                                                OMB No. 2050-0119
                                                                Expires 12/31/92
                                                                ID* 0121
 QUESTIONNAIRE FOR FACILITIES THAT UUp DISPOSE MEWLV-IDCNtlFIBD ORGANIC TC  4STES


 5  .tlon B,    LAI. J DISPOSAL -NITS (continued)

 C. Surface Impoundmente (continued)

16. Complete this question ortr/Sthi
wffl be closed by 1995. (Check t
test judgement or «*tt'ng p/ans
O Tanks wffl be hstaOed to
Estimaed annual volume
Units:



| Surface Impoundment No.
i surface impoundment was
as •basis.)
replace the u
ol waste to t
(Proceed
O Unt was or wai IN dosed with wastes
uwt)
O Waste was or win be r«moved from the
qusstronl?)
Q A partial removal of wastes was or w3
remairing in the imft. (Continue to qttt
17. Expected voturra of waste to oa removed boot

W*ttkw*ter«2
^

RCRA conUmlnated
*ofl
RCRAcontandiwtcd
.a— tijl—
vVOtlV
1992




1993




*
nit.
« removed di
to next option
in place. (Pra
iunHaspart(
a.
be conducted
tstion IT)
unit:1 (Ussy
1994



•.
Types of consaminated debris (use Appendix C codra):

t closed by end of 1991 or
fttes for ffw LT
-------
 I J.S. ENVIRONMENTAL PROTECTION AGENCY
                                                                    Form Approved
                                                                    OMB No. 2050-0119
                                                                    Expires 12/31/92
                                                                    ID* 0121
 3UESTONHAJRE FOR FACILITIES THAT UNO DISPOSE NEWLY.IDEKnflED ORGANIC TC WASTES



 Section IL    LAND DISPOSAL UNITS (continued)

 0. Watte P«e*
                                                                j Waste Pile No.

   Answer the totlaitmo Questions tor each waste pile unit g the site that received newty-identHied
    organic TC wastes during 1991.
    18.    Type of waste pile:

      O Storage

      Lj Treatment (specify ty using Appendix B crtes or written description].
    19.    Commercial status ot the waste pile: (Check HI tttatappty)

      O The waste p8e is only wabble (or management ol hazardous waste generated on site.

      D The waste pOe k available only to firms owned by the same company.

      D The waste pite is available to a limited group ol establishments for commercial
          hazardous waste management.

      O Trw waste pile is available to any firm or establishment lor commercial hazardous waste
          management

   20.    No-migration petition status lor this unit (Specify one or trie following categories)

      LJ A no-migration petition has not been submiied lor this un/t. and there are no plans to
          do so.                                                          .

      LJ Date no-migration petition was submits*	.
          a) Status or the petition: (Check one)
            	Approved.
            	Rejected or withdrawn.
                  Pending.
          b) Does the approved or pending no-migration petition allow lor management of TC
            wastes in this unit?
            	Yes.
            	Na

      LJ Facility intends to submit a no-migration petition lor this unit,  but has not done so at the
          present time.
          a) Expected submission date of the petition:	
          b) Does the approved or pending no-rrugra-Joo pcinkxi allow for management ol TC
            wastes in this unit?
            	Yes.
            	Na      i
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Page 9

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 U.S. ENVIRONMENTAL PROTECTION AGENCY
Form Approved
OMB NO. 20500119
Expires 12/31/92
ID* 0121
  QUESTIONNAIRE FOR FACBJT1ES THAT LAND DISPOSE KEWLY-IDENTIFIED ORGANIC TO WASTES


 Section IL    LAND DISPOSAL UNITS (continue*!)

 E.  Underground Injection Welle	
                                                | Underground Injection W«n No.

    fjtswcr the following Questions tor eeeft underground infection wefl ar ifta site that received
    newto-Kieatitiet} organic TC wastes during 1991.

    21.    Commercial status of me weft (Cftee* «V Oar apply)

      O The wcfl is only available tor management of hazardous waste generated on site.


      LJ The wel is available only to firms owned by the same company.


      O The wel is avaBabta to a Imfted group of establishments tor commercial hazardous
          waste management.                                         '

      O The wal is available to any nm or estabGsnmant for commercial hazardous waste
   22.    No-migration petition status forihis unfc (Specify one of the following categories)

      LJ A no-iTMgraiion petition has not been su&nvned for this unit, and there am no plans to
    *     dosa

      O Date nc-fliigration petition was submitted: _
          a) Status of the petition: (Check one)
             _ Approved.
             _^^ Rejected oc wKhdrawn.
             _ Pending.

          b) Doas the approved or pending rxxnigration petition allow for management of TC
             wastes in this unk?
             _ Yes.
             _ No.

      LJ FaciBty intends to submit a no-migration petition for this unit, but has not done so at the
          present time.

          a) Expected submission date of the pecSon: _

          b) Does the approved or pending no-migration petition aDow tor management of TC
             wastes in this unk?
             _ Yes.
           • _ No.
                                         f»;!s
                                         p. as-«
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-------
 VS. ENVIRONMENTAL PROTECTION AGENCY
                                                                 Form Approved
                                                                 OMB No. 2050-0119
                                                                 Expires 12/31/92
                                                                 ID* 0121
 QUESTIONNAIRE FOR FACILITIES THAT LAND DISPOSE NEWLY-IDENTIFIEO ORGANIC TC WASTES


 Section HI.    NEWLY-IDENTIFIED ORGANIC TC WASTE STREAMS MANAGED IN LAND
              DISPOSAL UNITS (LANDFILLS. LAND TREATMENT UNITS. SURFACE
              IMPOUNDMENTS, WASTE PILES. AND UNDERGROUND INJECTION WELLS)

    TIMS section requests Information on the waste sreams managed in your facility's land disposal
 units. We win use this information and the proposed LDR treatment standards for TC wastes to assign
 each waste stream to an appropriate treatment train such thai the waste will meet the proposed
 treatment standards. Although wo us* facfflty spedfic Wbrmatfen to estimate the national demand for
 treatment as a re&ufc of the LDRs, this assignment is lor analytical purposes only. We are not making
 any a priori judgemeras on how your faciBty wOl actually respond to tno LDRs.

    Copy and complete Section III lor each waste snam managed on site that exhibits a newly-
 identified organic TC, including residuals gene/and as a result of on-site treatment and TC-  -
 contaminated soil and debris.T TVs section is to be completed for each waste stream managed at
 your facility, including wastes received from off site and one-time wastes produced from on-she
 closures of units. Do not report waste streams that are shipped oft site. All responses are to retted
 management in the 1991 calendar year.  Assign a mque number to eectt waste stream end indicate
 tra number. H applicable, indicate the EPA ID Aurnder of the off-site generator from whom you
 received the waste.

 A.  W«t«D*»otpttwt		
                                                           Watt* Stream No.
                       EPA ID No. of Oft-»Ke Generator (H applicable)	I
   23. Indicate waste origin.

      LJ Generated and managed on site. (Go to Question 25)

      LjRecefved from off site. (Continue to question 24)
   24. Indicate ttw forms in whicfi you receive waste stream. (Check all that apply)

      D Ron-oil bin                      .  D Rigid toto

      Dart car                          Q Carboy

      OTanker trucks                     D Pallet

      Osteel drum, specify sizes     	

      LJPoly drum, specify sizes      	

      LJ Tiber drum, specify sizes

      Q Bag c< otter flexible container, specify sizes   	

      Odher. specify              	
    sis
1  ill
 ii:i;,
 ial!S
 t=«8S «
 l»s*3
 P-8-st
    2 o-S
    is:
    ss»  .
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   *Awul»i»**incwibt>inMur«flliraitw;cant*qu*i4r. *M»ly4d«ntil<»4ocgwiicTC«nil«b«wmo<>DOt8 Owoueh
0041
                                                                                                                     )

-------
 U.S. ENVIRONMENTAL PROTECTION AGENCY
Form Approved
OMB NO. 20500119
Expires 12/31/92
ID* 0121
 QUESTIONNAIRE FOR FACILITIES THAT UNO DISPOSE NEWUMDENT1RED ORGANIC TC WASTES


 Section tn.    NEWLY-IDENTIFIED ORGANIC TC WASTE STREAMS MANAGED IN LAND
              DISPOSAL UNITS (LANDFILLS, LAND TREATMENT UNITS, SURFACE
              IMPOUNDMENTS, WASTE PILES, AND UNDERGROUND INJECTION WELLS)
              (continued)

 A. Waste Description (continued)  	                     	
                                                          Waste SlTMm No.  •
                       EPA ID No. of OfMte Generator (K eppOcaMe).	
   25. Waste descr^ptkxi Piwide a short lanson cUng lowce (e.g., type of production process.
      dosurt of unit) and generic cherricat name or primary organic and hazardous constituents.
      (For residuals, describe the management procedures resulting in generation of the
      residual.)
   26. List all EPA hazardous waste codes (including ncwty-identified organic TC wastes and other
      wastes) contained hi the waste stream:


   27. Which at the following categories best describes the physical form of the waste?

      Ouqukt (Chuck one e/Ae following.)

         _ Wastewater (Contains <1% total organic carbon and <1% total suspended soMs)
         	Non-wastowaer (AJ IqufcJs not meeting the wastewater definition)  •

      Qpumpabte Sludge


      DNon-pumpaWe Sludge


      DsoCd

      Osoa


      Doebris: Type (Us* Appendix C codefs; or tpeciry type)   .
                                                                                                         I}L
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Page 12

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US. ENVIRONMENTAL PROTECTION AGENCY
                                                        Form Approved
                                                        OMB No. 20504119
                                                        Expires 12/31/92
                                                        10* 0121
QUESTIONNAIRE FOR FACILITIES THAT UNO DISPOSE NEWLY-IDENTIFIED ORGANIC TC WASTES
Section lit.   NEWLY-IDENTIFIED ORGANIC TC WASTE STREAMS MANAGED IN LAND
           DISPOSAL UNITS (LANDFILLS. LAND TREATMENT UNITS, SURFACE
           IMPOUNDMENTS, WASTE PILES. AND UNDERGROUND INJECTION WELLS)
           (continued)

A. Wa«t« Description (continued)
                                                                                            l\
28.ll
/
a
ti
29. fc
n
in
P

Wwta Stream No.
EPA ID No. of Off-*lt* Generator (If applicable)
denary each newly-ideflaied organic TC eonstHuent contained In this wane stream{see
ippendbt A ter a listing of si wnsffluana). N more than ft/e constituents, provide
iddiUonal Mormatkxi on a separate page. EPA will use this information lor assessing
te potential treatabffiy ol the wastes.
NEWLY-iDENTIFlED
ORGANIC TC CONSTITUENT
1:
2:
3:
4:
5:
CONCENTRATION (INCLUDE UNFTS)
AVERAGE

.



RANGE





SentSy constituents, other than those mentioned above, that affect the treatability or
KOvery of this waste stream. It more than foe constituents, provide additional
formation on a separate page. EPA wB use this information lor assessing the
Mental treatability of the wastes.
OTHER CONSTITUENT
1:
2:
3:
4:
5:
CONCENTRATION (INCLUDE UNITS)
AVERAGE





RANGE




'
V

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-------
 U.S. ENVIRONMENTAL PROTECTION AGENCY
                                                                 Form Approved
                                                                 OMB NO. 20504119
                                                                 Expires 12/31/92
                                                                 ID* 0121
 QUESTIONNAIRE FOR FACILITIES THAT LAND DISPOSE NEWUMDENTIFIEfl ORGANIC TC WASTES

 Section BL    NEWLY-IDENTIFIED ORGANIC TC WASTE STREAMS MANAGED IN LAND
              DISPOSAL UNITS (LANDFILLS, LAND TREATMENT UNITS, SURFACE
              IMPOUNDMENTS, WASTE PILES. AND UNDERGROUND INJECTION WELLS)
              {continued)
 A. Wute Description (continued)	
                                                           Waste Stream No.
                       EPA ID No. of Off-alto Generator 01 applicable)	
   30. Provide -lati en the chemical composition of the waste that affects the treatabillty of
       recovery ot the waste stream. Potential/ relevant chajactortstics an provided below.
          .pH level
          .Flashpoint
          .SoiubKtyGn water)
          .Total organic content
          . Total suspended sotds
          .CHorkSes (ppm)
          .Cyanide (ppm)
          ^Sodhjm (pptn}
.BTU contort
          . Oi and grease content
.Water content
. Total wWs content
. Sotubiity (In sotvonQ: Provkte sohrent name: .
.Oroenfc and inorganic content
.Sulfur
.Potassium (pom)
.Total organic halogen
 Ottwr _
      How wS the propenies that you have indicated abova afloct the treatabiltty ol Uus waste
      stream?
   31. Type ot waste generation tor wastewaers and nonwastowatera (excluding soil end debrisl:

      ORoudne (e.g.. continuous industrial activity).

      LJ Sporadic (e,g., periodic cleaning ol lank bottoms).

      LjRemetfaL Provide the type 0! remedial action conducted:
         	cenciA
        . 	RCHA
         	State program
         	Voluntary private party clean-up
                                                                         o
.O
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Page 14

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.
                     U.S. ENVIRONMENTAL PROTECTION AGENCY
                                                                                   Form Approved
                                                                                   OMB NO. 2050-0119
                                                                                   Expires 12/31/92
                                                                                   ID# 0121
                     QUESTIONNAIRE FOR FACILITIES THAT UNO DISPOSE NEWLY-IDENTIFIED ORGANIC TO WASTES


                     Section «L   NEWLY-IDENTIFIED ORGANIC TC WASTE STREAMS MANAGED IN LAND
                                 DISPOSAL UNITS (LANDFILLS, LAND TREATMENT UNITS, SURFACE  '
                                 IMPOUNDMENTS, WASTE PILES. AND UNDERGROUND INJECTION WELLS)
                                 (continued)

                     A,  Waste Description (continued)	
                                                                              Wacte Stream No.
                                           EPA ID No. of On-«lte Generator (K applic«ble)__	~
                       32. Type ot waste generation lor soil and debris streamy.

                          ORoutine (e.g., spills, fitters, PPE).

                          Osporadfc (e.g.. periodic tank cteareng. StAbng docommfeskxvng, plant retrofming).

                          O Remedial. Provide tne type of remeda action conducted:
                             	CERCLA               	Stase program
                             	ftCRA                 	Vok«*ry ptlvate party dearvup
                       33. Quantity managed in on-site land disposal \r*a In .1991:
                          Quantity ot TC wastes (excluding sol and debris): 	
                          Quantity of TC-comaminated soit               	
                          Quantity ot TC-contaminated debris:            	
                                                          tons gallons (circle one)
                                                          tons gallons (circle one)
                                                          tons gallons (circle one)
                    6. Wtcte Management
3-
I. For this waste stream, indicate in the table below 1) how the waste stream is being
managed in land disposal unit (e.g.. storage, disposal, treatment or recovery (see Appendix
B tor system codes]), 2) the type of land disposal unit the waste stream is being managed
in (j-e* landfill, land treatment unit, surface impoundment, waste pile, or underground
Injection wet) and 3) the quantity of the waste stream being managed within each land
disposal unit in either tons or galons. if the waste stream is managed in multiple types ot
land disposal units, indicate each type of unit and the volume ot the waste stream being
managed in each land disposal unit
Type of Management




Land Oltpowl Unit
-



Quantity




Unite




.

Page 15
                                                                                                            SJJS
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 1
  \

'f\
              U.S. ENVIRONMENTAL PROTECTION AGENCY
                                                                            Form Approved
                                                                            OMB NO. 20500119
                                                                            Expires 12/31/92
                                                                            ID* 0121
OUESnONHAIBE FOR PACIUT1ES THAT LAND DISPOSE NEWUY.IOEKT1FIEO ORGANIC TC WASTES


Section m.    NEWLYJOENTIFIEO ORGANIC TC WASTE STREAMS MANAGED IN LAND
             DISPOSAL UNITS (LANDFILLS. LAND TREATMENT UNITS, SURFACE
             IMPOUNDMENTS, WASTE PIUS, AND UNDERGROUND INJECTION WELLS)
             (continued)

C. Waste Minimization
   Only complete this section tor waste streams generated m g«e.   	
                                                         Waate Stream No.      \

  35. Do you ntantc begin waste minimization acthttos or expand existing waste minimization
      activities that may. In the future, result in a decrease in the waste stream?  .
                           Answer questions 96-41.  (Us* your oest judgement)

                   DNO: ProceedK> next waae stream.

                36. imficate type o» acttoy.
                   __ Equipment of technology niodfficatiOfVtUbaitutioo
                   	Process or procedure modification/substitution
                   	Refotm^ation or redesign ol product
                   '   MotfftcationfimbstKutiQn of raw material
                   	Improved efficiency oC operations
                   	Waste aream segregation
                   	Reeycfing or reoowery for reuse
                   	Closed loop recycSng
                   	Othet:	
                37. Provide a brief description of the actrrty.
                38. Provide date when ac&rity wffl begin..
                39. Provide an estimate of the annual reduction in the generation of waste as a result of this
                   activity. Quantity;	Unit of measure: tons gallons (c/rcte one).

                40. Describe any changes in the physical and/or chemical characteristics of the newly-identified
                   organic TC waste stream as a result of thi activity:
                41. Win these changes resuft in the waste s?eam no longer being:

                   LJ   A newty4dentified organic TC hazarcous waste?

                   D   A RCRA hazardous waste?
                                                                                                                        5»
                                                                                                                        *5i
                                                                                                                       El1!
 §5***
 ^113
 §j°«s
 a * 
-------
 U.S. ENVIRONMENTAL PROTECTION AGENCY
                                                            Form Approvoo
                                                            OMB No. 20500119
                                                            Expires 12/31/92
                                                            ID* 0121
 QUESTIONNAIRE FOR FACILITIES THAT LAND DISPOSE NEWLY-IDENTIFIED ORGANIC TC WASTES
 S«ctlon IV.   TREATMENT OR RECOVERY SYSTEMS FOR MANAGING NEWLY-IDENTIFIED
              ORGANIC TC WASTES
    Did the lacffity treat or recover newty-idertified organic TC wastes, including TC-contaminated
    soO and debris. *\ 1991 or does the facility have plant to treat or recover newty identified TC
    wastes, including TC-contaminated sol and detxis. during 1992 to 1995?

    L_l Yes: Copy and complete Section IV tor ej£ft treatment or recovery system used tor or
            ' planned to be used tor managing the newty-ldemlfiod organic tC wastes. For
             planned uses of a particular sysem. on/y /ocficore loose treatment or recovery
             systoms, tfnf /n your judgementare appropriate tor managing organic* ana are
             capable of treaeng the wastes to ffw c/iaracterteb'c levete. As*/gn a unique number
             ro each system and irrficam lAe nurnoer on eocft page.
    n
No:  ftoceetf lo Section V.
    This section requests information on on-ste treatment or recovery systems that are being used or
could be used to manage organic TC wastes. Folowing promulgation of the LDRs for TC wastes,
some on-ske systems vritt be used to treat wastes that are currently being managed In land disposal
units. We wfflise the ktomakxi in tffc section to dwermto
systems 1or managing TC wastes requiring treattiient loB»«^ promulgation of the LDRs. Therefore,
based on this WormaSon, we wB adjust the total national volumes ol TC waste that win require off-site
commercial ueatment Although we use tactBcy-spectfc Information lor the capacity analysis, we are
not making an/ judgements on how your facfity wB actually manage wastes following promulgation of
the LDRs fie., our use of the information is tor analytical purposes only).

    For each treatment or recovery system. Questions 42 through S3 request Irrtormawxi on the
operational status of the system, the types and Quantities of wastes being managed, and the
limitations and potential obstacles in the use of the system for TC wastes. Questions 54 through 56
address whether the system can treat newty-identified organic TC wastes to or below the
characteristic levels.
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                                                                                                            J

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 O.S. ENVIRONMENTAL PROTECTION AGENCY
Form Approved
OMB NO, 20500119
Expires 12/31/92
ID* 0121
 QUESTIONNAIRE FOR FAOUTiS THAT UNO DISPOSE NCWLY-tDENTIFlEO ORGANIC TC WASTES


 Section IV.    TREATMENT OR RECOVERY SYSTEMS FOR MANAGING NEWLY-JDENTIFIED
              ORGANIC TC WASTES
                                                               \ System No.      j

    42. General description at the system.* (tocfocto a description of tfm processes in tfws system)
    43. System type: {Use AppvxS* B codes or speedy Svirwn).
   44. Is IM$ system subject to RCRA pern* requirement?
      O No: This system is exempt from RCRA pern* requirement.

      LJ Yes: Ai or pan of this system is subject to RCRA permit lequirements.
          Describe the pans requiring a RCRA permk:	
   45. Current operational tutus:
      O Operational (includes routine downtime for standard operating procedures, stack
         demand, and normal maintenance).
      LJ Temccrariy idto (e.g.. non-routine downtime such as major repair).

      LJ Under construction. Expected completion date:     •

      O Wanned, not yet under construcfioa Expected completion dale:	

      LJ Permanent dosed.
                                              ,-. n
                                              ™ sr
                                              O
                                              OO
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                                              71
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   1A system is one or more processes linked together to treat or recover hazardous wastes (see
Appendix B for examples).
Page IS
                                            	j

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U.S. ENVIRONMENTAL PROTECTION AGENCY
                                                                 Form Approved
                                                                 OMB No. 2050-0119
                                                                 Expires 12/31/92
                                                                 ID* 0121
OUESnONNMHE FOR FACOJTIES THAT UNO DISPOSE NEWLY-IDENTIFIED ORGANIC TC WASTES
Section IV.    TREATMENT OR RECOVERY SYSTEMS FOR MANAGING NEWLY-IDENTIFIED
             ORGANIC TC WASTES (continued)
                                                                                                            I
                                                                                                        srl5"
                                                             • I System No.      |
46, Commercial status of system: (CAecfc «ff that «ppJy)
    LJThe system is or wffl be available only lor management of hazardous waste generated
       on site.
    LjThe system is or win be available ony to firms owned by the same company.
    rOThe system is or win be available to a broted group of estabfishments lor commercial
       hazardous waste management  Percent available commercially:	
    LJThe system is or wfll be available to any firm or establishment tor commercial hazardous
       waste management
    dottier.  Please describe:	;	
47. list afl RCRA waste codes entering the system In 1891: {Leave Wan* g system is in
    planning stages or is not cwrenfy oeinj used tot newt/ identified organic TC wastes.)

48. Quantity or wastes entering system in 1991. Units:  tons  gallons  (circle one;
   (Leave Mw* V system is In pluming stages.)
  Total1:           	   RCRA Total:   	
  Liquids:          	   Liquids:          ;	
  Sows/sludges2:    	   Solid/sludges*:	
    Sea
    Debris:
                                              Soil:
                                              Debris:
  49.  Maximum operational capacity (same unfis »* above):
    Total1:            	•        RCRA Total:
    Liquids:          	  Liquids:
    SoW/shjdges2:     	  Sotid/sludges*:.
    Sot             	  Soil:
    Debris:           	  Debris:
                                                                                                              O
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  1 Total includes both RCRA hazardous and non-hazardous wastes.
  2 Quantity should Include both solids and sludges, but not include soil and debris.
                                                                                                            UOl
                                                                                                              J

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O.S.
                                                      Form Approved

                                                      OMB NO. 20504)119

                                                      Expires 12/31/92

                                                      10* 0121
Section IV.   ORGAN|C TC WASTES (continued)
                                                      System No.
d
       wastewaer
Q
                           soa
       haw mwnwm operational capw*y.
       ves: Please prw»e a M* ^scriptioo.
        M: Please prwWe a brief desertion.
                                                                                             lHl
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 U.S. ENVIRONMENTAL PROTECTION AGENCY
Fern Approved
OMB No. 20S04119
Expires 12/31/92
tD# 0121
 CUESnONNMRE FOR FACBJT1ES THAT UNO DISPOSE NEWLY4DENTIFIED ORGANIC TC WASTES
 Section JV.   TREATMENT OR RECOVERY SYSTEMS FOR MANAGING NEWLY-IDENTIFIED
             ORGANIC TC WASTES (continued)
                                                                | System No.

   EPA b examining two approaches for setting treatment standards tor newly-identified organic
   TC wastes: 1} treatment standard levels would be at the characteristic level lor the TC
   constituent; and 2) treatment standards may be below the characteristic level for the TC
   constituent (e.g.. at the concentration levels for F039 wastes).

   54. Car. the system, as currently operating or planned, treat newly-identified organic TC wastes
      TO (he characteristic levels (CFR 261.24)?
      DNO

      ONotsunr

   55. in o»neral. canthe syaem tre« rwwV-Wentified organic TC wastes BELOW the
      characteristic levels? (Use your best judgement and, for the purpose rt this question,
      consider the lower than characteristic levels' to be those lor F039 wastes.)

      LJYes (Prcce«tfrotto next system)
             (Contuiua to Question 56)

      LJNot sure (Continue to question 56)

   SS. Please 1st the specific waste codes whose treated tevete may be above those for F039
      wastes. (Use your best judgement)
   57. Please indicate the types of modifications, a any, that could be made to the system such
      that the wastes could be treated to below trie characteristic leveS. Also include an estimate
      ot the time required to complete the modifications and obtain necessary permits.
                                       >!»
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                                                                 Form Approved

                                                                 OMB NO. 20500119

                                                                 Expires 12/31/92

                                                                 ID* 0121
         uattfon FAOUTTES THAT LAND txspose NCWLY-I
                                                                                                          V
Section V. ADDITIONAL INFORMATION
                                                (SO Federal Register 55160) EPA has
58. In the Federal Register notice o( October 2*. 1991 (W Feoer* negww »,v~,.	

   indicated plans 10 develop land disposal restrictions (LORs) lor newly4denuned organic TC
             ! plans to develop wxj oispwaw •»«>.—___,	,  .
      wastes. Please describe any unique factors at your laeiltty that could potential^ arfect the

      generation or managementoT these wastes after the LDRs are etleetive.  Msopleasa

      provide any additional Information that you want to be considered h EPA'$ evaluation ot the

      capacity impacts of the LDR rule.

* afta
       o
       H
                                                                                                                fs
                                                                                                              'I
 Hi
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   Page 22

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       -  -  .                                   '                Form Approved

                                                               OMB No. 20SO-OU9

                                                               Expires 12/31/92



U.S. ENVIRONMENTAL PROTECTION AGENCY	          ID* 0121	



QUESTIONNAIRE FOR FACILITIES THAT UNO DISPOSE NEWLY-IOEMTIFIEO ORGANIC TC WASTES
Section V. ADDITIONAL INFORMATION (continued)
                                             foresee in the future generation or
   59. Please provide inlormatton on any changes you	.
      management of newly-identified organic TC wastes (e.g., wastes generated as a result of

      future corrective actions).  Please locus on any changes that will likely occur before the end
     60. Wou« yo* fce to receive Wormation summarizing me resuhs ol EPA's data co,,ect,on
                                                                                                         fgd«s
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    Page 23

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                           APPENDIX A

KEWLWOENTIFIED ORGANIC TC HAZARDOUS WASTE COOES AND THEIR CONSTITUENTS
v  Hi.

        Sower 40 CFB 261.24
EPA Huartou* WMM Cod*
0018
0019
0020
0021
D022
0023
0024
0025
0026
0027
0028
0029
0030
0031
0032
0033
0034
0035
0036
D037
0038
0039
0040
0041
0042
0043
Constituent
Beewerw
Carbon letnehloride*
Chkxdarw
ChkxobvnterM
Chlofofonn
o-Cr*sol
m-Crwsol
p-Crtsol
Crcsot
1 ,4-Oichkxob«nzene
1.2-Dichloractharw
Li-Ofchtoroemylwie
2.4-OinArauiuMW
HtpOChkK "
Hexachtwobenzww
Hex*cMoro.l .3-txnadieoa
Kexaehioronluna
Methyl ettiyl ketoci*
Nitrobenzene
Pentachkxophenol
Pyndine
Tetraehioroetnytone
Trichloroetriytene
£3.S-Trichlo«>piienol
2.4.6-TrichtoiOprwrwi
Vinyl CWOfWt
                                                                                   O
                                                                                   w
                                                                                   NJ

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                                            APPENDIX B

                          POTENTIAL ORGANIC TC TREATMENT OR RECOVERY SYSTEMS
•of
 'i
Code

24
25
26
27
28
29
30
31
Treatment or Recovery System
Sod Ti«mm«nl Sy«tem»
Cftemie*! Extraaion
So< Washing
DecNorinuion
Low-T*mporature Thermal Desorption
HigfvTempertthjf* Distillation
Thtmal Destruction
Stabibation
Vernation
                                                                                                  o
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                                        APPENDIX C

                                       DEBRIS TYPES
t.)
Cod*
01
02
03
04
OS
08
07
08
09
10
11
12
13
14
IS
18
17
18
19
29
21
22
Ocbrl* Typ«
Asbestos
Intact Sanenes
Battery CasM
Bncks, Refractory
Bricks. Other
Ceramics > '
Cloth
Concrete
Electrical w>-es. Switches. Eic.
Electronic Coroponeflts
Equipmert and Structures
pTH^- ^ —- *-j *M~.~ —
rnflf uannogev
Glass
Metallics
Paper or Cardboard
Personal Protection Equipment
Plastics. Not Otherwise Specified
PVCPipe
Rock or Other Non-Sot Geotogfc Material
Rubber OOfKii
Slag
Wood
                                                                                                o
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                                                    APPENDIX 0
                                              SAMPLE BLOCK DIAGRAMS
                                                                                           •. .-1
                                                                                                            C «r

                                                                                                          Si1
                                                                                                          £•<*'
&
                                                 TC PROCESS WASTE
                                                                          sr
                                                                        0-8
                                                                        c s
'•?•*
     O
                                         BKK.OGICXL
                                                       TC WASTE STREAM
                                                                             SUBTITLE C
                                                                             LANDFU.
                                        EXEMFrMPDES
                                       •  DBCHARCE
                    TC WASTE STREAM.
SLUDGE DEWATOUNO
    IN SURFACE
  IMPOUNDMENT'
                                            HNON-T
                  TC WASTE STREAM
                                                                           UNDERGROUND
                                                                             INJECTION
                                                                               WELL
                                         SUBTITLE D
                                          LANDFILL
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                                                                        CO
                                                                        N)
                                                                        hd
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                                                                                                                T^

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                                       APPENDIX 0
                                   SAMPLE BLOCK DIAGRAMS
                f C-CONTAMINATED SOIL AND DEBRIS MANAGMENT
                             ROUTINE GENERATION
>*«

SPILL
ICCOHT.
SOI*
DOJUS

TCCOOT.
SPILL
CLEANUP
DEMO
TREATMENT
NW-TC
>EMB
                                     ICCOKT.
                     SPORADIC AND REMEDIAL GENERATION

REMEDIATION-
DERIVED
WASTES

1

IN SITU
TREATMENT

1
                                           o
                                           00
                                           NJ
                                           71
                                           O
                                           O
                DECOMMBSONINO
                 MAINTENANCE
                    OTHER
                                      ON-SFTE
                                     TREATMENT
 OFF-SITE
TREATMENT
                                                       SUBTITLED
                                                        LANDFILL
                                      SUBTITLE C
                                      LANDFILL
                                           CO

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                   For summaries of the TC Survey Jain provided by non-CBI facilities, please refer

             to the Capadty Analysis Background Document in the docket for the proposed rule.

            •This appendix also provides summaries of the TC Survey data for five facilities that were

             not included in the proposed rule.
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                                                 OffMle TC Sumy Stuuurj
                  EPA ID No:
                  Questionnaire NOJ
                  Facility Name
                  Facility Contact:
                  ICFCoaucc
                  Date Received:
MUXXXBZffiSi
0118
The Upjoha Company
Jama Turedc
Liserte Lambrefts
10 April. 1992	
                        The Upjoha Company is • phirmaceaikal company. The «ajiewaier fenerated (ram routine
                 pharmaceutical production proceuc* curia three TC wasta coda. In addition to these, the waste
                 conitiei 24 other commoa sotwao. The Upjoha Coaptay reports thit this viste b not compatible with
                 coDveuiioul mstemter imtaem qtteat.

                        Patke Dei optntet two deepvcUs for maufcmcot of wasta feaenied on site. The taciltty
                 submitted a no-nifRtioa petition in September 198S. which has beat approved, bat does not spcriflrally
                 mention orpnic TC watiet.

                        The bdUqr ha* an ongoinx waue mmimiatton profitm, iadodlax equipment and process
                 modification, waste stream sepefatioo. (ecydla( tod rtcovery for reuse, and dated loop recydinf. In
                 December 1991 the ttdttrjr added a steam suippiai syitems coatlstiai of equallzatioa tanks, snipping
                 colmnn and iceovtty tanks. This treataeat synem b expected to reduce the concentration of some TC
                 opattHaeus fcy 90%^ tmt the faciBty w« mcenaig this woald be aeneivtble for D028 and DC3*.
WASTE STREAMS MANAGED
Waits
Stream
rfVmtMBT
i
Wm»U Codes
D02S/3S/M
DOOW
Methyjeae CUewtde
1.4-Dtaane,
' Mnhanol .'u.ttoiu.
Ethyl acetate.
TctrujrQfonuuu
HcptiBCk t'Botttol,
Totneat. Xyteac. .
B*PropoBol. HonCt
EtkaaoI,a-B^ji
Aoanedtrik. n^j*
akokol.Etkrlcne
isobayl fcetooe,
CydohenM.
Cjdohexuot
Type of
OtaerackM
Roatiae
Time of
Generation
1991-
Typ«
of
Watt*
WW
Qoadty
61500
toai per
year
MuafemeBt
Ualt
UI
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~^i
'• t
 »
                            SU"*
                            illbl

 !2s£
 *.*:*
                           E.
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  f I !
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                                  Organic TC Sumy Sumo«rj
 EPA ID No:
 QuestioinaiieNo:
 Facility Name
 Facility Contact:
 ICF Cnraa:
 Date Received:
HDDOS6766395
0114
Hawaiian ladcpendeat Refinery
Leonard K. Younj
James Hsu
5/22/92
        This {aciliry hat two stirfaoe impoundments that manage TC wutes generated on-site.  la October.
 1994. the siniace impoundments will be closed wita the TC wastes ia puce. The suffice inpountfmeau wilt
 be repliced by a new above {round wastevaur treatment sysiem.

        Waste stream *1 Is wutewater jeoented routinely from petroleum refiainj prooessea.- The watte
 strem i»nt»to benzene (D018). Wane minimiiaUon aorvities (process modification and rate tegreption)
 are currently on-joinj.  The modtficadon of tee te|reptioa process will allow tie discarded petroleum
 product samples to be placed ia containers for recyde. This tiaafe will beip giinimiae the amogat of benzene
 is ite ntsttwater itream.  However, this tidtity did not taw to estiaate of the annual reduction ia the
jeaentioa of wane ts a result of the waste mintmi'Titioa activities.

        Both surfice impoandtneatt are toed u rreaoaeat ttdlities; ooe for oil sldmmint and the other for
biolofiial treatmeat.  In 1991, the treanneat system treated, 16&WO tons of liquid  wzstewater and has a
mrnrntn operational capacity of 191,000 UBS of liqtttts. The treatment syttem treats the D018 »«te to
below in caaraaerisiic level                                                                •

Wiste
Stroun*
1
1
Waste
Cods
D01S •
D018
WASTE STREAMS MANAGED
Typeof
Genenttcm
Routine
Roctiae
Time of
Generation
1991-1993
1994
Type of
Wane
WW
WW
Quantity
168400
tOtt^T
140000 tons

KvUttfCfflCDt
Unit
SI
SI
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                              PHONE LOG
 EPA ID:    HEDOS6786395

 EPA Region:     9

 Facility Name and Address:
                      Questionnaire No.: 114
Hawaiian Independent Refinery, Inc.
91-325 Komohana Street
Em Beach, HI 96707
Contact;    Mr. Qiris Jansen
           Environmental Coordinator

Phone Number    (808) 547-3242

FAX Number

CaJlen      James Hsu
DATE           DISCUSSION

5/1         Asked when the TC Questionnaire would be completed.  Mr. Jansen
           indicated that it would be completed within a week.
  c 8 E

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                               PHONE LOG
EPA ID:    PAD0716I2683

EPA Region:      -3

Facility Name and Address:
                                       Questionnaire No.: 36
                 BP Oil Company
                 Marcus Hook Refinery
                 P.O.Box 428
                 Marcus Hook, PA 19061
Contact:    Mr. Colin Franks
           Environmental Coordinator

Phone Number:    (215) 499-7023

FAX Number:

CaDen     lames Hsu
DATE

4/1


4/17


4/30


Sfl4


6/15


7/30
      DISCUSSION

Inquire as to the status for completing TC Questionnaire for the refinery.
He indicated that he would complete them as soon as possible.

Inquire as to the status for completing TC Questionnaire for the refinery.
Left message
   *                     •
Called to inquue about itttus of TC Questionnaire for the facility. Left    >
message.                    .

CtSMtoinqfatbGMrtBMrtttQvcniamitofmrtefvafy. Left
menage.

Inquired as to the status of TC Questionnaire for the faafity. Left
Inquired is to the status of TC Questionnaire for the facility. In
Hantibutg.  Talked to Demonic Murry, he wfll convey the message to Mr.
Franks
                                                                                   frs
                                                                               >   *5»
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                                 PHONE LOG
EPA IEh    PAD07I6I2683

EPA Region:       3

Facility Name and Address:
                                                      Questionnaire No.: 36
                              BP Oil Company
                              Marcus Hook Refinery
                              P.OJJax 428
                              Marcus Hook, PA 19061


7/31
Contact:    Mr. Colin Franks
            Environmental Coordinator

Phone Number:    (215) 499-7023

FAX Number

CaBec      James Hsu


                  DISCUSSION
           Mr. Franks responded to message left on 7/30 and provided information for
           toe Organic Toticrty. Characteristic Watte (D01S-D043) Questionnaire over  *
           the phone.
                                  • *                  .
           Mr. Franks Indicated that the refinery has one land-based waste
           manzgcBjent unit, a surface impoundment, that manages TC wastes
           generated oa the. This impoundment is • storage impoundment and it
           scheduled to dote prior to the effective date of mtnjmmn technological
           requirements (March. 25, 1994).  The •••iniiHfl quantity of contaminated
          'sou1 and debris generated from closure of the surface impoundment it 450
           tons and 50 toss, respectively. The refinery recently completed dredging
           F038 wwte» from the surface impoundment (3,400 wet tons of F038 was
           dredged oat), aad therefore, Mr. Franks expects that the quantity of F038
           wastes accumulating in the impoundment from now until the tone of
                 : would be small
                                                                                                   is
                                                                                                     O
                                                                                                     CO
O
O
           Mr. Franks identified the following TC wastestreams generated at the
           facility:

           •     WastettresuD 1 * refinery wastewaten (a combination of process
                 wastewaters and itormwaten) it characteristic for benzene (D018).
                 This wastestream is classified as a wastewater and it generated.
               -.  routinely at a rate of 2,100 gaOonsAmnute (4.6 million tons^rear).
                                                                                                     —I
                                                                                                                            '

                                                                                                                      ill! :.   4

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                  This wastestream flows through the surface impoundment, which is a
                  pan of the wastewater treatment system. The treated wanewater is
                  discharged under a NPDES permit

            •    Wastestream 2 • sludge generated from cleanout of crude storage
                  tanks.  This waste is characteristic for benzene (D018) and is
                  . generated sporadically at an estimated rate of 3.000 wet tonsfyear.
                  This wastestream is not managed in the surface  impoundment.  It is
                  recycled through a centrifuge where the organic constituents, such as
                  benzene, are separated from the sludge.  The residual cake from the
                  centrifuge does not exhibit the D018 characteristic.

            *    Wastestream 3 - spent catalyst that is characteristic for benzene
                  (D018). This wastestream is generated sporadically at an estimated
                  rate of 200 tons per year. This wastestream is not managed in the
                  surface impoundment. It is seat off site for commercial disposal
                  (not land disposal).

      The only on-site treatment of TC wastes is the removal of benzene from the
refinery wistewater (Wastestream 1) using the API separator and polishing filters in the
wastewater treatment train.                                                     '
n
                                                                                                        O
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                               OrtmoJc TC Sumy Suwnary
 EPAlDNa
 Questionnaire No.
 Facility
 Ftdlity «mi*a
 ICF contact
 Date received '
 0023
E.L Du Pont de Nemours, Chamber* Works. Deepwater. NJ
Dt» Alfred Pagaiio
Franco Steinacker
413/92
       This facility has • landfill available only for hazardous wasw fenented oo site. The ratal quantity
ofnaardDBS wastes eaterinf the landfill in 1991 was 11,106 was.

       Waste IDCUB 1140-L-5 b mono nftreeUorobeueBe with wtt and debris from a ipltt cleanup.
rottinely toierated and disposed la the landfill. It fc (entnlly only about 10 percent soil and und. wiib
the naaiader alttodtotabettttae. The ititaa b TC doe to a (DQ21) eolorobeasene eonteat 0(02% and
a (D036) Blooberaese coaieu of 05%. lie entire qtuntity was assiped to NWW. Thus 80% or this
stK*n«is usCpol to 0021 and the remainder to D036V

       Waste sutam 114ai-10, torn D030 sofl eBmtion. is routinely |enente4 and disposed in the  -
landflO. Since no dfflere«iatk« was made betwcea toil tad wdt o««=iu75% p» torn) of the quantity
WM istlped to soO and 25* (110 tow) to 4ebtfc.
                                                                                  ••mi
                                                                                     *
                                                                                     igs
                                                                                     § ~ a
                                                                                     fto »
       Waste sraa 1221-H. dfadtroboowie with sofl. b I
laad&n. It bjeneraDy only about 10 pereeat sofl and tand. the r
                                       ed and disposed in tne
                                       tatdtaitiobewene. 3tons'
       Wane sown 7724*3, fiDC wot* onk sod tod asphalt, ta sporadJeaDy (enerated and dbposed ta
thctudffiL Ttetedtty pitas tobefbi «tm mMmia*« ixtivWei, bw 411 aw provide any detaBs as to
the settedBfe,Mta}C. or extern o( these actMtki. li is abou 74% dirt. <% mter. and 20% aspbalL Water
«rii>twts added to sofl wdjht tot i>»rtboninjp«pose«, 90 tow were ani|B«4 to sofl tad 23 tons woe
assipted to debrb,                                      .       '
o
                                                                                       o
                                                                                       o
                  U6^T4,toBbotta|s,iispomlfe>i^
soQ stteuB has • atooheneae coateat of4U ppm and a lead mien of 19 ppo.

       Waste sttesm IC39-U3. enrated 4ln. wood, aad stof^b ipondiGa^r jene»«ed and dbpojed to
shelaadfflL ttbabo«90*s«o»eoddin,S%e»em^asphaB,o»hnnbet.»»d2%wai«r. 70%
       Wa
disposed ia tfae
oom
15*
                                           The tmaa b abota
         was atrtpad to aoffl aad JS% 10 debrte. aad the m*m wit
Tae fadttry has 2 vettinett lysteof.

The wKiewater m*oncw plant b ased to treat a hamdov waste i
The total itnca quantity treated.ta 1991 «a» 40J84 osmioa tons; the RCRA ««»« sntaa total was
                                    k that k 99J pi
                                                                                                           -C

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 21.416 million toes.  Madman operational capadty it 73 million toot.  War* coda curied fey ibc
 wtstcwiten tednd* DOOI-D043 tad tone K, P. tad U coda. T&S system a or will be available 10 iny
 flnn far ooanxnisl haxardovt wane Baaajeaeai of waucwaien. but tbc waste most be compatible *iib
 the Onaben Worta atntt ud aay tinduiioas set by refutations. The lynem caanot treat f natty
 Jlndie 10 below TC cbaimoerinic leveto. tad the ftoliiy b iajuUinj u indnenior 10 ni*B*|e these «ist«.
 The wittemter treatment pint feaenta »pptnnm*t«ly 100 dry iomtt*y ofiiodfe. ni» iludj* may Deed
 to be iacincnted if orpate tratment itudirds we set below Hie TC levcb. The wutewiier treatmeat
 plut slud|e it pretitJled to pteapiute metib.  The ili>d|e may require metib t ubiliatioa if inorpaie
 tTetUBiat lUBdirdx ire set below die TC teveli.

The U^nid iBjeaten iadnentor. it miltble otJy to muige huuxtouj wastei leaeRted by fiimt owned by
the s««e eomptay.  The tool lueut quamliy mated n 1991 WH 4416 toot: the RCRA wiste ttretm
wtal «tt 727 tons.  Mtdantffl openUou! ctpvaty b 6^00 IOBL Wtste oxies curied by Ute vtstewuen
      : D001, DOQ2. 0003. D008. D01HXM3, RW1-POQJ (only from on
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                             PHONE LOG
EPA ID No:
  NJDOQ23SS730
  2
     Row 130
     r>u pun i. NT nnfrn
none*:

Cdsc
                                                                      ISao-as


                                                                      PHI
                                                                      » * »£"
                                                                      P-jj-ffy


                                                                       III
  Ftuco Stdudxr
U23  Dr.FipaowffliBj|nae|<*. Kariy trnpooible u MKAd te 3 weeks
           on th««. ud raodw 30.000 tnctlMdiMiy from of «Jte.
eoacenfeit Qaertonufre. Received ud •ottej oa fc

 nun of fMrtonikc; «ffl 0M on aid let m bow.
                                          bmtona
2A4  NA
2/19  t*ft
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                              OrpnfcTC Survey Sofflauiy
EPAIDNo.
Questionnaire Kb.
Faeflhy
Facility oosnct
1CF co&tact
Datei
                TXDOOB123317
                0019
                Da Font, Victoria. TX
               Steve Bir|cr
               RUCH Sffjpafkgf
      TM» facility ttaaafei TC wastes feoenied both oo-tite and off4ite ia landfills, tad tome
feaerated m-ctte in Baderpoaad tojeofea web. Some of the HC wmua tie (con ^flh, tnd «e nwied
to badflU vit tpfll deucpt TCmtc saami *1 thmfh f 4 MB nutf«d In nb« Un4a|roaad Injeaion
«dis (UIWi *1 threacb «9), «bew ao-mipWK» petfdon (rabniiutf 9/28A9) WH ipprowd (only
•nibble to mste fenemed n
      The foOo«ia|Bewl]r lined orisaicTC Waste Stnua are ttutfed in tandfilk.-
          I #8 -
Waste Sma #10-
Waste Sana #11-
Waste Stream #12-
^Ifff fffFBlHI #13 *•
Waste Stma #14 -
Waste Saecm #15-
Waste Streaaa #16-
Waste Stmai #17-
          l#18-
                       	soO
                       debtiiiype22.08.19
                       detail type 18.17,19
                       deb* Met, 19
                       deMiqrpel9
                       detail op* aa i
                       «ebrkiype6
                       debris me 19
                                                                                                    o
                                                                                                    71
                                                                                                    o
                                                                                                    o
WasteSot*m#5-
                             »ate cany the F039 code, o4 ttas are likely IP almdy be
                         onridfe (D018, PQ39 tcMi Qpe 12)
                                •anh Otter sM (DOU. R09)
                              ctotk (DOU. BD9 detaH type 7)
                                           (DOU.DGaC.RD9}

                                           My fcwe the
                                           BIFttfafcukm to 1991. tt«M wdto
                               (DtKU, D002, DOUl DQ26, aad DUOS). Tha*j«l«BBHa
                                                 aoaaad
                                                        b 1991. b«M«ed tat
                                                    f.DOU.DaU,adD035). T
                                       «(222J001ivridMl. Tk««*••««
                            222300-119.994- 102J06 Ifcprid t

-------
       [deduced, not specifically provided by facility u sadt)
       System 3 indode* a item stripper B> treat WHIM for benzene NESKAFS prior to deepweU
      • Undoa (type 15). Tito system will tadnde treatment tad iiontfe oaks tobjeet to RCRA.
       Medina capacity wffl be 200 afflloa |»Hon» (S33J33 uni). lie wane must be puipablc and
       low to tottdf coBCCBintioa; IBM It cannot handle ooataolMwd wU and detail Tie qitem it
       todereoanrMioaaadikonUbecottpktedinAB|istori9n.  It will only be available for
       mint ftaented on die. It wfll mat be able to treat TC waste* to or below the cbxnacrisiic
       leveb without addlttou] itrippini colgmitvtinta. which would take a year, pliu
      'Dhidt wooU take 6 months to a year.

   wan; mtatatottofl actMty was adicued hi the queHkmnatre.
                                                                                                         
-------
EPA ID No:
t»A Region:
                 TXDOOB123317
                 6

                 El Da Pont
                 PO Box 2626
                 Vfc»rfi,TX 77902-2626

                 Sieve Bcrger, Eminnncatil Scrvioei
                 312-572-2213
DAIX DISCUSSION

UN  71
     dooMhl ttei the dm to aaapnaind.
     nodvadi 1C tea oftttt (eatnton - Da Pout tta> to the
                                                                    hta
VU   Hneone

1A7   WfflMBd

209
                             Mtup orpak TC nmtti fa Lud-Btted Unto
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                                                                                          *"**"**!
                                                             . €
                                                                             O
                        APPENDIX E

DATA ON NEWLY IDENTIFIED TC ORGANIC MIXED RADIOACTIVE WASTES
 O
•g

-------
ilGH LKV1L TC HUSO WASTESTREAKS
S ID
H~W113
N-W11JI
H-Wllll
N-W113
S-W113
II-W113
K-W113
N-M113
N-W13
S-W113
X-W114
S-VJ.14
' '14
14
.--'•;i4
5-W114
H-W114
S-WJ.14
S-W114
K4
3
0
V CODI
ooia
DO 19
0021
0022
D02fi
D928
DO 32
D034
D035
0940
ooia
D019
O021
D022
002$
D028
D032
B034
D035
D040
D01S
0018
If TYPE
KLW
HLW
KLW
KLH
KLH
KLW
HLW
HLW
KLW
KLW
KLW
KLW
HLW
KLW
KLW
KLH
HLW
HLW
KLW
KLW
HLW
HLW
FORM
1100
1100
1100
1100
1100
1100
1100
1100
1100
1100
3116
3116
3116
3116
3116
3116
3116
3116
3116
3116
1220
1290
INVENTORY
6723
6723
6723
6723
6723
6723
6723
6723
6723
6723
3729
3729
3729
3729
3729
3723
3729
3729
3729
3729
275
0.012
94 VOL
"700
700
700
700
700
700
700
700
700
700
465
465
465
465
465
465
465
465
46S
465
117
0.1
3W LEWJL TC KX3XD HASTE STREAMS
3 19
~W002
-W004
-WO 04
-WO 04
-W004
-vail
-W012
-W016
-won
•won
•won
-won
-K01S
-K019
-W020
-W021
•W022
-W(,?S
-W02*
:-W027
-W027
:-W02?
•-W031
•WOJ1
-«031
-W032
•W032
-K026
-woes
-KOSO
-KOS3
-H090
W COOK
D040
0019
O023
D026
D040
0035
0040
O021
OOlt
D023
D024
D02S
D019
0040
0023
D01I
DC40
D019
D022
3023
0024
002S
S023
3024
D02S
OOlt
0023
0018
0019
3018
0019
D023
W TTPX
' KLLW
KLLW
KLLW
MLLW
KLLW •
MLLW
KLLW
KLLW
KLLW
KLLW
MLLW
KLLW
KLLW
KLLW
•MLLW
KLLW
MLLW
KLLW
KLLW
KLLW
' KLLW
KLLW
KLLW
KLLW
KLLW
KLLW
KLLW
KLLW
KLLW
MLLW
KLLW
KLLW
FORK
6110
4200
4200
4200
4200
3120
5490
6140
2900
2900
2900
2900
2210
2900
2900
2900
2900
3230
3230
2200
2200
2200
3229
3229
3229
3223
3223
• 6400
5120
2110
2110
2110
INVENTORY
0.002 MC
0 NC
0 NC
0 NC
0 NC
0.026
6.42
0.012
0.21
0.21
0.21
0.21
0.02
0.42
0.1S
0.21
0.21
0.21
0.21
0.42
0.42
0.42
0.42
0.42
0.42
0.21
0.21
1.98333 MC
3.40267
9.845
9.945
9. 645
94_VOL





0
0
0
0
0
0
0
0
. 0
0
0
0
0
0
0
0
0
0
0
0
0
0

0
0
0
0
                                                                          3

                                                                          
-------
 D040
 D01*
 DOlt
 0018
 0018
 D018
 D018
 D018
 0018
 DQ22
 D035
 O018
 D018
 D040
 D018
 D018
 D018
 D018
 0018
 D01B
 D01B
 D018
 0022
 D018
 D040
 D018
 0035
 D018
 O018
 ooia
 D018
 D019
 D040
 0018
 D018
 001*
 D028
 D018
 D018
 D019
 D021
 0029
 0040
 D03S.
 D029
 0040
 D029
 0040
 D03S
 D040
 0018
 D040
 0019
 DO 29 '
 S040
0029
 0018
0019
0019
D022
D028
O029
 MLLW
 HLLW
 MLLW
 MLLW
 MLLW
 KLLW
 MLLW
 MLLW
 KLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 MLLW
 KLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
HLLW
MLLW
KLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
2110
2210
2210
2J10
2290
2220
3290
8200
2210
2210
2210
3211
2900
3200
2000
2000
S3 00
2200
2000
220D
5300
5400
5400
2220
3220
5400
2220
3220
2220
2000
1000
1000
1000
5300
3120
1110
1110
2220
2200
2200
2200
2200
2200
3220
3220
3220
5400
5400
3220
3220
5300
2210
2210
2210
2210
3220
6110
6110
2210
2210
2210
2210
9.845
0
0
177.228
0
3. OS
0.98667
0.27
0
0
0
18.934*7
0.006
0.2
0.2
0.2
1.2 NC
6.4 NC
0.2 SC
0.2 NC
0.4 NC
0.2 NC
1.4 NC
0.2
0.4
0.2
0.2
1.6
0.2
0.2
6.
6.
6.
4.
40
1.
1.

4.
4.
4.
4.
4.
0.
105.
105.
5.
5.
1.
0.
0.
2.
1.
NC
NC
NC












.







!.«'
1.6
0.6
0.2
0.2
S6
56
56
56
0
a
0
0
0
0
0
0
0
0
0
0
0
0
0
0







0
0
0
0
0
0
0



0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
o
o
o
                        '

-------
H-WlS-i
M-W1S4
H-W1S9
M-W1SH
M-V15H
H-W161
M-wic:>
K-wi6:t
M-WICI
M-vica
K-wi6i;
•4-H1S7
1C- VI 67
1-W16V
X-H16T
X-W167
3-V1CE
.1-*16E
M-W173
.•f-H172
K-W173
S-W17J
K-W173
4-V1S1
*-W181
•i-witi
«85
.7
92
4-W198
•J-WZOl
4-N201
1-W217
4-H22?
4-W227
1-V227
4-H247
4-W2S3
•I-W285
•f-M2*S
•C-W286
4-W28*
1-M309
1-W312
I-W313
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SR-W048
SR-W04B
SR-H048
SJ.-H048
SR W048
SR W048
SR-W04?
SR-W04.
SR-V04.
SR-W048
SR-W048
WS-W010
WS-W011
WS-W014
•S-W015
PS-W017
TIS-W017
WS-W017
us-won
KS-W017
KS-W018
WS-W018
WS-W026
WS-H028
WS-W029
WS-W030
WS-K032
WS-W032
VS-V032
WS-V032
WS-H038
WS-TO44
WS-TO50
WS--40S1
NS-W052
WS-V073
WV-W01S
WV-K01J
W-H019
WV-U01S
wv-nois
W-W01S
WV-W019
WV-W019
MV-W013
KV-»'019
KV-V019
WV-V019
WV-V019
KV-K019
DM3
Dill
D)15
D')20
D)J1
Di)22
DD23
DDJ4
DD25
OII26
DII37
DII38
DH2S
&030
D(>31
DC 32
0(33
5C34
:35
.40
:4i
C042
D04J
D040
D040
D018
9040
D018
0022
D028
SO 15
D010
ooia
0019
DO 18
DO 18
DO 15
DO 15
DO:LB
D0:»
DO:IS
OO'IO
D0:i8
Do:.e
001,0
oo:.a
00<.0
DO::O
D01.8
D019
DO; 2
DO: 3
DO; 4
DO;S
D02S
DO] 7
003 8
0029
B030
D032
0033
D034
MLLtf
KU.W
MLLW
MLLW
MLLW
MLLW
• KLLW
MLLW
KLLW
MLLW
MLLW
•MLLW
MLLW
KLLW
KLLW
KLLW
MLLW
MLLW
KLLW
KLLW
KLLV.
MLLW
KLLW
MLLW
KLLW
MLLW
MLLW
KLLW
KLLW
MLLW
KLLW
MLLW
MLLW
MLLW
KLLW
KLLW
KLLW
KL:>*
MLi
MLL
KLL»
KLLW
KLLW
KLLW
KLLW
MLLW
MLLW
KLLW'
KLLW
KLLW
MLLW
KLLW
KLLW
KLLW
MLLW
KLLW
MLLW
MLLW
MLLW
MLLW
MLLW
MLLW
1000
4900
4'Ofl
4. JO
4&00
4900
4900
4900
4900
1430
4900
4900
4900
4900
4900
4900
4900
4900
4900
4900
4»00
4900
4900
3230
5310
2120
1100
3230
3230
3230
3230
3230
2200
2200
3132
2200
2200
3132
2200
2200
2200
2200
2200
3132
1100
2220
3220
3120
2000
2000
2000
2003
203 i
2000
2000
2000
2000
2000
2000
2C30
ICr.O
2000
    0
 18.1
 18.1
 18.1
 18.1
 18.1
 18.1
 18.1
 18.1
 18.1
 18.1
 18.1
 18.1
 18.1
 18.1
 1B.1
 18.1
 18.1
 18.1
 18. 1
 18.1
 18.1
  0.2
  0.2
  8.7
  2.1
  0.2
  0.2
  0.
  0.
  0.
  O.
  0.
  0.

  0.
  0.
  0.
  0.
  0.
  0.
  0.
  0.
  0.
  0.
  0.
  6.
.0739
.0739
.073»
.0739
.0739
.0739
.0739
.0739
.0739
.0739
.0739
.0739
.0739
.0739
O.CCC7
0.66S7
0.66S7
0.««7
0.66C7
0.66C7
0.6667
0.6CC7
0.6667
0.6667
0.6667
0.6667
0.666-
0.6667
                                                             O
                                                             O
                                                             O
en

-------
•P-wois
»»-W019
*»-W019
W-W019
W-W019
XP-W001
TO-W003
»rW003
*P-W003
•ST-W003
3P-S003
J»-T»03
3*-W003
3P-W003
TO-W003
YP-W003
YP-W003
YP-H003
W-TW03
YP-W003
W-W003
YP-W003
YP-H003
YP-K003
W-W003
— -W003
-W003
-W019
.'?-W019
YP-W023
JTP-W024
{•V-W027
Bfr-W027
YP-K041
YP
D018
D01»
D022
D03S
D040
D018
0035
ooia
D018
D03S
D043
ooia
D01B
D03S
0043
0018
D03S
ooia
O035
D035
DO 18
D027
HLLW
KIXH
KLtM
KLLW
MLLW
HLLH
KU.W
HLLW
KLLW
MLLW
MLLW
KLLW
KLLW
KLLH
HLLW
HLLW
MLLW
HLLW
KLIN
KLLW
MLLW
KLLW
KU.W
KLLW
KLLW
KLLW
KUM
KLLW
KLLW
MLLW
MLLW
MLLW
KLLW
MLLW
KUM
MLLW
KLLW
KLLW
KLLW
KLLW
MLLW
KLLW
KLLW
KLLW
MLLW
MLLW
MLLW
MLLW
HLLW
KUM
MLLW
KLLW
KLLW
KLLW
KLLW
KLLW
KLLW
MLLW
KLLW
KLLW
KLLW
KLLW
2000 4.0739
2000 4.0739
2000 4.0739
2000 4.0739
2COO 4.0739
S300 •
5300
5300
5300
£300
5300
5300
5300
$300
5300
5300
5300
5300
5300
5300
5300
5300
5300
5300
5300
5300
5300
1.55667
.SS667
.55667
.55667
.55667
.SS667
.SS667
.55667
.55667
.55667
.55667
.55667
.55667
.55667
.SS667
.SS667
.55667
.55667
.55667
.55667
.55667
.55667
2000 2.0S007
2000 2.05007
3900 0.06047
3100 0.0997
5300 0.35039
5300 0.3S039
2000 0.2
2000 0.04S4S
5300 0.04S4S
8200 0.05303
8200 0.05303
8200 0.05303
8200 0.05303
8200 0.06061
2000 129.5541
2000 129.5541
2000 129.5541
2000 129. $541
2000 14 . 864
2000 14.864
2200 0.00045
3900 7.70911
3900 7.70911
3900 7.70911
3900 3.48305
5490 18.7612
5490 1S.7«12
5490 18.7612
S400 10.33267
5400 10.33267
2000 4.58848
3100 1.57289
3900 0.4
5400 2.60179
5400 2.60179





HC
HC
NC
NC
NC
NC
NC
NC
DC
NC
NC
HC
NC
NC
NC
HC
NC
NC
NC
NC
NC
NC
NC
NC


NC
NC
NC
NC

NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC


NC
HC
0.6C67
0.6667
0.6667
0.6(67
0.6667
























0
0




0






















0
0


o
l/J
o
o
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-------

YF-WJ83
YP-K183
YP-H18*
YP-WJ90
YP-W104
YP-WL22
YP*IT122
YP-W1123
YP-K123
YP-WU41
YP-W!i43
YP*W7.4€
»-1P»47
T9-W!.48
IP-It 49
YP-Wi.49
YP-K3 54
TP-W154
YP-WJ54
YP-W1S4
YF-WI63
VP-W64
YP-W169
YP-W171
YP-OT7I
«72
73
74
YP-«fl7«
YP-W176
W-W177
W-WI77
YP-W179
YP-WI80
YP-W182
D03!i
D04il
DOKI
D03!>
0040
O01!>
004 2:
D01S
0043
DOlt
0011
0011
Doia
0011
DOlt
0043
DOU
D022
D028
0029
D018
0018
D019
0018
D03S
0018
MIS
0035
D018
O035
0018
0035
aoia
0018
0018
TRWstnuwic TC
MS ID
xiMni2
is -in 12
n-tnu
nr-Wll2
IN-W1L2
IK- VI 12
XB-W1U
IM-W112
IK-WllJ
UI-W1.I2
llt-Wl$4
XH-W157
IN-Wll>9
IK-WlliS
IH»WX1I8
IS- Will •
:H-W1!I7
rs^wijts
:a-wi«i§
;K-W20B
:H-W2(H
:H-W2(I8
:X-K2{>9
HUH
KLLW
KLLW
MLLW
KLLW
KLLW
KLLW
KLLW
KLLW
KLLW
KLLW
•KLLW
KLLW
KLLW
MLLW
MLLW
MLLW
MLLW
KLLW
KLLW
MLLW
KLLW
KLLW
MLLW
HLLW
KLLW
KLLW
MLLW
KLLW
MLLW
KLLW
HLLW
KLLW
KLLW
KLLW
5400
5400
2000
5300
5400
3900
3900
3100
3100
2030
3900
4100
2000
2000
5400
5400
5400
5400
5*00
5400
2000
3900
5300
2000
2000
2000
2000
2000
8200
8200
2000
2000
3000
8200
8200
2.60179
2.60179
0.02727
0.03697
0.00909
0.69697
0.69697
0.06091
0.06091
0.57455
1.77273
0.85757
0.22728
0.04091
0.42423
0.42423
0.06061
0.06061
0.06061
0.06061
0.35773
0.1303
0.00061
0.1759
0.17S9
0
0.0909
O.OOOS
0.13633
0.13633
0.1137
0.1137
0.10607
0.0718
0.0682
NC
NC
NC






HC
HC
HC
HC
HC
NC
HC
HC
NC
NC
RC
NC
HC

NC
HC

NC
NC


NC
KC
HC





0
0
0
0
0
0













0


0


0
0



0
0
MXED HASTESTREWSS
W CDI>B W TYPE
0018
D019
0021
D022
D026
0028
D032
0034
D03S
D040
0022
DO22
D022
0029
0022
0028
0022
0022
0029
0022
D028
0029
0022
tfTRB
KTR7
Mnta
KTRO
Mnto
KTRO
wraa
KTRD
KTRO
unto
KTRU
unco
KTIOT
KTRO
tana
KTRU
KTRD
KTRO
WTRO
MTRO
WTRO
KTRU
KTRQ
FORK
5410
5410
5410
5410
: 5410
5410
5410
5410
5410
5410
3150
3150
5440
5440
3150
3150
5440
5310
5310
• S410
5410
5410
5410
INVENTORY
20.4
20.4
20.
20.
20.
20.
20.
20.
20.
20.4
1.91
164.09
5774.64
5774.64
1.06
1.06
778.34
170.38
170.38
26.24
26.24
26.24
60.16










NA
HA
NA
NA
NA
HA
NA
NA
NA
NA
NA
NA
NA
94 VOL
6.
6.
6.
6.
6.
6.
6.
6.
6.
6.













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-------
feH-V209
PH-W209
1H-W216
XN-W216
IK-W218
IN-W218
XK-H22*
IN-W228
XK-V243
IN-W247
XH-W247
XH-M252
IK-H252
IH-W2S3
•IH-«76
IK-V376
IH-W294
IH-H29C
XN-M296
IH-H311
KA-W16
KA-H01S
XA>mi6
Ui-W019
R1-W134
SR-W026
SR-W026
1SR-W026
SR-W026
SR-V026
SR-W26
Kt-H02£
Bnt-H027
5R-H027
SR-W027
SR-W027
SR-W027
SR-W027
SR-W027
SR-W044
SR-V044
0021
0029
0022
D02»
0022
002t
9022
D028
0029
003«
0029
0022
D028
0029
0022
0021
O022
D028
O029
0021
ooia
D03S
0040
0040
0019
001 •
0019
0022
0023
0024
0025
0026
0018
0019
0022
D023
0024
D025
0026
001S
9040
HTRO
KTRO
MTRO
KTRO
KTRO
MTRO
MTRO
MTRO
KTRO
KTRO
WTRO
MTRO
MIRO
MTiUI
KTRO
KTRtJ
tsaea
MTRD
KTRO
WTRO
KTRO
MTRO
. MTRO
KTRO
MTRO
HTRO
KTRO
MTRO
KTRD
Kl'KU
KIWI
HTTO
KTRO
MTRO
KTRJJ
mm
M'KU
MTRO
MTRU
KTRO
KTRO
5410
541.0
3150
3150
3150
3150
3121
3121
5220
•900
8900
5311
5311
5311
5000
5000
5100
5100
5100
3140
5000
SOOO
SOOO
2110
$190
5400
5400
5400
5400
5400
5400
5400
5400
5400
5400
5400
5400
5400
5400
2100
2100
  CO.IE
  CO.16
2531.01
2S31.01
 459.19
 459.19
 1236.8
 1Z9C.B
  247.7
 199.45
 199.46
 ICO.23
 160.23
 1G0.23
 391.78
 391.78
 443.21
5243.44
5243.44
   6.57
      0
      0
      0
    0.3
   0.21
   66.9
   66.9
   66.9
   66.9
   66.9
   66.9
   66.9
 495S.5
 4955.5
 4SSS.S
 4955.5
 4955.5
 4955.5
 4955.5
     1.3
     1.3
KA
HA
HA
KA
HA
HA
KA
HA
KA
HA
KA
KA
KA
KA
HA
HA
HA
HA
HA.
KA
     0.036
     0.036
     0.036
       0.3
      0.61
       371
       371
       371
       371
       371
       371
       371
         0
         0
         0
         0
         0
         0
         0
o
C/l

                                                                                   J

-------
                                                                   "1
                                                       •Iff'
                                                       ll
                                                       o
         APPENDIX F

DATA ON DEEP WELL INJECTED WASTES
                                                        I


                                                        4^
                                                       un

-------
          APPENDIX C


DATA ON DEEP WELL INJECTEDED WASTES
                                                        O
                                                        C/3
                                                        to
                                                        cn

                                                        on

-------
                                                                                                 a**^f!*Nf
     EPA has vary limited information which differentiates high
TOC D001 ignitable wastes from  low TOC D001 ignitable wastes,
particularly with reference to  the type of Class I injection well
(i.a. nonhazardous versus hazardous) the wastes are disposed
into.  However,  the information the Agency does have indica~.es
that both D001 ignitable  wastes and 0012 - D017 TC pesticide
wastes are deep well injected into class X hazardous wells with
no-nigration petitions.   EPA estimates that, based on management
practices, little if any  diluted high TOC ignitable waste is
injected into Class I nonhazardous wells, and no more than 419
tons of 0012 - D017 pesticide wastes are deep well injected into
Clasn I wells without no-migration petitions.
                                                                             iff!'
o
C/3
to
71
o
o
                                                                                   	<
                                                                                                      •

-------
  41-1207

   934-3000

 ZFINCORPORATED
MEMORANDUM
                                                                    July 9. 1993
H
            Bengie Carroll

            Sarah Stafford and Mario Kerby

  JBJECT:   Deepwefl Injected 0001 Wastestreams
  o
      In the Phase 1! proposed rule. deeharacterized high TOG Ignttabto (0001)
   twastewaters may no longer b* injected into Class I nonhazardoua weds. Th* atlachtd
                               0001 wastaslraams raporttd In th« i989Bitnnial
  to
  71
  o
  o
»
  sportng Syttam (BBS) database Thto Momwdon was attracted from the GM form which
  -ovide* Information on wiste generatkm and management For each wistasiream, me table
:!Kfie*tM the name and EPA ID of the facility generating each waste stream, codes for al the
wastes in each stream, whether the waste was deepwel injected on- or off-tit*, the volume of
each wactattream, and the statue of any no migration petttton at the fadnty. (Under thfc
oropota). tf a wed has a tufty approved no migration petition, the faculty may continue to
-oepweB Inject treated Ngh TOC OOOt wastes.)

      Them are two major ImltatJona In using this data to determine the volume of wastes
,-tfected by tWs provision.  First, facBttes an not required to dWngutoh between high TOC
  \A low TOC 0001 wastes. Thus in the BBS database. H cannot be determined whether a
  •»1 wastestream could be affected by this rule. Second, the BBS does not distinguish
   ween nonhazsntous and hazardous deep wells. Therefore, in estimating the volume of
   :tee aflected by this proposal, we can only use the BBS to provide an upperbound
  -imate.
                                                                                                      CO

-------
                             MM M* EXTRACT Of OCCPWEU. INJCCTa 0001 WAfTCSTNEAMS
V».G       fACUTYNAME
                                      COOl
                                            STREAM   WASTE
                                                      cope
           ftEDlMNBCAMUeM
ALPOOOOMM  CiAIJ&UCASINC
AlDtMOMOTO MAtUCK HOWLS TEPMINAL.
AU0007000M  MOBIL! TANK WASHING
           CEDJ A CHBI1CAL CORPORATION
CAOOOOO»4»t MATUCKINC
                                        4U1
IIHOI wwroQMRcncum
                                       iati
           OHM i we
UOMOTTIM* omn,
                                       4M1
           NALCO
                                IftW
         I UMO»MOO
OUAKTITY
 IN TON*
                                                                               PETITION
                                                                               STATUS"
                                                   DOOI
                                                   ooot
                                                   Mil
                                                   MIT
                                                             OFF
                                                                           4i.it INOTKNOWN
                                                 •  DOBI
                                                   fOtt
                                                             Off
                                                 9  DM1
                                                   CM*
                                                             OFT
                                                 a  oooi
                                                             Off
                                                 t  00*1
                                                                          aai .n
                                                 *  oooi
                                                             off
                                                                          111.M
                                                 a ooot
                                                   DOM
                                                             or*
                                                                          tTt.0*
                                                It  OOOI
                                                             Off
                                                                            7.\\
                                                   oST
                                                 •  0001
                                                                            0.00
                                                 4  DOOI
                                               riioooi
                                                   DOW
                                                   0011
                                                             Off
                                                10 oooi
                                                             Off
                                                                            IJt
                                                 T OOOI
                                                                            0.10

                                                 1  0001
                                                 2 DOOI
                                                                           SMO
                                                 o 0001^
                                                 « OOOI
                                                 • OOOI
                                                                                Of ERATINa A8 NONBAI.
                                                                                NOTKNOWN
                                                                                NOT KNOWN
          NOT KNOWN
          WT KNOWN
                                                                                NOT KNOWN
                                                                                NOT KNOWN
                                                                                NOT KNOWN
               •ttinuWn tan CMA Untftynun* MjMtai Cawot Pragram •*•*>«. fMnury 1001.
                                                JULY0.10O9
                                                                                                                           IS!
                                                        O
                                                        (75
                                                                                                                              O
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                                                       en
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-------
                       lOOttM fXTBACTOF OEEPWEI.L WJBCTS) 0001 WASTMTR6AU*
0«i; 	 MOUTVIMMl *C STREAM WASTE OWOfF OUA/mTf FetmOK
oooe OOOE srre MTOM STATU«-


VSDOM7M4M
30MMM3M
3KD041I91M7
3KDOTMMIO*


H

AUERECO ENVIRONMENTAL SEF.V 47H
MM INC Ittl
OOWELLKHUIUaneEHTECKN IMO
ueooNNELOoueiACTiiUA mi

CHEMUNK MM
EHVinONMENTALUAMMEUENTI Nil
US KAW LTV AEJO«>ACe 171 1
UtNAVYCOtWUSCHWCn
0007

t 0001 Off **» INOT KNOWN
* 0001 .OFF tit
a 0001 OFF i at
»01
FOOS
FOOt
S 0001 OFF 10M
» O001 OFF l«i»e»
oooo
0007
ooot
7 D001 ' OFF 1.00
ooot
U1M
Ut» ' .
1 0001 OFF '.1-00
Met
OOM
0004
POM
OOM
OOOT
OOOO
DOM
MM
0011
F001 - .
IMS
• OM1 OFF 1.00
OOM
OOM
OOOT <
OOM
OOM
Ml*
aoii
It OOOt OFF MO
OOM
MOT
MM •
M10
M11
FOOt
FOM
FOM








                                                                                                                    30.55
                                                                                                                  9 g "
                                                                                                                  I.
inMn fHtban «ttii ttkn *wn CUA unMrgrauM ki|M«in Condrt Fray** Ktatne. F*bn«nr 100)1.
                                                                                                                     o
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                                                                                                                     71
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                                          JVH.Y0.1

-------
   ___
QUANTITY
 IN TONS
                         PETITION
                         STATUr
» ocoi
  OON
  OOOT
  0«M
  0010
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