United States
                             Environmental Protection
                             Agency
Office of
Solid Waste and
Emergency Response
Publication 9234.2-08/FS
May 1990
      OB*        ARARs  Q's  &  A's
                             Compliance With the Toxicity Characteristics Rule:  Part I
 Office of Emergency and Remedial Response
 Office of Program Management OS-240
                                  Quick Reference Fact Sheet
    Section 121 (d) of CERCLA, as amended by the 1986 Superfund Amendments and Reauthorization Act (SARA),
requires that on-site remedial actions must at least attain (or justify a waiver of) Federal and more stringent State applicable
and relevant and  appropriate requirements  (ARARs) upon completion of the  remedial action.  The 1990 National
Contingency Plan (NCP) requires compliance with ARARs during remedial actions as well as at completion, and compels
attainment of ARARs during removal actions, whenever practicable. See NCP, 55 FR 8666, 8843 (March 8, 1990) (to be
codified at 40 CFR section 300.415(i)(1990)), and 55 FR 8666, 8852 (March 8, 1990) (to be codified at 40 CFR section
300.435(b)(2)(1990)).

    To implement the ARARs provision, EPA has developed guidance, CERCLA Compliance With Other Laws Manual:
Parts I and II (Publications 9234.1-01 and 9234.1-02), and has provided training to Regions and States on the identification
of and compliance with ARARs. This "ARARs Q's and A's" is part of a series that provide guidance on a number of
questions that arose in developing ARAR policies, in ARAR  training sessions, and in identifying and complying with
ARARs at specific sites. This particular Q's and A's Fact Sheet addresses compliance with the recently promulgated Toxicity
Characteristics Rule (55 FR 11798 (March 29, 1990)).
Ql.  How are wastes characterized as hazardous under
     RCRA?

A.   RCRA Subtitle C requirements are applicable to
     CERCLA response actions if the waste is a RCRA
     hazardous waste, and either the waste was initially
     treated, stored, or disposed of after the effective date
     of the particular RCRA requirement, or the activity
     at the CERCLA site constitutes treatment, storage,
     or disposal, as defined by RCRA.  RCRA uses the
     following  two procedures  to  define  wastes  as
     hazardous: (1) the listing procedure, which involves
     identifying specific industrial or process wastes that
     pose hazards to human health and the environment;
     and  (2)  the  hazardous  characteristics procedure,
     which   involves   identifying  properties   or
     "characteristics" that,  if exhibited  by any  waste,
     indicate a potential  hazard  if the waste is not
     properly controlled. See 40 CFR section 261.3(a)(2).
     The new Toxicity Characteristics (TC) rule concerns
     one of four characteristics that indicate a potential
     hazard (the others are ignitability, reactivity, and
     corrosivity).   A waste is a  TC waste if any of the
     chemicals listed in  Highlights 1 or 2 are found in the
     leachate at concentrations equal to  or greater than
     their regulatory levels.
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                                                                                     Printed on Recycled Paper

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Q2.   What are the major provisions of the new TC rule?

A.    The final TC rule adds 25 organic chemicals to the
      list of waste constituents which, if present in waste at
      or  above the regulatory  levels set in  the rule (see
      Highlight  1),  make the  waste  a  hazardous waste:
      These 25 chemicals have  been added to the 8 metals
      and 6 pesticides on the existing list  of  TC waste
      constituents (see Highlight  2).  The  TC rule also
      announced that  13 additional chemicals may be
      added to  the TC list  after EPA  establishes their
      regulatory levels. Finally, the new TC rule replaces
      the Extraction Procedures (EP) with another test for
      determining toxicity (for both the  new and  existing
      chemicals regulated for the characteristic of toxicity).
      The new test is called the Toxicity Characteristics
      Leaching Procedure (TCLP).  The impetus behind
      the development  of  the TCLP was  the need  to
      identify  those  wastes  that are  likely  to  leach
      hazardous concentrations of organic compounds.

      Note:  To determine compliance with RCRA land
      disposal regulations,  the EP  is still  available for
      wastes that are not considered wastewater (i.e., for
      soils and sludges that contain more than 1% total
      suspended  solids)  and  that  contain either any
      amount  of lead,  or arsenic  when  it is the primary
      hazardous constituent, i.e.,  the highest  consituent
      concentration in the waste (see section  3(e)(8) of the
      final RCRA Third Third Rule, unpublished at the
      time of this printing).
Highlight 2: CHEMICALS ALREADY
REGULATED FOR
CHARACTERISTICS AND
REGULATORY
Arsenic
Barium
Cadmium
Chromium
Endrin
Lead
Lindane
Mercury
Methoxychlor
Selenium
Silver
Toxaphene
2,4-Dichloro-
phenoxycetic acid
TOXICITY
THEIR LEACHATE
LEVELS
5.0 mg/I
100.0 mg/1
1.0 mg/1
5.0 mg/1
0.02 mg/I
5.0 mg/1
0.4 mg/1
0.2 mg/1
10.0 mg/1
1.0 mg/1
5.0 mg/1
0.5 mg/1

10.0 mg/1
2,4,5-TrichIoropheno-
xypropionic acid
1.0 mg/1




















Q3.   How  does  the  new TC rule affect the regulatory
      levels of the potential TC wastes already regulated?

A.    The regulatory levels of the eight metals and six
      pesticides remain the same (see Highlight 2 for their
      levels).  These constituents must now be tested using
      the TCLP  to determine whether they exceed their
      regulatory  levels.  It is important to note that  the
      EP and the TCLP may  produce different results;
      wastes  not hazardous   under  the EP  may  be
      hazardous under the TCLP

Q4.   How does the TCLP differ in approach from the EP
      in identifying the toxicity characteristic?

A.   The primary differences between  the TCLP and  the
     EP are:   (1)  the TCLP  uses  two leaching  media
     where the medium is determined  by the pH  of  the
     waste (there is no continual pH adjustment); (2)  the
     TCLP requires  the waste to be ground or  milled
     (there is no structural integrity procedure); (3)  the
     TCLP requires a shorter extraction  time (18 hours
     for the TCLP versus 24 hours for the EP); and  (4)
     the TCLP is easier to run and the  test results  are
     more easily  reproduced.

Q5.  What  is the current status  of the TC rule as a
     potential ARAR  for the Superfund program?

A.'  The TC rule was promulgated on March 29, 1990. It
     became a potential ARAR for all decision documents
     (i.e., RODs and action memoranda) signed after that
     date.   For actions carried out during the interim
     period prior to the effective date (i.e., between March
     29, 1990 and September 25, 1990), the TC rule would
     not  be  applicable,  but  may   be relevant  and
     appropriate.

Q6.  How will the TC rule  affect  Superfund Records of
     Decision (RODs) that have already been signed?

A.   The NCP states that ARARs "freeze" at the time of
     ROD signature.  See 55 FR 8666, 8757,  March 8,
     1990, (to be  codified at 40 CFR 300.430(f)(l)(ii)(B)).
     TC requirements were promulgated on March  29,
     1990, and thus  would not be  ARARs for RODs
     signed before  that date.   For such RODs, the  TC
     requirements are newly promulgated requirements,
     and thus  should  be attained  only  when  EPA
     determines that these requirements must be met  for
     the remedy to be protective.  Newly promulgated or
     modified  requirements  like  the  TC rule will  be
     considered during the 5-year review of the remedy, or
     sooner, if appropriate, to determine  whether  the
     remedy is still protective. Regions should review pre-
     TC rule RODs to ensure that  any on-site disposition
     of wastes still meets the standard of protectiveness.
     (This issue will be discussed further in  the forth-

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      coming TC implementation pact Sheet.)   If EPA
      determines during the remedy review that the TC
      requirements must be attained, a ROD amendment
      or  Explanation of Significant Differences  (BSD)
      should be issued.  See 55 FR 8666, 8757 (March 8,
      1990)   (to    be   codified   at   40   CFR
      300.430(f)(l)(ii)(B)).

Q7.   What are some potential overall effects of the TC
      rule on the Superfund program?

A.    Wastes  containing  any  of  the   newly-regulated
      chemical constituents in the TC rule may be subject
      to  RCRA  regulations  based  on  the  toxicity
      characteristic, regardless of the source of a particular
      waste or whether the waste is a RCRA listed waste.
      In addition, because the TC rule expands the list of
      potential  TC   wastes,  the  amount  of  wastes
      considered to  be RCRA hazardous wastes  at  a
      CERCLA site will potentially expand. Once a waste
is considered to be a RCRA hazardous waste, other
RCRA requirements may be applicable or relevant
and   appropriate,   such  as   closure,  minimum
technology, and  the  land disposal  restrictions.   In
addition,  remedial  alternatives  involving  off-site
shipment  of  TC wastes must  involve Subtitle C
facilities, rather than Subtitle D facilities.
NOTICE:  The policies set out in this memorandum
 are  intended  solely as guidance.   They are not
 intended, nor can they be relied upon, to create any
 rights enforceable by any party in litigation with the
 United States.  EPA officials may decide to follow
 the guidance provided in this memorandum, or to act
 at variance with the guidance, based on an analysis of
 specific site circumstances. The Agency also reserves
 the right to change this guidance at any time without
 public notice.
     In the near future, OERR will issue another Fact Sheet that discusses technical issues that may arise during the
     implementation of the TC rule at Superfund sites. The TC implementation Fact Sheet will be Part II to this
     ARARs Q's & A's Fact Sheet on the TC rule.

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