ILLINOIS POLLUTION CONTROL BOARD
March 11,
 1993
IN THE MATTER OF:
 )
AS 91—3
PETITION OF PEORIA DISPOSAL CO.
 )
 (RCRA Delisting)
FOR AN ADJUSTED STANDARD FROM
 )
 (Adjusted Standard)
35 Iii. Adm. Code 721 Subpart D)
ROBIN R. LUNN
AND
MICHAEL O’NEIL OF KECK,
MAHIN
 &
CATE
APPEARED
ON BEHALF OF PETITIONER, PEORIA DISPOSAL CO.
WILLIAM INGERSOLL
AND
MAR1~GURNIK OF THE DIVISION OF LEGAL
COUNSEL APPEARED ON BEHALF OF CO-PETITIONER ILLINOIS
ENVIRONMENTAL PROTECTION AGENCY.
FRED C. PRILLAMAN
AND
STEPHEN F. HEDINGER OF MOHAN, ALEWELT,
PRILLAMAN
 &
ADAMI
APPEARED ON BEHALF OF INTERESTED PERSON
ENVIRITE CORP.
OPINION OF THE BOARD
 (by J. Anderson):
This matter is before the Board on the April
 9,
 1991
petition of Peoria Disposal Co.
 (PDC)
 for an adjusted standard.
The petition seeks an adjusted standard from 35 Ill. Adm. Code
721.Subpart D.
 The petition essentially seeks a hazardous waste
delisting for certain listed hazardous wastes generated by PDC at
its Peoria County facility.
 This opinion supports the Board’s
order of February 4,
 1993 granting an adjusted standard on a
 joint motion for expedited decision,
 as explained below.
PROCEDURAL HISTORY
Peoria Disposal Co.
 (PDC)
 filed its initial petition on
April
 9,
 1991.
 A Board Order dated April 25,
 1991 cited certain
deficiencies in the petition.
 PDC filed its certificate of
publication on April 29,
 1991, and a response to the Board order
on May 15 and June
 6,
 1991.
 A Board order dated July 11,
 1991
requested additional information.
 PDC filed a status report on
January 29,
 1992, and the Agency filed one on February 3,
 1992,
in response to a hearing officer order of January 9,
 1992.
 PDC
filed an amended petition on March 2,
 1992,
 in response to a
hearing officer order dated February 10,
 1992.
 The Board
accepted the amended petition on March 11,
 1992.
 PDC filed a
second amended petition for adjusted standard on May 29,
 1992,
with the Agency as co-petitioner, which the Board accepted by its
order of June 4,
 1992.
 PDC again amended its prayer for relief
in its post-hearing brief filed August 18,
 1992.
The Board received a request for a public hearing from Mr.
Stephen Rone, of East Peoria, on May 13,
 1991.
 Envirite Corp.
(Envirite), a competitor of PDC, filed an appearance and a motion
01 ~0-0
 105
2
to intervene on August 19 and September 3,
 1991.
 PDC filed in
opposition to intervention on August 23.
 The hearing officer
denied intervention on September 11,
 1991,
 but granted Envirite
leave to participate at hearing as an interested person.
 On
March 9,
 1992, Envirite requested a public hearing.
The Board held a public hearing in Peoria on June 29,
 1992.
PDC, the Agency, and Envirite participated.
 Envirite filed a
motion for extension of time to file its post-hearing brief on
July 27 and its brief on August 3,
 1992.
 PDC filed a motion for
extension to file on August
 4 and its post-hearing brief on
August 18,
 1992.
 The Board hereby grants both motions for
extension of time and accepts both briefs.
PDC and the Agency filed a joint motion for expedited
decision on January 14,
 1993.
 Envirite responded on January 26.
The Board granted the motion on January 21,
 1993, and we granted
the requested adjusted standard, with conditions, on February 4.
This opinion supports the Board’s order of February 4,
 1993.
During the course of this proceeding, the Board docketed
three public comments.
 The first public comment
 (PC 1), dated
July 29,
 1991, was from Stephen B.
 Smith, Vice President,
Envirite.
 A letter, dated July 16,
 1992 and given public comment
number
 3
 (PC
 3), was a copy of correspondence sent by Stephen
Smith to Robert Kayser,
 Chief, Delisting Section, USEPA.
 Public
comment number
 2
 (PC 2), dated July 27,
 1992, was from Robert
Kayser to the hearing officer.
The petition filed in April,
 1991 originally sought an
adjusted standard as to K061 and F006 wastes treated by PDC.
 The
petition of March,
 1992, the amended petition of May,
 1992,
 and
the amendment requested in the August,
 1992 post-hearing brief
each sought an adjusted standard as to F006 wastes.
 PDC has
stated that it will seek relief as to K061 wastes at a later time
and in a separate proceeding.
 (March
 2,
 1992 Amended Petition as
2.)
 The Board will therefore consider those portions of the
record pertaining to F006 wastes.
FACTUAL BACKGROUND
PDC owns and operates a permitted hazardous waste treatment
facility in a 7200 square foot building located on a 2—acre site
near Peoria.
 It receives about 30,000 cubic yards
 (yd3)
 of F006
wastes into this Waste Stabilization Facility each year.
 This
waste is sent from about 20 to 30 different platers, anodizers,
chemical etching and milling, and circuit-board manufacturers.
F006 waste
 is, by definition, wastewater treatment sludge from
 electroplating operations.
 (~g 35 Ill. Adm. Code 721.131(a).)
PDC has operated this facility since August,
 1988.
01 ~0-0
 106
3
PDC treats the F006 wastes it receives at this facility with
proprietary reagents in order to stabilize them so that they do
not leach their hazardous constituents into the environment.
 It
has historically then landfilled the wastes in a hazardous waste
landfill that it owns and operates.
 The incremental increased
costs to PDC’s customers is about $65.00 per ton for disposal of
the treated residue as a hazardous waste over what it would cost
to dispose of this waste as a non—hazardous waste in an
industrial landfill.
 This added cost and the desire to preserve
its RCRA-permitted landfill capacity are the reasons PDC has
sought to delist the treated residues pursuant to 35 Ill. Adm.
Code 720.122 and 106.Subpart G.
PDC has established procedures for screening incoming wastes
before accepting them and for verifying that treatment has indeed
stabilized the wastes received.
 PDC has each prospective
customer submit certain information about its waste and waste—
generation.
 This includes a material safety data sheet; the
results of treatability studies from PDC Laboratories, Inc.;
 and
a certification
 (or analytical results) indicating that no
pesticides or herbicides,
 PCB5,
 or dioxins are used in the
production of the wastes, and that they do not appear in the
wastes.
 After waste treatment and curing, PDC tests each treated
batch of the wastes to assure that stabilization has in fact
occurred.
 These tests for selected contaminants involve using
the same RCRA TCLP procedure of 35 Ill. Adm. Code 721.124 that
PDC uses to test the effectiveness of its treatability testing.
If the treated waste residue is still hazardous,
 PDC either
retreats the waste for further stabilization or disposes of the
waste as hazardous waste in its RCRA-permitted landfill.
The adjusted standard granted with conditions by the Board
on February 4,
 1993 allows PDC to dispose of stabilized waste in
its industrial landfill.
 The stabilized waste that meets the
delisting conditions
 is no longer considered a hazardous waste.
PDC asserts that its compliance alternatives to an adjusted
standard are limited.
 It asserts that the F006 waste cannot be
recycled, reused, or treated to render it nonhazardous.
 The only
alternative to the adjusted standard is the continued disposal of
this waste in a RCRA-permitted facility.
 Additionally, PDC and
the Agency assert by the joint motion for expedited decision of
January 14,
 1993 that the decision in Envirite Core.
 v. IEPA
 (3d
Dist. Jan.
 8,
 1993)
 (No. 3-92—0202), that each of PDC’s customers
must individually have separate Section 39(h)
 authorization for
landfill disposal of hazardous wastes,1 threatens to cause it to
Section
~
 prov~.des
in
s
 ni~i~ant
 part
 as
 tkaws
~
 hazardous
 waste
 stream
 may
 flQt
 be
 depos~ted~
 in
 a
U
 I L~0-0
07
4
stop receiving the FOOG wastes for RCRA-permitted disposal, which
would leave PDC with
 a cessation of operations as the only
alternative for compliance unless the Board granted the adjusted
standard.
THE
 ADJUSTED
 STANDARD
The adjusted standard granted on February 4,
 1993, effective
as of that date, renders non-hazardous up to 50,000 tons of F006
waste treated by PDC using a mechanical mixer.
 The treated
residues must meet certain verification and testing requirements
to qualify.
 Those wastes that do qualify are subject to the non-
hazardous solid waste disposal regulations of 35 Ill. Adm. Code
810 through 815, rather than the Illinois RCRA regulations of 35
Ill. Adm. Code 703 and 722 through 728.
The verification and testing condition requires PDC to
perform certain tests, both before and after waste treatment.
PDC must perform bench-scale treatability testing before
 accepting wastes for production—scale treatment.
 PDC must
perform tests on the treated residue to verify treatment using
the methods of SW-846 for certain specified inorganic and organic
parameters on daily- and monthly—composited samples.
 PDC must
periodically submit the results of the treatability tests and
other information requested by the Agency together with a
certification, and it must maintain its records of those tests
open for state inspection for
 a minimum of three years.
PDC must test a daily composite sample composed of grab
samples from each batch of the treated residue for certain TCLP
inorganic parameters
 (cadmium, chromium,
 lead,
 nickel, and
silver) and for total distilled-water-leachable cyanide before
disposal.
 If the treatment residue exceeds any of the levels set
al::
generator
 an
thed.ieposatsite owneran~
operato~for~
 khe
deposit
 o~tha~t
spe~it~~hazaroU~
 waste
 strea*~
~ei~
 m~grant
 ~
I~azardo~
 ~wa~te
 ~treain~~
o~1y
aftr~
 ~generat~r~ha
~easorzab1~r
 demonstrated
 tbati
~
~eäs~tUt~r
 ~M
 e~c~mt~
 ~easo
 eS~~the
~aste
 cannot
 te
 rea~oflab1~t
 ~4jEJd
 ~
 reuse,
 nor
in~ine~ted
~
 e~ai~a~y~
 ~psa~)~o~
 oq~n~y
txeated~so
as
 to
 render
~it
 ~
0i~0-O
108
5
for TCLP inorganics or total leachable cyanide2, PDC must manage
the treated residue as a RCRA hazardous waste.
PDC must also daily test a representative grab sample of
each treated batch for certain TCLP organic parameters
 (acetone,
bis-
(2—ethylhexyl)phthalate,
 chloroform, ethylbenzene,
naphthalene, N—nitrosodiphenylamine, styrene, and total xylenes).
If the initial daily test for a specific treated batch for
organics exceeds any of the levels set for TCLP organics~~DC
~ay
 ana~tyze
~ se~n4 sa~Le~ it
 t1~e~
 se~~a~e
 a1s~~eed~
any
 ~o~an~Q
 para~ne~ter~
 ~
 ia~Ist~
 manage the
 )*tth*. as
 ~.a
2~~A
haz~r4o~aw~ete
to
 the
 meanix~g
of
 the
 word
 ‘¼ompoeite~’
 as
 applJ.ed -to
 organic
pai~ame~e
~ntfrmat
 ton
 ~am~L&ng, in~
 p
 r~grapb~
 4~o) o~
th~
~b~ua~t’~
 4
 ~3
 order~.
 We
 wish
 to
 a1v~oi~
 aner~o~iea~s
inte~pretat~n
that
 ~*composited
 refers
 to
 combining
 grab
 samples
•~•~••••~•~••
 one
 treated
 batch.
 (~g
 PC
 2
 at
 2—3
 (IJSEPA
comment).)
 This
 is
 not
 the
 Board’s
 intent.
 Rather,
 we
 intend
 to
allow
 PDC
 to
 composite
 grab
 samples
 from
 a
 single
 treated
 batch
in
 order
 to
 allow
 it
 to
 assure
 that
 the
 confirmation
 sample
 taken
is
 indeed
 representative
 of
 the
 treated
 batch.
In
 addition
 to
 the
 daily
 analyses,
 PDC
 must
 perform
 a
 more
complete
 monthly
 analysis.
 PDC
 must
 take
 a
 grab
 sample
 from
 each
daily
 sample
 and
 composite
 them
 for
 a
 single
 monthly
 TCLP
 test
for
 all
 the
 126
 priority
 pollutants
 listed
 at
 35
 Ill.
 Adm.
 Code
423,
 App.
 A
 except
 the
 pesticides,
 PCBs,
 asbestos,
 and
 2,3,7,8—
TCDD
 (dioxin).
 PDC
 may
 reduce
 the
 testing
 frequency
 to
 semi-
annually for any constituent found to be below the detection
limit
 for
 six
 consecutive
 months.
 PDC
 must
 continue
 or
 resume
monthly testing for any constituent that appears above the
detection
 limit
 in
 any
 sample.
The
 adjusted
 standard
 granted
 is
 substantively
 very
 similar
to
 that
 requested
 in
 the
 May
 29,
 1992
 second
 amended
 petition,
further
 amended
 by
 PDC’s
 post-hearing
 brief.
 The
 post—hearing
brief
 added
 the
 limitation
 to
 the
 use
 only
 of
 a
 mechanical
 mixer,
thereby
 dispensing
 with
 the
 original
 request
 to
 allow
 mixing
 in
 a
concrete-lined
 pit
 by
 a
 backhoe.
 The
 adjusted
 standard
 granted
differs,
 however,
 in
 that
 the
 failure
 of
 a
 single
 repeat
 daily
~
 ~/I
 ~for
 ~cathniwn~I
 9
m~f
 I
 fO~~thromiWa~ ~
 ~
L ~
 mgfL
 ~or~n.t~ke3~,
 ~U~2
 ~ng~(I~
 ~tI~e~
 ~
 3~
 B
fox~
 ~oy~aXu~de~
16~mg/i for
ac~etone~
 O.O5i~
mqfI
 for
 ~
phtba~ate~G4.3.4 ~mg/I
 ~o~r~h1or
 o~a~
 ~3
 3
 mgfI
 ~
 hyIk~enae.r~e,
~m~/I
 ~or
 naphthaIene~
 Ii I3~~gJ
 3.
 foi~
~
~~i~o-0~09
6
sample
 for
 TCLP
 organics
 triggers
 the
 need
 to
 manage
 the
 treated
residue
 as
 a
 RCRA
 hazardous
 waste,
 and
 the
 second
 amended
petition
 and
 the
 post-hearing
 brief
 requests
 that
 the
 failure
 of
a
 second
 repeat
 sample
 (i.e.,
 the
 failure
 of
 a
 third
 sample)
triggers
 the
 need
 to
 manage
 the
 residue
 as
 hazardous.
 The
 post—
hearing
 amendments
 more
 would
 clearly
 require
 a
 third
 failure
REGUlATORY STANDARD
 FOR
 RELIEF
35 Ill. Adm. Code 720.122
 (derived from 40 CFR 260.22)
provides for delisting of hazardous wastes.
 Subsection
 (a)
provides
 for
 delisting
 of
 Part
 721,
 Subpart
 D
 (40
 CFR
 261,
Subpart
 D)
 listed
 wastes
 from
 a
 particular
 facility
 if
 the
generator
 demonstrates
 that
 the
 waste
 exhibits
 none
 of
 the
criteria
 for
 which
 it
 was
 listed,
 and
 the
 Board
 determines
 that
 no
 additional
 factors
 warrant
 retaining
 the
 waste
 as
 hazardous.
Subsection
 (b)
 provides
 for
 rendering
 inapplicable
 the
 “mixtures
and
 derived-from”
 provisions
 of
 35
 Ill.
 Adm.
 Code
 721.103—
(a)
 (2)
 (B)
 and
 (a)
 (2)
 (C)
 (40
 CFR
 261.3(a)
 (2)
 (ii)
 and
 (a)
 (2) (iii)),
which
 basically
 maintain
 that
 any
 mixture
 containing
 a
 Subpart
 D
listed
 waste
 and
 any
 material
 derived
 from
 a
 Subpart
 D
 listed
waste
 are
 hazardous
 wastes.
Since
 PDC
 treats
 the
 F006
 wastes
 from
 multiple
 generating
sources
 to
 produce
 a
 waste
 deemed
 a
 F006
 hazardous
 waste
 by
 the
“mixtures
 and
 derived—from
 rule”,
 it
 appears
 that
 pursuit
 of
either
 alternative
 of
 subsections
 (a)
 and
 (b)
 might
 have
 resulted
in
 rendering
 the
 RCRA
 regulations
 inapplicable
 to
 the
 PDC-treated
residue.
 PDC
 nowhere
 explicitly
 states
 that
 it
 approaches
 the
Board
 under
 either
 subsection
 (a)
 or
 subsection
 (b).
 However,
since
 PDC
 nowhere
 mentions
 either
 Section
 721.103
 (a)
 (2)
 nor
 full
characteristic
 testing
 pursuant
 to
 35
 Ill.
 Adm.
 Code
 721.Subpart
C,
 and
 the
 thrust
 of
 the
 petition
 is
 aimed
 at
 demonstrating
 that
the
 treated
 residue
 no
 longer
 exhibits
 either
 the
 characteristic
for
 which
 F006
 was
 listed
 or
 any
 other
 characteristic
 warranting
continued
 management
 as
 a
 hazardous
 waste,
 the
 Board
 infers
 that
PDC
 submitted
 its
 petition
 pursuant
 to
 35
 Ill.
 Adin.
 Code
720.122(a).
Under
 subsection
 (a),
 PDC
 is
 viewed
 as
 the
 waste
 generator.
For
 a
 grant
 of
 an
 adjusted
 standard
 delisting
 its
 waste,
 PDC
 must
demonstrate
 that
 the
 F006
 waste
 it
 generates
 does
 not
 exhibit
 the
toxicity
 characteristic
 (cadmium,
 hexavalent
 chromium,
 nickel,
 or
cyanide)
 for
 which
 USEPA
 listed
 F006
 wastes,
 and
 the
 Board
 must
determine
 that
 there
 is
 no
 reasonable
 basis
 other
 than
 that
 for
which
 F006
 was
 listed
 that
 warrants
 retaining
 the
 treated
 F006
residue
 as
 RCRA
 hazardous.
 (~g
 35
 Ill.
 Adin.
 Code
 720.122(a)
 and
(d),
 721.111(a)
 (3),
 721.131,
 and
 721.Appendix
 G..)
 Additionally,
PDC
 must
 demonstrate
 that
 the
 waste
 will
 be
 generated
 or
 managed
in
 Illinois
 (35
 Ill.
 Adm.
 Code
 720.122(p)),
 and
 the
 Board
 will
not
 grant
 the
 delisting
 if
 it
 would
 render
 the
 state
 RCRA
 program
~~i~0-01
jo
7
less
 stringent
 than
 the
 federal
 program.
 (35
 Ill.
 Adm.
 Code
720.122(q)
.)
DISCUSSION
 OF
 ISSUES
 RAISED
Envirite,
 PDC’s
 competitor,
 by
 its
 participation
 throughout
this
 proceeding,
 and
 TJSEPA
 by
 PC
 2,
 raised
 a
 few
 issues
 relating
to
 the
 requested
 adjusted
 standard.
 This
 resulted
 in
 the
imposition
 of
 the
 second-failure
 trigger
 for
 dealing
 with
 the
treated
 waste
 as
 hazardous
 based
 on
 the
 organic
 parameters.
Several
 other
 arguments
 did
 not
 result
 in
 substantive
 amendment
of
 the
 requested
 adjusted
 standard.
The
 easiest
 issue
 to
 dispose
 of
 is
 that
 relating
 to
 whether
the
 waste
 will
 be
 generated
 or
 managed
 in
 Illinois.
 The
 facts
indicate
 the
 PDC
 will
 both
 generate
 and
 manage
 the
 waste
 at
 its
facility
 near
 Peoria.
 Neither
 Envirite
 nor
 USEPA
 challenged
 the
petition
 on
 this
 basis.
 Therefore,
 the
 Board
 finds
 that
 the
waste
 is
 both
 generated
 and
 managed
 in
 Illinois,
 as
 required
 by
Section
 721.122(p).
Before
 beginning
 the
 discussion
 of
 the
 issues,
 the
 Board
wishes
 to
 take
 note
 of
 the
 Agency’s
 joining
 as
 co-petitioner
after
 discussion
 with
 the
 PDC
 and
 careful
 examination
 of
 details
of
 the
 petition
 and
 supporting
 documents
 (see.
 e.g.
 •
 Tr.
 97-103,
re
 sampling
 protocol,
 and
 110—11,
 re
 analytical
 procedures).
While
 ideally
 such
 scrutiny
 and
 the
 Agency’s
 decision
 to
 join
 as
a
 co-petitioner
 would
 take
 place
 before
 PDC
 initially
 filed
 its
petition,
 the
 procedure
 used
 nevertheless
 provides
 welcome
assistance
 to
 the
 review
 process.
 (~,g In
 re
 Petition
 of
KeYstone
 Steel
 and
 Wire
 Co.
 for
 Hazardous
 Waste
 Delistinc~,
 No.
 AS
91—1,
 (Feb.
 6,
 1992)
 at
 9—10.)
Additionally,
 USEPA
 submitted
 comments
 on
 the
 proposed
adjusted
 standard.
 (PC
 2.)
 It
 is
 worthy
 of
 note
 that
 USEPA
commented
 that
 PDC
 submitted
 ample
 data
 with
 its
 petition,
 with
the reservation that
 it
 would
 have
 sought
 groundwater
 monitoring
data.
 (PC
 2 at 1.)
 USEPA did not comment adversely to the Board
granting the requested adjusted standard.
 Rather, USEPA noted a
small number of conditions it would impose.
 For example, USEPA
would require more infomation before allowing use of backhoe
mixing, USEPA would require PDC to manage batches of waste as
hazardous until shown to meet the delisting criteria, and USEPA
would add analyses for additional organic contaminants to the
testing conditions.
 (PC
 2 at 2—3.)
 We discuss these issues
topically below.
The first contested issue relates to whether PDC has
demonstrated that its treated F006 residue is stable over time.
Envirite contended that PDC’s analytical results
(~
 March 2,
1992 Amended Petition at app.
 E, tables 33-51)
 indicate increased
metals mobility with time,
 and a rapid drop in pH with time
ci
i
 0
 —
 0
 1
 I
 I
8
indicates that this trend will continue.
 Envirite cites the need
to continue the testing to follow up on such a trend and cites
USEPA method 1320 in support of this contention.
 (~gEx.
 1 at
1-2 and App.
 B; Envirite post-hearing brief at 5 and 12—13.)
PDC responds that it properly applied the appropriate
testing for the proper duration.
 PDC responds that it employed
the TCLP (USEPA method 1311) procedure of 35 Ill. Adm. Code
721.124 and 40 CFR App.
 II to perform the tests.
 It
argues
 that
this TCLP test has supplanted the former EP toxicity test to
which the multiple extraction procedure (MEP)
 of method 1320
applies, and the TCLP procedure is far more aggressive than the
EP former toxic—MEP procedure because of the selection of acids
and the repeated agitation of samples.
 PDC questioned the
relevance of the aggressive TCLP procedure to the realities
encountered by the waste disposed of in a landfill.
 (PDC post-
hearing brief at 14-16;
 Tr.
 117—21.)
USEPA did not question the trend in the analytical results.
Rather, USEPA stated generally that “PDC appears to have provided
an extensive set of analytical data to support its petition (PC
 2
at 1),
 and “In general,
 the testing conditions included in the
proposed delisting are consistent with the format that USEPA has
used in past delistings.”
 (PC
 2 at 2.)
 However, we note that
this is not an issue specifically raised in PC 3, the letter of
July 16,
 1992 that Envirite sent to USEPA.
Initially, the Board agrees with PDC’s assertion that there
are no fixed criteria for evaluating the MEP results using the
TCLP procedure.
 In examining the results tabulated by PDC in the
March 2,
 1992 amended petition that also provide initial TCLP
results
 (app.
 E, tables 33 through 48), we do not see any
distinct trend or correlation between the slight drop in pH in
subsequent days’ testing
 (about 1 pH lower on day nine than at
the start of testing) and the appearance of metals in the TCLP
leachate.
 Of sixteen samples, only two that would have passed
the TCLP test subsequently showed elevated metals concentrations
at levels of regulatory concern, two showed elevated metals
concentrations in the initial TCLP that diminished below levels
of regulatory concern in subsequent days, and one showed an
elevated metal concentration in the initial TCLP as well as in
later tests.
 The Board does not see a distinct or significant
trend in these data,
 as argued by Envirite.
Envirite
 next
 argues
 that
 some
 of
 the
 testing
 results
contained in the petition indicate that some of the treated PDC
residue contains hazardous constituents at levels above those of
12
9
regulatory
 concern.4
 PDC
 does
 not
 dispute
 this
 assertion.
 USEPA
expresses concern that PDC manage no treated waste residue as
non—hazardous until it is shown to meet the delisting criteria.
(PC 2 at 2—3.)
The
 Board
 agrees
 that
 PDC
 failed
 to
 show
 that
 13
 of
 18
samples of treated residue met the delisting criteria.5
 The
Board also agrees that PDC should handle no batch of treated F006
waste as non—hazardous until testing shows that the batch meets
the delisting criteria.
 However, this is no basis to deny a
delisting.
 The adjusted standard granted requires PDC to manage
all treated F006 batches as RCRA hazardous waste until testing
demonstrates that each batch meets the delisting criteria.
 When
an individual treated batch
 is shown to meet the delisting
criteria, PDC is free to dispose of that batch as a non-hazardous
solid waste.
 This is despite whether the waste passes the test
nearly immediately after treatment or PDC allows an extended cure
time before it meets the delisting criteria.
 (~
 Pr.
 181-83.)
Envirite next cites laboratory quality control deficiencies
and sampling deficiencies in the PDC petition.
 After review of
the petition and transcript, the Board agrees with USEPA.
 PDC
has “provided an extensive set of analytical data to support its
petition.”
 (PC 2 at 1.)
 Further, as stated above, that PDC
sampled over a limited time from random or selected receipts of
waste is immaterial because this adjusted standard does not
delist the waste stream.
 Rather, the adjusted standard granted
applies only to those treated batches that meet the delisting
criteria.
Another issue raised by Envirite, and noted by USEPA,
relates to a lack of groundwater monitoring data in the petition.
(Envirite post-hearing brief at 5; PC 2 at 1.)
 While the Board
agrees that the provision of such data would have been useful
under certain circumstances, those circumstances do not exist
here.
 Although the permitted PDC RCRA hazardous waste landfill
includes treated F006 residue in the fill, the record indicates
~ PDC employed USEPA’s composite model for landfills (EPACML)
in
 conjunction
 with
 the
 Agency
 to
 determine
 the
 levels
 of
regulatory
 concern
 at
 the
 compliance
 point
 based
 on
 the
hypothetical disposal of 50,000 tons of treated residue per year.
(~
 March 2, 1992 Second Amended Petition at tab 2, pp.
 3-5; Pr.
93—95.)
~ Two
 failed
 for
 cadmium,
 one
 for
 chromium,
 one
 for
 lead,
 one
for nickel, three for acetone alone and one for acetone and ethyl
benzene
 (a’though
 acetone
 appeared
 in
 all
 blanks),
 one
 for
naphthalene, one for N—nitrosodiphenylainine and styrene and one for
N-nitrosodiphenylamine
 alone,
 and
 one
 for
 bis-(2-ethylhexyl)—
phthalate.
01i~O-0I
13
10
that this is in conjunction with other wastes.
 (Tr.
 122-23.)
Groundwater monitoring data would have included information
relevant to the co-disposed wastes, and not wholly relevant to
the treated F006 residues.
The final issue raised by Envirite, and noted by USEPA,
relates to the adequacy of PDC’s monitoring and verification
program.
 (~
 Envirite post-hearing brief at 5-6; PC 2 at 2-4.)
The Board believes that the adjusted standard granted adequately
addresses these concerns.
We bear two things in mind in examining the testing and
verification plan.
 These are the standard for issuance of a
waste delisting and the fact that the Agency or PDC can petition
the Board for modification of the adjusted standard if future
information indicates that this is necessary.
The standard for delisting, cited above,
 is that the waste
must show none of the criteria for which USEPA originally listed
it, and there must be no other basis for determining that the
petitioner should continue to manage the waste as hazardous.
 As
noted, USEPA listed F006 waste as a “T”
 (toxicity) waste due to
its cadmium, chromium, nickel, and cyanide content.
 (~
 35
 Ill.
Adm. Code 721.App.
 G; 40 CFR 261, App. VII.)
 PDC must test each
lot of treated waste for each of these contaminants.
 Further,
partially in response to the Agency’s suggestion
(~
 Tr. 97-
98.),
 PDC selected additional contaminants and tested its wastes
for those, then selected the treatment parameters based on the
results obtained.
The petition indicates that PDC tested its treated residues
for a host of contaminants not included in the delisting
criteria, and its untreated F006 wastes for a few more.
 (~g~
March
 2,
 1992 Amended Petition at app~E, tables 21-32.)
 This
indicates that PDC did not include all the hazardous constituents
or TCLP parameters
(~
 35 Ill. Adm. Code 721.124 or 721.App.
 H;
40 CFR 261.24 or 261, App. VII) tested in the delisting criteria
because either these did not appear at levels of concern, when
considering a dilution and attenuation factor
 (DAF)
 of
 19
 (e.g.,
mercury, selenium, chlorobenzene, trichloroethylene, tetrachloro—
ethylene),
 or because there was no reason to suspect that the
wastes would contain the contaminants
 (pesticides,
 PCBs,
 and
dioxin).
Finally, PDC must periodically test its treated residues for
all the 126 priority pollutants (except the pesticides, PCB5,
 and
dioxin)
 and submit those results as required by the Agency.
 The
broader list of contaminants includes the two of concern to
USEPA:
 trichloroethylene and tetrachloroethylene.
 (PC
 2 at 3.)
The Board is not unmindful that if the Agency later finds cause
for concern because these constituents appear at levels of
significance,
 it can then deal with the situation by filing an
O1L~0-OI
lL~
11
appropriate
 petition
 for
 modification
 of
 the
 adjusted
 standard
before the Board.
 The record includes nothing specific to
indicate that the Board should add contaminants to either the
delisting criteria or the periodic testing regime.
CONCLUSION
The Board examined the petition to determine its
completeness in light of the factors of 35 Ill. Adm. Code
720.122(i).
 We have considered the arguments opposed to a grant
of an adjusted standard and the public comments received.
 After
review of the petition and the record, the Board has determined
to grant the adjusted standard delisting PDC’s treated F006
residues that meet the delisting criteria proposed by PDC and the
Agency.
 The petition supports the delisting criteria proposed by
PDC and the Agency.
 It adequately describes the PDC process for
treating F006 waste and the methods and procedures PDC will use
to accept and treat this waste and assure that the treated
residue meets the delisting criteria.
 Further, the petition set
forth an ongoing regime of testing that will have the effect of
either confirming PDC’s delisting criteria, procedures, and
process, or it will ultimately highlight any inadequacies to the
Agency and PDC.
In granting this adjusted standard, the Board has made one
substantive change in the adjusted standard as proposed by
limiting the number of retests PDC may perform if any particular
batch fails to meet the delisting criteria.
 We believe that PDC
should be allowed to retest a failed batch,
 since sampling or
analytical errors could occur.
 Further, additional curing time
could result in a more stable waste residue.
 However, we believe
also that PDC must either re-treat the waste or dispose of it as
a RCRA hazardous waste if the second sample confirms the first.
In addition to this single substantive change, the Board has
made a handful of minor stylistic revisions to the proposed
language.
 None of these warrant individual discussion.
In short, PDC has met its burden under 35 Ill. Adm. Code
720.122 of showing that the adjusted standard granted assures
 1)
that PDC’s treated F006 waste residue that meets the delisting
criteria do not exhibit the characteristic for which USEPA listed
F006 waste, and 2) that there is no other basis for retaining the
waste as RCRA hazardous.
IT IS SO ORDERED.
ORO-Ul
 15
12
I, Dorothy M.
 Gunn, Clerk of the Illinois Pollution Control
Board,
 do hereby certify that the above opinion was adopted on
the
 //~/-~
 day
 of
 ~7~i
 -~I---”,
1993,
 by a vote of
 ~‘
 —~)
/
 1
/
/•2~’
 ~
 /2~.
 ,..
Dorothy
 M.
 Gupr~, Clerk
Illinois
 PolJ~?ion
 Control
 Board
OI~O-O1
 16