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