1. 60-182
      2. were granted.”
      3. 80-184
    1. 60-191
      1. —20--
      2. IT IS SO ORDERED,
      3. Page 4
    2. Manganese (Mn)Nickel (NI)
      1. Copp*r
      2. 6O~2i8
    3. Page 4
      1. Specific Organics
    4. 15, 1985 ~ndevery year thereafter.
      1. Dr. Yaron Sternberg
      2. 60-222
      3. j) Provisions for reporting the status of the correctiveaction;
      4. detection monitoring program in Attachment A shall then be reinstated.

ILLINOIS
POLLUTION CONTROL BOARD
October
1,
1984
WASTE MANAGEMENT,
INC.,
)
)
Petitioner,
)
v.
)
PCB 84—45
PCB 84—61
ILLINOIS ENVIRONMENTAL
)
PCB 84-68
PROTECTION AGENCY,
)
(Consolidated)
)
Respondent.
DIXIE LEE LASWELL, D. KEVIN BLAIR, AND ANDREW
H.
PERELLIS
(ROOKS,
PITTS, AND POUST) APPEARED ON BEHALF OF PETITIONER;
AND
ROBERT
E. DAVEY
AND
FINIS
E. WILLIAMS, ASSISTANT ATTORNEY’S
GENERAL, APPEARED ON BEHALF OF RESPONDENT.
OPINION AND’ORDER OF THE
BOARD
(by J.
Anderson):
These consolidated appeals concern permits for which Waste
Management,
Inc.
(WMI)
applied to the Illinois Environmental
Protection Agency
(Agency) regarding operations at its Environ-
mental SaUitary Landfill,
Inc.
(ESL)
site located in Elmwood,
Illinois.
PCB 84—45,
filed April
9,
1984,
is an appeal of various
conditions in Permit No.
1984—16—SP issued March
2,
1984.
~2his
permit relates to installation and operation of
a 46 well
groundwater monitoring program.
PCB 84—61,
filed May
25,
1984,
is an appeal
of the Agency’s April 20,
1984 denial of
a permit to
operate a new trench at the site, Trench 11, which was designed
and constructed pirsuant to a development permit for disposal of
hazardous waste.
PCB 84—68,
filed June
4,
1984,
is an appeal
of
the Agency’s April
30,
1984 denial of 599 supplemental permits to
dispose of various waste streams at the site,
specifically in
Trench 11.
These cases were consolidated for hearing by the
Board on June
29,
1984.
Discovery in the action was extensive, prior
to initiation
of nine days of hearing which concluded September
7,
1984.
The
record in this case,
which was filed with the Board September 10,
1984, consists of slightly over 2,000 pages of transcript, ten
12” x
L6”
banker’s boxes of documents,
and briefs filed by WMI,
the Agency,
and several citizens.
This case is being decided on
the last day of the statutory decision period as extended by WMI.
The Board must note that this deadline has been extended by WMI
80-173

—2—
reluctantly
and
only
for
short periods of
time,
as
the
site
has
had no disposal capacity for
“some
months before” January
19,
1984
(R.
1409), resulting
in estimated revenue losses of
$20,000/week
(Pet.
Emergency Motion for Sanctions,
p.
1,
July
9,
1984).
PENDING
MOTIONS
Pending
are
several preliminary matters.
The Agency’s
motion to file brief instanter is granted,
as the filing delay
has
not
seriously
inconvenienced
the Board,
The Agency’s motion
to
cite
supplemental
authority
is
granted,
as
the
recent
September
6,
1984
appellate
court
opinion
involved
is
relevant
and
would
have
been
discussed
by
the
Board
even
had
each
party
not
kindly
provided
a
copy
to
the
Board.
On
September
10,
1984,
Waste
Management
moved
the
Board
to
vacate
the
August
31
verbal
order
of
its
Hearing
Officer
allowing
intervenor’s
status
to
Gisela
Topolski,
Sherry
Artis,
Mabel
Brockett,
Norma
T.
Rourke,
Robert
Whitler,
Robin
Mc
Williams, Lesley
R. Marr,
Sheryl
L.
Sadowski,
and
Judy
Garthus
“on
a
briefs
only”
basis
(R.
1139—1152).
These
citizens
made
no
objection
to
intervention
on
this
basis,
and
the
Agency,
by
the
Attorney
General,
voiced
lack
of
objection.
The
Hearing
Officer’s
August
31
order
was
a
reversal
of
a
decision
he
made
when
hearings
commenced
August
27,
denying
intervention
on
the
grounds
that
neither
he
nor
the
parties had
previously
received
petitions
to
intervene2
and
that
untimely
intervention would prejudice the parties
(P..
17-23),
WMI’s objections to intervention are that:
(1) intervention
in a permit appeal is not authorized by Sections 39(a),
40
and
61
of the Illinois Environmental Protection Act (IlL~Rev,
Stat,
ch.
111½,
SS1001 et seq.)
(Act),
or by
35
Ill.
Adm. Code Part
105,
(2) the intervenors would not be “adversely
affected” because
they
do
not
share
the
same groundwater system as ESL and live on
the
other
side of the river,
(3) the petitions were filed.
untimely and improperly
in contravention of the 48
hour
pre—hearing notice requirements of
35
Ill. Adm. Code
103.142,
and
(4) denial of intervention would not harm the citizens,
as
their
right to present oral and written testimony is clearly stated in
Sections 40(a)(1) and 32 of the Act,
and 35
Ill. Mm.
Code
103.203.
On September 18,
1984 Norma Rourke filed a response
in
opposition, which response has been considered by the Board
since
WMI’s
motion was filed on the Board’s filing cut--off
deadline~.
Mrs. Rourke in essence argues that any procedural irregularities
should be waived, that the intervenors are “adversely affected”
because property values “are lowered badly
.
.
because of the
proximity to a hazardous waste landfill,” and that these citizens
have been “watch-dogging” ESL since 1979.
60-174

The Board notes that some petitions to intervene were filed
with the Board prior
to hearing, specifically on August
15
(Rourke),
21 (Whitler),
23
(Mc Williams),
24
(Marr),
The Board
al
so
notes
that statements and
in. some cases exhibits were pre-
sented by citizens Topoiski
(Group Exh,
1 with 21 attachments),
Rourke
(Rourke Exh,
1-2), Whitler,
the Ruettigers
(Ruettiger
Exh.
1), Garthus,
Lembcke,
Marr,
and Kennedy,
and that briefs were
filed by Topoiski, the Ruettigers,
Rourke,
and Marr.
As a
practical matter, under the hearing officer’s “briefs only, no
cross—examination” rule,
at hearing the citizens gained no rights
by being named “intervenors” which they did not otherwise have.
The intervention question,
then,
involves whether the citizens by
right may initiate or participate in the anticipated
appeal of
this case.
WMI’s argument that the Board
lacks authority to allow
intervention in a permit appeal case is initially premised on the
fact that Sections 39(a),
40 and 41 of the Act provide no right
of intervention,
WMI notes that the legislature has expressly
provided intervention rights under Section 39.3(d) to citizens at
the Agency hearing level concerning permit applications for
initial development of new regional pollution control facilities,
or
modification
of development permits to allow first time
disposal
of
hazardous
wastes,
WMI contends that
a similar right
under Sections 39(a),
40
and
41 of the Act cannot
“be
lightly
implied”
(WMI motion, p.3).
As to the Board’s regulations, WMI observes that no right of
intervention is expressly provided in Part
105,
although such
rights are expressly provjded in Section 103.142 in enforcement
cases,
Section 104,141 in variance cases,
and Section 103.202(a)
in artificial cooling lake demonstration cases,
While Section
105.102(a)(6) provides that permit appeal proceedings are
controlled by the rules in Part 103
(enforcement proceedings),
WMI alleges that the Board is prohibited from construing this
provision as applicable in this context,
on the basis of the
Supreme Court’s ruling in ~
fill
Inc. v.
PCB,
74
Ill,
2d 541,
387 N.E. 2d 258
(1978),
Landfill involved a challenge to a Board
procedural rule authorizing third party appeals of granted
permits.
The court invalidated this rule,
finding that the
participation of private persons to effect the purposes of the
Act is via the citizens’ right to bring enforcement cases under
Section 31(a) of the Act, rather than by participation as parties
in Sections 39(a)-40 permit appeal proceedings.
In the words of
the court,
the “statutorily established mechanism for persons not
directly involved in the permit application process to protect
their interests
,
,
,
is
Section 31(a)
which
authorizes
citizens’s complaints against alleged violators of the Act
.
.
74
Ill.
2d at 559,
The Board historically has been liberal in its allowance of
intervention rights,
in fact having previously allowed
60.

—4—
intervention in the case of
a permit granted for development of
a
sanitary landfill, Hamman v.
IEPA,
PCB 80—153,
40/PCB/521, Order
of February
19, 1981,
The Board’s November 19,
1981 Supplemental
Opinion and Order
in this action,
44 PCB 753, was the subject of
an appeal brought by one of the intervenors,
Mathers v.
PCB,
107
Ill,
3d
729,
438 N.E.
2d 213
(1982),
While the Third District
upheld the intervention over Hamman’s challenge on other grounds,
the Board~sauthority to allow intervention was not
at issue,
the
primary issue being whether the intervenors’
were “adversely
affected”.
Thus, the Mathers case provides no guidance here on
the authority question,*
The Board observes that
in this case,
the citizens support
the Agency action rather than opposing it as was their posture in
Landfill.
Nonetheless, the Board must find Landfill controlling
in this area,
The Board recognizes that the legislature has
provided
special third party
appeal rights to those opposing
issuance of “RCRA permits”
(~S40(b)and 3(vv), c.f.
§39,2(b)
granting similar rights regarding local government~sgrant of
site location suitability approval), but these
are not such
permits (see infra,
p.13).
In the light of the strong admonition
of Landfill,
and lack of explicit statutory authority or explicit
Board regulation
allowing intervention, the hearing officer~s
ruling
is
vacated,
The Board
has, however,
fully considered the
oral
testimony,
exhibits,
and briefs submitted by the citizens as
autorized
and required
by Sections 40(a)(1)
and 32 of the Act,
and
35
Ill. Mm, Code 103,203.
No
further challenges
were
made
in the briefs
to
any
other
hearing officer
rulings,
although objections to some
were
pre-
served
on
the
hearing record.
In its review of this voluminous
transcript the Board finds no evidentiary rulings which mandate
reversal,
The Board wishes
to express its appreciation for the
unusually fine job done by its hearing officer in moving this
proceeding along at a swift, but orderly and fair,
pace.
The final
preliminary matter is WMI’s renewal
in its brief
(p.
23—24)
of its oral motion at hearing for
a ruling that the
Agency has defaulted this action due to irregularities in and
delay concerning the filing of the permit appeal record as
prescribed in 35
Ill.
Adm,
Code 105,102(a)(4).
The
Board
notes that the permit record
in this case is
voluminous,
consisting of five boxes of paper, bound only by
*The Board would, however, find that the citizens’ concerns
for their property values and groundwater
(see generally
R.1789—1813,
1887—1914,
and Ruettiger Brief p,3,
Marr Brief,
p.1)
provide
as sufficient a showing
of
adverse effect as the concerns
for
inadequacy of roads and contamination of wells in Mathers,
60~476

rubber
bands
and
paperclips,
and
bearing
“Bates~ number
stamps
with
several
gaps
in the numbering sequence.
The
permit
record
“dribbled in” over the course of the summer, pursuant to orders
granting leave to supplement in order to
insure
that
the
Board
was reviewing all
relevant
documents,
WMI’s
current
motion
additionally
recites
that
the permit
record did
not
contain
add~.tional
information
received
by
the
Agency
and which was
or
should
have
been
relevant
and
material
to
its decision,
The omissions included,
among other things,
several
quarters of groundwater monitoring data showing no contamination
which the
Agency
stipulated it had received, but had indeed
failed to include in the permit record,
(R.
885, 961),
The
Board
cannot
condone
the sloppy manner in which the Agency has
handled
its
files
and paper
in this case,
However,
in
a case
such as this involving hazardous waste and groundwater
monitoring,
as
a
matter
of good government the Board will not
find
that
this
inefficiency
has
resulted
in a default which would
preclude
review
of
this
issue on
the
merits.
THE
WITNESSES
Twenty
witnesses
were
called by the parties,
some of whom
also testified as
adverse
witnessses.
To aid
in orderly pre-
sentation
of the facts of this case,
the witnesses are listed
below
with
a
brief
description of their qualifications,
and where
not
obvious,
their
relation
to the permit issues,
Gary
Dietrich
President, Clemont Associates
former
director
of the office of
solid waste U.S.
EPA
who managed and supervised writing of federal
RCRA regulations
David M. Hendron
Vice
President
and
Senior
Associate,
Woodward
-
Clyde
Consultants
Dr.
Yaron M.
Sternberg
Professor of Civil Engineering and University
of Maryland,
Director
of
International Rural
Water Resources Development Laboratory
Consultant
for
Will County Environmental Network
since
1982
Dr.
Ian Christopher Nisbet
Vice
President
and
principal
science
advisor,
Clemont
Associates
-
consultant
for
hearing
purposes
in
area of risk assessment
Robert G, Kuykendall
Manager,
Division
of
Land
Pollution
Control,
IEPA
60477

Lawrence
W.
Eastep
Manager,
Permit
Section,
Division
of
Land
Pollution
Control,
IEPA
Harry
A.
Chappel
Manager,
Facilities
Permitting
Unit,
Division
of
Land
Pollution
Control,
IEPA
Monte
Nienkerk
Groundwater
Advisor,
Division
of
Land
Pollution
Control,
IEPA
Linda Kissinger
Permit
Reviewer,
Division
of
Land
Pollution
Control,
IEPA
Mark A.
Haney
Manager, Facilities Compliance Unit,
Division
of
Land
Pollution
Control,
IEPA
David
Favero
Employee,
Compliance
Monitoring
Section,
Division
of
Land
Pollution
Control,
IEPA
Stanley
A.
Walczynski
Professional
engineer,
Environmental
Management
Department,
Chemical
Waste
Management
Dr. Don L. Warner
Dean
of
the
School
of
Mines
and
Metallurgy
and
Professor
of
Geological
Engineering
at
the
University
of
Missouri
Rolla
consultant
retained
by
Attorney
General
for
hearing
purpose~
Sherry Otto
Geologist,
Manager,
Drill
Regional
Unit,
Division
of
Land
Pollution
Control,
IEPA
Kevin Pierard
former
Environmental
Protection
Specialist
and
Groundwater
Monitoring
Coordinator,
Division of Land Pollution Control,
IEPA
John
Hurley
Manager,
Organic
Laboratory,
Division
of
Land
Pollution
Control,
IEPA
Kathleen Kozack
Investigator, Environmental Control Division,
Office of the Illinois Attorney General
-
prepared
Resp.
Exh.
40
for
hearing
Dr.
Daniel
Hryhorczuk
Head
of
Clinical
Toxicology
Section
Division
of Occupational Medicine, Cook County
Hospital,
Assistant
Professor
of
Environmental
Health
and
Epidemiology,
University
of
Illinois,
School
of
Public
Health
-
consultant
retained
by
Attorney
General
for
hearing
purposes
Craig
Liska
Regional
Groundwater
Monitoring
Coordinator,
Division
of
Land
Pollution
Control,
IEPA
80-178

Walter
Barber
Vice
President
for
Environmental
Management,
Chemical
Waste
Management,
and
formerly
with
the
U.S.
EPA
where
his
most
recent
position
was
as
Director
of
the
Office
of
Air
Quality
Planning
and
Standards.
PERMIT
CHRONOLOGY*
The ESL site consists of about 260 acres located southwest
of Laraway and
Patterson
Roads
in
Will
County.
This
location
is
southeast of the
DesPlaines
River
and
about
2.5
miles
southwest
of the City of Joliet.
The northwestern approximately 160 acres
is the currently
permitted
operations
area,
containing
a
municipal
refuse
disposal
area
to
the
west
and
the
hazardous
waste and other operations to the east and north,
The
southeastern area is a proposed expansion area
(Pet.
Exh,
5,
p.
1) but was denied
local
site
location
suitability
approval
by
Will County pursuant
to
Section
39.2,
Since the site’s
acquisition
by
Waste
Management
in
1973
(Resp.
Exh.
22,
p.
01666),
the
site
has
received
numerous
permits
for various disposal
and
other
activities
(summarized
through
1981 in Resp,
Exh,
21,
p.
01223—01230).
The
following
gleanings
from
the general
permit
history
are
thought
to
have
particular
relevance as general
background.
Permits
for
Trenches
1—10,
in
which hazardous waste
has
been
disposed,
called
for
the trenches
to
be lined with in
situ
clay
soil;
the
trenches
were
constructed
in this manner as
required.
The
original
site
development
permit
had called for installation
of
a
subsurface
leachate
collection
system,
some portion of which was installed before the
system
was
made “obsolete”
by
issuance
of
the
first
permit
in
1978
for
“secure trench disposal”
of
liquid
wastes
in
drums,
Apparently
pursuant
to
the
original
permit
and
a
1978
supplemental permit,
a “G series” of
monitoring
wells
had
been
installed.
(Resp,
Exh,
21,
p, 00938.)
A
“P series”
of wells
were installed in December 1979
and January 1980,
using a then
common practice of using solvent glue on the well joints
(Res.
Exh, 8).
*Respondent~sExhibits 21-25 were introduced to,
apparently,
provide the Board with a chronological compilation of the more
important documents
in
the
permit
record,
The
documents
are
not
chronological,
are
often
duplicative,
are
often
illegible,
and
finally are not filed in any numerical
sequence,
To the extent
that the Board’s attempt to give
an overview of the site’s permit
history is somewhat vague
prior
to
the
time
of
events immediately
surrounding these permit appeals, this is attributable to the
quality of the record and the shortness of the Board’s review
time.

—8—
The monitoring
wells,
as other facets of the
site,
were
scrutinized
for compliance
with the USEPA’s draft regulations to
implement the Resource
Conservation and Recovery
Act of 1976
(42
U.S.C~ §S6901—6987))
(RCRA Act)
by Woodward—Clyde Consultants,
The
May,
1980
study
found
that
several
improvements
were needed,
including
improvement
in
the
locations of the wells in
the
monitoring
system
(Pet,
Exh,
4,
esp.
p.
15), hut
that the site
was acceptable
for
design
and operation of
a hazardous waste
facility.
Pursuant to this study
and other work,
in
the
meantime
a permit
was
applied for and received
in May, 1982
to modify
and
relocate some monitoring wells,
as
welL
as to modify testing
t.o
comply
with
RCRA requirements
(Resp.
Exh.
22,
p.
01251—02303),
No
further
supplemental
permits
with monitoring conditions appear
to
have
been
issued
between
the
May,
1982
permit
and
the
permit
which is the subject
of the
appeal
in
PCB
84—45.
In
December,
1982,
samples from monitor
well
G105
showed
the
presence—-barely
over
the
detection
limit-—of
trichloroethylene,
at
a level
the
Agency
at
the
time
stated could he caused by
a
sampling
or
laboratory
error
(Pet,
Exh. 28).
These reports
raised Agency and
citizen concerns, triggering a major
focus on
groundwater and site
geology issues,
At
some
point
in
the
spring
of
1983,
Mr.
Kuykendall
advised
WMI
that
the
Agency
was
placing
an
“administrative
freeze”
on
further
issuance
of
supplemental
waste
stream
authorizations
for
the
ESL
site
(R,
827),*
Waste
Management
withdrew
its
applications
as
a
result of this “freeze”.
Several
Agency
concerns were outlined
in
Mr.
Kuykendall’s
“letter
of
concerns”
dated April
25,
1983
(Resp.
Exh.
13).
Specifically,
the
Agency
asked
Waste
Management
to
perform
certain
geologic
and
hydrogeologic
studies
for
the
purpose
of
developing
a
new
groundwater
monitoring
system
(R.
828-33).
Mr.
Kuykendall
also
requested
that
Agency
personnel
be
in
attendance
when
these
studies
were
performed.
Finally,
Mr.
Kuykendall
instructed
WMI
to
apply
for
a
permit
once
the
new monitoring well
system
was
designed
(Reep.
Exh,
13).
On
April
27,
1983,
Waste
Management
met
with
Mr.
Kuykendall,
Mr.
Harry
Chappel,
Mr. Monte
Nienkirk,
Ms.
Sherri
Otto
and
other
Agency
employees
(R.
1379).
During
the
course
of
this
meeting,
the topic of discussion
was
the
concerns
expressed
in
Kuykendall’s April
25,
1983
letter,
and it was decided
that
further study would be done
(P..
1379),
At
the
time, the Agency
acknowledged WMI’s application
for
a development permit for
Trench 11 (formerly Trenches 11
and 12).
(Pet.
Exh.
24.)
*Nowhere in the Act
is
a freeze on decisionmaking authorized,
It in fact is contrary
to
the
mandate
of Section 39, requiring
a
decision to issue
or deny
a permit within
a time
certain,
In like
fashion,
a Board “freeze” on decisionmaking in these complex permit
appeals would be contrary to Section 40.
80-180

On
May
17,
1983
the
Agency granted
the
development
permit
for
Trench
21
~Pet,
Exh.
24’,
The
develoo~ent
permit
specified
thet
the
trench
must
~eve
at
least.
10
feet
of
clay
in
the
bottom
and sidewalls,
with a mLnutum two
feet
of
ci ~
being
removed
and
renlaced
in recompacted form
(Pet.
Exh..
24).
The
development
permit also specified
tnat.
t,he
trench
contain
a
synthetic
liner
of
60
mil
high
density
pOiy~thylenC
synthetic
liner
(HDPE),
Because
a
synthetic
:iiter
was
recuired,
the
development
permit
contained
no
speci.f:~cafion
for
maximum
nermeafility
of
the
underi’~inq
clay.
hr~’
tr~uth
was
subsequar.W~v installed
(R,
1391. :~.
On ~hil~-
21,
:~:;
a
meet~nq was
held
between
WMI,
repre~
sentat:Lves
of
Woodward-Clyde
and
the
EPA.
The
purpose
of
th~
meeting
was
to
discuss
the
results
of
the
qeological
studies
requested
by
the
Agency
(R.
1380—81).
The
Anenc.y
asked
that
sore
additional
work
he
performed.
This
follow--up
was
performed
and.
the
July,
1983
Woodward—Clyde
report
was
prepared
(Pet~
Exh.
On
July
12,
19~3,
Mr.
Walczynski
forwarded
WMI’s
application
for
an
operating
permit
for
Trench
11
to
the
agency
for
processing
(Pet,
Ext.
.2;
R,
1383).
Theraai.~er
the
Agency
erkfi.
that
the
application
he
withdrawn,
and
this
request
was
accomplished
by
letter
dated July
27,
1983
rR,
i385-~86; Pet.
fib,
36).
in the
meantime, ESL’s disposal
capacity
was
dwindling
as
the
only
active
disposal
unit,
Trench
10,
was
filling
up.
~
On August
4,
1983,
1’~NI
attended
a
pubi.Lc
meeting
at
th~:
Holiday
inn
in
Joliet
~R,
1389).
By
this
time
Dr.
S~.ernbena oa~
bean
retained
by
the
Will
County
Environmental
Network,
a
cjtiZeflS
group,
at
Waste
~anagerftent’s
expense
(R,
507).
The
Woodward~-Clyde report
was
officially
presented
to
the
pubiic
~R.
1388),
and
comments
were
offered.
At
this
meeting
Mr.
Kuyeidefi
then
stated
that
~4I
must
install
a
new
system
of
monitoring
wells
before
the
Trench
ii
permit
would
:Lssue
(H,
1390).
On
August
17,
the
Agency
sampled
the
P
series
wells.
Laboratory
results
dated
August
19
showed
the
presence
of
tetrachloroethylene
in Well P1 and dichlorof~Luormethanein ~~ell
P
5.
*Some
activity
not,
specifically
related
to
state
permifi
also
commenced
in
this
period.
A
groundwater
assessment
plan
(Resp.
Exh.
32)
was
submitted
to
the
Agency
in
June,
1983,
ani
amended
September,
1983.
(The
submittal
of
the
plan
was
to
satisfy
requirements
of
35
III.
Mm.
Code
Part
725,
Subpart
F
interim
status
groundwater
monitoring
requirements.)
As
a
result
of
a
communication
regarding
cited
deficiencies
(Resp.
Exh.
3o--3:L,~,
a
revised
plan
was
submitted
in
November,
1983
(with
an
annual
report
being
submitted
on
the
1983
calendar
year’s
activities
on
1~pril
9,
1984)
(Resp.
Exh,
32—33),

—10—
During the
following
months
further
study
and.
oermeability
testing was performed
by
Woodward
Clyde
in cooperation with the
Agency~sMonte Nienkirk
and
Sherri
Otto
(H.
151,
173,
231,
1395).
On
December
8,
1983
WMI
again met
with
the
Agency,
this
time
to discuss the latest Woodward-Clyde study results.
This study,
referred
to
as
the
“Confirmation
Study”
(Pet,
Exh,
6,
7)
confirmed the previous
results
submitted to the Agency in July
of
1983.
Several questions were posed
by
the
Agency
and
were
answered
by
Woodward~Clyde and
Dr.
Sternberg
(H.
400).
The
proposed
new
monitoring
well
network
was
also
presented
(H.
231).
The
network
proposed
consisted
of
forty-six
wells
spaced
approximately
185
feet
apart
(Resp.
Exh,
2,
Pet.
Exh.
6,
7).
The spacing
and
number
of wells was based on a computer
model designed to detect
a “worst
case”
“pinpoint”
leak
fifty
feet from the waste disposal boundary
(P..
225,
426,
427,
Pet.
Exh.
6,
7).
On
December
28,
1983 WMI
submitted
two
permit
applications
(H.
1402,
Pet,
Exh,
37,
38).
The
first
was
the
application
for
a
groundwater monitoring permit required by Mr.
Kuykendall
in
his letter
of
April
25,
1983
(R.
1404,
Resp.
Exh.
13).
The
second was an application for the operating permit for Trench 11.
At this point in time the disposal activities at ESL had ceased,
as Trench 10,
the last disposal unit in operation, had been
filled
(R.
1409),
On January 10,
the Agency notified WMI that it
considered the Trench 11 application incomplete
(Pet,
Exh,
39).
On February 15,
1984 the Agency forwarded
a draft ground-
water monitoring
permit
to
WNI
for comment
(Pet.
Exh,
27,
Resp.
Exh.
16).
Various discussions were
had
of permit conditions.
On March
2,
1984 the Agency issued the groundwater
monitoring permit
(Pet.
Exh,
1).
WMI also re—applied. for an
operating permit for Trench 11.
Installation of the 46
monitoring
wells was completed and certified to the Agency
April
2
(H,
952,
Pet,
Exh,
23).
On
March
30,
1984
WMI
wrote
Mr.
Lawrence
Eastep
questioning
whether
more
information was needed before
an operating permit
would
be
issued
(Pet.
Exh,
22),
At hearing
Mr.
Eastep
acknow-
ledged
receipt
of the letter, but he testified that he never made
a
specific
response
thereto
(P..
956).
The
next
Agency
action
was
its
denial
of
the Trench 11
operating
permit
on
April
20,
and
wastestream authorizations “frozen” since spring 1983 on April
30
1984.
THE ACT
AND
THE REGULATORY FRAMEWORK
This appeal raises several
substantial
issues concerning the
inter-relationship
of
the
Illinois
Environmental
Protection
Act,
60-182

—11—
the RCRA Act, the federal RCRA regulations, the Board’s
“identical in
substance”
RCRA
regulations,
and the Board’s
Solid
Waste regulations
which
pre~existed
RCRA.
Exposition of the
relevant
existing
statutory
and
regulatory
framework will enhance
presentation
of the parties’ arguments in this matter,
Title
V
of
the
Illinois
Environmental
Protection
Act
has,
since
its
inception
in
1970,
established
a
regulatory
and
per-
mitting
system for
the
disposal
of
waste,*
Under
the
scheme
of
the
Act,
the
Board
is
charged
in
Section
5(b)
to
“determine,
define,
and
implement
the
environmental
control
standards
applicable
in
the
State
.
.
.
and
to
adopt
rules
and
regulations
.
-
.
“.
The
Agency,
for
its
part,
has
the
duty
to
“administer
.
.
.
such
permit
.
.
.
systems
as
may
be
established
by
(the
Act
or
by regulations”,
to
‘~investigate
violations of
the
Act
or
of
regulations
.
.
,
or
of
permits
“,
and to “appear
before
the
Board
in
any
hearing
.
.
Id.
§1004
(g,
e,
f).
In
colloquial
terms,
the
Board
is
the
rulemaker
and
judge,
while
the
Agency
is
the
permitting
agency,
policeman
and,
in
conjunction
with
the
Attorney
General,
the
prosecutor.
Section
12(a)
of
the
Act
provides
in
general
terms
that
“No person shall:
Cause or
threaten
or
allow
the
discharge
of
any
contaminants
into
the
environment
in
any
State
so
as
to
cause
or
tend
to
cause
water
pollution
in
Illinois,
either
alone
or
in
combination
with
matter
from
other
sources,
or
so
as
to
violate
regulations
or
standards
adopted
by
the
Pollution
Control
Board
under
this
Act;”
Section
22
specifies
the
Board~s authority
to
adopt
regulations
concerning
waste
disposal,
in
accordance
with
Title
VII
of
the
Act,
while
Section
21(d)
of
the
Act requires a
permit
for
waste
disposal
operations.
In
1973,
pursuant
to
the
predecessor
of
what
is
now
Section
21(d),
the
Board
adopted
rules
governing
waste disposal in
a proceeding entitled
In
the
Matter
of
~
8
PCB
659
(July
31,
1973).
These
regulations,
codified
as
35
Ill.
Mm. Code
Part
807,
have
remained virtually unchanged since their adoption.
Section
39(a)
of
the
Act
charges
the
Agency
that:
“When the Board has by regulation required
a
permit
for
the
construction,
installation,
or
operation of
any
type
of
facility,
(or
equipment,
.
.
.
the applicant
*A11
citations
to
the
Act
refer to Sections as currently
numbered,

12—
shall
apply
to
the
Agency
for
such
permit
and
it
shall
be
the
duty
of
the
Agency
to
issue
such
a
permit
upon
proof
by
the
applicant
that
the
facility
(or,
e~ipment,
will
not
cause
a
violation
of
this
Act
or
of
regulations
hereunder,
The
Agency
shall
adopt
such
procedures
as
are
necessary
to
carry
out
its
duties
under
this
Section,
In
granting
permits
the
Agency
may
impose
such
conditions
as
may
be
necessary
to
accomplish
to
the
purposes
of
this
Act~
and
as
are
not
inconsistent
with the
regulations
promulgated
by
the
Board
hereunder.
~
if
the
Agency
denies
any
permit
under
this
Section,
the
Agency
shall
transmit
to
the
applicant
within
the
time limitations
of
this
Section
specific,
detailed
statements
as
to
the
reasons
the
permit
application
was
denied.
Such
statements
shall
include,
but
not
be
limited
to
the
following:
1.
the
sections
of
this
Act
which
may
be violated
if
the
permit
were
granted;
2.
the
provision
of
the
regulations,
promulgated
under
this
Act,
which
may
be
violated
if
the
permit
were
granted;
3.
the
specific
type
of
information?
if
any,
which
the
Agency
deems
the
applicant
did
not
provide
the
Agency
and;
4.
a
statement
of
specific
reasons
why
the
Act
and
the
regulations
might
not
be
met
if
the
permit
were
granted.”
Congressional
adoption
in
1976
of
the
Resource
Conservation
and
Recovery
Act
and
the
USEPA’s
adoption in May,
1981
(45
Fed.
Reg.
33066)
of
interim
final
implementing
regulations
thereto,
codified
at
40
CFR
Parts
260
through
265,
created
a
federal
hazardous
waste
permitting
system
preempting
state
programs
inconsistent
with
or
less
stringent
than
the
federal
RCRA
program.
However,
RCRA
also
provided
that
state
programs
could
operate
“in
lieu
of”
the
federal
program
provided
those
programs
were
“at
least
as
stringent”
and
“not
in
inconsistent
with”
the
federal
program
(42
U.S,CO
Section
6902(b),
The
federal
RCRA
program,
as
well
explicated
by
Mr.
Dietrich
at hearing
(see
generally
H.
75-81),
sets
up
a
two
phase
authorization program.
Phase
I
relates to so called “interim
status”
facilities.
These facilities were
in existence and
operating
in
November,
1980,
have
filed
specified
notifications
to
USEPA
and
filed
Part
A
RCRA
permit applications.
Such
facilities
are
covered
by
broad,
minimum
interim
operating
rules,
and
are
deemed
to
have
RCRA
permits
during
the
possibly
several
years
until
RCRA
permits
are
issued
under
Phase
II.
Phase
II
involves
the
actual
permitting
of
each
facility.
Phase
II
rules
contain
the
technical
standards
for
issuance
of
RCRA
permits, allowing for tailoring of permits to site-specific
conditions after
public
input.
80-184

—13—
Then,
in 1981, the
Illinois
legislature
in
order
to “avoid
the existence
of duplicative, overlapping or conflicting
state
and
federal
programs”
Act,
(Section 20(a)(8),
required the Board
in
Section
22.4(a)
to
adopt
regulations
within
180
days
“identical
in
substance”
to
the
federal RCRA program without
regard
to
the
Act’s
Title
VII
notice, hearing and public comment
requirements or the notice
and
review requirements of the
Illinois Administrative Procedure Act
(IAPA)
(Ill.
Rev.
Stat.
oh,
127 §1001 et s~q~)
in
order
to gain state authorization to manage
its
own
program.
(However,
Section 22,4(b)
permits
adoption
of
“not inconsistent”
and
“at
least
as stringent” additional
rules
provided
Title
VII
(and
IAPA)
requirements
are
fully
followed.
Permit
requirements
under
Section
21
of
the
Act
were
also
specifically
amended
by
creation
of
new
Section
21(f),
the
general
waste
disposal
provisions
of
Section
21(d)
having
been
made
expressly inapplicable.
Section 21
(f) provides
in
Part
that no person shal1:
“Conduct
any
hazardous
waste-storage,
hazardous
waste—treatment
or
hazardous
waste—disposal
operation:
1.
Without
a RCRA
permit
for the site issued by the Agency
under
Section 39(c)
of this Act,
or in violation of any
condition imposed by such permit,
including periodic
reports and full access to
adequate
records and the
inspection
of
facilities,
as
may
be necessary to assure
compliance
with
this Act
and
with
regulations
and
standards
adopted
thereunder;
or
2.
In violation of any regulations or standards adopted
by
the Board
under
this
Act;
or
3.
In
violation
of
any
RCRA permit filing
requirement
established under standards adopted by the
Board
under
this Act;
4.
In violation of any order adopted by the Board
under
this
Act,”
In response to
its
RCRA
rulemaking charge,
the Board has
completed two sets
of
RCRA rulemakings.
The first rulemaking
related to Phase
I
interim
status
rules,
InReThe
Matter
oL~~osedR3llesjorRC~,R81-22 Preliminary Opinion and
Order,
43
PCB
427,
September
16,
1981,
and Final Opinion
and
Order,
45
PCB 317, February
4,
1982,
adopted,
inter
alia,
as 35
Ill. Adm.
Code
725
rules
identical in substance to the federal
interim
status rules,
The Board also
adopted
a Part 700, preserving the
effectiveness of
35
Ill.
Mm,
Code
Parts
807
and
809
(old
Chapters
7
and
9).
This
rulemaking
served
as partial basis for
Illinois’
receipt, on May
17,
1982, of federal authorization
to
operate
Phase
I of the federal RCRA program
(47 Fed. Reg.
21043),
The Phase
I rules ware amended to reflect federal Phase
I amend-
ments in P.82—18,
51 PCB 31, January 13,
1983.
80-185

—14—
Rulemakings related to Phase
II
are
In The
Matter
of
Phase
II,
51 PCB 285, Proposed Rule, March 18,
1983
and
RCRA Rules,
R82—19,
53
PCB
131,
Final
Rule, July
26,
1983 and
In the Matter of Technical Corrections to Phase
II RCRA
Rue~~—24,
55
PCB 31, December 15,
1983.
These
rulemakings,
among other
things,
adopted rules as Part 724 identical in
substance to the federal Phase
II permitting rules.
It also
adopted permitting standards and procedures in Parts 703 and 705.
Certain of these Phase
II rules were reviewed and
affirmed
in
Commonwealth_Edison
Co.
and
Ill.
Power
Co. v.
IPCB,
Nos, 3-83-0749
and 3—84—0024
(consolidated),
September
6,
1984.
The State has not,
as
yet,
received federal authorization to
administer Phase
II,
the
permitting
part,
of the
RCRA
program.
As
a
final note,
it
should be mentioned that in adopting
“identical
in substance”
RCRA
rules,
the Board made necessary
adjustments from the
federal
administrative scheme,
where USEPA
serves as rulemaker,
“policeman”,
prosecutor,
and judge,
to
accommodate Illinois’ bifurcated
scheme that separates these
functions between
the Board
and the Agency.
GROUNDWATER MONITORING PERMIT INTERIM
STATUS
VS.
PERMIT
REQUIREMENTS
The
March 2, 1984 groundwater monitoring
permit
consists
of
a
letter
which
contains 17 special conditions,
and
an
Attachment
B
“Compliance
Schedule” which contains 10 conditions.*
WMI
challenges
the
permit as a whole,
on grounds to be set
forth
below,
WMI is also challenging,
on other grounds, Special
Conditions 12,
13,
14,
16 and 17,
in Attachment A special
conditions 2,
3,
4 and
5
and Attachment B
in
its entirety.
As an interim status hazardous waste landfill ESL is
required by Phase
I regulations to meet certain groundwater
monitoring requirements.
The groundwater monitoring program must
be capable of determining the facility’s impact on the quality of
groundwater
in
the
uppermost
aquifer
underlying
the
facility,
35
Ill.
Adm, Code 725.190,
To meet this
goal,
the regulations
require
that
the groundwater monitoring system
consist of
monitoring wells
(at least one) installed
hydraulically
upgradient
from
the limit of the waste management
area,
and
monitoring wells
(
at least three)
installed hydraulically
downgradtent at the limit
of
the waste management area
(S725,191,
R.
80—84).
The groundwater
samples
obtained
from the monitoring
wells
must be analyzed during the first year
of operation for drinking
*While it is not usual Board practice
to
do so,
this 15 page
permit is attached hereto as Attachment
1 as an aid to the reader’s
understanding of the complexity of the issues herein,
60-186

—15—
water parameters
(Part
725
Appendix
III),
for parameters
establishing groundwater quality
(chloride,
iron, manganese,
phenols,
sodium
and
sulfate)
and
parameters
used as indicators of
groundwater
contamination
(pH,
specific conductance, total
organic carbon and
total
organic
halogen).
After the first
year,
the annual
analysis
includes
the
parameters establishing
groundwater
quality,
and
the
semi—annual analysis is for the
parameters
used
as
indicators
of
groundwater
contamination
(S725,192,
R.
80—84).
After
the
first
year
of
analyses,
comparisons
are
made
between
the
upgradient
and
the
downgradient
wells,
If
these
results
determine
a
significant
increase
(or
pH
decrease)
the
owner
or
operator
develops
and
submits
a
groundwater
quality
assessment
program
which
must
be
implemented
by
the
owner/operator
(S725.193).
If
the
owner
or
operator
determines
that
hazardous
waste
constituents
from
the
facility
have
entered
the
groundwater
then
he
continues
to
implement
the
groundwater
quality
assessment
plan
quarterly
(S725.193(d)(7),
R.
81—84.
The groundwater monitoring
permit
on
appeal
here,
briefly
summarized, requires
the
installation of 46 monitoring wells
completely encircling the closed
and future waste disposal areas
of the interim status
landfill,
Special Conditions
1,
2,
5,
6,
7,
8,
9
10; Conditions
1,
6,
7,
8,
9
and 10 to Attachment
A.
The
wells are spaced approximately 185 feet apart
(R.
224).
Four of
the wells are background wells and thirty-seven are hydraulically
downgradient.
These
wells
are screened in the uppermost aquifer
underlying
ESL,
Five
wells
are
screened
in
the clay
till.
WMI
does not dispute the number or
location of the wells,
although it
believes the number of wells and the till monitoring requirements
are
in excess of
that
needed
to adequately monitor ESL.
The permit imposes a schedule for sampling and analyzing
groundwater collected from the wells in Condition
5 to Attachment
A.
In
addition
to
the
parameters imposed by Part 725, Subpart
F--drinking
water
parameters,
parameters
establishing
groundwater
quality
and
the
parameters
used
as
indicators
of
groundwater
contamination--the
permit
requires, during the first year,
analysis
of
samples
from
certain wells for over seventy-five
hazardous waste constituents identified at 40 C.F.R. Part 261,
Appendix VII
(“Appendix VII parameters”)* as well
as analysis of
samples from all the wells for eleven additional inorganic
parameters and thirteen additional organic parameters
(Special
Condition 13; Conditions
2,
3,
4 to Attachment A;
R.
86).
*The
Board
suggests
that
the parties
are
actually referring
to Appendix VIII
to
40
CFR
Part 261,
as Appendix VII is the “Basis
for Listing Hazardous Waste”,
rather than “Hazardous Constituents.”
However,
the Board
will
continue to refer
to
Appendix
VII in order
to
avoid
confusion.
60-187

In
addition to the 46 new wells, the
8 old P—series wells
must
still be sampled and analyzed
(Special Conditions 12,
13;
Condition
2 to
Attachment
A;
R.
87).
After the first year,
these
samples must be
analyzed
for
eight
organic parameters in addition
to those required by Subpart F
(R. 87).
Additionally, the permit
allows the Agency to require
a continuation of the monitoring
of
the P—series and nearby wells for additional
analyses (Condition
2 to Attachment
A;
R.
87).
At
any
time,
and
in
addition
to Subpart
F, when monitoring
indicates
a
change
in
concentration
of any of the 54 parameters,
some
in
concentrations
as small as 10 parts per billion,
WMI must
develop
and
submit
for
Agency
approval
a
groundwater
quality
assessment program
which
must
include
a
risk assessment
as an
initial
step
(Conditions
1,
2,
3,
4,
5,
7 to Attachment
B;
R.
89—91),
If
upon
completion
of
the
plan,
the
Agency
decides
at its sole discretion
that
there
“may” be
a violation of Section
12(a)
of
the
Act
or
that
there
“is a risk of harm to public
health or the
environment,”
an
engineering
feasibility
plan
for
corrective
action
must
be
prepared,
submitted to the Agency for
its approval or
modification
at
its sole discretion,
and imple—
mented to
the
Agency’s satisfaction (Conditions
5,
6,
8 to
Attachment B;
R.
94).
Corrective action is not terminated until
the corrective
action
performance
standards have been met for
three consecutive
years
(Condition
9 to Attachment B),
GeneralPermitObi~ections
WMI’s challenge
to
the
permit as a whole
is
premised on
alleged lack of Agency authority to issue any permits other than
the “RCRA permits” defined
in Section 3(vv)
and authorized by
Section
21(f)
of the Act,
The Agency does not presently have the
federal authorization to issue such Phase
II RCRA permits.
It is
uncontested that ESL is an interim status facility “treated as
having
been
issued a
(RCRA
permit” pursuant to 35
Ill, Mm, Code
703.153.
WMI
argues
that
its
only groundwater monitoring
obligations,
then,
are established by
the
Board’s interim status
groundwater monitoring rules,
35
Ill.
Adm. Code 725, Subpart
F.
WMI
asserts that no Agency permitting authority could flow
from
35
Ill.
Adm. Code 807--old Chapter 7--because those regulations
were promulgated pursuant to Section 21(d)
of the Act, now
expressly inapplicable
to
hazardous waste sites pursuant to
Section 21(f),
This argument is rejected.
First,
Part 807 was promulgated
pursuant to
~ection 22 of the Act.
More importantly, the Board
had asserted the
continued
vitality
of
its
pre—RCRA
solid
waste
regulations in
adopting
both
the
Phase
I
and
Phase
II
RCRA
rules
and
modifications,
As
previously
noted,
the Board’s position has
recently been affirmed by the Third District Appellate Court
reviewing R82—19
and R83-24,
in Commonwealth Edison Co.
and
Illinois
Power Co,v.IPCB.
The
court stated that:
80-188

“Prior
to
t1~e t~i~n~he
Illinois
legislature
determined
to
administer
a
hazardous
waste
~nanagement
program
which
satisfied
tn.~ ~:egn~
eu~nts
of
the
federal
RCRA,
there
was
in
place
in
the
starc
n
gram
which
regulated
the
disposal
of
wastes.
Admius~.~~-
~u~es
which
govern
the
administration
o.~
L
~
icr
waste
program
are
codified
in
35
Illinois
Adininist~~
code,
Part
807.
In
the
rules
proposed
to
implen
nt
z~tn
PLRA
program
in
Illinois,
the
IPCB
determined
that
3
t
I
J~
Illinois
RCRA
program
is
finally
accepted
bj
t~c
~in
~c
hates
Environmental
Protection
Agency,
hazardon.
.~.
innagement
owners
and
opPrators
must
obtain
perwi:e
in
c~:ca~c~
with
the
RCRA
and
the
prior
Illinois
waste
ran
~
annnt
law,
This
rule,
set
forth
in
section
70J.50j~,
ubJc~Led to
by
the
petitioners.
W~
agree,
as
the
petitroners
point
out,
that
no
express
statutory
authority
exists
for
section
700.501
in
the
legislative
enactmcnt
which
provided
for
state
rather
than
federal
administratio~
of
the
RCRA.
Nevertneless,
the
legislature’s
action
clearly
demonstrates
an
intent
to
provide
for
continuing
government
supervision
of
this
very
pressing
public
henith
problem.
If we
are
not
to
frustrate
this intent for
conLlnuing
supervision,
we
must
find
the
authority to propose reasonable transition rules from the
prior program to t .e new regulatory frame..crk to be implicit
in the legislatu~e s action authorizing the IPCB to adopt
rules to implement a utate-wide RCRA program.
(34
Ill,
L.
&
Prac,
Statutes,
section
113,)
Without
such
transition
rules,
a gap periocr would be created in which the state
would be powerless to issue
any permits for hazardous waste
facilities,
It
fc~i~nwsthen
that
until
the
United
States
Environmental
Pic
~tnon
Agency
issues
autnorization
to
the
State
of
Illinoi~
to
issue
permits under
a state
administered
RCHA
program,
the
proposed
transition
rule
which
continues
thn
sta~e permitting
process
is
valid”
(slip
op.
p.
5—6).
WMI
has
also
ehallen~ed
multiple
conditions
of
this
permit
on
grounds
of
lack
of
compliance
with
the
Illinois
Administrative
Procedure
Act,
These
arguments
are
rejected,
as
1)
the
procedures
for
permittrrg
under
Chapter
7
were
in
existence
in
1973,
long
before
the
July
1,
1977
applicability
“grandfather
clause” of Section 2
of
the
IAPA,
and 2)
the
Act
has
-never
by
reference
expressly
adquted
the
IAPA.
(See ~
100
III.
App.
3d
862,
427
N.H.
2d
415
(1981).
Prior
to addressi.ig the challenged conditions in detail, the
Board will not maka factuai findings as to which of any permit
conditions WMI agreed,
and will reject any argument that any
condition
is
valid
by
virtue
of
the
fact
that ~MI
allegedly
agreed
to
it.
WMI
corccctly
points
out
that
a
permit
is
not
a
contract
to
be
negotiatsd
~y
the
Agency
and the permittee as the
Board
has
consistently
~eld,
~
~~nInc,v,IEPA,
PCB
60-189

80--189
and
80
190,
45
~°3
397,
February
17,
1982,
and
~~aste
~~~ement9er~zicesvEPA,
PCB
76-166,
24
PCB
419,
February
16,
1982.
Some
furtt~
~
a~icn is
necessary
here,
as
one current
running
through
the
I
~u~~in
~ i~ that
the
instant
appeal
is
somehow
unfair
or
~eui
~i
i~
because
“a
bargain
is
a
bargain.”
A
permit
cannot
he
~nsl~e~ed
as
a
contract
where
various legal
rights
and
privileges
can
hn
~-raded
and
shifted,
because
a permit
affects
not
ins:
~ne
~,h
)f
the
Agency
and
the
permittee,
but
also
those
of
tI~eci~
~n
Were
a
permit
to
be
considered
a
contract,
in
the
nypot~.
~.
~a.
worst
case
a
shoddy
operator
could
negotiate an “anything go~,’permit if he could
locate
an un--
acceptably “flexThle” 1vc~ypermit writer,
Even putting aside
such
a
possibility,
the
r~ght of
the
state’s
citizens
to
a
healthful environment would be no better
served by negotiations
which
would result
in ~rsnance of
an arguably less—stringent—than—
believed—necessary
operating
permit
in
consideration
of,
for
example,
a
substantial
donation
to
the
Environmental
Trust
Fund
to be
used for
environmental
purposes;
the
environment
would
still
be
at
the
mercy
or
personalities,
rather
than
of
state
regulatory
policies
arrived
at
after
opportunity
for
public
input
and
administrative
and
judicial
review
c.f.
~an~g~mentof
~
PCB
82—55,
56
PCB
55,
February
22,
1984
rejecting
a
propo~ed
stipulation
under
Section
39.2
includ-
ing
conditions
judicially
ruled
outside a county’s authority in
c~y2fLa!s~~.IPc!~jal,,
120
Ill.
App.
3d
89,
457 N.E.
2d
1309
(1983),
and
banning
disposal
of
out—of-state
waste
in
potential
violation
of
the
Commer
e
Clause
of
the
United
States
Constitution,
Conditions
Incon ~
To the extent
that
the
Agency
has
authority
to issue the
instant permit,
such
authcrity
must flow from
Part
807,
and
from
Sections 12(a)
and
39
d)
of
the
Act.
As the
Board
has acknow--
ledged in the
past,
the
decade—old
Part 807
is
“sadly out—of—date,
under-comprehensive,
and under specific,” with several
attempts
to
generate successor rules having failed,
In The Matter of
Permits
~
22
atm
Criteria, P82—21 and R82—22,
52 PCB 431 June
16, 1983,*
Part 807 itself does not specifically require groundwater monitoring,
containing only
a prohibition against development or operation of
a site if “damage or hazard will result to waters of the state”
(Section 807,315),
and
an application requirement for a “description
of groundwater condrtior
.
.
and
an appraisal of the effect
of the landfill on groundwater”
Section
807,316(7),
Groundwater
monitoring was, however, clearly within the intent of Chapter
7
upon its adoption,
as
the
Board
noted that
*However,
in the mo~ recent docket R84—17,
there is promise
of completion of this four year old effort,
60-190

—19—
“Complete groundwater
and
subsurface
characteristics
of
the
landfill site may be required if
the
Agency determines that
such investigation is necessary to prevent pollution of
any
waters
of
the
State.
The
Agency
may
also
require
that
the
groundwater
be
monitored
at
such
reasonable
frequencies
as
it
deems
necessary.”
(In
The
Matter
of
Chapter
7:
Solid
Waste
Regulations,
R72—5,
supra,
8
PCB
at
697.)
While
Part
807
does
not
specifically
authorize
the
Agency
to
issue
“groundwater
monitoring
permits”,
it does authorize
issuance
of
development
permits,
operating
permits
and
supplemental
permits
(Sections
807.201,
807.202
and
807.210).
The
Board
construes
the
instant
permit
as
a
supplemental
permit
modifying
a
development
permit.
Within
its
four
corners Part
807
does
not
contain
specific
groundwater
monitoring
standards promulgated by the
Board.
Section
807.206
does,
however,
reiterate
the
stricture
of
Section
39(a)
of
the
Act,
allowing
the
Agency
to
establish
only
such
permit
conditions
“as
may
be
necessary
to
accomplish the
purposes
of
the
Act,
and
as
are
not
inconsistent
with
Regulations
promulgated by the Board thereunder.”
The Board construes its
RCRA
rules as providing guidance for use of Part 807 permitting
authority.
In
so
finding,
the
Board
believes
that the Agency is
thereby provided with sufficient direction to obviate any
question of unlawful delegation of the Board’s rulemaking or
adjudicatory authority c.f.
Peabody Coal Co.
v.
IPCB,
36
Ill,
App.
3d
5,
344 N.E.
2d 279
(1976); U.S.
Steel Corp.
v.
IPCB,
52
Ill.
App.
3d
1,
367 N.E. 2d 327
(1977); Commonwealth Edison,
supra.
Mr. Dietrich,
author of the 40 CFR Part 265 interim status
groundwater monitoring requirements,
as well as the
40 CFR Part
264 Phase II permitting groundwater requirements,
identified
several
conditions
which
he
believes
to
be
“inconsistent”
with
the
virtually
identical
Board
Part
725
and
Part
724
rules.
Mr.
Dietrich
believes
that,
to
the
extent
that
the
permit,
through
its
conditions
“is
an
integral
part
of
the
state
program
and
to
the
extent
it
deviates
and
is
inconsistent
with
the
Part
725
regulations of the state,
and is inconsistent with the Part
264 regulations of the federal goverment,
it could
jeopardize,
it may jeopardize the granting of final
Phase
II
authorization.”
(R.
117.)
The “inconsistencies” observed by
Mr. Dietrich
are
laid out in
the transcript at
R. 95—97,
99,
107—109.
These “inconsistencies”
fall into the following general
categories:
monitoring for
additional parameters,
sampling of till wells
in addition to
aquifer wells,
the
setting of detection monitoring triggers
requiring- assessment monitoring, establishment of
a 10 ppb
groundwater protection standard,
and
various conditions allowing
60-191

—20--
the
Agency
to
require
assessment
and corrective actions without
permit modification or review.
The
Board
does
not
challenge
Mr.
Dietrich’
s
reading
of
which
conditions
are
different
than
RCRA
requirements.
However,
the
Board
does
not
view
all
of
these
“inconsistencies”
as
being
fatally
infirm,
and
in
contravention
of
the
RCRA
regulations
and
their philosophy.
As heretofore indicated,
Part 725 contains minimum standards
established by USEPA pending its ability to review existing
facilities on
a site—by—site basis,
which minimum standards
were
“passed
through”
by
the
Board without substantive change pursuant
to legislative mandate.
The Commonwealth Edison court has agreed
that the existing
state hazardous waste
system is not displaced
by
with the RCRA system during the period before
Illinois’ receipt
of Phase
II permitting authorization.
Therefore,
in scrutinizing
the challenge of conditions, the Board will consider
a) whether
the conditions flow from legitimate Agency exercise of Part 807
permitting
powers previously recognized by
this
Board and the
courts,
b)
whether
such
Part
807
based conditions bear
a
reasonable relationship to activities at the
site,
and finally
c)
whether the
conditions are fundamentally
incompatible with the
procedures
or other specific
requirements of the Act or the Phase
II
RCRA rules adopted by the Board.
~nce
Schedule
lç9nd it
i2x~s 16
and
17
Special
Attachment
B
must
be
stricken
in
its
entirety.
WMI
contends,
and
the Board agrees,
that this attachment amounts
to
an
administrative
compliance
order,
The
Board
has
previously
found
that
the
Agency
has
no
statutory
authority to issue
administrative
compliance
orders
~
Ill.
Power
Co.
V.
IEPA,
PCB
83--53,
55
PCB
13,
16,
December
1,
1983,
and
finds
this
one
to be particularly repugnant given the public debate, through
comments, contained within
the
Phase
II
RCRA
rulemakings,
The Agency’ s permit manager Mr.
Eastep
has
stated
that
Attachment B could be deleted and
a facility would
still be in
compliance with the Board’s interim status Part 725,
Subpart F
regulations
(R.
955—956); as is amply demonstrated by testimony
of various Agency personnel ~
R.
835,
1346),
the essential
reason for inclusion of the schedule is to get “quick” response
if anything goes wrong.
However,
in the interests of expediency,
the power
of
the
Board
to
set
environmental
control
standards
and
the rights of the
piblic to
participate therein has been usurped,
a permittee’s due process rights have been extinguished,
and the
enforcement ability of the public, and of elected law enforcement
authorities such as the
Attorney
General and the state’s
attorneys has
been eliminated.
60-192

—21--
In Condition 1,
the 10 ppb assessment trigger is
an
attempt
to devise
an environmental control standard by the Agency,
an
activity which the courts have recognized is within the sole
province of the Board (~~ill
Inc.,
~
~~lCo,
v.
IPCB
36
111. A
3d5
~
Commonwealth
~Tson,
~j~ra
.
The balance of the conditions allow the Agency
to initiate and exclusively approve,
and allow termination of
assessments and corrective actions without permit modification
with
attendant public participation and appeal rights.
This is
nowhere authorized in Part 807 or Part 725, and was specifically
prohibited
in Part 724 after considerable public comment
(Phase II
RCRA,
~
53 PCB 156—157),
Similarly,
Special Conditions 16 and
17 would permit the
Agency “at its sole discretion”
to require additional monitoring
devices and parameters and to otherwise modify the permit as
deemed necessary.
These conditions,
as drafted,
are beyond the
Agency’s authority to impose,
and violate basic rights of due
process in the same
manner
as does Attachment
B.
Part 807 allows
for unilateral permit modification arguably only
in Part 807.209,
directing
the Agency to “revise any permit
issued
.
.
to make
it
compatible
with
any
relevant new
regulations
.
,
.
.“
While
Section
702.183 of the Board’s
RCRA rules allows the Agency the
right of unilateral
modification under
certain conditions
(Section
702.183),
these
rules
do
not become operative
until
Phase II
RCRA authorization is received
(Section
700,106(d),
Further,
in adopting the unilateral modification
rule,
the
Board
took
pains to explain
and
limit the unilateral
modification
right, recognizing that,
as a practical
matter,
permit
modification could be impermissibly used as a substitute for the
enforcement
mechanism
set up under the Act to guarantee
public
participation
and
Board review (Phase II RCRA,
~
53 PCB
155—157),
The
practical
effects of these
Agency
actions used as
an enforcement substitute will be discussed at the conclusion of
this Opinion.
weus”
and
G
we 11
monitor in
ar
ameters and
fre
enc
:
~lCondition12and13;AttachmentAConditions2,3,4,5,
As has been previously discussed
~
p.
7),
WMI’s
P
series wells
were installed to replace the G wells,
and have been
monitored
-to
comply with both the federal interim
status rules
and
the
Board’s
interim
status
Part
725,
Subpart
F
rules,
The
P
series wells,
since constructed with joints welded
by solvent
based
glue,
are
susceptible to providing samples showing
“false
positive” readings of low level organics contained in
the
glue
(R.
409, 944,
1094).
In this context,
Mr. Eastep
has noted that
“if
you really
had
a question about the
well
construction,
the
prudent thing to do would be to put in a new well”
(R.
945--46).
Some of the wells are
sometimes dry,
or incapable of
yielding
sufficient volume
to gain samples on other than
consecutive days
(see ~
R.
1165,
Resp.
Exh,
26,
p,
2).
60-193

--22--
In
its
permit
application,
WMI
had
proposed
to
decommission
these wells,
upon
installation
of
the
new
46
well
monitoring
system.
The
permit
as
issued
requires
continued
testing
of
the
P
wells,
incorporating
the
ongoing
assessment
plan
already
required
by §725.193.
In addition, the P wells and eight new wells
closest
to
each
P
well
must
be
monitored
for
the
over
75
hazardous
waste
constituents
contained
in
Appendix
VII
of
40
CFR
Part
261,
a
requirement
not
in
the
Board’s
Part
725.
Upon
submission
on
July
15,
1984
of
an
assessment
report,
if
the
Agency
should
determine
that
the
facility
“has
not
affected
the
groundwater”,
P
wells
could
be
decommissioned
(Attach,
A,
No.2),
However,
any
P wells the
Agency
found
to
be
affected
would
possibly
require
assessments,
approvals
and
corrective
action
pursuant
to
several
conditions
of
Attachment
B~
WMI
challenges
the
Special
Conditions
12
and
13
Attachment
A
concerning
P
well
monitoring
on
grounds
of
inconsistency
with
Section
725.193,
and
on
unreasonableness (Attachment B arguments
will
be
discussed,
infra),
The
specific
reasons for
the Agency’s inclusion
of
the
conditions relative
to the P wells
are
contained
in
the
testimony
of Linda Kissinger, primary author of the permit
letter
and
Attachment A
(R.
1150--1214)and David
Favero,
primary
author
of
Attachment B and contributor to Special Conditions
12,
13 and
Attachment
A, Condition 2
(R.
1324-1375).
In the
words
of
Ms.
Kissinger
“The P series wells were included
in
the
permit
in accordance with the assessment that had been going on
once they had found
a statistically significant increase in
the indicator parameters
in
the P wells.
(Special Condition 12
was included
because
the
G
series wells would not have
had
background
quality
established
for
the
next
year,
and
this
allowed
ongoing
testing
and. statistical comparisons to be made
during
that
time
frame,***
They
had
proposed in
the
application
to
sample
the
P
wells
the
first
quarter
to
complete
the
assessment,
and
we
wanted
them
to
be
sampled
during
the
collection
of
back--
ground data
on
the
new
G
series
wells
so
we
could
look
for
similarities
between
their
old----not old
analysis,
their
old
wells
and
samples collected from those,
and
samples
collected from the new
ones
for
the
same
time
period,
and
also
to complete the groundwater assessment started under
725.”
(R.
1174—1175.
Also see Favero,
R.
1341,
1344--1345.)
As
to Special Condition 13, Mr.
Favero
testified
*Thjs,
and
other guidance documents referenced
in
Mr.
Favero’s testimony are not included
in this record or
specifically cited
so as to be accessible to the Board.
80-194

--23--
“After
a
revised
assessment
plan
was
submitted
to
the
Agency
in
November
by
Waste
Management,
we
received
some
guidance
from
the
Federal
Government*
on
conducting
assessment
plans,
assessment
programs
at
hazardous
waste
facilities,
and
it
included
specific
testing
procedures
and
paramenters
to
check
for,
and
by
way
of
this
permit,
we
wanted
to
include
this
latest
technical
guidance
and
apply
it
to
the
ESL
facility.
Additional
wells
were
selected
in
order
that
we
could
try
to
phase
out
these
key
wells,
and
know
exactly
the
construction
details
and
the
integrity
of
the
wells
we
were
dealing
with,
and
to
also
make
sure
that
we
got
a
sample
from
the
aquifers
in
the
vicinity
of
the
P
wells,
and
not
necessarily
from
the
till
materiaL.”
(H.
1215,)
The
record
does
not,
however,
specifically
explain
why
testing
is
required
for
every
Appendix
VII
hazardous
waste
constituent,
as
opposed,
for
instance,
to
those
identified
in
the
facility~s
leachate,
The conditions at issue here are different from those
contained in Part 725 to the extent that they
a) deal with the
phasing--outof wells whose detection capabilities are questioned
by WMI, various Agency personnel and Dr. Sternberg,
who partic~-
pated in the design of the new
46
well
detection
monitoring
system,
b) the conditions
specify
which
hazardous
constituents
must
be monitored for,
and c) Attachment A, paragraph two allows
the Agency, rather than the owner,
to determine which
P wells
have been affected by the facility, before decommissioning
them.
Under
Part
807,
the Agency has
historically
had
fairly
wide
latitude
to
require
what
should,
under
the
RCRA
~stem,
be
called
“detection
monitoring”,
As
the
Board
has
previously
commented
“the
monitoring
of
groundwater
is
as
yet
an
inexact
science
(or
art),
and
the
Board
believes
that~initially,
refinement
is
less
important
than
comprehensive
coverage,
no
matter
how
preliminary
or
approximate
.
.
.
Frinks
Industrial
Waste,
Inc.v.1EPA,
PCB
83--10,
52
PCB
447 June 30,
1983,
The
latitude
which
has
been
afforded
the
Agency
under
Part
807
to
require
“detection
monitoring”
is
also
in
line
with
various
duties
to
collect
and
require
inf or--
mation
under
the
Act,
see Section
4(b,c,h),
However,
under
the
circumstances
of
this
case,
these
challenged
conditions
are,
in
part,
unreasonable,
The
intent
of
WMI’s
assessment
plan,
as
reiterated
in
its
1983
groundwater
monitoring
report
(Resp,
Exh,
32~33),
was
to
decommission
the
wells
because
of
their
unreliability
after
completion
on
June
15,
1984
of
the
assessment
required
under
Part
725,
Yet,
the
Board
sees
the
logic
of
the
Agency’s
desire,
as
expressed
by
Ms.
Kissinger,
to
have
sampling,
although
of
highly
questionable
usefulness,
continue
in
the
P
wells
while
background
quality
w~s
established
in
the
G
wells.
Continuation
beyond
that
time
of
the
P
wells
monitoring,
however,
serves
no
useful
purpose.
80-195

--24--
As to the
parameters
to
he
sampled,
this
issue
is
intertwined
with
the
challenge
to
the
sampling
parameters
contained
in
Conditions
3
and
4
to
Attachment
A,
requiring
sampling
and
analysis
for
certain
leachate
parameters
and
Appendix VII constituents
in
addition
to
those
required
by
Section
725,192.
As
a
threshold
matter,
that
portion
of
Condition
4 which
allows
unilateral
modification
of
the
list
of
parameters
to
he
monitored
is
stricken,
for
the
reasons
expressed
regarding
Special
Conditions
16
and
17.
The
Board
finds
that
Part 807 would authorize
sampling
for
parameters
beyond
those
contained
in
Section
725.192,
but
only
to
the
extent
that
such
parameters
or
classes
of
parameters
are
those
which
could
be
found
in
the
facility’s
leachate,
based
on
the
waste
material
there
disposed
of
Pet,
Exh,
15
and
Resp.
Exh,
40)
cf.
Q~~Cor.
(East_Alton)
V.
IEPA,
PCB
80--126,
45
PCB
389,
February
17,
1982.
The
unverified
findings
of
organic
contaminants
of
trace
levels
in some
monitoring
wells
provides
a
modicum of additional
support
for requiring detection monitoring for organics at the facility,
to determine whether or not
organics
are
present.
The
parties
have not advised the
Board
as
to
whether
all
of
the
Appendix
VII
constituents meet the above criteria,
and
due
to
the
shortness
of the Board’s review time the Board
is
itself
unable
to
make
the comparison.
The Board further finds that Condition 5 to Attachment A
requiring quarterly rather than semi-annual monitoring is also
within the permissible
scope of Part 807.
Summarizing the Board’s holdings on these conditions:
Special
Condition
12
is
affirmed
as
modified
in
the
Order,
Special
Condition 13 Paragraph 1
of
Condition
2
to
Attachment
A
and
Con--
ditions
3 and
4 to Attachment B
are
affirmed
subject
to
comparison
of
the parameters to the facility leachate
(although the modification
portion of Condition 4 is stricken), Condition
5 to Attachment A is
affirmed,
and
Paragraph 2
of
Special
Attachment
A
shall
he
revised
to allow for decommissioning
of
the
P
wells
once
background water
quality
for the G wells
is
obtained.
~p~al
condition 14
This
condition
~s
stricken
as
a
restatement
of
existing
law
not necessary for administrative
convenience
or
to
accomplish
the
purposes of the Act see
Illinois
Power,
~
This
condition
is
easily distinguishable from,
for instance,
a
condition
in
an NPDES
permit which contains a specific
effluent
limitation
which
is
a
verbatim
restatement of a limitation contained
in
a
Board
regulation.
That repetition is
convenient
both
to
the
operator
and the Agency, providing in a single document a facility’s
operational
standards,
and is expressly provided for in Section 39(b)
of the Act,
To the extent
that
inclusion
of
the
limitation
allows for “double enforcement” against alleged Violation on the
grounds of violation of a permit condition and
a Board regulation,
such double exposure is clearly part of
the statutory scheme.
60-196

—25--
The
instant
whole scale
incorporation
by
reference
of
Subpart
F
in
its
entirety
is
in
furtherance
of
no
legislative
purpose,
and
is at
best
mere
surplusage.
At
worst,
it
leads
to
the
query
of
whether,
since
the permit
does
not
also
incorporate
the
Act
by
reference,
WMI
is
relieved
of
any~obligations
thereunder
by
virtue
of
the
omission.
THE
TRENCH
11_OPERATING
PERMIT_AND
SUPPLEMENTAL
WASTESTREAM
AUTHORIZATIONS
The
stated
bases
for
the
denial
of
WMI’ s
operating
permit
for
Trench
11
are
contained
in
Mr.
Eastep’s
April
20,
1984
letter,
as follows:
“Prior
sampling
by
this
Agency
and
by
Waste
Management,
Inc.
has
indicated
the
presence,
or
potential
presence
of
hazardous
waste
constituents,
in
the
groundwater
at
the
ESL
site.
Furthermore,
the
applicant
has
not
satisfied
the
requirement
of
35
IAC
Part
725,
Subpart
F:
Groundwater
Monitoring.
With
regard
to
the
‘P’
series
wells,
the
applicant
has
not
satisfied
the
requirements
of
35
IAC
725,193(d)(4),
With
respect
to
the
‘G’
series
wells
per-
mitted
under
IEPA
permit
1984—16—SP
(March
2,
1984),
those
wells
have
not
been
sampled
and
analyzed
pursuant
to
the
permit
and
to
35
IAC
725,192(a)
and
(b).”
On
April
30,
1984,
previously
applied
for
wastestream
authori—~
zations
were
also
denied
for
the
same
reasons
which
formed
the
basis
of
denial
of
the
Trench
11
permit.
Prior
to
discussing
these
issues,
it
is
important
to
note
the
scope
of
the
Board’s
review
powers
in
Section
40
permit
appeals.
As
the
Board
has
noted
on
reconsideration
in
another
case
involving
operating
permit
denial
on
the
basis
of
alleged
groundwater
monitoring
deficiencies,
Frink’slndustrialWastev,
IEPA,
PCB
83--10,
52
PCB
447,
Opinion
and
Order,
June
30,
1983,
Order
on
reconsideration
54
PCB
25,
September
8,
1983:
“Since
1972, the Board has consistently held
‘that
the
issue is,
in a Section
40 hearing, whether the Agency erred
in
denying the
permit,
not
whether
new
material
that was not
before the Agency persuades the Board’ the Agency was wrong
Soil Enrichment Materials Cor
,
v.
IEPA, PCB 72--364,
Octo er
.
5
PCB at 27.
The
Board’s
view
of
its
Section
40
role
has
been
confirmed
by
reviewing
courts,
~
Mathers,
~
In
this
context,
then,
the
Board
must
mention
the
testimony
of
Dr.
Warner
and
Dr.
Hryhorczuk
These
experts
had
no participation
either
in
the
preparation
of the permit applications,
or
in
the
Agency’s
permit
decision

--26--
deliberations.
The
hearing
officer
a
;~ow~d
-~-~aa
testimony
of
these
two
doctors
“for
purposes
of
rebuttiaq
a wthint’
that
dfl~
witness
presented
on
hehali
of
~1asre
Mdnagemerlt,
nut
tnct
as
independent
evidence
in
support
of
the
Aqency
-
s
actions
in
this
case”
(R.1253),
While
the
Board
does
not
find
the ruling of
its
hearing
officer
allowing
this
testimony
on
a
~‘~ry
limited
rebuttal
basis
so
c~ear~yerroneous
as
to
merit:
reversa
their
test.:h~onycar
lawfully
be
accorded
hu~: little
weight.
Much
of
the
testimony
of
these
q:arts,
n~ we
I
as
Lhat
of
citizens
and
Agency
witnesses,
e~-.oenriailv
:~evoivsd
around
the
issuea
of
a)
whether
waste
d:isposai
should
ea’cr
have
been
allowed
at
the site
given the
“geology
of
the
site”,
it
ceing
st:ipniated
that
the construction
and
design
of
Trench
11
~n
and
or
ir~elf
is
not at
issue
(R.
68) and b)
whether
a
new
1984
“state
of
~ns
art”
Trench
11
should be allowed
to
operate
at
a
site
initialiy
per-
mitted
in
1972,
when
experts
generaJi~
agree
th~t
all
landfills
will eventually leak
and the
site
as
a
who.e
has
rio
active
leachate
collection
system,
trench
by
L~encn ~ynthstic
liners,
or
other
mechanisms
to
prevent
esoape
of
contar:inanrs
from
toe
areas
in which they have been
disposed.
Again,
these
issues
are
not
before
the
Board.
In
IbPAv.IPCB,
86
Ill.
2d
390,
427
N.E.
2d 162
(1981)~ the
irprome
Court
was
reviewing
a
denial
of
a
permit
to
the
‘1..
.teal
Corp.
on
the
stated
basis
of
lack
of
compliance
with
air
rule
203~a),
At
hearing,
issues
arose
concerning
compliance,
with
air
rule
203(f).
The Supreme Court
stated
that
“We
do not believe,
however,
that
the
issue
of
compliance
with
Rule
203(f)
was
even
before
the
Board
Section
3~ ci
the
Act
(citation
omitted
requires
that
the
Agency
state
reasons
for
denial
of
a
permit:
‘If
the
Agency
denies
any
permit
under
this
Section,
the
Agency
shall
transmit
to
the
applicant
within
the
time
Irmitations
of this
Section
(90
days
specific,
detailed
statements
as
to
-the
reasons
the
permit application was
denied,
including
(ii)
the
pcovision
of
the
regulations,
promulgated
under
this
Act,
which
may
be
violated
if the permit
were granted’
citation
omitted,
The Agency’s letters
did not specify any violation of
Rule
203(f).
Although
section
40
of
the
Act
citation
omitted)
provides that,
on
review
of
a
permit
denial,
‘the
burden of
proof
shall be on
the
petitioner,’
it
also
states
that
‘ftlhe Agency
shall
appear
as
respondent
in
such
hearing.’
In.
0
scar ~
&
Co.
v.
T&nv irenmental
Protection
A~enc~
(1978),
30
Ill. P,C.B.
3p.
397,
399,
the
Board
stated:
£In
a
Section
40
oroceeding
the
Agency
must
file
within
14
days
of
notice,
the
entire
record
of
the
permit
application,
including
the
application,
correspondence,
and
the
den:~ai,
The
applrcation
is
60-198

necessary
to
establIsh
the
facts
which
were
Lofore
the
Agency
for
consideration.
The
correspondence
file,
if
any,
supplements
the
application
insofar
as
it
provides
additional
fncts~
The
denial
statement
is
necessary
to
verify
that
the
requircoent
of
Section
39(a)
of
the
Act
has
been
fulfilled.
This
material,
in
the
opinion
of
the
Board,
should
be
sufficthnt
to
frame
the
issue
of
fact
or
law
in
controversy
in
any
hearing
on
a
Section
40
petition.’
We
believe
that
the
Age.
~y
had
a
duty,
reading
sections
39
and
40
of
the
Act
together,
to
specify
reasors
for
the
denial,
including,
if
it
intended
to
raise.
the
issue
before
the
Board,
the
lack
coopliance
witi
Rule
203(f),
orbe
~cluded
from
raisinq
that
issue,***~
(427
N.E.
2d.
at
169—70)
(emphasis
added),
With
this
statutory
framework
in
mind,
then,
the
Board
will
first
turn to
the
stated
reasons
for
the
Trench
11
and
wastestream
denials.
While
questioning
the
ne~essity
of,
or
its
authority
to,
address the other
concerns
which
surfaced
at
hearing,
the
Board
will
do
so
to protect
all
parties’
rights
to
a
speedy
determination
of
this
controversy
by
avoiding
a
remand
by
any
reviewing
court
for
Board
deliberation
of
the
concerns
unstated
in the permit denial
letter.
~leedPresenceorPotentialPresenc~ardousWaste
Constituents
in
the
Groundwater
at
the
ESL_Site
Agency
testimony
~
p.
870,
937-38)
indicates
that
this
concern
stems
principally
from
the
sample
results
of
December,
1982 from
well
G
105,
and
from
August,
1983
~‘amples
fror
~-he P
wells showing extremely
low
levels
of
organic
constituents,
The
G
105 well
sample
result,
which
even
in
January,
1983
one
Agency
employee believed could
be
the
result
of
a
sampling
or
laboratory
error
(Pet.
Exh.
28),
provides
insufticient
basis
for
denial
on
this ground:
the
sample
was
unverified
and
the
sampling
results
for the
subsequent
five
quarters
showed
no
contamination
in
this
or
any
other
wells
(Pet
Exh.
17-21,
see
also
R.
1451,
1054),
The most persuasive
testimony
concerning
the
August,
1983
results
of tests
from
the
P
wells
is
that
of
Mr.
Hurley,
head
of
the Agency’s Springfield
laboratory,
which
exclusively
handles
organic analyses.
August 17,
1983
samples
taken
at
ESL
showed:
for wells P2,
2 ppb
tetrachloroethylene;
P5,
13
ppb
dichlorofluor-
methane;
P1,
P4,
P6,
P7,
P8
none
detected
(R.
1673~1674,
Resp.
Exh,
4),
In performing the
analyses,
the
laboratory
used
a
gas
chromatograph
(gc) mass
spectrometer
for
organics
identification
generally,
and
a
gc Hall
detector
for
volatile
organics,
primarily
chlorinated organics
CR.
1664—1668).

Mr.
Hurley
testified
that
ne
c~
~o.
tiow
ii
any
~yoe
reaction
that could occur
between
PVc
or~e a~-( tha
ccrr~ounds
~istecl
in
the
P well glue sample
that
would
~a~oJOc-’
~hc
chlorinated
~r
fluorinated
compounds listed
above
He
s~
so
~setv~
that
these
compounds
are
not
a
natural
constituent
~n
~o1r~-
s~n or
‘A.
1a8i—683~
although
he
did
not
know
whether
otl’er
~
~
i~ht
he
in
tIe
glue
IA.
1734).
He
did
rot
believe
th
~
s
~ers
caused
by
laboratory
error
CR.
1684).
Regarding
sample
collect.
,
1’
turley
ackno~lcdged
a)
that
he
does
not
know
how
the
wel
3~TU
o~
wero
~a2cfr
and
b)
that
the
laboratory
does
not
use
the
a
a~ z.
ci
UdEPA
procecure
of
using
both
trip
blanks
and
field
blank’
as
to
el
~rnate
the
possi-
bility of airborne
contaminCtLor
Ct
8
69J)
Inst~d,
the
laboratory
sends
out
trip
bi ants
O~o o
ie
t~o tug
at
il
1983
trip
blanks
sent
out
in
the
fr~ d
r
r
a
4ty
cortro~
was
returned
unopened,
but
contaminated
with
about
1
tob
of
~,1
trictloroethane,
while
the
other
blank
was
no.
A.
1
Q2~1633)
1he
ttrst
blank
was
run on
the
Hall
detecthr
~
a3
tIer
a
~
on
ate go
mass spectrometer.
Mr. Hurley ack
qlcd7~~ ye ~cbab~l~y
of
laboratory contamination
or
pos’ib~
ambient
air
.intamrnatIo~
(the level was in
the
range
of
ate
~gvireo
well
~ .ter
testing
for contaminants),
but
could
no~ t.’pl
in
qh1
on~y ore
bottle
was
contaminated.
He was
concerted
a..~out thssc
re~
-
3
out ro
further sampling or
analysis
wct~
oCtc,
t
‘iij.
Rcyerding
detection limits on
both
instr’ime~ts
he
~s~i
ad
tlat
~.key
could
vary from 1-5 ppb for
the
gc
mass
spe
trom
tl1er
I
I
ppb
for
the
Hall
(R.
1699—1706),
and
tlat
aethod
~y
p”r
a
t
when
testing materials close to the dete~ i.~r
lev~
~.
~73
.—l/34)
Mr.
Eastep
testified
th
t
..
at
~c ma tu.
iqust,
19~3
P—series
well
tests
and
did
nih roe.
see’.rg “to
s bseq~ant
negative
tests
after
August,
19
3
and
pror
to
the
April
20
1984
denial
letter
(R.
937—938).
Th
A
eaty
was
or
stoi
Id
have
osen,
well
aware
that
future
samples neat-
at
at
analyzed
“before
a
determination
can
be
made as to wheth~ra well ~s showing con—
taminents”
(See
Pet.
Exh.
28),
and certainly wher initial results
are close to the detection limit.
Part 725 and good scientific
practice
dictate
confirmation
of results
As Dr
S~ernberg
stated, regarding pre—assesement detection monitoring,
“When one takes a groundwrter senp)e,
or for that
matter,
in
any
scientific
field,
that
I know of,
if you
measure something and you ge5 a—-~et’~’
cr11 it a positive
reading one,
that does
r
it,
it
the ~cient.if~ccommunity eye,
imply that this is a confirmec. reading~
That only tells you
tat’. voi
sh”~lc proceed ~‘ithcaution,
namely, that blip or positive reading, or aromaly or whatever
you want
to
call
it,
requires
furthet
attention.

what
it
requiat
at
anTi
io. .~l or
sutsequent sampling,
subseanent testing~
~
at~
a.-.
Th
revs
to
me,
look,
octeatiallv thsr
at
,v
“th..
...
~t’.;re,What we need to do is
Is
gc~irvc~trgs~at frrter
A.
541)
Here,
the
Agency
did.
not
do
s~
There
is
no
evidence
in
this record that the Agency even reatewed the subsequent
quarterly test results on any
of the wells,
which information
was
a~ai1abIeto
it.
Arl c~ibsequ~rtnecative results challenge the
validity of
an initial
test just
C
suos~quentpositive results
serve to confirm an ‘u’~traltest
R~-
icst~onand repetition
are
essential,
to detern’ri~enot j:st whether
there is contamination
hut
the
precise
nature
and amoirt o’
it,
Otterwise,
attempts to
locate
the
source
of
the
contamatat
c
~
and to implement any
subsequent
remedies
can
turn
into
a
~i1a
goate
chase
which
ill-serves
the
public.
The
Board
notes
that this was not an eargert situation where
the
statutory
deadline
requIred
at
.rat.
lasel cr~just-~rece~ved
results,
or where a waiver had seen
so gh
and refused while
results were being
confirmed,
Based on the e~iderLcehere
presented,
as
interpreted
in the atght of its tecnnicai
expertise, the Board
finds
the unconfirmed tu~usu, 1983 teat
results to be an insufficient basis ~r
denyirg the Trench 11 and
wastestream permits.
Part 725
and
the
P
Series
Wells:
AJe~
Failure to I~piement
an
Assessment_Plan
Mr.
Haney,
manager
of
the
Pam.
ities
Compliance
Unit
of
the
Division of
Land.
Pollution
Co~t~.ol Tet
pith
Messrs.
Eastep
and
Chappel on or about April 20,
1984
(A.
1272)
and.
inferred them
that ESL was
in
violation
of 3~111
Adm. Code §725,193(d)(4)
because he had no evidence which proved that Waste Management had
implemented
an
assessment
olan
(A,
12’~0),
Mr.
Easoep apparently
relied
on
Mr.
Haney’s
representation and relayed it on April
20
to
Mr.
Kuykendall,
who
made the dec,sion to deny
(A,
744).
The
April
20 and 30,
1984, denia
letters included the statement as a
basis for denial.
The
Board
finds ample cv dance
it
blat recoru to show that
the
Agency,
as
a
whole,
knew or should have known that the
assessment
plan
filed
June,
1983 ~see p.9,
~,
footnote) was
being
implemented,
Mr.
Waluzyr1ski had nutified the Agency of
the
implementation
of
the
assessment orally and
in writing in
September,
1983
(Pet.
Exh.
31,
A.
1458).
The Annual Groundwater
Monitoring
Report
filed.
March
1,
1984 indicated that the
Assessment
Plan
had
been
implemented:
“the
groundwater
at
the
facility
is
being
monitored
to satisfy
the
requirements
of
Section
725,193(d)(4)
.
,
.
(Pet.
Exh.
30,
p.
2).
While
the
assessment
plan
by
its
terms
called for
a report on
March
1,

1984,
paragraph
13 of the
).~çh
2,
98’ qasutiwater
nor.. tsring
permit,
written
by
Mr.
Fairro
a
‘ieiati~ ~
pane’ ~
specifically
refers
to the qrc~ncIraterassessment prorran and
grants
WHI
an
extension
at tare :~ ~fluatno rile the assessment.
report
(Pet.
Exh.
1,
par.
..3
The
Board additionnull
no
c-n
t
at
the dates cont~inedin the
assessment
plan
for
Phase
~
at
or
aty
(HeIr.
Ext’
32,
p
02535),
indicates
that
the
trmetahic
~
ontinjent on Jantary
1,
1)84
Agency
approval,
and prs-’ma.Iry uer.it .~rq,of the new gtourd-
water monitoring network,
batt.
an
it;..
aopl’ ~“-aon su.anittal
December
1.
WMI submitL~d
i
a
qup
at
tic’. Deatmber
28
foatovinq
December
consultations
wilh
tat
Ajeicy
“cn’erning
.he
Woodward—Clyde
report
(a
~u~:a
p
9
Tn’
entire
nisLorl
of
the
groundwater
monitori
icy
‘ii
-
‘r
slort,
is
indioatio-.~ of
efforts
to
implement
an
assessment
plan
Failure
t~ Test
the
New
G
Series
Wells
The
final
stated.
basis
for
fate
~lpril
1984
den
al
of
the
Trench
11
permit
was
that
the
iew
wells
rnstalled
pursuant
to
the
March
2,
1984,
groundwater
permit
had.
not
been
sampled
and
analyzed.
The
March
2,
1984
pe.nit
did.
not
by
ate
terms
require
WMI
to sample the wells
bef can—
Y~y ~.nd
the
results
3f
the
sampling analyses
were
not
duo
untL.
July
i~
(Reap.
rxh
ii,
Special Condition
1),
In its letter
of
March
3~ at
Mr.
F-astep
(Pet,
Fxh
22,
p.
2),
WMI
specifically
asked
tether
tIe
Agency
zc’b
it
needed
samples
from
the
new
system
an
order
to
rake
ecnsicn
on
the
Trench
11
application
Mr
Tosteo
~~stitieo
t
at
‘at
did.
rot
reply
to
this
letter
(A,
949
see
alsc
A
72~,
The
record
does
not
otherwise
indicate
that
WMI
either
received
an
ar.swer
to
its
question,
or
that
any
AJency
~er~cinnel
independently
expressed
a
desire
for
such
sampling
results,
Indeed,
Mr.
Kuykendall
testified
that
in
February-March
he
had
“no
position”
as
to
whether
such
results
were
neecred
(A.
721—22,
26),
The
Board
finds
that
at
stated.
grouna
cannot
support
denial
of
these
permits.
In
a
atmilar,
pratt
case
involving
multiple
attempts
to
gain
permats,
eateit
a
r
permits,
ate
Board
rejected
a
similar
Agency
ack
at
information
as
OCCiC
for
denial
argument.
The
Board
stated
that
“when
the
Agency
cinnot
ate
a
reasoned
decision
on
the
basis
of
the
information
submitted
in
the
application
as
well
as
other
data
at
cuatolaray
and
reasonably
relies
upon,
it
shall
notify
the
applicant
of
the
specific
additional
information
necessary
for
its
determination,
It
would
be
a
somewhat
c~pricioua
exercise
of
its
powers
under

3 1—’
the Act for the
Agency to
deny
a
permit
on
its
merits
for
insufficiency
of
information
proving
nonviolation
while
knowing
that
if
specific
additional
data
or information were
provided
or
were considered
it
could
maKe
a
better~informed
decision
on
the
application.
Indeed~
Sherex
many
times
invited
the
Agency
to
recuest
Sherex
to
provide
any
additional
information
the
Agency
miht
deem
necessary
in
order
to
make
a
determination:
on
its
application.”
Sherex
Chemical
Co.
Inc. v.
IEPA,
PUB
80—66,
39
PCB
527—528
(1980),
affd,
sub
nomn.
IEPA v.
Sherey.
Chemical
Ct-.
and
IPCB,
100
111.
App.
3d 735
N.E.
2d(1981).
In
a
case
even
more
on
point~,
Fnink’
a,
~
the Board
reversed
an
1~gencydenial
of
a:-t
operating
permit
to
four
above—ground
storage
tanks
located
on
a
4.
8
acre
waste
disposal
site.
waste
had
previously
been
stored
on
the
site
in
underground
storage
tan~~
and
in
lagoons
since
abandoned
(closed),
Groundwater
contamination
was undisputed,
although
there
was
some
question
of
whether
contamination
was caused by
leakage
in
the
underground
tanks,
en
by
excavation
of
the
lagoon
at
Agency
direction,
Frink’ a
had,
shortly
before
permit
denial,
suggested
that
an
operating
permit
include
a
condition
that
its
proposed groundwater
monitoring
system
be
put
in
place.
One
of
the
cited
reasons
for
denial
was
failure
to
install
monitoring
wells for which a permit had
been
applied
for,
but not issued or
denied,
The
Board
there
found
it
“impermissible to
deny
an
operating
permit
on
the
grounds
that no wells
had
been
installed
where
wells
could
not
be
installed without a
permIt.”
(52
PCB
at
457).
The Board finds
it equally impermissible here,
equally
a
“Catch-22”
situation,
to
deny
ermits
on
the
ground
that
sample
results
were not
submitted
by
April
20
or
30, when the ground-
water
permit did
not
by
its
terms
require
sample
results
until
July
15,
and
WMI
was never
asked
for
results
prior
to
the
denial
decision.
THE
UNSTATED BASES FOR
PERMIT
DENIAL
Geeloaf
the
Site
Mr.
Eastep
acknowledged
that,
although
he
was
aware
of
the
Act’s
requirements,
concerns
about
geology
were
not
contained
in
the
letter
of
denial
(A.
1086-87).
However,
as
aft-re—mentioned,
the
Board
will
address
the
geology/hydrogeology
issues since,
properly or not, the
Agency
at hearing raised this as an
issue.
While
a
number
of
witnesses
reference~ii
the
geology
and
hydro-
geology
of
the
site,
the
witnesses
whose
testimony
is
touched
upon
below
appeared
to
have
been
the ones primarily
relied
upon
by
the Agency for
their
evaluations
and
conclusions
(except
that
Dr.
Warner,
as earlier noted,
played
no part in the
Agency’s
decision),
$0—203

To repeat,
there
were
a
turner
o~ irvestLjatiats
and.
data
reviews
of
the
geology
and
h1ci
ator
gy
cd
ant.
CitCr
going
back
to
1972.
Between
1980
and
~aat
~
“-hs~o
crc
erformed
by
Woodward—Clyde
Consultants,
enco
a
~ae’ era~
thousand
maybe”
hours
of
effort.
The
most
recert
studa~
ol.
Lecemoer,
1983
(Pet.
Exh.
6
and
7),
following
or
patv
‘c-s
tudies,
mere
performed
for
WM1
in
consultation
with
the
O;al
citizens
uroup
and
their
consultant,
Dr.
Sternberg,
Dr
at
si..y
of
Maryland,
with
involve-
ment
by
the
IEPA
and
the
State
Ge~
;cal
en
qey
(A.
152,
229—235,
511—513),
Mn,
Hendron
testified
at
a
~oocr
~r
at
Ire
studies
Uhe
area
consists
geologically
a
trite
he
~ppermost
bedrock,
underlain
at
depths
of
a~e~’al
a
nd
ed
feet
by
Ordovician
deposits.
Maquoke
a
Stale
restrict,
the
flow
between
these
two
formations,
Hydroge
icaaty,
the
Si,lunian
Dolomite
is an aquifer
as is
the
Ordovi~ aa
the
Jatter
~roriding
a
source
of
iminicipal
water.
OverJay~
p
o~dr’ .f
a
~arIa~e
clay
deposit
into
which
the
waste
dat
a
at
p
a~ at
H.
146~151),
Woodward—Clyde concluded
based
on
ater
pat.
nt-at
~~ork
and.
con-
firmation studies,
that
the
site
at
acceptable
fo~ tne
design
and
ope~-ation of
a
hazardous
wasat.
f
ilaty
and
that
Trencn
at
is
properly
designed.
This
corcat’a.
a’
prem
~Fd
‘ma
large
measure
on
the
cohesiveness,
uniformity
arc
te
meaci
aLy
findings
con-
cerning
the
glacial
till
deposiiat
(I
~53,
218
2L).
Regarding
the
uppermost
aquater
V’oodward-”Jycie
determined
that
the
groundwater
primarily
ato~ed. horizontally
to
the
north-
west
towards
the
Des
Plainies
River,
arid
tha
tue
gradient
of
flow
is
flat——about
10
ft/ni
ov
coat
of
tie
site
tendIr.p
to
steepen
towards
the
Des
Plaines
Rlver-~ to
‘maxitrur
1
35
40
it/au
(A.
190,
191,
199).
A
water
well
su~vcv showed
no
wells
north
or
west
of
the
site,
The
residential
wells
are
primarIly
located
in
a
southern
and
eastern
direat
~r
it
a
L.he
sate.
Mr.
Hendron
does
not
believe
contaminants
could.
corceiveably
reach
these
wcnls.
(A.
198).
((The
municipal
we-Irs
sen
ing
Charnabon
and.
part
of
Joliet
are
in
the
deeper
Ordova
ian
bedrock
(A.
198,
see
Exh,
7,
Fig.
33).1
Mr.
Hendron
testatatd
atat
giver
the
groundwater
gradient
and
calculated
flow
rate
‘present
techaology
Ior
containment
and
retrieval
sh
vi
be
more
than
adequate’
in
the
event
of
a
release
(A.
202),
Dr.
Sternherg,
who
partic’anated
in
design
of
the
ultamately
accepted
monitoring
well
system
af ten
reviewing
the
hydrogeology
of
the
site,
agreed
that
the
grou~dwater
flow
as
primarily
in
a
westerly
or
northwesterly
direet~on
(A.
523
641).
and
that
the
wells
will
detect
a
leak
that,
as
with
all
landf ails,
he
believes
will
inevitably
occur
(A.
53°’
He
emphasized
that
the
well
system
was
established
not
for
assessment
monitoring,
but
as
a
detection
system,
sufficient
to
scientifically
lead
to
proper
documentation
and
further
review
if
a
sample
shows
a
positive

—33—
reading, ultimately
leading
to
~
action
:e
avoid
a
health
hazard
if
one
were
found
(d~ 5~2~
HE.
also
stated
ahat
an
Olin
gypsum
pile
and
tailing
ponds
to
t
e
north
cu
the
atte
could
have
a
localized
contaminatina
eIrect
on
the
groundwater.
Dr.
Sternberg
does
not
know
of
any
sciertifac
or
technological
reason
why
Trench
11
could
no-
opatatte.
He
also
believes
that
the
P
wells
are
inadequate
for
..orattrirg
(A,
547,
348)
Dr.
Nisbet
testified
that,
apecatically
for
Trench
11,
the
groundwater
gradient
is
exclu~iatlt
aowarcs
the
northwest
(A,
584).
He
also
stated
tha-t,
eat.
-
hypothetically
there
were
volatilization
of
an
earlaer
urdethcted
leak
at
the
bottom
of
the
Des
Plaines
River
bluffs,
its
car
ert~ation
would
be
far
below
any
health
concern——40—70
nanoqrn’ms/m
(a
nanogram
is
one
billionth
of
a
gram)
(R.583).
Apaat
from
the
frenca
11
area,
he
verified
that
there
may
be
some
southwesterly
flow
of
groundwater
from
the
southwestern
part
of
‘he
aite,
but
not
tot
a
significant
distance
because
of
higher
jrou’md.w~t~ e
e’ata
na
a
uth
and
southwest
of the
site
(A,
58S
536
Mr.
Nienkerk,
geological
ad.vasor
of
the
A3ency,
testified
that
the
likelihood
of
contamanatatn
reaching
a
re’—’idential
well
was
slim,
that
the
uppermost
aquife.,
the
one
of
‘oncerr,
is
being
properly monitored,
a ad
Ira
t
t
he
predomir ann
f” ow
f
the
groundwater
is
northwest,
Mr.
‘iicr.ktrK
ra.~scd concerns
abcut
site
geology,
particularly
of
the
Inc
al
Irall
ace
the
fractured
Dolomite
(R.
1095-1097).
Although
WMI
and
performed
‘~urthei
studies in response
to
Agency
a
‘cc
at
r~gaana ~g th-~ a
te’s
geology,
culminating
in
the
“e
~nocr
1
83
Wood.ward
Clyde
“in
consultation”
study
earlier
e
a
~ad
Mr.
~“icr.kerk
an ‘-nowledged
that
he
did
not
read
thIs
s~vd
I
rd.epend~n~stud~-.s,
“ance
he
had
already
concluded
tha~..
a’
oate.no
about
the
site
could
not
be
sa,tisifed
(A.
1132-1137),
Re
also
a;reed
that
Mr.
Chappel
disagreed with some
of
his
conclusions
about
the
site.
but
that
the
Agency asked
for
additional
informatIon,
ir
part
hated
on
his
concerns.
This
was
provided
ir
tue
December,
1983
Woodward—Clyde
report
(A.
1130—1131),
Dr.
Warner’s
testimony
was
a
loved
for
purposes
of
rebuttal
only,
since
he
played
no
role
if feating
the
Agency’s
permit
denial
decisions
(A.
1251—1254,
1.536~,
He
visited
the
sate
and
reviewed
various
reports,
particularly
the
Woodward—Clyde
July
and
December,
1983
reports
(A
at84,
1539).
He
concluded:
that
the
groundwater
moved
in
all
directions,
360
degrees,
away
from
the
site;
based
on
the
specific
atmductivity
values
(Pet
Exh,30)
the
groundwater
is
presently
coat
minated
(A.
1488
1491;,
and
that
the Olin gypsum pile was not the cause
(A,
1492),
that
the
organic
contaminants
in some of
the wells could have dome from
the trenches
(A,
1497); that the large scale permeability
of the
site may differ from the permeabiatty studies performed
(A.
1500)
and that the permeability could be larger
(A.
1502-1504);
and that
6O~2O5

large
scale
vertical
migratiot or
Li.
m atiatan$ kite though the
till
is
inevitable
absent
a
laat~att;~oIlectiurmsystem
(existence
of which
was
disputed)
(A,
I5~r
10,
13
3).
rr, ~‘aaner
disagreed
with
the
average
ve~cit~at f’ow calcula~.aors (A.
1519) and travel
time
(A.
1522-~15’
.
Dr
Warner had no opinion
regarding
the
accuracy
or reliabiatty of the organic
sampling
results
(A,
1546)
and
acknowatd.gec
hat
if
subsequent
sampling
analyses from well 0 105
and. cthers
s’moved negative results it
would affect his opinion
(A
15’2
Mr.
Hendron, testified in
e
+ta
o Dr. Warner,
Regarding
specific conductivity,
he beli’ ‘e
Ira
the high y mineralized
groundwater,
not
properly
reeoj
ize
a
hr
Warner,
led
to
an
erroneous
conclusion
of
high
arc’
~
~-
cont m’nat~cn (P
1921).
Reviewing the
same
data,
he
clad rot
see eat.~vatedlevels of
organics but possibly of sulfate
A
1922)
which
if
so, would
be
coming
from the adjacent 01
r
a oem
pile
‘-at ponds
(A,
1925,
1980).
Regarding
groundwater
at
felt
b-i Fiauze
at,
Exh.
7 opposes Dr. Warner’s cord
a
a
1
d
£iO
s’mo~angin the
Figure 33 of flow to the east
0
~9a
)
Regarding per-
meability,
Dr. Warner had te.~taatedti-at ‘~cod.wac Cly
found
agreement~through four lines
,f em d.enat tha- the
“10
for the
till is a very reasonable vanue’
H
937)’ tha- both field
and
laboratory tests closely apprcx
‘-
at
th
r’a~ war icabIr ity
(R.
1939),
and that the fractures
r’t p~.o
‘i.e
oreferential path-
ways
(A.
1940—1948),
In reupora-e
o
D’-
W”rne;
a atstarrony
concerning velocity
rates,
Mr. Honiror
teatif’-ed
thai’
Dr.
Warner’s velocity figures won’-
(
~
ar a
a ‘-e to
0,000
cu/ft/yr/acre, which,
in the
at
~‘u
ord.
sute
‘m’o.
d
leac
to an
organics level
of several thou ~d
o
1” per ba’-l on today
in the
P and W series wells closer
t
-a
ai
E
A
3
Ii a ~y
Mr.
Hendron believes that in Trench at
lesigr
rfal,.ration wall be
eliminated
to the best engineeraig extent poc’atble
(A,
1316—77).
The Board,
in reviewin) a
a
e
“-e-sranon~ regarding the
geology and hydrogeology of the site
and particularly the data
and conclusions presented to the Agency prior
to its decision,
is
persuaded
a)
that
this site h
e be~ probed,
,ested
and evaluated
to
an
unusual
degree,
b)
that
the
oreponderan~e
of
professional
testimony,
especially
by those ~ao conducted independeat studies,
indicates that the site’s charactaristata are not such that it as
inherently
unmanageable,
c)
tha
at ~ra as
ar. u~aaputed ‘worst
case” design of the detectior
-‘a nat.or.n3 w’~ll sjetem and a
state-of—the—art design of Tre
a
11 and d) there
are protective
remedies ~ailable
in the evert
or venafaea contamination,
particularly since the groundwater
onatorang regulatory scheme,
for Trench 11 as well as for the rest of the
site,
is premised
on
the anticipation
of
a
leak,
~seences~~it~d”EnvaronmentalProtection
One of the bases argued by the Agency throughout this pro-
ceeding is that its denial
is justified by Section
12(a)
and

39(a)
of the Act, which in ccr’~trctnori~l’.reet
that the Agency
shall issue permits if an applicant proves that operation of
a
facility will not “cause or threaten or allow the discharge of
any contaminants into the environment”
(S12(a)J,
In examining
this ground, the testimony of Mr
Kuatendali is of particular
importance.
Mr. Kuykendall has testified
at various points concerning an
evolving Agency policy,
first applied here
(A.
874—75),
concerning technology
“needed in terms of future haaa~d.ouswiste landfill trench
design,
operational
things, the
‘management of liquids in
landfills,
what
constitutes
ar
adequate
groundwater
monitoring
plan
in terms of meeting the needs of the State
of Illinois, versus what as ~quared
ur,der the Federal
Regulations
under
Subpart
F
poli y taint’
ataons
(A.
750,)
“The policy we are Lu ataarg
a
.
(that
a
hazardous waste
land
disposal
facility
.
.
.
seeking new
trenches or expansion within an existing facility, must be
in compliance with the gro atwater regilations before we can
believe that they could
go I
--~‘
a,Ld
~jti
pcniuitting further
trenches.”
(A.
840).
The question of what constitutes “compli’ance” is illuminated
in Mr. Kuykendall’s testimony concer’—iing optidns available to the
Agency once the old G and P well systems were determined to he
inadequate:
“The options the Agency had at that point were to,
one,
attempt to negotiate out a groundwater monitoring permit
that would have in it a q,qup~anceschedule of the
installation of wells
.
.
.
where ~P’-~ou
an fact say the
company had a groundwater monitoring system
in place,
that
they would over time come into compliance with the Subpart
F
-—
the groundwater monit ring regulations.
Other options that existed
at that time,
still exist,
are
referral
to
the Board,
Illinois Pollution Control Board,
of
an enforcement action;
third option is referring to the
USEPA Region V office
for
issuance of federal
administrative
orders.”
(R.
835, emphasis added).
Mr.
Barber
explained
th’a4a in a February 17,
1984
meeting
(R.
1866—1868)
at which Mr.
KuyRerdall was present, he or another
Agency person explained to DM1 that the Agency:
“had an interest in having
a permit go beyond merely
installing and building wells, because this would expedite,
for them, the ability to get these policies related to
remedial action codified, relative to rule making.

We had
a brief dia~uesa
Joit t.~t..~hlenaof rule-
making in the state,
and
ti-a
.
h’f
t~at
takes many
months,
and
they
felt that
a 1ernit such as the one they
outlined
would
in fact be
a~-’m-a’ar.cenlei
ir the way of
assuring environmental
protm. “the
,
and
tI ~t It would be of
big
benefit
to them if no
a fat
.cald. agree to
a permit of
that type***”
~R. 1870
Mr.
~uykendall
has also
at LeE
that a” the time of
the
permit denials he did not be ~e’c Lhore was
ax
enforceable
monitoring system in place,
no
.~c of VMI’
a appeal
A
841—42),
The
Board notes that this at’ur~.
a
“‘
incorrect
Appeal
of
a
permit does not extinguish
it
I
e acn’estel
acr.d.itaon..
of this
permit ware never
stayed by B
at Order
a
by
.perataor of
law.
The Board cannot find
ti
t
‘c
ona 12(a)
and 39(a)
authorize the Agency
s issuance of the aaund~ten permit with
all
of its
conditions,
or
ju’t:
‘y
enma.
the
Trench
11
and
supplemental waste stream p
r
rio as
e a~’ea
the
Agency’s
“policymaking”
violate
~1r’m
a
of Agency Board
functions established in the
c
ae
poatch”
pon which the
Trench 11 permit was denied run
u
t
o
he permit decision
precedent established
in a prev
at
resar no
.-a cc Board ruling,
and
c) the substitution of
ad.ma
a
a itive
rat
~ for enforcement
as
required
by
the
Act
acts at
oatga
a n o:
he rig
a
af the
permittee
and
the
public,
and
a
.,t ‘nirinoc” upon the ability
of
the
Agency
to
function
effecatvely
As
WMI
argues
(see
DM1 Br;ef
p.
60.—6~ a-a. cases
cited.
therein esp.
at p.
62),
this
‘-‘
mo~ o ‘expedte” promulgation
of
environmental
standards can’m
t
no
.o ~
1’,f
denia
of this
permit.
The
legislature
has vestea. the quasi.~.1egacaLativepower
of
rulemaking
in
the
Board
(Ccc
a
5
tmitle VII,
see also
Landfill,
supra,
It has also
catted
in Section 2?.4(b)
of
the
Act
the
path
rulemaking
not
“ace itica~an substance”
to ~CR
is
to
take,
Lengthy
as
the “full dress” Title VII
IAPA rulemaking
path
may sometimes
be,
the
legasla
are
determined
to
insure
full
rights
of
participation
by
tie
p
bI Ir
as
r”ll
as
by
the
regulated
waste
generators
and waste dac~pset~
This
type
of
“rulemakang
t
tue Aj acy as additionally
infirm
because
it
usurps legaaath’e
as well
as Board,
prerogatives.
Upon
Agency
requet yin the legislative process,
the
legislature
has
occasionally
aorferred quasi—legislative
powers
upon
the Agency
as,
for
a
-
~sce
at its creation of the
short—term
(45
days,
with a poss-ibi Ity to renew for 45
days)
provisional
variance
mechanism cc tamed
in Sections 35(b),
36(c),
and
37(b).
Such
delegations
am”
a
illy severely circumscribed;
the
policy
which
the
Agency
has aFt..~mptedto implement in
exercise
of
“its
sole
discretion”
has
unasually broad potential
applications
and
ramifications
on
the
waste dasoosal policy and
practices
of
this
state.

To put
it
simply,
were
‘Ire
.3o~d
tO
allow tie Agency
to
itself
determine
what
constitute~ groundwater monitoring
compliance for
sites which have accepted wastes pre—RCRA,
and
to
validate
denial
of
additional
orw~rstlnapermi’s on the
sole
basis
of
that
Agency
determination,
ll-noia could find that it
had
de
facto
issued
a
shut—down order
far
all exisr-Lng hazardous
waste
sites
once
their
current,
perna’ ted dasposa.
‘apacity is
exhau sted,
Specifically,
ESL is entreat y
iOt
operating due
to
the
instant
dispute,
being de fat
a
a p
5’—
~losura monitoring
mode,
it
is
generally agreed t
a’
nat
Ia ~i’-ls will leak
at
some time
in
the
future,
The RCaA A
and
he ACRA rules
promulgated
by
USEPA and the B
r
“innowledge the deficiencies
of
what
were
the
“state
of the
a-f”’ disposal practices of the
past
and
have
imposed
tougher row design and operation standards
which
have
a
focus
on
management
f leaking contaminants as
well
as
on
“entombing”
them
so
a.
tr
an maze
l’akage.
It is
agreed
that
Trench
11
meets
these eta
rd~
It
Is designed and
intended
to
be
operated
to ma
rar
introduction of
liquid
into
the
trench.
It
is
designed
wit
c~ysem
to
collect
leachate,
to
bring
it
out
of
the
trench
ratio
than merely ~-ocontain
it
in
the
trench.
The
trench
is not op~ratang
so that
if there were
currently
contamination
at the
-‘
Trench I1 is obviously
not
its cause.
But groundwater
“e
ri~
at”
a”
has been questioned
under the
Agency’s
policy
Based on a determination or
ron-’-corplianco
and given
the
Section
12(a)
prohibition
again”
ca
s’-rg or
‘atowing pollution,
the
argument
is
that
no
permit
ld
,‘ssue
If Trench 11 never
accepts
waste,
Trench
11 car
an
attn-u
a the leakage
which can be anticipated from
coin
of the older portions of
the
site,
Thus, failure to permit aall ensure that there is never
pollution from this source,
However
based on this record,
the
Board cannot allow
such
a
polaty t.
gaau a foothold
In its resolution of the Frank’s case,
the Board had
pre-
viously determined that permit issuance was mandatory upon proof
that
a
particular
portion
of
a facility--there above-ground
storage tanks-—would not cause pollution.
Here,
as in that case,
the Board can find no factual n°xus, or
Ii ikage,
suggesting
that
there
is
some
~~~fic
and j,~~icu’-arprevious design
or
operation aspect of
Trenches
1-10 and
ti-c codisposed area—-as
opposed
to
any
general
objection based on their mere
existence—-
which
indicates
that
Trench 11 ba~not i-oem des4gned
or
wall not
be
operated
to
meet
RCRA
standards,
Again,
in
Frink’s,
the Board. found ti-at permit
denial
could
not
take
the
place
of
an
enforcemert action revoking permits to
close
a
facility
about
which
the Agency had groundwater
concerns
related
to
other,
closed,
portions of the facility.
Finding
repetition
of
the
same
error
in
this case, the Board
is
constrained
to
add
to
its
previous comments,

Enforcement by permit dea..at
~
taoi ta cuttang off the
participation
rights of cbs
cc,
at
a
Lan’ p~btic and
the
permittee,
eliminates the Agen~a
~‘
S~act’aon39(i)
statutory
right
to deny permits based on the
~-
a~’~r’~
~‘cionhistory of vio-
lations as established th-o
g”m
r.
C
a
t enfoatement actions,
(Agency documents an tuas
‘t’
a.
II
-
a
hut at
‘east one
employee considered
and rejest
..aa ~pproaca
asaimably for
lack of
a
“paper trail”
(ke’p
at
2
a
~ —rc dates #1.
The attempted use of acr~
,aace o’de~as
substitute
for
enforcement also has danqen~
-
a
thor
ha
elimination of
public
participation nights
and. plae
‘-
than
RCRA authorization
in jeopardy.
When the Agency
at
or
~s
at~el the sate dis-
cretion to define and orde’
a
hi
ut either
‘he
ight
of
permit appeal
or finding of vao a-
by t’us Board,
it
is
shifting to itself the aecountab
“y
hi-
t ~hou1d rest
aith the
permittee.
What if the p~rat
~
at
‘aft
remediai.
strategy solely dictated and
at
.me
ice ~y, and
ar
environmental upset occurs~
‘ma
t
“t
o ma
at
ots in
the Environmental Protectat
at
to
u-i.
rat
by whom?
On what
grounds
can the Ager
ar e.~or’ere~taction
against
the
permittee?
It
at
~-~‘
j
rc’
iot
than’
pcrart’~ee,
that
has
used
its
sole
discretion
at
o
a
t
atna
dam
eta
egy;
the
permittee
is
merely
folbowir
at
era
-.n
‘.‘su,~.g
h~,e
permit,
the
Agency
has pre-~-ap
its
~wn a
at
a a and
assumed
responsibilities,
as
well as
a
placd
0”
the perruttee.
The Board notes that the Aa~ncyhas after recognized this
danger,
as
when,
for
example,
-
a
xnguathe’
‘a activities
from that of a consultant enqioce
~.
any oth r robe
that might
be construed as shIfting tie
at.
a
Ir
hi
ci
he ocrmit
applicant to itself.
In conclusion,
the Board d.oes not question the Agerr’y’s
good intentions,
Howo~er, t ~o
at~’
~“
nat ‘~ato~cper
conditions or permit denials tint anor~carcu~tpublic
and.
private rights clearly estatbashed
an the Act
“he Board
believes that such attempts serve
-
prolona
rather
than
so
“expedite”, environmental path e
Finally,
based
on the ob
a
sod
t
‘me aic
a sneedy
resolution
of this matter
eat
a
it
he
nat for appea’m,
the
Board will truncate the
25
d.a
at
cideratatr
period of
35
Ill.
Adm.
Code 103.240—241.
Any
mo’s’
a.
a
r re’onsidenation
shaat be
filed
on
or
before
Cctoher
at
i
at
:~
~er~
fiec. on
or
before
October
22,
to enabb
at
at
to ~a~e aation on any
such
motions
at
its
October 25 meet.
a
This Opinion constitutes
t
-
a d’s
faida.ngs at fact
and
conclusions of law in this matter

—39—
ORDER
1.
The Agency’s
permitting decisions concerning Permit
1984—16—SP,
issued March
2,
1984,
are affirmed
in
part
and
reversed
in part.
The permit is remanded
to
the
Agency.
Within
45
days
of
the date of this Order,
the
Agency
shall
issue
a
revised
permit,
striking Special Conditions
14,
16,
17,
and Special Attachment B in their entirety,
and
amending
Special
Conditions 12 and
13 and Attachment
A, Conditions
2,
3, 4~and
5
consistent
with the above Opinion.
2,
The
Agency’s
April
20,
1984 denial
of
an operating
permit
for
Trench
11,
and its April
30,
1984 denial
of about
599
supplemental
wastestream authorization permits
is
reversed.
The
Agency
shall
issue
these permits within 45
days
of
the
date
of
this
Order,
3.
The September 10,
1984 motion to vacate the hearing
officer’s
order
granting
intervention is granted.
4.
Petitioner’s
various
motions for default are
denied,
IT
IS SO ORDERED,
J.
P.
Dumelle
was
not
present.
B.
Forcade dissented
on
Paragraph
3
of
the
Order,
and
con-
curred
in the balance
of
the Opinion and Order,
I,
Dorothy
M.
Gunn, Clerk of the Illinois Pollution
Control
Board,
hereby
certify
that
the above Opinion and Paragraphs
1,
2,
and
4
of the
Order
were
adopted
on the~~~day
~
1984
by
a
vote
of
?‘-~
,
and that Paragraph
3
of
the
Order
was
adopted by
a vote of
~
Dorothy M.
Gunn, Clerk
Illinois Pollution
Control
Board
60-211

(
(
II1+nois Envir~nmentai
Protect~ion~geraz:y 2200(a~k0iRo~uESpr
rietd,U~
Z~27O5
2’~
7/7a2~~
9282
Refer
to:
Site No.
19704502
-~
hill
Courrty
Jol iet/ESL
Permit
No.
1984-’lG-IrD
Nàrch
2~1984
waste
Management,
Inc.
~nviroru~enta1
Sanitary Landfill,
Inc.
Route
1,
Box
109,
Lar~vay
Road
Elv;ood, lUlnois
60421
Gentlemen;
Supp1em~nta1permit Is
hereby
granted
to
Waste
Management,
mc,
to
modi&
the
groundwater
monitoring
program
all
in
accordance with
the
application
and
plans
prepared
by
Stanley
A.
Waiczynski,
P.E,~, dated
December
28,
1983
a~~d
received
by
the
Agency
on
December
29,
1982,
and
additional
information
received
February
2,
1984,
February
8,
1984k
February
13,
1984,
February
14,
1984,
February
15,
1984
and
February
21,
1984,
This
supplemental
permit is
further
subject
to
the
following
special
con
tions:
1~
Your
ground~iater
monitoring
program
is
hereby
approved
in
accordance
with
Attachments
A
arid
B,
and
‘is
subject
to
the
conditions
contained
therein,
All
required
groun&iatar
monitoring
points
shall
be
tnstalled
such
that
grounc~ater samples
may
be
taken
during
April
or
t1ay~1984
and
results submitted to
the
Agency by duly ~
1984.
2.
With1~~4xty
days
of
Installation
of
any
monitoring
point,
boring
logs,
as—built diagrams,
and
field
reports
of well
c~velo~ent
shall
be
submitted
to the
Agency,
As
built
diagrams,
for
each
monitoring
point
Installed,
shall
include
the
type
and inner diameter
of
casing
xnaterlal
used,
type
and
length
of
screen, packing material
used,
type
and length of seals
used, type
of backfill
used,
finishing
details,
groun~aterlevels,
elevation
of
the
top
of
casing,
ground surface
elevation, bottom
elevation,
interval
screened,, and depth.
All
surface elevations
are
to
be
measured
to
the nearest 0.01
foot
and.
reported rounded to
the
nearest
0.1
foot,
All
internal
well
elevations and
levels
are
to
he
measured
and
reported
to
the
nearest
0.1
foct.
3.
If replacement
of any monitorjng
point
becomes
necessary,
the Agency
shall
assign a
new designat~~,
to
the
point.
Agency
designations
are
not transferable.
Replacement
or
inclusion
of a
new
or additional
monitoring point Into
the
monitoring
program
is
a
modification
of
the
facility permit and
thus
‘requires
a supplemental
permit
prior
to
Thcleson
into the plan.
The
permittee
may install monitoring
points
for
Internal
use, but
later
incorporation
into the monitoring program
permitted therein Is subject to
Agency
approval.
Att~hrn~~t
1

(
Illinois
Environmental
P~otectior~
~~gency
2200
Churchill
R~oad,
Springfield,
IL 6270$
Page Z
4.
All
borings
not
utilized
as
monitoring
points
shall
be
backfilled
with
expanding
concrete
or
a hentonite
and
soil
mix,
Details
for
bore
hale
plugging
are
to
to
submitted
to
the
Pgency
with
as~built
diagrams.
5~.
For
the
proposed
wells
or
an,
replacement wells,
the
annular
space
(the
space
between
the
bore
bile
and
the
well
casing~
above
the
top
of
the
screen
~ist
he
sealed
with
a
suitable
material
(e.g.,
expanding
cement
grout
cr
hentoni te)
to
wi thin
four
feet
of
the
surface
to
prev~1t
contamination
of
sarTipies
and the groundwater,
An
expanding
concrnte
plug
shall
be
placed
from
four
feet
below
the
surface
to
a
point
above
the
ground
surface
and
be
sloped away from
the
well
casing
so
that
surface
water will
he
diverted
away
from
the
well
casing
and bore
hole.
All
other
aspects
of
proposed
wells
GIll
through G151 or
any replacements
wells
shall
he
constructed
in
accordance with
“Schematic
of
Construction
Planned
for
the
Uppermost
Aquifer Monitor
Wells
at
ESL”,
Fehrua~y,1984.
However,
screen
length shall
not
exceed
30
feet.
All
other
aspects
of
proposed
wells
GT1O through GT14
or
any
replacements
shall
he
constructed
in
accordance with
uSchematlc
c’
nst’uil~nn ~Car~ied
for the Tifl
Monitor Wells at
~SL’~,February.
1984,
6.
Sampling equipment,
either
a.
bailer
or
submersible
pump
system
(Well
Wizard),
shall be
dedicated
to
each
monitoring
point
‘in
Attachment
A,
special condition
1.
7.
Upon
installation
all monitoring points
‘in Attachment A,
special
condition
1
shall be
pump tested to determine
permeabiuity~K,
and
transmlssivity,
T,
~f the
screened
internal,
Test
method used and
results
shall
be
submitted
to
the
Agency
with
items
requested in
special
condition
2
above.
8.
The portion of
the well
casing,.
extending
above
the
ground
surface,
must
be
protected
to minimize
damage
or
tampering.
9.
Wells
shall
be
easily
~isib1e
and identified
with
Agency
monitoring
point designation,
10.
Al
monitoring
points
shall
he
maintained
such
that
a sample
may
be
th
ta i
ned.
11,
The
G
series
wells~ 5101,
5102,
5103,
5104,
5105,
5105,
and
5107,
shall
be
plugged
and
abandoned
as
follows:
a.
Remove
protective
cas’ing
pipe
arid
cap
assembly.
b.
Drill/Auger out
the
well
casing
down
t~
the
top
(+ 2 foot) of
the
gravel outwash
or
c~1
cmi to
bedrock
shoul
ci
that
he
the
strata
below
the
clay
till.

Illinois
Environmental ?rotertio~A1
v
2P
~C)
C
urriiil Poad~Springfield,
IL
627~-
c.
Fill
~nd plug
tbe
~c
grout to 2
feet b’~u
d.
Fill
the
rema~nde
of
12. The P Series
wells,
P1,
P
meintained,
sampled,
and ‘~a
condition 13
below
and
~
h
13, As a
part
of the
current
grc
P—series wells
and
the
one
~o
condition
I
closest
to
each
°
the
hazardous
waste
constit
Appendix
VII,
The
fol1ow~ng
Organlcs,
method
8240
and
ins
method
7470;
all
other
me~
method
In “Section
7, T~zt
SW-~6”.
The method
detecti
used,
The current
asses~y~
extended to July
15
198
evaluated as part
of
the
.,.i
14.. Until
such time as
the
p
rn
facility all Interim
Stat
Ad~inlstrative Code,
Sub
I
‘IS,
Permittee
shall
notify
the
Ag
submitted
to
the
Agency
in
~
Operating
permit
for
this
~l”’
any
ch4n~es
in
the
names
or a~
titleholders
to
the
here”in..~e
i
be
made
in
writing
within
f~f~a
Include the name
or
dames
of
i
of their. place of
abode’
o
~f
Its
registered
agent
l7~This permit Is
subject
to
.e
s
deemed necessary to
fulfi
t~
Environmental
Protection
I~c
and regulations.
Except as modified
in
the
above
and
operated In
accordance
wit”
t
1972—21, dated March 27,
1972,
as
subsequent
supplemental
permits.
r
Ira
er~.t arid
bentonite
“~
so
I
lush
w’th
grade.
P
6,
P
and P8,
shall be
i
~ordar~e wIth
special
c
~r
quality
~ssessnent
program,
the
ecu
tor
well
of
Attachment
A
special
elI
shall
be
sampled
and
analyzed
for
ained
i
40
CFR
Part
261,
yt
1
in
~ho a
s”all
be
used:
82
0. ~yar .e
mcthnd 9010; Mercury,
i
u
ci
be’ana1yzed
by
tbe
applicable
C
for
Cvalu
t n~Solid
Waste,
r
t for tb~semethods shall be
‘~I’
‘c
10
~n
u~,c.
~
~..
~hat
hove
cata
can
be
a
a.
rt
B
per sit
for
the
r
v
~
inois
C
a
US
t
tFapply
r
oh
nge~fror
the
information
i;
“o
for
a
D~velopmentand
r
:t~e~
‘ci’
~l notUy
the
Agency
of
r’
‘es
f
both
beneficial
and
legal
t~
site,
Such
notification
shall
i
(15
days
of
such
change
and
shall
pa’t’e
in
interest
and
the
address
a
corporation,
the
name
and address
eq
‘re installation of additional
lection
of
oararreters
to
be
ei(,e
~s
moy
be
necessary
to
~r
‘r
nrerta
Protection
Act,
~
~o’4’f’cit~o
by
the
Agency
as
il’
t
ndproserf
the
1 a~p‘~cab1eerv’ronmental rules
0
ulent
t~esite
shall
be
developed
a
t~r~s
ard
condi~’ionsof
Permit
~o.
eviced
‘lovember
18,
1981 and all
Page 3
16,.
This
Agency reserves
the
rig
t
~o
monitoring devices,
to
alter
analyzed and to
alter
mon’~
fulfill
the intent
of
the
II’

C
Illinois
Environmental
Protection
Agency
2200 Churchill
Road, Springfield. IL 62706
Page
4
All
certifications, logs,
or
reports
which
era
required
to
be
submitted
to
the
Agency
by
the
permittee
shall
be
mailed
to
the following
address:
Illinois
Environmental
Protection Agency
Compliance
Assurance Unit
Compliance ~4onit~ning
Section
Division
of
Land
Pollution Control
2200 Churchill
Road
Springfield,
Illinois
62706
Very
trul
yours,
?reflCei~~E,,~er~
~~ermit Section
Division
of
Land
Pollution
Control
LI4E
:LJK:bjh/sp/04440/l
,4
cc: Northern Region
Ccn~pliance
Monitoring
Section
(2)
Dr. Yaron Sternberg,
P,E.
Division File
60~2i5

(
flu
nois Environmental
Protection
Agency
2200 Chur~hiflRoad, Springfield,
IL 62706
Refer to:
Site
No,
19704502
.~
Will
County
Joliet/ESL
Peri’i~it~
l984-16~SP
(Wl16)
(14117)
March
2,
1984
ATTACHMENT A
I~ATERMONITORING
PROGRAM
1~.
The following
monitoring points shall
be included
in
the water
i~onitoringprogram for the facility:
~jcantDesig~ation
Agency
Designati
on
‘~Glil
*0111
*0112
*0113
*0113
*Gfl4
0115
0115
0116
S116
0117
(14114)
G117
0h8
~l3
0119
0119
0120
0120
0121
0121
0122
(14106)
0122
0123
0123
0125
0125
0126
0126
0127
0127
0129
0129
0130
0130
0131
0131
0132
0132
0133
0133
0134
(14118)
0134
0135
0135
G136
0136
G137
0137
0138
G138
0139
(WIll)
0139
0140
0140
0141
0141
G142
0142
0143
0143
0144
(W1l2)~
0144
0145
0145
?iO-2.Ib

(
Illinois
E~vironmenta1
Protection
Agency
2200 Churchill
Road, Springfield,
IL 62706
Pages’
~ntDesination
0146
0146
0147
0147
0148
0148
0149 (Wl09)
0149
0150
(14108)
0150
Gl5l
0151
$0210
(14107)
30110
$G2l1
$0111
$0212
$0112
$0213
(14104)
$0113
#30214
#$GT14
Proposed
well
G2l4
(0114)
shall
be relocated within 50 feet of well
GilL
*Denotes
upgradient
monitoring
well,
$Denotes
till
monitoring
well,
#Denotes background
till monitoring
well
2.
The
following
existing
monitoring
points
shall
be
used
as described
be’ow
to
obtain
data
for
the
current assessment, before they
are
abandoned
and
plugged:
~ant
Desi
nation
~yDesinatjon
P1
P1
P2
P3
P3
P4
P4
P5
P5
P6
P6
P7
P7
P8
P8
For
the
April
or
May, 1984 sampling,
analyze
samples from each
of. the
above ~onttorlng
points for the
constituents
listed
in
Appendix
VII
of
40
~fl Pert !6!
as
detailed
in
Item
13
of
this
permit
letter,
The
new
aquifer well
closest
to each P~we11 shall also be sampled and
analyzed
for the constituents in Appendix VII.
This data shall besubmitted as
part of
the assessment
plan
report
due
July
15,
1984,
Upon submission of
this assessment report, and determination and
acceptence by the
Agency that the facility has not affected the
groundwater, the P~~series
wells
shall
be
decommissioned,
abandoned and
plugged
according
to
the procedure described in Special
Condition
11
of
the
permtt letter,
Those
P~we11s
determined to be affected by the
facfltt4y
shall
be
included in further assessment
of
groundwater quality,
6O~217

C
Illinois
EnvironMental
Protection
Agency
2200 Churthill
Road, Springfield,
IL 62106
The concentrations
or
values of t~parameters
in Special
Condition
3
m
water
s~p1esfrom
the monitoring points above
shell
he determined during
April
or
May,
1984
and
reported to the Agency
by
~Ju1y
15,
1984.
3,
To
establish
initial
water
quality
for
the
monitoring
points
described
in
Special
Cofldition
1
of
this
attachment,
the
concentrations or values
of
the following parameters in
the water
samples
shall
be
detere~inedand
reported
quarterl.y
during
the first
year.
Alkalinity (total
as
CaCO3)
Arsenic
(As)
~oron(B)
Calcium
(Ca)
Chretnium (Cr) (total)
Fecal Coliform Bacteria
Lead
(Pb)
Manganese (Mn)
Nickel
(NI)
*pH (Field
Measured)
Potassium
(K)
Residue
on Evaporation
(180°)
Selenium
(Se)
Sodium
(Na)
Zinc (Zn)
Gross
Alpha
LI
ndane
Radium, Total
*Total
Organic
Halogen
(TOX)
2,4-0
Copp*r
~~nT~onia
(N)
Barium (Ba)
Cadmium
(Cd)
Chloride (Cl)
cyanide
CCN)
F7uoride
(F\
Magnesium
(Mg)
Mercury
(Hg)
~itrate-~Hitri
te
(N)
Phenol
(Unfil
tered)
Silver
(Ag)
Sulfate
(204)
Endrin
Gross
Beta
Methoxychi or
*Total
Organic
Carbon
Toxaphene
2~4~5:~T
(Sfl
Vex)
*Sppcj
fic
Conductance
(Field
Measured)
iron
~Fe)
(TOC)
(Iinfilterec
(SC)
Specific
Organics
~Wenzene
1,1 Djchloroethane
‘1,2
Dichloroethane
Ethylbenzene
Ethyl
Acetate
Methylene Chloride
Tol
uene
1,1,1 Trlchloroethane
Triehloroethylene
frlchlorofluoromethane
Methyl
Ethyl
Ketone
Tetrachi oroethylene
~‘lene
*Oenctes
four replicate measurements
required
for tne
upgradient
~on1tor1ng
wells,
6O~2i8

C
C
lI11no~s
Environmental
Protection
Agency
2200Churchill
Road. Springfield, IL 62~OG
Page 4
Upon
the completion
of
the first four
quarters
(first
year), the
background value
(mean)
and
variance
of
each
parameter
shall
be
calculated for the
upgradient
monitoring wells, and reported to the
Agency.
Values
for
Wells
G1I1~G112, G113
and G114
shall
be
averaged
to yield
one
background
value for each
parameter
according
to
the
formula
n
where
n
64
i=l n
for th. parameters reçui ring
repi~ate
values at the upgradient
wells.
4,
After
Initial
water quality
has
been established,
each
of the
taordtorlng points described in Special
Condition
I
of
this
attachment
shall be sampled quarterly
and
the
samples
analyzed
for
the
following
parameters:
*pfl (Field
Measured)
*Total
Organic
Halogen
(lOX)
*Total Organic Carbon
(TOC)(Iinfiltered)
*Speclflc Conductance
(SC)
(Field
Measured)
Specific
Organics
Benzene
Methyl
Ethyl Ketone
Methylene
Chloride
Tetrachloroethylene
Toluene
1,1,1
Trichioroetharie
Trichloroethylene
*Qenotes four replicate
measurements
required
semi~-annually and
singular
measurements for the alternate two quarters beginning with
the results due July
l5~
1985 for monitoring points Gill through G151.
In
addition to the
parameters specified above,
the till wells
shall
~
s~wp1ed
and analyzed for the following parameters
quarterly
k~inningwith
the
results due July 15, 1985:
Boron
CI~1oride
Sulfate
Specific
Organics
1,1 Dichioroethane
1 ,2 Dichioroethane
Ey1 benzene
Ethyl Acetate
Trichl orofi uorornethane
Tetrac hI
0 roe thyl ene
60-219

C
Illinois
Environmental
Protection
Agency
2200
Churchili
Road, Springfield, IL
62706
Page E
The above
lists
may he modified
based
on the results
of
first
year
initial qualtty sampling
In Special Condition 3 above~
Notification
of a change
In this
list
may
he
made
by the
Agency
in
a
suppimental
permit.
In accordance
with
725~l92
all
monitoring
points’in
special condition
I
above shall be sampled
and
analyzed
annually
beginning
with
the
results
due July
15,
1985
for
the
following
parameters:
Chloride
I
ron
Manganese
Phenols
Sodium
Sulfate
Monitoring points GuS
through 0151
shall
be compared
individually to
the
mean
of
Gill
through
0114,
The following statistical
procedure
shall
be
used
each
quarter
in
determining
whether
background values
of pH, TOX, TOC,
and
specific
conductance
have
each
been
exceeded:
A.
If the background
value has a sample coefficient
of variation
less than
1,00, the
mean
of
the
concentrations
of
each
of
the
above
parameters
at
each
monitoring
point
shall
individually
be
compared to that
parameterLs
background
value to
determine
whether
the
difference
is
significant
at
the
0,01
level using
the
Cochran~s
Approximation
to
the
Behrens~Fisher
Student~s
t-test
as
described
in Appendix
IV of
40
CFR 264.
If
the test
indicates that the
difference is significant,
the permittee must
either
(1)
repeat
the
same
procedure
(with at least
the
same
number
of
portions
as
used
in
the
first
test)
with
a
fresh
sample
from
the
monitoring well, or (2) use an
equivalent
statistical procedure for determining
whether
a statistically
significant change
has
occurred.
If
this
second round of
analyses indicates
that the difference
is
significant,
the
permittee
must
conclude
that
a
statistically
significant
change
has occurred,
Such
an alternate statistical procedure
must
reasonably
balance
the probability
of
falsely
identifying
a
non~contaminating
unit and the probability of
failing to
identify a
contaminating
unit in a manner that is
comparable to
that of the
statistical procedure described above
and must
be
approved by the
Agency prior to submission of
the first
quarterly analyses
evaluated
by
this
procedures
8.
If the background
value
has
a
sample coefficient
of
variation
greather than or
equal
to i~O0,the
permittee must use a
statistical procedure
providing reasonable
confidence that
the
migration of
hazardous constituents from the
facility
into
and
through the
aquifer
will
he
indicated,
The
statistical
procedure shall:
60~220

C
Illinois Environmental
Protection
Agency
2280
Churchill
Road,
Springfield,
IL 62706
Page 6
I.
be appropriate
far
the
distribution of
the
data
used to
establish
backqround
vaiue~ and
ii.
provide a reasonable balance
between
the
probability
of
falsely
Identifying
a
non~contaminatingunit
and
the
probability of
failing to identify a contaminating unit.
‘UI.
be
submitted
to
the Agency
for
approval
prior to the first
quarterly analyzes evaluated by this
procedure.
5. For
all
monitoring
points
the
schedule
for
sample
collection
and
submission of
subsequent
quarterly
water
monitoring
results
is
as
follows:
Results Due
to
Samples to be
Collected
the
Agency
by:
During
the
Months
of:
TS~hof
Januá~y
October
t~ovember
15th
of
April
January
February
15th
of
July
April
May
15th of
October
July
August
6. Wells Glil through G151
in
Special
Condition
I
above
shall
have
a
minimum
of
three
well
volumes
of water removed
prior
to
sampling.
A
minimum of one well volume
of
~iater shall
be removed from wells GT1O
through
GT14
prior
to
sampling.
Wells GTIO through GT14
may
be
sampled
over
3
consecutive
days if enough sample
cannot
be
obtained
for all
required
analyses
immediately after till
well evacuation.
7.
The
fallowing items A through C shall
be
determined
each
time
a
sample
is obtained and
item D shall
be determined annually
beginning July 15,
1984,
and shall
be reported
with
the analysis:
A.
Elevation, as rererenced to mean sea level
(MSL), of the
groundwater
surface
at
each
monitoring
well.
This determination
is to be made prior to any
water being withdrawn
from
the
monitor
well.
These
elevations
shall
be
measured
and
rPr~~rted
to the nearest 0.1
foot.
B.
The
temperature
of the water sample.
C.
The
height
of
the
stick-up.
This
is
the
measurement of the
length
of
casing
extending above the ground surface.
D.
Depth
to the bottcrn of
the
well,
as
measured
from the top of the
casi ng.
8.
The
enclosed
water
monitoring instruction packet must be utilized
in
sampling and reporting under your approved water monitoring program.
6O~221

C
C
Illinois Environmental Protection Agency
2200
ChurchiU
Road,
Springfield, IL 62706
Page
7
9.
Groundwater flow rate
arid
direction in the uppermost
aquifer
shall
be
determined annually
and reported
with the monitoring results
due
July
15,
1985
~nd
every year
thereafter.
10.
Deep
aquifer
wells W120 and W121
shall be
maintained such that a
sample qan be
obtained,
if you have
any
questions
concerning
Attachment A~please
contact
Linda
Kissinger at
2i7/7B2~6762,
LJK:hv/sp/0330D/14
cc: Compliance Monitoring Section
Northern
Region
Dr.
Yaron
Sternberg
60-222

C
C
Illinois
Environmental Protection
Agency
2200 Churchill
Road, Springfield,
IL SZ7QS
Refer to:
Will
County
Jol
iet/ESL
PermIt
No.:
1984~l6aSP
March
2,
1981
ATTACHMENT
B
COMPLIANCE
SCHEDULE
1.
The
following
criteria
shall
cause
the
facility
to
iaplement
a
groundwater
quelfly
assessment
program.
A.
For
the
till
monitoring
wells:
a)
During
the
first year
when
background
quality
is
being
established,
the
detection of
one or
more
of
the
specific
organic
constituents
(greater
than
or
equal
to
10 ppb)
in
wells
GT1O,
GIll,
(ff12,
or
GT13
and
the
presence
verified
by
an
immediate
resampling
and analysis,
or
any
of
the
constituents
exceed
the
Water Quality
Standards
for
Underground Waters
(Sec
303.203
or
303.201)
in
these
wells
and
not in
the
background
well
(GT14),
or
the concentration
of
any
of
the
constituents
in
wells
GT1O,
GT11,
GT12,
or
9113
Is
significantly
higher
than
the concentration
of
that
constituent in
the
background well
(GT14).
b)
In
succeeding years,
the
detection of
one or
more of
the
specific
organic
constituents
(greater
than
or
equal
to
10
ppb)
in
wells
GT1O,.
6111,
6112,
or
GT13
and
the
presence
verified
by
an
immediate
resspli ng
and
analysis.
B.
For
the
aquifer
monitoring
wells.
a)
During
the first year
when
background
quality is
being
established,
the
detection of
one
or
more
of
the specific
organic
constituents
(greater
than
or
equal
to
10
ppb)
in
any
dowugradient wells
(6115
through
6151)
and
the
presence
verified
by
an
immediate
resampling
and
analysis,
the
concentration of
any
of
the
constituents
exceed
the
Water
Quality
Standards
for Underground
Waters
(Sec.
303.203)
in
the
downgradient wells
but
not in
the
upgradient
wells,
or
the
concentration
of
any
of the
constituents
in
any
downgradient
well
is
significantly
higher
than
the
concentration
of
that constituent
In
the
upgradient wells.
b)
In
succeeding
years,
a
statistical
increase
(or
decrease
in
the case
of
pH)
in
the
value
of
one
or
more
of
the
indicator
parameters
in
the
doimgradient well s
or
the
detection
of
one
or
more
of
the
specific
organic
constituents
(greater
than
o~
equal
to
10
ppb)
in
any
downgradient
well.
60-228

lUinois Environmental
Protection
Agency
2200
Churchill
Road, Springfield. IL
62706
Page
2
2.
The
Agency
shall
be
notified ~ithir~
seven
days
of
the
confirmation
of
a statistical change
in
the ctowngradient
wells~,the presence of
organic constituents
(greater than or equal
to
10 ppb) in the
downgradierit wells~the concentration of any constituent(s)
that
exceeds
the
Water Quality Standards for Underground Waters
(Sec.
303.203) in
the downgradient wells but not
in
the upgradi’ent wells,
or
the
concentration
of
any
constituent that
is significantly higher
than the concentration
of that constituent
in the background
wells,
that
the facility may be affecting
the
iroundwater (Section
725,193(d)(2)).
3.
A
groundwater
quality
assessment
plan
shall
be submitted to the
Agency
within 15 days
of
the
above
notification
(Section
‘~5.l93(d)(2.~5)L,
4.
The Agency shall
approve
as
submitted,.approve
with
modification,
or
disapprove with reasons for disapproval,
the
groundwater
quality
assessment plan.,
If
approved
as
submitted or approved with
modification, the
plan
shall
be
initiated within 30 days of
notification,.
If disapproved,
the plan
shall
be corrected in
accordance with reasons
for
disapproval,
and
resubmitted within 15
days.
5.
In
addition
to
the
requirements of
Section 725~l93(d),the following
shall
apply:
A)
The program shafl
be capable of determining
the location within
the facility of the source affecting groundwater.
B)
The assessment
shall
include
a
risk assessment including:
a)
the population at risk (he, potentially affected
residential wells);
b)
amount
of
substance(s);
C)
hydrogeoligic
factors;
d)
climate;
e)
hazardous
or
toxic
properties
of
the substance(s); and
f)
environmental
factors
C)
If the groundwater quality assessment program determines that
there
is
no
impact
to groundwater quality from the
facility,
monitoring
shall
retur~i to detection monitorir~g
D)
The assessment shall
&ddress
any change
in
the background water
quality over time,
6,
Upon submis~j~~
of the results of the approved groundwater quality
assessment
prograim,
the Agency sh~lidetermine whether such
results
indicate that there may be
a
violation
of Section
12(a) of
the Act
or
whether such results demonstrate
a risk of harm to public health or
60-224

Illinois
Environmental
Protection
Agency
2280
Churchill
Road,
Springfield, IL 62706
Page 3
the
environment,
(f
the
Agency
finds
that
such
a
violation
may
exist
or
that
such
a
risk
has
been
demonstrated,
it
shall
direct
the
Permittee
to
submit
an
engineering
feasibility
plan
for
corrective
action
to
the
Agency
within 120 days.
A.
This engineering
feasibility plan for corrective action shall,
at
a minimum, address
the
following
items:
a)
Review and confirmation of the risk
assessment;
b)
Source control, and/or removal or
in situ treatment of
hazardous waste constituents
in the groundwater;
c)
Short and
long
term methods
for providing an alternate
source of drinking water for affected water supply wells;
d)
Establish
performance
objectives for corrective action;
e)
Details and specifications of the corrective action with an
emphasis
on use of established technology;
f)
Evaluation
in
terms
of engineering implementation or
constructability;
g)
Assessment of the extent to which the corrective action is
expected to effectively mitigate
arid
minimize damage to and
provide adequate protection of public health, welfare and
the environment;
h)
Analysis
of any adverse environmental impacts and methods
for
mitigating
these
impacts;
1)
Groundwater
monitoring
program
to
demonstrate
the
effectiveness
of
the
corrective
action;
j)
Provisions
for
reporting
the
status
of
the
corrective
action;
k)
Listing of local,
state,
or federal permits necessary to
carry out the corrective action;
1)
The need for
phasing the corrective action to insure that
the Implementation is not unnecessarily delayed (e.g..
source control actions could be taken in conjunction with
further
assessment of
the
groundwater);
7.
If
the current groundwater quality assessment determines the facility
is affecting groundwater the permittee shall
within
60 days
meet
the
requirements of special condition 5 and,
if necessary as determined
by the.Agency, subsequent special conditions of this attachment.
60-225

Illinois
Environmental Protection
Agency
2200 Churchill
goad. Springfield,
IL 62706
Page 4
8.
The Agency
s~ail
approve as submitted, approve with modification, or
disapprove with
reasons for
disapproval,
the
engineering
feasibility
plan for
corrective
action.
if approved as submitted or approved
with
modification,
the
plan
shall
be
initiated
within
30 days
of
notification.
If disapproved the plan shall
be corrected In
accordance with the rea~onsfor disapproval, and
resubmitted within
30 days.
9.
Corrective actions may
be terminated
when
the corrective action
performance standards
have
been
met
for
three
consecutive years.
The
detection monitoring program in Attachment A shall
then be
reinstated.
10.
The provisions and requirements of special conditions
5
through 9
of
this Attachment B shall not become effective until the effective date
of an Agency permit to operate Trench
ii..
UK:bv/sp/0330D/8..l 1
60-228

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