ILLINOIS
POLLUTION
CONTROL
BOARD
February
25,
1988
IN
THE
MATTER
OF:
)
DEVELOPMENT,
OPERATING
AND
)
R88-7
REPORTING
REQUIREMENTS
FOR
)
(see
R84-17)
NON-HAZARDOUS
WASTE
LANDFILLS
PROPOSED
RULE.
FIRST
NOTICE.
PROPOSED
OPINION
OF
THE
BOARD
(by
J.
Anderson):
SUMMARY
OF
TODAY’S
ACTIONS*
This
Proposed
Opinion
articulates
the
rationale
for
actions
taken
by
the
Board
in
four
separate
Orders
in
various
regulatory
dockets.
The
purpose
of
all
of
these
related
actions
is
modernization
of
the
state’s
regulations
for
the
management
of
non—hazardous
wastes.
1)
Opening
of
Docket
R88—7
2)
Dismissal
of
R84—17,
Dockets
A,
B,
C,
D.
In
Docket
R88—7,
the
Board
has
adopted
a
set
of
proposed
regulations
for
first
notice
publication
in
the
Illinois
Register.
These
proposed
regulations
contain
development,
operating
and
reporting
requirements
applicable
to
new
and
existing
landfills
which
dispose
of
non—hazardous
waste.
In
*
At
the
outset,
the
Board
wishes
to
commend
the
Board’s
Scientific/Technical
Section
(STS)
for
the
quality
of
its
participation
in
this
proceeding.
A
special
acknowledgment
is
due
to
Richard
A.
DiMambro,
both
as
coordinator
of
the
various
consultants
and
other
experts
whose
testimony
has
been
sponsored
by
the
Board’s
STS
during
the
course
of
this
proceeding,
and
as
principal
author
of
the
STS
Recommendations.
The
Board
also
acknowledges
the
contributions
made
to
the
STS
Recommendations
by
STS
environmental
scientist
Dr.
Harish
Rao,
Dr.
Gilbert
Zemansky
(during
the
course
of
his
former
employment
as
STS
Chief),
and
Karen
Mystrik
(during
the
course
of
her
former
employment
as
STS
librarian).
The
Board
also
wishes
to
acknowledge
the
special
contribution
made
by
attorney
assistant
Kathleen
M.
Crowley,
who
has
served
as
Hearing
Officer
throughout
these
proceedings,
and
who
has
participated
in
the
drafting
of
the
Board’s
Opinion
and
Order
in
this
and
related
matters.
86—649
—2—
adopting
this
proposal,
the
Board
has
considered
the
extensive
record
developed
in
R84—17,
Dockets
A,
B,
C
and
D.
The
Board’s
proposal
is
largely
based
on
the
proposal
submitted
by
the
Board’s
Scientific/Technical
Section
(STS)
which
was
the
subject
of
hearings
in
R84—l7,
Docket
D.
This
Opinion
must
be
read
in
conjunction
with
the
STS
“Recommendations
For
a
Non—Hazardous
Waste
Disposal
Program
In
Illinois
and
A
Background
Report
To
Accompany
Proposed
Regulations
For
Solid
Waste
Disposal
Facilities,
Part
A:
Landfills”
(Final,
March
7,
1988)
which
is
entered
as
Exhibit
1
in
Docket
R88—7;
as
explained
in
more
detail
later,
this
Opinion
does
not
reiterate
much
of
the
analysis
of
the
proposals
submitted
in
Dockets
A,
B,
and
C.
R84—17,
Dockets
A,
B,
C,
and
D
are
being
dismissed
by
the
Board
to
make
quite
clear
that
the
Board
does
not
intend
to
adopt
as
its
own
any
of
these
proposals
in
their
entirety,
although
elements
of
each
proposal
are
included
in
the
Board’s
R88—7
proposal.
The
Board
will
accept
written
comments
concerning
its
R88—7
proposal
for
45
days
following
the
publication
of
the
proposal
in
the
Illinois
Register.
Decision
on
the
number
and
scope
of
any
additional
hearings
in
this
docket
will
be
deferred
until
after
expiration
of
the
comment
period.
3)
Dismissal
of
Docket
R84—22(D)
The
R84—22(D)
docket
was
initiated
to
make
technical
corrections
to
the
Board’s
existing
regulations
for
financial
assurance
for
closure
and
post
closure
care
of
waste
disposal
sites.
The
docket
is
being
dismissed
because
1)
the
technical
corrections
are
being
addressed
in
the
R88—7
proposal,
and
2)
the
interrelationship
between
matters
of
financial
assurance
requirements
for
closure
and
post
closure
care,
and
the
design
and
operating
standards
being
proposed
in
R88—7
are
such
that
it
is
no
longer
necessary
or
advisable
to
treat
them
in
separate
dockets.
4)
Opening
of
Docket
R88—8
The
records
developed
in
the
R84—17
and
R84—22
dockets
highlights,
in
the
absence
of
reporting
requirements,
the
lack
of
data
concerning
the
location
of
permit
exempt
waste
generators
who
treat,
store
or
dispose
of
waste
generated
by
their
own
activities
on
that
site,
let
alone
the
types
and
quantities
of
waste
treated,
stored,
or
disposed
at
such
sites.
The
Board
has
opened
Docket
R88—8
for
the
purpose
of
considering
proposal
of
regulations
requiring
a
“census”
of
such
facilities,
and
has
directed
staff
to
prepare
a
regulatory
proposal
designed
to
elicit
basic
information.
Finally,
the
Board
notes
that
it
is
currently
investigating
new
regulations
to
address
other
facilities
that
handle
solid
waste,
temporary
waste
storage
areas,
solid
waste
treatment
86—650
—3—
operations,
surface
impoundments,
and
recycling
operations.
Regulations
are
under
consideration
for
haulers
and
generators
of
solid
waste.
A
separate
Board
proceeding,
R85—27,
will
address
the
issues
surrounding
special
waste
evaluation
and
handling.
PROCEDURAL
HISTORY
The
Board
adopted
its
“Chapter
7”
regulations
covering
operations
of
sanitary
landfills
in
1973.
These
regulations,
since
codified
as
37
Ill.
Adm.
Code
Part
807,
have
remained
virtually
unchanged
since
that
time,
save
for
the
addition
of
regulations
concerning
financial
assurance
for
closure
and
post—
closure
care.
In
1976,
the
Board
adopted
its
“Chapter
9”
regulations
concerning
the
hauling
of
special
waste.
These
regulations,
since
codified
as
35
Ill.
Adm.
Code
Part
809,
have
also
existed
virtually
without
change,
except
for
the
addition
of
regulations
concerning
hauling
and
disposal
of
hazardous
hospital
waste.
Abortive
attempts
to
modernize
these
rules
commenced
in
the
1980.
Docket
R80—20
was
initiated
by
a
proposal
of
the
Illinois
Environmental
Protection
Agency
(Agency)
to
update
Chapter
7,
and
Docket
R8l—31
was
initiated
by
a
Board
proposal
to
update
Chapter
9.
These
proposals
were
consolidated
and
dismissed
by
Order
of
the
Board
on
October
5,
1982,
after
hearings
indicated
that
extensive
revision
of
the
proposals
was
necessary.
In
that
Order,
the
Board
noted
that:
The
Agency
and
the
Illinois
State
Chamber
of
Commerce
[ISCC]
indicated
that
they
were
working
together
on
a
substitute
proposal
which
would
replace
both
Chapters
7
and
9.
During
[the
hearing]
process
it
has
become
clear
first
that
the
subject
matters
of
Chapters
7
and
9
require
coordination
to
insure
consistency
and,
second,
that
it
will
be
difficult
to
relate
the
testimony
on
the
former
proposals
to
the
evolving
combined
proposal.
The
Board
therefore
hereby
consolidates
R80—20
and
R81—31,
and
at
the
same
time
dismisses
both.
In
that
same
Order,
Docket
R82—2l
was
opened
to
consider
the
anticipated
Agency/ISCC
proposal
for
permits
for
waste
management
and
hauling,
and
Docket
R82—22
was
opened
to
consider
the
antici
pated
proposal
for
landfill
operating
criteria.
The
Agency
filed
a
proposal
in
the
R82—21
docket
only,
which
proposal
was
the
subjebt
of
hearings.
Both
dockets
were
closed
by
Order
of
June
16,
1983,
as
a
result
of
Agency
withdrawal
of
its
R82—2l
proposal.
The
proposal
was
withdrawn
as
the
Agency
believed
that
86--651
—4—
the best
solution
to
various problems
identified
at
hearing
was
submission
of
an
amended
and
expanded
proposal.
This docket, R84—l7,
was initiated
to
consider
a
draft
proposal filed
by the
Agency on May
31, 1984.
Two inquiry
hearings
were
held
at which participants
identified
concerns
with
the
proposal
and questioned
the Agency
concerning
its intent.
At
the last hearing
the
Agency indicated
its
intention of filing
a
revised proposal.
As
the Board noted
in its
Resolution of
December
6, 1984 announcing
its
intention
of committing
some of
the resources
of the
Scientific
Technical
Section
(STS)
to
this
proceeding,
no revised
proposal
had been submitted.
Although the
Agency has
been
a very
active
and helpful
participant
in
subsequent
phases
of
this
proceeding,
it has
not filed
a new
proposal or
presented
evidence
in
support
of the existing
draft
proposal.
OnApril 4,
1985, the ISSC
filed
an alternate
proposal.
By
Order
of April
18, 1985,
the
Board established
Docket
B for
consideration
of this
proposal.
Four hearings
were
held in
Docket
B concerning
this
proposal.
On August
15, 1986, Waste
Management
of
Illinois
filed
another
alternate
proposal,
which the
Board designated
as R84—l7
Docket C. This
proposal
was the subject
of nine hearings.
Concurrently
with the
hearings held
in
Dockets
B and
C, the
Board held additional
hearings in Docket
A.
The purpose of
these
hearings
was
presentation
of testimony
by
various
consultants
and
other scientific
experts
whose
appearance
was arranged
by the
STS. These
consultants
and other
experts
did not critique
the
various
proposals pending
before
the Board,
but instead
provided
testimony
concerning their
research
and
experience concerning
subjects
integral
to analysis
and/or development
of
comprehensive
regulations
for
the management
of waste.
By
its
Order
of February
19,
1987,
the Board
determined
that
only
one
additional
hearing
would be held
in
Dockets
A, B, and
C.
One basis for
this
determination
was that:
“The record
to
date
in
R84—l7
is
sufficient
to
enable
the Board
to determine that,
while
each
proposal
has
meritorious
components, no
single
proposal
pending
before it
is
sufficiently
refined
or
comprehensive
to be adopted
by the
Board
as the
Board’s own
proposal
for
the
purposes
of
first
notice
publication
pursuant
to
the Illinois
Administrative
Procedure
Act,
and
resulting
additional
hearings.
It
is
clear
to the
Board that
the Board
itself,
with
the
assistance
of its
scientific/technical
and
legal
staff,
must
craft
a proposal
to
address
86—652
—5--
the
sum
of
the
various
concerns
which
have
been
brought
to
the
Board’s
attention.”
The
Order
went
on
to
establish
the
form
and
procedures
for
the
filing
of
a
proposal
by
the
STS,
including
required
filing
of
documents
for
public
inspection
contemporaneously
with
distribution
of
copies
to
the
Board
Members,
consistent
with
ex
parte
restrictions
articulated
in
the
Board’s
“Protocols
of
Operation
For
the
Scientific/Technical
Section”,
RES
86—1,
January
26,
1986
and
the
Board’s
Procedural
Rules,
35
Ill.
Adm.
Code
101.121.
By
Order
of
March
5,
1987,
the
Board
established
that
the
final
hearing
in
Dockets
A,
B,
and
C
would
be
held
on
April
28,
1987,
that
the
public
comment
period
would
close
on
May
20,
and
that
the
Board
would
commence
deliberations
on
May
28,
1987.
Consistent
with
the
directives
in
the
Board’s
Orders
of
February
19
and
March
5,
1987,
on
May
22
and
May
26,
1987,
the
STS
filed
an
initial
set
of
proposed
regulations
consisting
of
new
Parts
810,
811
and
812
with
its
supporting
“Recommendations
for
Non—Hazardous
Waste
Disposal
Program
in
Illinois
and
A
Background
Report
To
Accompanying
Proposed
Regulations
For
Solid
Waste
Disposal
Facilities”
(Background
Report).
On
June
12
and
June
21,
1987,
the
STS
filed
another
set
of
proposed
regulations,
consisting
of
Parts
813
and
814
and
a
supporting
Background
Report.
By
Orders
of
May
28
and
June
22,
1987,
the
Board
authorized
the
STS
proposal
for
hearing.
The
May
28
Order
established
a
Docket
D
for
consideration
of
the
STS
proposal.
The
Board
expressly
noted
that
it
was
taking
no
action
at
that
time
on
the
proposals
in
Dockets
A,
B,
C.
The
STS
proposal
was
the
subject
of
ten
hearings.
To
expedite
the
proceedings,
participants
were
required
to
file
written
questions
and
comments
concerning
the
STS
proposal,
to
which
the
STS
provided
written
responses
to
be
discussed
at
hearing.
The
comment
period
was
closed
in
Docket
D
on
December
30,
l987.*
*
Post—hearing
comments
will
sometimes
be
referred
to
herein
by
Public
Comment
(P.C.)
number
without
identification
of
submitter.
The
following
is
a
listing
of
post—hearing
public
comments
by
number
and
submitter:
P.C.
42,
Wagner
Casting
Company
by
James
Mason,
Vice
President
Manufacturing
Services;
P.C.
43,
Andrews
Environmental
Engineering,
Inc.
by
J.
Douglas
Andrews,
P.
E.,
President;
P.C.
44,
Northeastern
Illinois
Planning
Commission
by
Lawrence
B.
Christmas,
Executive
Director;
P.C.
45,
Environmental
Reclamation
Company
by
Carl
Ball,
President;
P.C.
46,
McHenry
County
Defenders
by
Gerald
A.
(continued)
86—653
—6—
At
hearing,
the
STS
had
committed
to
redrafting
various
portions
of
the
proposal
in
response
to
testimony
and
to
consider
redrafting
in
response
to
any
subsequent
written
comment
received.
Accordingly,
the
STS
filed
revised
versions
of
various
portions
of
its
proposed
rules
and
Background
Report
on
January
15,
February
4
and
18.
Consistent
with
prior
practice
in
this
docket,
the
STS
dealt
with
the
Agency’s
untimely
comment,
filed
January
5,
1988,
as
a
matter
of
discretion
and
to
the
extent
that
time
permitted.
By
Order
of
February
4,
1988,
the
Board
adopted
an
Order
which
realigned
its
relationship
with
the
STS.
The
Board’s
Order
stated:
The
Board
has
been
deliberating
the
STS
revised
proposal,
as
well
as
the
records
in
Docket
A,
B,
&
C
since
January
21,
1988.
The
Board
has
limited
its
discussions
with
the
STS
consistent
with
the
February
19,
1987,
Order
and
the
Board’s
Protocols.
The
Board
has
found
that
in
order
to
fully
and
expeditiously
deliberate
these
matters
it
is
necessary
to
informally
consult
with
STS
staff
concerning
the
technical
details
in
the
voluminous
R84—17
record.
As
the
bases
for
and
comments
concerning
the
STS
proposal
are
a
matter
of
public
record,
the
Board
now
feels
that
it
may,
without
prejudice
to
the
integrity
of
its
process,
terminate
its
“arm’s
length”
dealing
with
STS
staff.
Accordingly,
as
of
this
date,
the
STS
staff
will
no
longer
be
considered
“exterior”
to
the
Board
within
the
meaning
of
the
Protocols.
STS
staff
is
directed
to
resume
communications
with
the
Board
in
the
usual
Board/staff
relationship.
The
ex
parte
constraints
of
35
Ill.
Adm.
Code
101.121(b)
shall
apply
to
STS
communications
with
persons
other
than
Board
Members
and
staff.
Paulson;
P.C.
47,
National
Soild
Wastes
Management
Association
Final
Comments
by
Fred
C.
Prillaman,
Esq.;
P.C.
48,
Pioneer
Processing,
Inc.
by
William
A.
Speary,
Jr.,
General
Counsel;
P.C.
49,
Land
and
Lakes
Co.
by
James
T.
Ambroso,
Environmental
Manager;
P.C.
50,
Illinois
Environmental
Regulatory
Group
by
James
T.
Harrington,
Esq.;
P.C.
51,
Waste
Management
of
Illinois,
Inc.
by
Percy
L.
Angelo,
Esq.;
P.C.
52,
Illinois
Department
of
Energy
and
Natural
Resources
by
Fred
Zalcrnan,
Esq.;
P.C.
53,
Illinois
Environmental
Protection
Agency
by
Phillip
R.
Van
Ness,
Esq.
86—654
—7.-
Deliberations
continued
on
February
5,
1988.
On
February
11,
1988,
the
Board
adopted
an
Order
directing
its
staff
to
develop
a
revised
proposal
for
its
consideration
on
February
25,
1988
finding
that:
The
Board
is
in
full
agreement
with
the
essential
elements
of
the
proposal.
However,
the
Board
wishes
to
see
regulatory
language
embodying
certain
concepts
which
either
are
not
contained
in
the
existing
proposal,
are
not
clearly
expressed,
or
are
alternative
to
those
presently
proposed.
By
its
Order
today,
the
Board
adopts
its
own
proposal
for
first
notice
publication
in
the
Illinois
Register.
MAJOR
PARTICIPANTS
The
record
in
this
matter
is
too
voluminous
for
the
Board
to
synopsize
all
testimony
presented.
The
following
individuals
and
organizations
have
made
contributions
to
this
proceeding
as
noted.
The
Agency
(Proponent
in
Docket
A)
Questions
concerning
the
Agency’s
Docket
A
informal
proposal
were
received
by:
Lawrence
Eastep,
P.
E.
Permit
Manager,
Division
of
Land
Pollution
Control
(DLPC)
Harry
Chappel,
P.
E.
Manager,
Compliance
Section,
DLPC
Monte
Nienkirk
Manager,
State
Site
Mangement
Unit,
Remedial
Project
Management
Section,
DLPC
Linda
J.
Kissinger
Environmental
Protection
Specialist,
DLPC
Scott
0.
Phillips,
Esg.
Enforcement
Programs
Virginia
Yang,
Esg.
Enforcement
Programs
Gary
King,
Esg.
Enforcement
Programs
86—655
—8—
Of
this
group,
Mr.
Eastep
and
Mr.
Chappel
have
continued
involvement
on
the
part
of
the
Agency,
which
is
currently
also
represented
by:
Edwin
C.
Bakowski
Manager,
Solid
Waste/UIC
Unit,
DLPC
Phillip
Van
Ness,
Esg.
Enforcement
Programs
ISCC
(Proponent
in
Docket
B)
Illinois
Environmental
Regulatory
Group.
The
Docket
B
proposal
was
prepared
by
the
Illinois
Waste
Regulatory
Committee
of
the
ISCC.
Testimony
concerning
the
language
of
the
Docket
B
proposal
was
presented
by:
Sidney
M.
Marder
Environmental
Consultant
Jeffrey
C.
Fort,
Esq.
Martin,
Craig,
Chester
and
Sonnenschein
The
Illinois
Environmental
Regulatory
Group
(IERG),
formed
in
1986,
is
an
affiliate
of
the
ISCC
which
currently
represents
some
34
Illinois
Industries
interested
in
the
development
of
the
state’s
environmental
regulations
(P.C.
50,
p.
1).
Since
formation
of
IERG,
ISCC
has
not
participated
in
the
R84—17
docket
as
a
separate
entity.
IERG
is
currently
represented
in
this
proceeding
by:
Sidney
M.
Marder
Executive
Director,
IERG
Katherine
D.
Hodge,
Esq.
General
Counsel,
IERG
James
T.
Harrington,
Esq.
Ross
&
Hardies
In
addition
to
presentation
of
testimony
by
Mr.
Marder,
both
ISCC
and
IERG
have
sponsored
technical
testimony
in
Dockets
B
&
D
concerning
the
properties
of
wastes
generated
by
certain
industries
and
the
state
of
the
research
concerning
disposal
of
such
wastes.
These
industries,
and
their
representatives
have
been:
86—656
—9—
Illinois
Steel
Group:
David
H.
Miller
Consulting
Engineer
Thomas
M.
Barnes,
Venture
Manager
Outokumpu,
Oy(sic)
Utility
Industry:
Thomas
Hemminger
Director
of
Water
Quality,
Commonwealth
Edison
Foundry
Industry:
Michael
Slattery
President,
Illinois
Cast
Metals
Association
Thomas
Kunes:
Executive
Vice
President,
RMT,
Inc.
Chairman,
American
Foundryman’s
Society
Committee
1OF
on
Water
Quality
&
Solid
Wastes
Waste
Management
of
Illinois,
Inc.
(Proponent
in
Docket
C)
Various
representatives
of
Waste
Management
of
Illinois
(WMI),
its
parent
corporation
Waste
Management,
Inc.
(WM,
Inc.),
and
Waste
Management
of
North
America
(WMNA),
another
WM,
Inc.
subsidiary,
presented
testimony
in
support
of
WMI’s
Docket
C
proposal,
as
well
as
considerable
comment
concerning
the
STS
Docket
D
proposal.
The
representatives
for
Waste
Management
have
been:
Peter
Vardi
Vice
President
For
Environmental
Management,
WM,
Inc.
Gary
Williams
Director,
Environmental
Compliance
WM,
Inc.
Ronald
Poland
Director,
Environmental
Engineering,
WM,
Inc.
John
Baker
Manager,
Environmental
Monitoring
Programs,
WM,
Inc.
Henry
L.
Martin
Manager,
Gas
Recovery,
WMNA
Tom
Tomaszewski
General
Manager,
CID
Processing,
WMI
Dale
Hoekstra
General
Manager,
Midway
Landfill,
WMI
86—657
—10—
Dr.
Jay
Lehr
Professor
of
Groundwater
Hydrology,
Ohio
State
University;
Executive
Director,
National
Water
Well
Association
E.
Clark
Boli
President,
Meredith/Boli
and
Associates
Carolyn
Lown,
Esq.
WM,
Inc.
Percy
Angelo,
Esq.
Mayer,
Brown
&
Platt
STS
(Proponent
in
Docket
D)
The
STS
sponsored
the
testimony
of
various
witnesses
in
Docket
A,
which
testimony
served
as
the
basis
for
some
components
of
the
STS
proposal
supported
by
further
testimony
in
Docket
D.
The
STS
witnesses
and
consultants,
and
the
subjects
of
their
testimonies
were:
Richard
DiMambro
Environmental
Engineer,
STS
Dr.
Richard
C.
Berg,
Thomas
M.
Johnson,
Dr.
William
R.
Roy,
Dr.
Robert
A.
Griffin
Illinois
State
Geological
Survey
Dr.
David
E.
Daniel,
Assistant
Professor
University
of
Texas
Dr.
Robert
K.
Ham,
Professor
of
Civil
&
Environmental
Engineering
University
of
Wisconsin
Dr.
Cecil
Lue—Hing,
Director
of
Research
and
Development
Metropolitan
Sanitary
District
of
Greater
Chicago
Dr.
Aaron
A.
Jennings,
Associate
Professor
of
Civil
Engineering
University
of
Toledo
(Ohio)
STS
Proposal
Various
geological
consid
erations
regarding
landfill
siting
and
potential
for
groundwater
contamination
Landfill/Liners
and
other
earthen
barriers
Generation
and
character
istics
of
landfill
leachate
and
gas
A
case
history
of
landfill
leachate
treatment
at
a
publicly
owned
treatment
works
(MSGDC
Calumet
Sewage
Treatment
Works)
Groundwater
contamination
modeling
86—658
—11—
Department
of
Energy
and
Natural
Resources
The
Division
of
Energy
and
Environmental
Affairs
of
the
Department
of
Energy
and
Natural
Resources
(DENR)
has
participated
throughout
these
proceedings
for
the
purpose
of
determining
whether
DENR
would
prepare
an
economic
impact
study
concerning
the
various
proposals
and
the
scope
of
any
such
study.
DENR
employees
present
for
these
purposes
have
included:
Bonnie
Eynon
Meyer
Coordinator,
EcIS
AnalysIs
Program
Elliott
Zimmerman
Resource
Planner
Stanley
Yonkauski,
Esq.
Fred
Zalcman,
Esq.
Technical
testimony
concerning
special
waste
disposal
issues
was
presented
by
a
representative
of
another
division
of
DENR:
David
Thomas
Director,
Hazardous
Waste
Research
and
Information
Center
The
Board
further
notes
that
the
Illinois
State
Geological
Survey
is
also
a
division
of
DENR.
Illinois
Chapter,
National
Solid
Waste
Management
Association,
and
Various
Landfill
Operators
The
Illinois
Chapter
of
the
National
Solid
Waste
Management
Association
(NSWMA)
has
sponsored
testimony
and
comments
on
behalf
of
the
Illinois
Chapter
and
its
various
member
disposal
facilities.
As
the
Illinois
Chapter
has
not
provided
the
Board
with
a
membership
list,
the
Board
is
unsure
of
how
many
of
the
individual
waste
management
companies
who
have
participated
in
this
proceeding
are
NSWMA
members.
In
listing
these
companies
in
this
section
for
convenience,
the
Board
is
not
implying
that
these
companies
are
necessarily
affiliated
with
NSWMA.
These
participants
have
been:
Joseph
R.
Benedict
Chairman,
Illinois
Chapter,
NSWMA
Director
of
Regulatory
Affairs,
Sexton
Companies
86—659
—12—
Dr.
Charles
A.
Johnson
Technical
Director,
NSWMA
Dr.
Edward
Repa
Institute
of
Solid
Waste
Disposal,
NSWMA
Bob
Peters
State
Program
Manager,
NSWMA
Fred
A.
Prillaman,
Esq.
Mohan,
Alewelt,
&
Prillaman
James
Ambroso
Environmental
Manager,
Land
&
Lakes,
Co.
Carl
Ball
President,
Environmental
Reclamation
Co.
Paul
DeGroot
President,
States
Land
Improvement
Co.
Leo
Lentz
Modern
Landfill
Co.
Francis
J.
O’Brien
Environmental
Control
Manager,
Browning
Ferris
Industries
of
Illinois,
Inc.
William
A.
Speary,
Jr.,
Esq.
General
Counsel,
Pioneer
Processing,
Inc.
Environmental
Groups
Various
environmental
groups
have
participated
in
these
proceedings
through
their
directors,
as
well
as
through
counsel
representing
a
coalition
of
groups.
(Individual
members
of
these
groups
are
too
numerous
to
list).
These
have
been:
Patricia
A.
Sharkey,
Esg.,
representing
Citizens
for
a
Better
Environment
(CBE),
Great
Lakes
Sierra
Club,
McHenry
County
Defenders
(MCD),
Center
for
Neighborhood
Technology,
Coalition
For
Appropriate
Waste
Disposal,
South
Chicago
Development
Commission
CBE:
Kevin
Greene
Research
Director
Dr.
Robert
Ginsberg
Midwest
Research
Director
86—660
—13—
MCD:
Gerald
Paulson
Executive
Director
Grey
Lindsay
Environmental
Consultant
Environmental
Consultants
In
addition
to
those
previously
listed,
various
environmental
consulting
firms
have
participated,
particularly
in
Docket
D,
on
behalf
of
themselves
or
their
clients.
These
include:
James
Douglas
Andrews,
P.
E.
Andrews
Environmental
Engineering
Darryl
Bauer
Baxter
and
Woodman,
Inc.
Daniel
P.
Dietzler,
P.E.
Patrick
Engineering,
Inc.
Richard
W.
Eldredge,
P.E.
Eldredge
Engineering
Associates,
Inc.
Roberta
L.
Jennings
Consultant
Hydrologist
WMI
Objection
to
February
4,
Order
On
February
10,
1988,
WMI
filed
an
objection
to
the
February
4
Order
realigning
the
relationship
of
the
Board
and
the
STS.
The
essence
of
WMI’s
objection
is
that:
While
fully
recognizing
the
good
faith
of
the
STS
staff
WMI
notes
that
the
process
of
first
creating
a
separate
staff
proposal
supported
by
informal
contacts
and
then
attempting
to
reestablish
the
usual
Board/staff
relationship
inescapably
presents
serious
conflicts
of
interest.
.
WMI
assumes
that
it
is
improper
for
an
advocate
of
a
certain
proposal
to
have
direct
access
to
the
Board
to
support
its
views
no
matter
how
much
it
believes
they
may
be
meritorious.
Certain
Board
Members
have
commented
that
in
agencies
it
is
sometimes
necessary
to
“wear
two
hats.”
If
that
means
that
agency
86—661
—14—
personnel
are
on
occasion
called
upon
to
be
both
advocates
and
decisionmakers,
we
respectfully
suggest
that
it
is
not
proper
for
such
personnel
to
assume
both
roles
in
the
same
case.
Once
a
“Chinese
Wall”
is
constructed
to
deal
with
a
potential
conflict
situation
it
is
not
possible
to
dismantle
it
when
it
becomes
inconvenient.
The
Board
notes
that,
while
WMI
has
lodged
an
objection
for
the
record,
that
it
has
not
either
generally
or
specifically
requested
that
the
Board
take
action
on
its
objection.
The
Board
accordingly
will
offer
only
three
comments
in
response
to
the
objection.
First,
as
a
matter
of
policy,
the
Board
is
now,
and
has
been
throughout
the
course
of
this
proceeding,
highly
cognizant
of
its
obligation
to
base
its
decision
on
information
contained
in
the
record.
Second,
the
Board
did
not
issue
its
February
4
Order
for
the
purpose
of
giving
the
STS
an
opportunity
to
“lobby”
the
Board
in
support
of
its
proposal;
the
Board
did
so
to
allow
it
to
ask
clarifying
questions
of
the
one
member
of
its
STS
staff
able
to
provide
timely
clarification
of
some
aspects
of
this
record.
The
STS
staff
currently
consists
of
three
members,
one
of
whom
has
been
assigned
to
this
R84—l7
docket
since
the
STS
was
staffed
in
1985
and
who
prepared
the
Docket
D
proposal
and
background
report
at
the
behest
of
the
Board.
Neither
of
the
other
two
STS
staff
members
is
familiar
with
the
voluminous
record
in
R84—l7,
and
neither
is
particularly
suited
by
way
of
scientific
training
or
recent
prior
experience
to
quickly
assimilate
this
record
and
respond
to
questions
by
the
Board.
One
member’s
primary
area
of
concentration
has
been
in
the
area
of
air
quality,
and
the
other’s
in
the
area
of
promulgation
of
state
rules
implementing
the
federal
NPDES
and
RCRA
hazardous
waste
programs.
Third,
the
Opinion
and
Order
adopted
by
the
Board
today
reflect
the
collective
judgment
of
this
seven
Member
Board
based
on
the
record
developed
to
date,
a
judgment
which
is
markedly
different
from
that
of
the
STS
in
a
number
of
areas.
INTER-RELATION
WITH
STS
BACKGROUND
REPORT
While
the
Board
has
not
adopted
the
STS
proposed
rules
without
change,
the
Board
does
endorse
the
technical
analysis
and
rationale
behind
the
major
components
of
the
proposal.
Areas
in
which
the
Board’s
first
notice
proposal
diverges
from
the
STS
Recommendations
will
be
discussed
in
some
detail
in
this
Opinion*;
in
areas
which
the
Board’s
thinking
is
similar
to
that
86—662
—15—
of the
STS,
this
Opinion
will
provide
only supplementary
comments.
This
Opinion
should
be
read
together
with
the
STS
Background
Report,
as,
for
the purposes
of this
first
notice
proposed
Opinion,
the
Board
has not
engaged
in
the
mechanical
task
of
selective
incorporation
of
portions
of the
Background
Report.
As
earlier
noted,
the
STS
Background
Report,
as
filed
on
March
7,
1988
with
final
edits
pursuant
to leave
of
the
Board
granted
in
its
Order
in R88—7,
will
be
introduced
as
Exhibit
1
in R88—7.
The
references
listed
at
pages 114—131
of the
Background
Report
will be
introduced
as Group
Exhibit
2.
DISMISSAL
OF
DOCKETS
A,B,C,
AND
D
AND
CREATION
OF
DOCKET
R88-7
At
several
earlier
points in
this
proceeding,
the
Board
has
indicated
that
the proposals
in
Docket
A, B, and
C would
not
be
adopted
by
the Board
for
first notice
publication,
and
indicated
in
its
February
11 Order
that neither
would
the
Docket
D
proposal.
In
its
December
30, 1987
public
comment
(P.C.
52),
DENR
raised
many
concerns
concerning
the
economic
impact
statement
(EcIS)
process
in this
proceeding.
One of
these is,
in
essence,
that
the continued
pendancy
in
this docket
of
proposals
other
than that
adopted
by
the Board
raises
questions
as
to
whether
an EcIS
must
compare
and
contrast
the
economic
effects
of
each
proposal.
In reviewing
this
record,
the
Board has
found
that
it is
virtually
impossible
to
compare
the
proposals
on
a point
by
point
basis,
as
the Docket
A,B,C
and
D
proposals
differ
so markedly
in
their
structure,
in their
proposed
scope
of
facilities
to
be
covered,
and in
their approaches
to a
variety
of
issues
such as
that
of
location
standards.
To remove
any
questions
concerning
the
Board’s
view
of the
status
of
these
proposals,
and of
the
scope
of
DENR’s
statutory
obligations,
the
Board
has, by
separate
Order,
dismissed
the
proposals
in Dockets
A,B,C
and
D and
two
established
a
new
Docket,
R88—7,
for
its
own
proposal.
The
record
in Dockets
A,B,C
and
D
are
incorporated
into the
record
in Docket
R88—7.
The
caption
in
this
proceeding,
which
was
drawn from
the
Agency’s
May,
1984
proposal,
will
also
be amended
to
reflect
the
fact that
the
R88—7 proposal
establishes
requirements
for
all
landfills,
*
In
areas
where
the
Board
has
declined
to accept
specific
STS
Recommendations,
the
STS recommendations
will continue
to appear
in
the
Background
Report,
but
will
be
discussed
without
a
prefatory
rule
number
heading.
The
purpose
in
so doing
is
to
provide
a clear
record
of
the
evolution
of this
proposal.
86—663
—16—
but
does
not
impose
requirements
for
generators
and
haulers
of
special
waste.
In
dismissing
the
Dockets
A,B,C,
and
D
proposals,
the
Board
wishes
to
note,
as
has
the
STS
in
its
Background
Report
at
p.
2—
3,
that
elements
of
each
of
the
proposals
have
been
incorporated
into
the
STS
Docket
D
proposal;
many
of
these
have
accordingly
been
adopted
by
the
Board
in
the
R88—7
proposal.
While
some
provisions
of
the
proposals
will
be
discussed
in
conjunction
with
various
provisions
of
the
Board’s
R88—7
proposal,
some
general
comments
about
these
proposals
in
Dockets
A,B
and
C
are
in
order.
Each
of
these
three
proposals
suggests
some
changes,
whether
small
or
large,
in
35
Ill.
Mm.
Code,
Part
809,
which
establishes
requirements
for
hauling,
delivery,
and
acceptance
of
special
waste.
The
Board’s
proposal
does
not
reach
to
Part
809.
Dismissal
of
the
proposals
to
amend
Part
809
should
not
be
construed
as
a
determination
by
the
Board
that
no
changes
are
needed
in
Part
809
specifically,
or
in
the
state’s
special
waste
system
generally.
Parallel
to
and
contemporaneously
with
the
R84—17
proceeding,
the
Board
has
been
considering
special
waste
issues
in
two
proceedings,
Docket
R84—43
and
Docket
R85—27,
into
which
R84—43
has
been
subsumed.
These
dockets
were
initiated,
respectively,
in
response
to
legislative
mandates
codified
as
Sections
22.01
and
22.9
of
the
Act.
Throughout
the
course
of
these
proceedings,
the
inter—relationship
of
landfill
design
and
operating
issues
with
special
waste
issues
has
been
a
subject
of
discussion
at
hearings,
and
the
question
has
arisen
as
to
whether
one
docket
could
proceed
in
advance
of
another.
The
Board
has
concluded
that
this
proposal
for
design
and
operation
of
landfills
can
appropriately
proceed
while
work
progresses
on
specific
special
waste
issues.
The
design
standards
contained
in
this
proposal
do
not,
by
their
terms,
depend
for
applicability
upon
whether
a
landfill
receives
waste
which
is
currently
classified
as
a
special
waste
or
which
may
be
so
classified
in
future.
Instead,
they
depend
upon
the
chemical
and
biological
properties
of
the
waste.
As
to
operating
standards,
this
proposal
does
contain
some
general
procedures
for
identification
and
handling
of
special
wastes
which
are
intended
to
supplement
Part
809.
It
is
clear
from
the
records
in
these
proceedings
that
there
may
well
be
specific
waste
streams
for
which
specific
more
stringent
disposal
standards
should
be
developed,
such
as
bulk
liquids,
as
WMI
suggests
in
its
Docket
C
proposal,
or
automobile
tires
and
incinderator
ash
which
are
recognized
in
the
popular
press
as
well
as
the
scientific
literature
as
posing
peculiar
public
health
and
disposal
hazards.
However,
at
this
time,
none
of
the
records
in
any
of
the
proceedings
before
the
Board
are
86—664
—17—
sufficiently
developed
to
allow
the
Board
to
propose
regulations
on
a
wastestream
by
wastestream
basis.
The
Board
believes
that
the
operating
standards
of
this
proposal
are
so
structured
as
to
permit
the
later
addition
of
more
specific
procedures,
and
that
proposal
of
the
general
rules
should
not
be
delayed
pending
development
of
rules
for
exceptions.
SUMMARY
OF
PROPOSAL
The
following
is
a
“broadbrush”
overview
of
the
major
elements
of
this
proposal.
It
must
be
read
in
conjunction
with
the
Board
proposal
and
STS
Background
Report.
Type
and
Number
of
Facilities
Affected
At
the
risk
of
oversimplification,
the
type
of
waste
which
has
been
the
target
of
this
regulatory
docket
can
generally
be
characterized
as
solid
waste
which
is
not
regulated
as
a
hazardous
waste
pursuant
to
Subtitle
C
of
the
federal
Resource
Conservation
and
Recovery
Act
of
1976
(RCRA)
as
amended
by
the
1984
Hazardous
and
Solid
Waste
Amendments
(HSWA),
42
USC
Section
6901
et
seq.
The
Board
has
adopted
rules
“identical
in
substance”
to
the
RCRA
rules
adopted
by
the
United
States
Environmental
Protection
Agency
(USEPA);
the
Board’s
rules
are
codified
at
35
Ill.
Adm.
Code
Parts
700—750.
For
the
purposes
of
this
discussion,
“solid
waste
management”
is
a
term
which
commonly
includes
a
variety
of
waste
handling
methods.
These
include
1)
the
permanent
deposit
of
solid
waste
in
landfills
which
meet
all
regulatory
requirements,
as
well
as
such
deposit
in
non—complying
facilities
which
are
categorized
as
“open
dumps”;
2)
the
combustion
of
solid
waste
in
incinerators
which
meet
all
regulatory
requirements,
as
well
as
such
combustion
in
non—complying
facilities
which
is
categorized
as
“open
burning”;
3)
the
treatment,
storage
and/or
disposal
of
solid
waste
in
waste
piles;
4)
the
treatment,
storage,
and/or
disposal
of
solid
waste
in
surface
impoundments
(also
known
as
pits,
ponds,
and
lagoons);
5)
application
of
solid
waste
onto
or
into
the
soil
(also
known
as
land
farming
and
land
spreading);
6)
temporary
storage
of
waste
at
transfer
stations
pending
its
transportation
to
another
solid
waste
management
facility;
and
7)
the
recycling
and
reclaiming
of
solid
waste
for
beneficial
re
use.
Today’s
proposal
does
not
cover
the
entire
universe
of
solid
waste
management
practices
and
facilities;
it
is
confined
to
facilities
here
defined
as
“landfills”:
areas
of
land
or
an
excavation
in
which
wastes
are
placed
for
permanent
disposal.
Excluded
are
facilities
whose
emissions
are
regulated
under
other
federal
or
state
programs
for
protection
of
land
application
units,
surface
impoundments,
and
injection
wells.
Included
for
8
6-6
65
—18—
the
present
purposes
are
waste
disposal
piles.
(See
35
Ill.
Adm.
Code
700.102(b)).
These
regulations
do
not
cover
facilities
which
haul,
treat,
store
or
recycle
solid
waste.
Such
activities
are
not
presently
governed
by
detailed
regulations
at
either
the
state
or
federal
level;
these
activities
will
be
addressed
in
future
regulatory
proceedings.
Today’s
proposed
rules
would
establish
minimum
standards
for
the
design
and
operation
of
all
new
landfills
whether
they
are
required
to
have
a
permit
or
are
exempt
from
permitting,
and
in
general
would
establish
requirements
for
the
upgrading
of
existing
landfills.
Landfills
which
are
exempt
from
permit
requirements
which,
by
way
of
example,
are
those
where
an
industry
disposes
of
its
own
wastes
on
its
own
property,
will
be
required
to
submit
to
the
Agency
essentially
the
same
type
of
data
which
is
required
of
permitted
facilities.
As
explained
later
in
some
detail,
the
Agency
reports
that
there
are
146
existing
landfills
with
permits.
No
data
is
presented
on
either
reported
or
calculated
remaining
lives
for
13
of
these
sites.
Of
the
remaining,
the
Board
calculates
that
some
64
expect
to
close
within
0—5
years,
25
within
6—10
years,
and
44
within
11—234
years.
Little
hard
data
is
available
concerning
the
number
of
currently
existing
landfills
which
are
operating
pursuant
to
the
permit
exemption.
Since
existing
rules
have
not
required
even
that
such
landfills
file
reports
concerning
their
operations,
their
existence
comes
to
the
attention
of
the
Agency
only
where,
in
the
course
of
other
business,
for
instance,
an
air
permit
inspector
notices
a
landfill
operation,
or
it
receives
complaints
of
environmental
problems.
Agency
personnel
testified
that
as
a
“ballpark
figure”,
the
Agency
knows
of
some
40—50
landfills
in
this
category.
New
Landfill
Design
and
Operation
Three
new
categories
of
non—hazardous
solid
waste
are
defined:
inert,
putrescible
and
chemical.
These
wastes
must
be
placed
in
disposal
facilities
best
equipped
to
prevent
the
escape
of
pollutants
into
the
environment,
with
the
“worst”
type
of
wastes
requiring
the
most
stringent
controls.
Inert
waste
will
not
burn,
biodegrade,
cause
an
odor,
serve
as
food
for
birds
and
animals,
form
a
gas,
or
form
a
contaminated
leachate.
The
requirements
for
disposal
of
inert
waste
are
minimal
and
mainly
deal
with
surface
water
pollution,
and
windblown
dust
and
debris.
Putrescible
waste
includes
household
refuse,
garbage,
commercial
waste,
and
any
other
material
that
can
biodegrade
at
a
rapid
rate
to
form
landfill
gas
and
a
contaminated
leachate.
86—666
—19—
Putrescible wastes must be placed in disposal
facilities
equipped
with
a
liner and
a
leachate collection
system to prevent the
discharge of leachate
to
groundwater.
Systems to monitor the
buildup and migration of landfill
gas must
be
placed around the
landfill and
groundwater monitoring wells must
be sampled on a
monthly
basis.
Chemical wastes are, generally, industrial
solid wastes that
are not hazardous but,
nevertheless, must be placed in
a facility
that controls and monitors the discharge of leachate.
Chemical
wastes are usually placed in
a dedicated disposal facility
on the
site
at
which they
are generated.
For new landfills, minimum
design requirements include
a
compacted three—foot earthen liner,
a leachate collection system,
and
a
series of
monitoring wells. Each new facility must
investigate the hydrogeology beneath
and around the site in
a
three—phase program
to determine potential groundwater
contamination
pathways. A groundwater impact
assessment is
specified so
that the adequacy of the liner design can be tested
at
the site.
The landfill owner
must determine the quality of the
groundwater
at
the proposed site,
including the background
concentrations of
certain indicator constituents. The
proposed
site design
must demonstrate that it will comply with the
performance standard: that
any contaminant emissions from
the
facility will
not cause an increase in the levels
of
the
background constituents within
100 years at a measuring point
100
feet from the
edge of the landfill’s disposal
area or at the
property boundary, whichever is
closer. (This measuring point
is
called the zone of attenuation.)
Additional, more stringent
design requirements will
be required if a site cannot
demonstrate
that it will
comply with this goal.
This
proposal
does not, with some exceptions
mandated by
statute, specifically pinpoint areas of the
state in which
landfills should or should
not be located.
In
cooperation
with the Board, the Illinois
Geological
Survey is conducting
a
computer
modeling project to
quantitatively assess the potential
for contaminant migration
through
15 sequences
of geologic
materials typical in Illinois
using two landfill design scenarios
and six contaminants.
(See
Background Report,
pp.
78—91)
One of the landfill designs is
that proposed here,
a three foot clay liner
and leachate
collection
system; the other, representing
current
design
practice, is a
10 foot
liner
and no leachate collection system.
The Survey’s
preliminary results indicate that using the Board’s
minimum proposed
liner/leachate collection system design, the
proposed “no increase in
background concentration” standard
could
be
met with various geological settings
which comprise
47.0% of
86—667
—20—
the
state’s
land
surface.
Of
the
remaining
areas,
it
is
possible
that
some
could
be
made
suitable
by
adding
to
the
minimum
design
standards
or
could
be
suitable
for
industrial
uses
producing
a
leachate
less
contaminated
than
that
produced
by,
for
instance,
a
municipal
waste
landfill.
Under
these
circumstances,
it
would
appear
that
the
economics
of
complying
with
more
stringent
design
requirements
would
naturally
motivate
a
landfill
operator
to
choose
a
more
geologically
preferable
site.
On
the
other
hand,
in
cases
where
use
of
a
less
preferable
site
is
imperative
for
reasons
of
industrial
or
economic
development,
the
opportunity
to
“design
up
to
standard”
is
available.
To
insure
that
predicted
performance
of
an
otherwise
suitable
design
is
not
undermined
by
shoddy
construction
techniques,
a
construction
quality
assurance
(CQA)
program
must
be
implemented
during
the
construction
of
each
structure.
The
regulations
are
intended
to
insure
that
the
facilities
are
constructed
to
meet
all
of
the
design
and
performance
requirements.
The
CQA
officer
must
be
a
person
other
than
the
operator
and
must
be
a
professional
engineer
registered
with
the
State
of
Illinois.
The
CQA
officer
must
be
present
at
various
stages
of,
and
certify
to
the
construction
including
installation
of
the
liner,
the
leachate
drainage
and
collection
system,
the
gas
control
systems,
and
the
final
cover.
Other
duties
include
sampling
the
quality
of
material
and
procedures
used,
supervising
all
inspectors
and
preparing
a
summary
report
for
each
day
of
construction
activity.
During
the
time
a
landfill
is
accepting
waste,
it
must
comply
with
general
standards
for
site
security,
surface
water
control,
daily
and
intermediate
cover,
maintenance,
fire
protection
and
flood
protection.
The
landfill
operator
must
monitor
the
environment
for
effects
produced
by
waste
disposal.
Groundwater
monitoring
effects
must
be
concentrated
in
an
inner
zone
defined
as
being
halfway
to
the
edge
of
the
zone
of
attenuation.
Any
unanticipated
seepage
of
leachate
will,
therefore,
be
detected
before
reachingthe
edge
of
the
zone
of
attenuation.
An
assessment
and
a
remedial
action
procedure
if
indicated,
must
be
implemented
if
a
statistically
significant
increase
in
the
concentration
of
any
contaminant
is
detected
by
the
monitoring
network.
Monitoring
must
continue
for
a
minimum
of
five
years
after
closure,
until
contaminated
leachate
is
no
longer
generated
at
the
facility.
Landfill
gases
are
also
extensively
regulated.
Methane
and
carbon
dioxide
are
the
primary
gases
produced
by
disposal
sites.
A
network
of
gas
monitoring
devices
must
be
placed
around
the
landfill
and
a
gas
collection
and
disposal
system
must
be
86—668
—21—
installed
if
excessive
gas
migration
is
observed.
Monitoring
must
continue
until
gas
is
no
longer
generated
in
significant
quantities.
Once
a
portion
of the
facility
ceases
to accept
waste,
that
portion
must
be
covered
with
a composite
cover
system
consisting
of
two
layers.
The
bottom
layer
is
intended
to
prevent
precipitation
infiltration
into
the waste
and
will
be
a
relatively
impermeable
compacted
earth
layer
or
synthetic
sheet.
The
upper,
protective
layer
is
intended
to
offer
protection
to
the
relatively
impermeable
layer
and
support
vegetation to
minimize
erosion
and
dust.
This
top
layer
will
consist
of at
least
three
feet
of
good
quality
topsoil
capable
of
supporting
vegetation.
The
facility
is
required
to
provide
proof
of
its
financial
ability
to
comply
with
all
required
closure
and
post—closure
requirements.
Permitting of
New
Landfills
In
the
existing
regulations,
facilities
are
required
to
obtain
development
permits,
operating
permits,
and,
if
accepting
special
waste,
supplemental
waste
stream
permits.
Except
for
the
latter
in
some
cases,
all
of these
permits
have
been
“life
of
site”
permits.
Under
this
proposal,
permits
would
be
renewable
every
five
years,
as
is
currently
the
case
for
air
and
water
permits.
In
the
usual
case,
an
owner
will
submit
an
application
to
develop
a
tract
of
land
for
landfill
use;
for
a number
of
economic
and
other
reasons,
this
proposal
fosters
subdivision
of
the
tract
into
planned
disposal
units.
That
is,
it
is
anticipated
that,
for
instance,
an
owner
would
plan
to
seek
authorization
to
develop
a
100
acre
site
by
sequentially
opening
and
closing
10
units
of
10
acres
each,
rather
than
digging
1
trench
of
100
acres.
To
avoid
controversy
as
to
what
permit(s)
are
renewable
at
the
end
of
five
years,
this
proposal
does
away
with
the
concept
of
separate
operating
permits.
The
facility
will
be
issued
one
permit,
the
development
permit,
and
authorization
to
operate
will
be
granted
by
way
of
modification
of the
facility’s
single
permit.
Regardless
of
what
year
during
a
five
year
permit
term
a
unit
is
authorized
to
begin
operations, the
time
for
permit
renewal
“relates
back”
to
the
issue
date
of
the
development
permit.
The
proposal
specifies
which
of
various
changes
which
can
occur
at.a
site
are
“significant”,
requiring
the
filing
of
an
application
for
permit
modification.
86—669
—22--
Existing
Landfills’
Design
and
Operation
As
a
practical
matter,
all
existing
facilities
cannot
be
expected
to
comply
with all
requirements applicable
to
new
facilities.
For instance,
retrofitting
of such
existing
sites
with
leachate
collection
systems
of
the
design
required
for
new
facilities
is clearly
impractical;
performance
of the
detailed
hydrogeological
site
investigation
may
also
be
impractical.
The
proposal
therefore
sets
intermediate
standards
against
which the
facility
must
assess
its
operations
to
determine
when
it must
begin closure.
Units
which
have
not
accepted
waste
prior
to the effective
date
of these
regulations
are
required
to
meet
all standards
for
new
facilities.
The
primary
yardstick
for
gauging
performance
is the
“no
increase
in background
concentration”
groundwater
standard.
Existing
units
which meet
the
standard,
are
equipped
with
some
type
of
leachate
collection
system
and
upgrade
their
financial
assurance
instruments
are
exempt
from
certain
location
and site
analysis
and
investigation
requirements;
these may
remain
open
for
a
period
greater
than
seven years.
Existing
units
which
cannot
meet
the
no—increase
standard,
but
which
can
meet
the drinking
water
standards
at a point
measured
at
the edge
of
the
unit
rather
than
at
the zone
of
attenuation,
may
remain
open for
up to
seven
years with
the
same
exemptions
and
upgrading
requirements
as for
facilities
above.
Facilities
which cannot
meet
either
of these
sets
of
requirements
must
initiate
closure
within
two
years.
Re—Permitting
of
Existing
Landfills
The
proposal
requires
existing
facilities
which
do not
intend
to close
within
two years
to
apply
for modification
of
their
existing
permits
no
later
than
48
months
after
the
effective
date
of the
rules,
or
one
year
after
the Agency
“calls
in”
the permit
for
review,
whichever
first
occurs.
Facilities
which
timely
file
applications
for
modification
may continue
to
operate
pursuant
to
the terms
of their
original
permit
pending
Agency
decision
on the
application
and
any subsequent
appeals
of
that
decision.
Reporting
Requirements
For
Non—Permitted
Landfills
Non—permitted
landfills
are
required
to
file
three
types
of
reports.
The
facility’s
initial
report,
to
be
filed
within
two
years,
must
contain
much
of
the
same
information
as
required
in
a
permit
application.
Annual
reports
must
be
filed containing
a
summary
of the
year’s
waste
disposal
activities,
modifications
made
to
the facility,
results
of
monitoring
data
concerning
86—
670
—23--
leachate,
gas
and
groundwater,
and
projected
activities
for
the
coming
year.
Quarterly
ground
water
modeling
reports
are
also
required.
Information
developed
pursuant
to
the
rules,
including
that
not
yet
submitted
to
the
Agency,
must
be
retained
on
site
for
Agency
inspection.
OVERVIEW:
THE
WASTE
DISPOSAL
SYSTEM
IN
ILLINOIS
Deliberations
in
this
docket
have
been
more
than
usually
complex
and
problematic
due
to
the
large
number
of
sources
potentially
regulated
and
the
lack
of
data
concerning
many
of
these
sources;
the
complexity
of
the
technical
issues
in
the
area
of
waste
disposal,
which
concern
effects
on
the
quality
of
air,
land,
surface
waters
and
ground
waters;
and
the
legislative
and
regulatory
initiatives
and
constraints
which
may
direct
as
well
as
circumscribe
the
Board’s
actions
in
this
area.
Some
prefatory
discussion
of
these
subjects
is
a
necessary
aid
to
understanding
the
Board’s
decision
to
proceed
with
regulations
at
this
time
and
the
form
these
regulations
take.
The
Statutory
Framework
Over
the
past
two
decades,
the
legislative
policy
at
both
the
state
and
federal
levels
has
been
to
impose
increasingly
more
stringent
controls
on
the
disposal
of
waste.
In
its
creation
of
the
modern
day
Illinois
environmental
system
through
adoption
of
the
Illinois
Environmental
Protection
Act
(Act),
Ill.
Rev.
Stat.
ch.
111
1/2,
par.
1001
et
seq.,
the
General
Assembly
specifically
noted
in
Section
20
that:
“economic
and
population
growth
and
new
methods
of
manufacture,
packaging
and
marketing,
without
the
parallel
growth
of
facilities
enabling
and
ensuring
the
re
cycling,
re—use
and
conservation
of
natural
resources
and
solid
waste,
have
resulted
in
a
rising
tide
of
scrap
and
waste
materials
of
all
kinds;
that
excessive
quantities
of
refuse
and
inefficient
and
improper
methods
of
refuse
disposal
result
in
scenic
blight,
cause
serious
hazards
to
public
health
and
safety,
create
public
nuisances,
divert
land
from
more
productive
uses,
depress
the
value
of
nearby
property,
offend
the
senses,
and
otherwise
interfere
with
community
life
and
development;
that
the
failure
to
salvage
and
reuse
scrap
and
refuse
results
in
the
waste
and
depletion
of
our
natural
resources
and
contributes
to
the
degradation
of
our
environment”.
86—67
1
—24—
As
part
of
its
intended
purpose
in
1970
of “upgrading
waste
collection
and
disposal
practices”,
in
Section
21
the
General
Assembly
banned
the
disposal
of
waste
in
sites
which
failed
to
meet
the
requirements
of
the
Act,
and
required
a
permit
for
waste
disposal
operations
with
one
significant
exception:
what
is
commonly
referred
to
as
the
Section
21(d)
on—site
exemption.
As
it
currently
exists,
the
exemption
provides
that:
“no
permit
shall
be
required
for
any
person
conducting
a
waste—storage,
waste—treatment,
or
waste—disposal
operation
for
wastes
generated
by
such
person’s
own
activities
which
are
stored,
treated,
or
disposed
within
the
site
where
such
wastes
are
generated”
The
Section
21(d)
on—site
exemption
does
not
apply
to hazardous
waste.
(This
exemption
will
be
further
addressed
in
later
portions
of
this
Opinion).
The
Board’s
existing
non—hazardous
waste
regulations
were,
when
adopted
in
1973,
“state
of
the
art”
regulations
proposed
by
the
Agency
and
designed
to
foster
abandonment
of
waste
disposal
in
“town
dumps”
in
favor
of
disposal
in
modern,
permitted
“sanitary
landfills.”
Examination
of
the
regulations
makes
clear
that
the
primary
operational
concerns
were
that
wastes
be
adequately
covered
and
litter
collected.
While
the
rules
contain
general
prohibitions
against
air
pollution
and
water
pollution,
as
the
STS
Background
Report
notes
at
p.
2
“they
barely
recognize
the
problems
of
landfill
gas
monitoring
and
collection,
groundwater
monitoring
and
liners
and
leachate
collection
systems.”
The
regulations
do
not
contain
specific
standards
for
facilities
other
than
“sanitary
landfills”,
and
none
have
been
proposed
to
the
Board
since
adoption
of Part
807.
In
1974,
USEPA
adopted
guidelines
for
the
thermal
processing
of
solid
wastes,
and
for
the
land
disposal
of
solid
wastes
(40
CFR
Part
243).
These
guidelines
are,
viewed
today,
no
more
sophisticated
than
the
Board’s
Part
807.
Congress’
adoption
in
1976
of
the
Resource
Reclamation
and
Recovery
Act
has
had
a
profound
impact
on
the path
that
the
state’s
regulatory
program
for
solid
waste
management has
taken.
While
Subtitle
D
of RCRA
addresses
disposal
of
non—
hazardous
solid
waste,
until
recently
Subtitle
D—related
activities
took
a
back
seat
to
activities
relative
to
the
Subtitle
C
hazardous waste
program.
The
Code
of
Federal
Regulations
contains
only
one
nine—page
Part,
Part
257 adopted
in
1979,
containing
criteria
for
non—hazardous
solid
waste
disposal
facilities
and
practices
pursuant
to
Subtitle
D
of
RCRA.
By
contrast,
since
1980
Subtitle
C
regulatory
activities
have
generated
over
40
new
parts
to
the
Code
of
Federal
Regulations
totalling
some
500
pages.
86—672
—25—
In
1981,
in
adopting
P.A.
82—380,
the
General
Assembly
amended
Section
20
of
the
Act
to
direct
the
Board
and
the
Agency
to
take
all
steps
necessary
to
secure
federal
approval
of
an
Illinois
hazardous
waste
managemeit
program
pursuant
to
Subtitle
C
of
RCRA
and
resulting
funding
of
such
program.
The
Board
and
the
Agency
have
done
so,
and
have
secured
the
necessary
federal
approval.
However,
one
of
the
inevitable
results
of
receipt
of
such
funding
is
that
the
state’s
regulatory
program
and
priorities
are
driven
by
those
of
its
federal
paymaster.
As
aforementioned,
while
the
Agency
has
made
abortive
attempts
to
develop
and
present
non—hazardous
waste
regulations
for
the
Board’s
consideration,
these
attempts
have
been
abandoned
in
favor
of
meeting
federal
requirements
of
the
Subtitle
C
program.
The
Board,
however,
which
has
not
heretofore
been
dependent
on
federal
funding,
has
devoted
considerable
resources
to
development
of
a
modern
non—hazardous
waste
program
while
at
the
same
time
fulfilling
its
obligations
under
the
Subtitle
D
program.
The
Board’s
efforts
have
been
particularly
aided
by
its
receipt
of
the
general
revenue
funding
which
created
the
Board’s
Scientific/Technical
Section,
which
become
operational
in
early
1985.
The
lack
of
modern
regulations
for
the
disposal
of
non—
hazardous
waste
has
prompted
both
Congress
and
the
General
Assembly
to
mandate
focus
on
this
area
by
regulatory
authorities.
The
1984
Hazardous
and
Solid
Waste
Amendments
(HSWA)
to
RCRA
require
USEPA
to
study
the
adequacy
of
the
Subtitle
D
criteria
and
its
efficacy
in
protecting
groundwater
and
to
recommend
whether
additional
authorities
are
needed
to
enforce
them.
USEPA
was
directed
to
promulgate
revisions
to
the
Subtitle
D
criteria
by
March,
1988.
While
the
record
in
R84—17
is
replete
with
references
to
federal
activity
concerning
Subtitle
D
regulations,
most
of
this
information
is
anecdotal.
USEPA
has
not
formally
published
draft
regulations
in
the
Federal
Register,
and
has
not,
to
the
Board’s
knowledge,
formally
announced
a
schedule
for
promulgation
of
Subtitle
D
rules.
The
General
Assembly,
for
its
part,
has
passed
several
bills
directing
regulatory
and
other
activity
by
state
agencies
in
the
solid
waste
area.
Section
21.1
of
the
Act,
adopted
in
P.A.
83—
775,
prohibited
operation
of
permitted
waste
disposal
sites
after
March
1,
1985
unless
the
site
possessed
a
performance
bond
or
other
security
for
the
purpose
of
insuring
closure
and
post—
closure
care
in
accordance
with
the
Act
and
Board
rules;
the
Board’s
implementing
regulations
are
codified
at
35
Ill.
Adm.
Code
807.501
et
seq.
The
Illinois
Solid
Waste
Management
Act,
enacted
by
P.A.
84—1319,
effective
September
4,
1986
and
codified
86—673
—26—
at
Ill.
Rev.
Stat.
ch.
ill
1/2,
par.
7051
et
seq.
establishes
as
state
policy
reduction
of
reliance
on land
disposal
of solid
waste
in
favor
of
(in
descending
order
of
preference) volume
reduction,
recycling
and
reuse,
combustion
with
energy
recovery,
combustion
for
volume
reduction,
with
landfill
being
the
last
preference.
While
no
regulatory
activity
is
mandated
by
this
legislation,
the
Agency
is
directed
to
annually
publish
a
report
on
projected
landfill
disposal
capacity.
DENR
is
directed
to
engage
in
various
activities
to
assist
in
initiation
of
a
comprehensive
statewide
approach to address
local
and
regional
solid
waste
management
needs;
some
of
these
activities
are
issuance
of various
grants,
provision
of
siting
and
technical
assistance
for
solid
waste
management
facilities,
and
coordination
of
solid
waste
research
by
the
University
of
Illinois.
Finally,
and
perhaps
most
importantly,
in
the
last
legislative
session
the
General
Assembly
has
enacted
legislation
which
sets
in
motion
a
massive
effort
by
numerous
state
agencies
and
local
governments
for
study,
classification,
categorization
and
protection
of
the
state’s
groundwater
resources.
This
is
the
Illinois
Groundwater
Protection
Act,
P.A.
85—863,
effective
September
24,
1987,
which
is
codified
at
Ill.
Rev.
Stat.,
ch.
111
1/2,
par.
7451
et
seq.
and
which
also
adds
several
new
sections
to
the
Act.
In
the
regulatory
arena,
the Agency
is
directed
to
propose,
and
the
Board
to
adopt,
regulations
in
the
following
areas:
A.
Comprehensive
Ground
Water
Quality
Standards
These
regulations
are
to
be
proposed
by
the
Agency
by July
1, 1989
and
adopted
by the
Board
within
two
years
of
proposal.
Section
8
of
the
Groundwater
Protection
Act,
codified
at
Ill.
Rev.
Stat.,
ch.
111
1/2,
par.
7458,
provides
in
pertinent
part
that:
(a)
In preparing
such
regulations,
the
Agency
shall
address,
to
the
extent
feasible,
those
contaminants
which
have
been
found
in
the
groundwaters
of
the
State
and
which
are
known
to
cause,
or suspected
of
causing,
cancer,
birth
defects,
or any
other
adverse
effect
on
human
health
according
to
nationally
accepted
guidelines.
(b)
In
promulgating
these
regulations,
the
Board
shall,
consider
the
following:
(1)
recognition
that
groundwaters
differ
in
many
important
respects
from
86— 674
—27—
surface
waters,
including
water
quality,
rate
of
movement,
direction
of
flow,
accessibility,
susceptibility
of
pollution,
and
use;
(2)
classification
of
groundwaters
on
an
appropriate
basis,
such
as
their
utility
as
a
resource
or
susceptability
to
contamination;
(3) preference
for
numerical
water
quality
standards,
where
possible,
over
narrative
standards,
especially
where
specific
contaminants
have
been
commonly
detected
in
groundwaters
or
where
federal
drinking
water levels
or
advisories
are
available;
(4)
application
of
non—degradation
provisions
for
appropriate
groundwaters,
including
notification
limitations
to
trigger
preventive
response
activities;
(5)
relevant
experiences
from
other
states
where
groundwater
protection
programs
have
been
implemented;
and
(6)
existing
methods
of detecting
and
quantifying
contaminants
with
reasonable
analytical
certainty.
B.
Maximum
setback
zones
for
community
water
supply
wells
Section
14.2
(Ill.
Rev.
Stat.
ch.
ill
1/2,
par.
1014.2)
of
the
Act
provides
for a
minimum
200 foot
setback
from
existing
drinking
water
wells.
Section
14.3
provides
a
mechanism
whereby
a
community
water
supply
well
may
request
that
the
Agency
petition
the Board
for
establishment
of
a
maximum
setback
where
“the
outermost
boundary
of the
lateral
area
of
influence
of the
well
under
normal
operational
conditions
exceeds
the
radius
of
the
minimum
setback
zone”.
Such Agency
petitions
may be
filed
after
July
1,
1989.
C.
Standards
for
Various
Waste
Management
Facilities
Section
14.4 of
the
Act
provides
that
the
Agency
is
to
propose
regulations
no later
than
January
1,
1989,
and
that
the
Board
is
to
promulgate
regulations
governing
existing
facilities
within
two
years
of
the
proposal’s
submittal.
Section
14.4(a)
86—675
—28—
and
(b)
provide
in
pertinent
part:
Section
14.4:
(a)
No
later
than
January
1,
1989,
the
Agency
shall
propose
regulations
to
the
Board
prescribing
standards
andreguirements
for
the
following
activities:
(1)
landfilling,
land
treating,
surface
impounding
or
piling
of
special
waste
and
other
wastes
which
could
cause
contamination
of groundwater
and
which
are generated
on the
site,
other
than
hazardous,
livestock
and
landscape
waste,
and
construction
and
demolition
debris;
(2)
storage
of
special
waste
in
an
underground
storage
tank
for
which
federal
regulatory
requirements
for
the
protection
of
groundwater
are
not
applicable;
(3)
storage
and
related
handling
of
pesticides
and
fertilizers
at
a
facility
for
the
purpose
of
commercial
application;
(4)
storage
and
related
handling
of road
oils
and
de—icing
agents
at
a
central
location;
and
(5)
storage
and
related
handling
of
pesticides
and
fertilizers
at
a
central
location
for
the purpose
of
distribution
to
retail
sales
outlet
s.
In preparing
such
regulation,
the
Agency
shall
provide
as
it
deems
necessary
for
more
stringent
provisions
for
those
activities
enumerated
in
this
subsection
which
are
not
already
in
existence.
Any
activity
for
which
such
standards
and
requirements
are
proposed
may
be
referred
to
as
a
new
activity.
(b)
Within
2
years
after
the
date
upon
which
the
Agency
files
the
proposed
regulations
pursuant
to
subsection
(a)
of
this
Section,
the
Board
shall
promulgate
86—676
—29—
appropriate
regulations
for
existing
activities.
In
promulgating
these
regulations,
the
Board
shall
consider
the
following:
(1)
appropriate
programs
for
water
quality
monitoring;
(2)
reporting,
recordkeeping
and
remedial
response
measures;
(3)
appropriate
technology—based
measures
for
pollution
control;
and
(4)
requirements
for
closure
or
discontinuance
of
operations.
Such
regulations
as
are
promulgated
pursuant
to
this
subsection
shall
be
for
the
express
purpose
of
protecting
groundwaters.
The
applicability
of
such
regulations
shall
be
limited
to any
existing
activity
which
is
located:
(a)
within
a
setback
zone
regulated
by
this
Act,
other
than
an
activity
located
on
the
same
site
as
a
non—community
water
system
well
and
for
which
the
owner
is
the
same
for
both
the
activity
and
the
well;
or
(b)
within
a
regulated
recharge
area
as
delineated
by Board
regulation,
provided
that:
(i)
the
boundary
of
the
lateral
area
of
influence
of
a
community
water
supply
well
located
within
the
recharge
area
includes
such
activity
therein;
(ii)
the
distance
from
the
wellhead
of
the
community
water
supply
to
the
activity
does
not
exceed
2500
feet;
and
(iii)
the
community
water
supply
well
was
in existence
prior
to
January
1,
1988.
In
addition,
the
Board
shall
ensure
that
the
promulgated
regulations
are
consistent
with
86—677
—30—
and
not
pre—emptive
of
the
certification
system
provided
by Section
14.5.
The certification
system
of
Section
14.5
allows
the Agency
to
certify
that sites
“represent
a minimal
hazard
with
respect
to
contamination of
groundwaters
by
potential
primary
or potential
secondary
sources
“as
defined
in
Sections
3.59
and
3.60
of
the
Act.
Such
certification
is to
be based
on the
type
of activities
which
have
or
will
take
place
at
the
site.
A certified
site
is
exempt
from
regulations
adopted
pursuant
to
Sections
14.2
and
14.4.
D.
Additional
Regulations
For
New Disposal
Activities
Section
14.4(c)
of the
Act
provides:
(c)
Concurrently
with
the
action
mandated
by
subsection
(a),
[set
forth
above]
the
Agency
shall evaluate,
with
respect
to
the
protection
of
groundwater,
the
adequacy
of existing
federal
and
State
regulations
regarding
the
disposal
of
hazardous
waste
and
the
off—site
disposal
of special
and
municipal
wastes.
The
Agency
shall
then
propose,
as
it deems
necessary,
additional
regulations
for
such
new
disposal
activities
as
may
be
necessary
to
achieve
a
level
of
groundwater
protection
that
is
consistent
with
the
regulations
proposed
under
subsection
(a)
of this
Section.
(d)
Following
receipt
of
proposed
regulations
submitted
by the
Agency
pursuant
to
subsection
(a)
of
this Section,
the
Board
shall
promulgate
appropriate
regulations
for new
activities.
In
promulgating
these
regulations,
the Board
shall,
in
addition
to
the
factors
set
forth in
Title
VII
of this
Act,
consider
the
following:
(1)
appropriate
programs
for
water
quality
monitoring,
including,
where
appropriate,
notification
limitations
to trigger
preventive
response
activities;
(2)
design
practices
and
technology—
based
measures
appropriate
for
minimizing
the
potential
for
groundwater
contamination;
86—678
—31—
(3)
reporting,
recordkeeping
and
remedial
response
measures;
and
(4)
requirements
for
closure
or
discontinuance
of
operations.
Such
regulations
as
are
promulgated
pursuant
to
this
subsection
shall
be
for
the
express
purpose
of
protecting
groundwaters.
The
applicability
of
such
regulations
shall
be
limited
to
any
new
activity
which
is
to
be
located
within
a
setback
zone
regulated
by
this
Act,
or
which
is
to
be
located
within
a
regulated
recharge
area
as
delineated
by
Board
regulation.
In
addition,
the
Board
shall
ensure
that
the
promulgated
regulations
are
consistent
with
and
not
pre—emptive
of
the
certification
system
provided
by
Section
14.5.
E.
Boundaries
of
Regulated
Recharge
Areas
In
distinction
to
most
areas
to
be
regulated
pursuant
to
the
Groundwater
Protection
Act,
there
is
no
timetable
set
for
determinations
concerning
boundaries
of
regulated
recharge
areas
pursuant
to
Sections
17.3
and
17.4.
These
sections
provide
in
pertinent
part
that:
Section
17.3
(a)
The
Agency
may
propose
to
the
Board
a
regulation
establishing
the
boundary
for
a
regulated
recharge
area
if
any
of
the
following
conditions
exist:
(1)
the
Agency
has
previously
issued
one
or
more
[groundwater
contamination
hazard]
advisories
within
the
area
[as
provided
in
Section
17.1(g)];
(2)
the
Agency
determines
that
a
completed
groundwater
protection
needs
assessment
[developed
pursuant
to
Section
17.11
demonstrates
a
need
for
regional
protection;
or
(3)
mapping
completed
by
the
Department
of
Energy
and
Natural
Resources
[DENR]
identifies
a
recharge
area
for
which
protection
is
warranted.
(b)
The
Agency
shall
propose
to
the
Board,
pursuant
to
Section
28,
a
regulation
86—679
—32—
establishing
the
boundary
for
a regulated
recharge
area
if
a regional
planning
committee
[establishing
pursuant
to
Section
17.2]
files
a
petition
requesting
and
justifying
such
action,
unless
the
Agency
[makes
certain
determinations]
Section
17.4
(a)
In promulgating
a
regulation
to establish
the
boundary
for
a regulated
recharge
area,
the
Board shall
... consider
the
following:
(1) the
adequacy
of
protection
afforded
to
potable
resources
groundwater
by
any
applicable
setback
zones;
(2)
applicability
of
the standards
and
requirements
promulgated
pursuant
to
Section
14.4;
(3)
refinements
in
the
groundwater
quality
standards
which
may
be
appropriate
for
the delineated
area;
(4)
the
extent
to
which
the
delineated
area
may serve
as
a sole
source
of
supply
for
public
water
supplies.
(b) The
Board
may
only
promulgate
a
regulation
which
establishes
the boundary
for
a regulated
recharge
area
if
the
Board
makes
a
determination
that
the
boundary
of
the
delineated
area
is
drawn
so
that
the
natural
geological
or
geographic
features
contained
therein
are
shown
to
be
highly
susceptible
to
contamination
over a
predominant
portion
of
the
recharge
area.
(c)
Nothing
in
this
Section
shall
be
construed
as
limiting
the
general
authority
of
the
Board
to promulgate
regulations
pursuant
to Title
VII of
this
Act.
The Decision
To
Adopt
A First
Notice
Regulatory
Proposal
At
This
Time
As the
foregoing
discussion
demonstrates,
after
years
of
inactivity,
solid
waste regulation
has
risen
to
the
top
of both
86—680
—33—
the
state and
federal
regulatory
agenda.
During
the
course
of
hearings
in
this
matter,
and
in closing
comments,
the
Board
has
been
requested
to
defer
adoption
of its own
proposal
for
publication
in
the
Illinois
Register
until
after
various
actions
are
taken by
the
legislature,
USEPA,
the
Agency
and
DENR.
The Board
does
not
believe
that
it
is
in
the
best
interests
of the
State
to delay
publication
of
the
Board’s
best
thinking
on
what
constitute
minimum
requirements
for
the
operation
of
new and
existing
landfills.
Prior
to discussing
the
specific
arguments
against
proceeding
at this
time,
the Board
will
discuss
the
two
overriding
arguments
in
favor of
expeditious
action:
the
need to
facilitate
siting
of
new and
expanded
landfills
which
are
defined
as
“new regional
pollution
control
facilities”
subject
to
the
local
government
site location
suitability
approval
process
of
Sections
39.1
and
40.1
of
the
Act,
commonly
known
as the
SB172
process,
and
the
need to
collect
data
concerning
the
operations
and
effects
of landfills
which
enjoy the
Section
21(d)
on—site
exemption
from permitting
and whose
activities
have
accordingly
been
largely
exempt
from
scrutiny.
The
Impact
of
the
SB172
Process
on
Illinois’
Landfill
Disposal
Capacity
In
its
first
report
pursuant
to
the Solid
Waste
Management
Act,
Available
Waste
Disposal
Capacity
For
Solid
Waste
In
Illinois
(R84—17D,
Exh.
31),
the
Agency
reported
that
in 1970,
there
were over
1,200
garbage
dumps
and
10 municipal
incinerators
operating
in
the
State.
In
1987,
there
are
146
permitted
sanitary
landfills
and
1
municipal
solid
waste
incinerator
in
operation.
(Id.,
p.
13, 15)
The
Agency
further
reports
that:
Of
the
State’s
102
counties,
24
have
no
landfills,
or
received
no
waste
at their
facilities.
This
means
that
these
counties
export
their
wastes
to
counties
with
available
capacity.
Only
34
of the
State’s
counties
have
the
capacity
to adequately
dispose
of
their
own
wastes;
many also
import
waste.
It
is
apparent
that
almost
half of
the
State’s
counties
must export
wastes
elsewhere,
to
counties
or other
states
with
available
capacity.
Counties
face
the
problem
of
adequate
capacity
that
is
accessible
at
a
reasonable
cost.
(Id.,
p.
18)
Based
on reports
that
the
state
disposes
of 51,906,710
cubic
yards
of waste
annually,
and
an
estimated
remaining
disposal
capacity
of
273,274,983
cubic yards,
the
Agency
calculates
that
the State,
as a
whole,
has
a
remaining
disposal
capacity
of
5.3
years.
(Id.,
p.
21) This
can be
further
broken
down
by
region,
as follows
based
on
information
and
tables
appearing
on
pp.
23—56
86—681
—34—
of
the
Agency’s Report:
PROJECTED REGIONAL LANDFILL-LIFESPANS
Counties
Remaining Years At
Number of
Region
Included
Current Disposal Volumes
Landfills
Boone
5.7
19
Bureau
Carroll
DeKalb
Jo
Davies
LaS
all
e
Lee
Ogle
Putnam
Stephenson
Whites ide
Winnebago
2
Cook
3.9
33
DuPage
Grundy
Kane
Kankakee
Kendall
Lake
Mdllenry
Will
3
Fulton
9.4
21
Hancock
Henderson
Henry
Knox
Mar shall
Mercer
McDonough
Peoria
Rock Island
Stark
Warren
Woodford
4
Champaign
8.0
24
Clark
Coles
Cr
awford
Cumberland
DeWitt
Douglas
Edgar
86—682
—35—
Counties
Remaining
Years At
Number
of
Region
Included
Current
Disposal
Volumes
Landfills
Effingham
Ford
Iroquois
Jasper
Livington
Macon
McLean
5
Adams
8.5
16
Brown
Calhoun
Cass
Christian
Greene
Jersey
Logan
Macoupin
Mason
Menard
Montgomery
Morgan
Pike
Sangamon
Schuyler
Scott
6
Bond
5.6
15
Clinton
Fayette
Madison
Marion
Monroe
Randolph
St. Clair
Washington
7
Alexander
33.0
18
Clay
Edwards
Franklin
Gallatin
Hamilton
Hardin
Jackson
Jefferson
Johnson
Lawrence
Mass a
c
Perry
86—683
—36--
Counties
Remaining Years
At
Number
of
Region
Included
Current
Disposal
Volumes
Landfills
Pope
Pulaski
Richland
Saline
Union
Wabash
Wayne
White
Williamson
Statewide
5.3
In
its
report,
the
Agency
notes
that
the
number
of
development
permits
applied
for
and
processed
annually
has
steadily
decreased
from
1981
to 1986,
with
a
slight
increase
in
1983.
Between
1981
and
1987,
the
Agency
issued
69 of
the
146
permits
applied
for:
21 permits
were
issued
in
1981,
12 in
1982,
19
in
1983,
7 in
1984,
4
in
1985,
3
in
1986,
and
3
in
1987.
Concerning
the decrease
in
the
number
of
applications,
the
Agency
speculates
that:
The
trend
toward
fewer
requests
for
development
permits
may
be
a
function
of
several
variables.
First,
the
State’s
siting
process
has
changed
significantly
since
the
passage
of
SB172
in 1981.
SB172
removed
siting
authority
from
the
IEPA
and
granted
county
boards
or municipal
governing
bodies
initial
approval
of
regional
pollution
control
facilities
(e.g.
landfills)
based
on
seven
criteria.
This
codification
of
seven
review
criteria
has
led
to
an
increase
in
the
amount
of information,
time,
money
and
scrutiny
devoted
to
siting
applications.
The
IEPA
cannot
begin
its
technical
review
of
a
development
permit
unless
siting
approval
has
been
granted.
Second,
the
closure,
post—
closure
and
financial
assurance
requirements
instituted
in
1985
increased
the
regulatory
and
financial
requirements
for
landfill
developers.
The
new
requirements
may
have
decreased
the
number
of
potential
applicants
by
eliminating
those
who
did
not
have
the
up
front
capital
to
meet
the
financial
assurance
requirement.
Third,
there
is
a
trend
toward
developing
larger,
more
regional
landfills
86—684
—37—
which
results
in
fewer
individual
applications.
(Id.,
p.
15—16).
The
Board
has
no
reason
to
doubt
the
validity
of
the Agency’s
second
and
third
speculations, and
the Board
has
the
experience
reason to
verify
the
accuracy
of its
first
speculation.
At the
outset,
the following
discussion
is
not intended
to
critize
or
“place
blame”
on
anyone.
Many
questions
and comments
in the
R84—l7
record
reflected
a concern
about
how the
Agency’s
permitting
process
under
the Board’s
proposed
regulations
and the
SB172
process
affect
each
other.
These
concerns
were
voiced
by
the
Agency,
the
waste disposal
industry,
and
the environmental
community
as a
result
of
its participation
in
SB172
proceedings. A bit
of history
might
be helpful
to
an
understanding
of
these concerns.
Since
passage
of
SBl72
in 1981,
the Board
has
received
41
appeals
of
local
sitting
decisions
(three
of which
are currently
pending).
As
the sole
state
agency
which
reviews
local
governments’
records
in their
entirety*,
the Board
is
uniquely
qualified
to
assert that
the process
is
proving
to be
a resource—
intensive
and
exhausting
experience
for
landfill
applicants,
local
government
officials,
concerned
citizens
and the
Board
alike.
A major
source
of the
local
“record
growth”
is
the evolution
of
criterion
2
of
SB172.
Criterion
2 requires
an applicant
to
prove
that
“the facility
is
so
designed,
located,
and
proposed
to
be
operated
that the
public
health,
safety
and
welfare
will
be
protected.
This
criterion
has been
interpreted
quite
literally,
to
allow, and
in
effect
to force,
local
governments
to take
on
the
role
of
making
technical
siting
decisions.
Historically,
the
disposal
of
solid
waste
has
been
a local
governmental
function.
Passage
of
the
Act in
1970
provided
for
state
involvement
in
the
solid
waste
disposal
process
by
requiring
issuance
of
landfill
permits
by the
Agency.
In 1972,
the
Illinois
Supreme
Court
held
that
Winnebago
County
could
not
use
a zoning
ordinance
to prohibit
development
of a
landfill
if
a
permit
was
obtained
from
the
Agency.
O’Connor
v.
City
of
Rockford,
52 Ill.
2d
360,
288
N.E.2d
432
(1972).
*
Contrary
to
the
belief
of
many,
the
Agency
is
not required
or
usually
requested
to review
the
local
SB172
record,
although
it
must
receive
proof
of
local approval
prior
to issuance
of any
permit.
Moreover,
Agency
personnel
have
testified
in this
record
that
if
the
Agency
receives
any
excerpts
of transcripts,
that
they
are
usually
submitted
by
landfill
opponents.
(R84—17D,
R.
1451—1452).
86—685
—38—
In
1976,
the
Court
held
that
a
non—home
rule
municipality
could
not
use
a
local
“environmental
protection
ordinance”,
which
includes
the
requirement
of
compliance
with
zoning
ordinances,
to
regulate
the
siting
and
operation
of
landfills.
Carison
v.
Village
of
Worth,
62
Ill.
2d
406,
343
N.E.2d
493
(1976).
Thus,
local
non—home
rule
governments
were
pre—empted
from
any
participation
in
the
landfill
sitting
process.
This
pre—emption
of
local
authority
generated
much
protest.
In
response
to
the
public
outcry
over
this
issue,
the
Illinois
General
Assembly
enacted
Senate
Bill
172.
This
bill
created
Section
39.2
of
the
Act,
which
allows
local
units
of
government
to
review
the
site
suitability
of
a
new
“regional
pollution
control
facility”
based
on
only
those
criteria
set
forth
in
that
section.
The
courts
have
held
that
local
governments
may
consider
technical
aspects
of
landfill
design
when
considering
Criterion
#2
two.
See,
e.g.,
Waste
Management
of
Illinois,
Inc.
v.
Pollution
Control
Board,
No.
87—0029
(2d
Dist.,
September
11,
1987);
McHenry
County
Landfill,
Inc.
v.
Illinois
Environmental
Protection
Agency,
154
Ill.
App.
3d
89,
506
N.E.2d
372
(2d
Dist..
1987).
This
has
resulted
in
each
locality
applying
engineering
and
technical
information
in
its
own
way.
The
Agency
is
not
required
by
statute
to
participate
in
the
SB172
hearing
process,
and
does
not
do
so
for
a
variety
of
reasons,
not
the
least
of
which
is
that
these
proceedings
are
very
resource
intensive.
(See,
e.g.
R84—l7D,
R.
1775—1778)
Additionally,
the
Agency
successfully
argued
and
won
a
case
very
early
on
in
the
life
of
SB172
which
establishes
that
under
existing
law
the
Agency
cannot
be
required
to
include
in
its
permits,
or
to
enforce,
conditions
which
local
governments
impose
as
conditions
on
SB172
approvals.
Browning—Ferris
Industries,
Inc.
v.
County
of
Lake,
120
Ill.
App.
3d
89,
457
N.E.
2d
1309
(2nd
Dist.
1983).
As
the
system
currently
works,
then,
the
local
siting
process
precedes
the
Agency
permitting
process,
and
both
make
determinations
about
landfill
design
and
operation
in
isolation
from
each
other;
the
Agency
does
not
make
necessarily
any
determination
at
all
unless
the
local
government
first
approves.
(See,
e.g.,R.
2322—2334).
One
result
has
been
that
the
public
focus
on
design
and
operation
matters
has
shifted
almost
completely
from
the
AGency
to
the
local
siting
hearings,
hearings
that
are
required
under
SB172.
The
Act
contains
no
explicit
Agency
public
participation
requirements
analogous
to
those
either
in
SB172,
or
for
those
existing
for
permits
to
be
issued
pursuant
to
the
Clean
Air
Act,
Clean
Water
Act,
or
RCRA;
these
require
the
Agency
to
respond
to
public
comment
and
hold
a
hearing
on
request.
While
the
Act
does
$
6—686
—39--
not
limit
the
Agency’s
authority
to
provide
for
public
participation,
this
record
indicates
that
practical
realities
of
resource
allocation
can
and
do.
The
Agency
has
stated
that,
as
a
matter
of
practicality,
where
SB172
hearings
have
been
held,
“it
doesn’t
seem
to
make
sense
to
reinstitute
another
public
participation
process”.
(R84—17D,
R.
2426).
The
Agency’s
decision
making
process
is
now
less
likely
than
before
to
involve
the
public.
It
has
been
strongly
suggested
to
the
Board
that
it
can
take
two
actions
which
will
improve
the
existing
landfill
siting
and
permitting
processes:
adoption
of
modern
technical
landfill
standards,
which
the
Board
is
now
proposing,
and
establishment
of
a
public
participation
process.
As
stated
in
testimony
on
behalf
of
Citizens
For
A
Better
Environment:
Given
the
active
interest
of
citizens
in
many
siting
cases,
we
believe
it
would
be
a
mistake
for
the
Board
not
to
adopt
specific
procedures
allowing
citizens
to
participate
in
the
Agency’s
permitting
process.
We
expect
that
participation
in
this
process
will
increase
after
the
Board
updates
its
solid
waste
regulations.
This
is
because
some
of
the
technical
issues
that
are
now
the
subject
of
many
siting
hearings
will
be
clarified
under
state
regulations.
As
a
result,
citizens
will
shift
some
of
their
attention
to
the
permitting
process
to
ensure
that
the
Board
regulations
are
fully
implemented.
We
believe
public
participation
procedures
should
be
required
for
permit
applications,
and
permit
renewals.
While
the
Agency
might
balk
at
applying
these
provisions
to
significant
modifications,
we
believe
that
there
are
long
term
benefits
to
updating
the
public
about
operating
changes
that
might
be
occurring
at
a
nearby
landfill.
Any
modifi—
cation,
assuming
it
is
appropriate,
would
more
likely
be
accepted
by
local
citizens
if
they
are
notified
in
advance
and
given
the
opportunity
to
ask
clarifying
questions
or
express
concerns.
If
citizens
find
out
about
the
change
after
it
occurs,
it
will
only
cause
more
distrust
of
state’s
environmental
system
at
the
local
level.
While
the
Agency
may
have
to
expend
additional
resources
in
explaining
its
activities,*
we
believe
it
will
benefit
in
the
long
run
as
citizens
become
more
familiar
with
the
state’s
updated
solid
waste
36—637
—40—
regulations.
(R84—l7D,
Exh.
41
and
generally
R.
2347—2352)
The
Board
can
proceed
with
only
one
component
of
this
suggestion:
adoption
of
technical
standards.
Adoption
of
the
suggested
procedural
requirement
would
be
beyond
the
Board’s
statutory
authority,
as
the
Act
has
been
interpreted
by
the
courts.
In
Village
of
Hillside
v.
John
Sexton
Sand
and
Gravel
Corp.,
434
N.E.
2d
382
105
Ill.
App.
3d
533
(1stDist.
1982),
one
of
the
issues
considered
by
the
Appellate
Court
was
the
validity
of
Board
regulations
which
required
the
Agency
to
adopt
procedures
for
the
transfer
of
landfill
permits
from
one
owner
to
another,
and
established
public
notification
requirements
to
be
followed
by
the
Agency
in
adopting
such
procedures.
Citing
the
Illinois
Supreme
Court’s
holding
in
Landfill,
Inc.
v.
Pollution
Control
Board,
387
N.E.
2d
258,
264,
74
Ill.
2d
541,
577
(1978)
which
invalidatedrules
which
purported
to
establish
rights
to
third
party
appeals
of
landfill
permits,
the
Appellate
Court
found
the
Board’s
rules
to
be
invalid.
After
examining
the
various
duties
and
authorities
allocated
by
the
Act
to
the
Board
and
the
Agency,
the
court
concluded:
We
think
it
clear,
in
light
of
the
statutory
scheme
and
case
law,
that
the
Act
requires
the
Board
to
adopt
rules
requiring
permits
and
to
set
substantive
standards
under
which
the
Agency
may
issue
such
permits.
The
purpose
of
the
Agency,
on
the
other
hand,
is
to
establish
procedures
for
the
administration
of
the
permit
system
in
order
to
insure
that
those
standards
are
met.
Thus,
the
Agency
is
authorized
to
determine
if
a
permit
should
issue
or
be
transferred
for
a
particular
*
At
hearing,
the
Agency
provided
testimony
that,
based
on
its
experience
with
RCRA
public
participation
procedures,
its
preliminary
estimates
are
that
such
a
program
for
non—hazardous
facilities
would
require
significant
expenditures
of
monetary
and
personnel
resources.
(R84—17D,
R.
2427—2432).
The
Agency
did
not
calculate
the
one
time
costs
for
re—permitting
the
146
existing
facilities.
Based
on
the
projected
submission
of
15—20
new
landfill
permit
applications
per
year,
the
Agency
predicts
that
some
4
1/2
to
5
work
years
would
be
required
to
comply
with
proposed
paperwork
requirements
for
Agency
preparation
of
summaries
of
permit
applications
and
its
proposed
permitting
actions,
and
responses
to
comments
received.
The
Agency
did
not
calculate
the
resources
necessary
to
conduct
transcribed
hearings,
but
did
note
that
newspaper
costs
of
notice
publica
tions
would
average
some
$250
per
required
notice.
86—688
—41—
refuse—disposal
facility
and
to
adopt
appropriate
procedures.
The
Board
may
not
require
the
Agency
to
adopt
procedures
or
impose
procedures
on
it
for
issuing
or
transferring
permits.
434
N.E.
2d
at
388.
Based
on
Hillside,
then,
it
is
clear
that
any
mandate
for
inclusion
of
a
public
participation
component
in
the
Agency
permitting
process
can
issue
only
from
the
General
Assembly,
and
not
from
the
Board.
The
Section
21(d)
Permit
Exemption
As
earlier
noted,
an
exemption
to
the
permit
requirements
of
Section
21(d)
has
been
contained
in
the
Act
since
1970.
While
in
its
original
form
the
exemption
was
for
“refuse
generated
by
the
operators
own
activities”
except
for
hazardous
waste,
since
1981
the
exception
has
been
limited
to
wastes
generated
by
the
operators
own
activities
which
are
stored,
treated,
disposed
or
transported
within
the
site
where
such
wastes
are
generated.
Since
its
inception,
the
exemption
has
been
troublesome
to
the
Board
and
the
Agency;
while
the
exemption
serves
to
reduce
paperwork
requirements
on
generators,
the
exemption
is
a
blanket
one
which
does
not
by
its
terms
require
consideration
of
the
suitability
of
the
site
for
disposal
of
the
type
of
wastes
there
generated.
Beginning
in
1975,
the
Board
began
construing
the
exemption
as
applicable
to
“minor
amounts
of
refuse
which
could
be
disposed
of
without
environmental
harm
on
the
site
where
it
was
generated”,
a
position
which
has
been
consistently
sustained
by
the
courts,
despite
the
“plain
language”
of
Section
21.
See
Pielet
Bros.
Trading,
Inc.
v.
Pollution
Control
Board,
442
N.E.
2d
1374,
1377—1378,
110
Ill.
App.
3d
752
(5th
Dist.
1982)
which
traces
the
legislative
history
of
the
exemption
and
case
law
at
the
Board
and
appellate
court
levels.
While
on—site
disposal
facilities
can
be
permitted,
then,
consistent
with
existing
law
when
problems
are
identified
by
citizens
or
the
state,
there
exists
a
larger
problem:
lack
of
the
sort
of
data
concerning
such
sites
which
is
ordinarily
generated
pursuant
to
conditions
contained
in
permits.
As
WMI
has
aptly
noted
in
its
December
30,
1987
comment:
There
is
great
pressure
today
for
adoption
of
an
Illinois
version
of
New
Jersey’s
ECR.k,
the
statute
which
requires
environmental
cleanup
upon
sale
of
an
industrial
property.
As
any
one
involved
in
the
environmental,
corporate
acquisition
or
real
estate
fields
knows,
how
ever,
very
few
properties
of
any
significance
aresold
or
financed
today
without
some
kind
86—689
—42—
of
environmental
review
or
investigation,
and
frequently
a private
agreement
for environ
mental
cleanup.
In
other
words,
if
the
infor
mation
as
to
environmental
problems
is
avail
able,
the
marketplace
will
often
force
cleanups
as
a condition
of sale
or financing.
The
big
problem,
however,
is
the
lack
of
information.
A purchaser
or lender
reviewing
a property
is handicapped
by the
lack
of
very
simple
information,
where
are your
refuse
disposal
areas,
where
are
your
tests
showing
what
went
into
the
fill,
what
are your
monitoring
results?
As
the
Agency
commented
at
hearing
in
Docket
D,
it
receives
frequent
enquiries
in
connection
with
purchases
of
properties
which
it
is
not
able
to
answer
because
of
the
lack of
on—site
reporting.
The
public
expects
the
Agency
to
have
this
kind
of
information
and
is frustrated
to
find
it isn’t
available.*/
[R84—17D],
R.
2312—13,
2315—16,
23l8_19.*/
This
lack
of
on—site
data
has
recently
been
the
subject
of
significant
public
attention.
See,
e.g., the
report
of
the
Joint Committee
on Hazardous
Waste
in the
Lake
Calumet
Area.
P.C.
51 at
p.
21—22
(footnote
in original)
As
a
first step
to remedying
this
lack
of data,
in this
R88—
7
proposal
the
Board
has
chosen
to
include
a
reporting
requirement
for all
landfills
exempt
from
permit
requirements.
As
the Act
does
not by
its terms
preclude
the
Board
from
requiring
such
facilities
to
file reports,
it
is
the
Board’s
belief that
it
can lawfully
adopt
such
rules.
However,
the Board
is aware
that there
may
well
be
legal
arguments
to be made
that
the Board
is
acting
beyond
the
scope
of
its
statutory
authority
by attempting
to
do
indirectly
what
it
cannot
do
directly,
i.e.,
to
require
in
the
name
of
“reporting”
data
which
otherwise
could
be required
only
in
the context
of
“permitting”.
While
such
arguments
have
been
raised
in
summary
fashion
in
this record,
they
have not
been
articulated
in
detail
or
fully
briefed.
As it
will
do concerning
other specific
points
in this
proposal,
the
Board
specifically
solicits
comments
concerning this
issue.
As
a
second
step to
remedying
this
lack
of data,
the Board
has today
in
a
companion
order
opened
another
docket,
R88—8,
Census
of Solid
Waste
Management
Facilities
Exempt
from
Requirements
for
a
Permit
pursuant
to
Section
21(d)
of the Act.
This
docket
directs
the
Board’s
staff
to
prepare
a proposal
applicable
to
all
facilities
which
treat,
store
and
dispose
of
solid
waste
and
which
are
subject
to the
Section
21(d)
86— 690
—43—
exemption.
The
Board
intends
that
the
Agency
be
notified
of the
existence of such
facilities
and
of the
type
of wastes
they
manage.
Economic
and
Legal
Concerns
Asserted
By
The
Participants
Having
discussed
the
strong
reasons
which
it
sees
in
favor
of
proceeding
with
this
proposal,
the
Board
will
now
turn
to the
reasons
advanced
against
so proceeding.
The
Economic Impact
Study
Section
27(a)
of
the
Act
charges
the
Board,
in
promulgating
regulations,
to
consider
the
“technical
feasibility
and
economic
reasonableness
of
measuring
or reducing
the
particular
type
of
pollution.”
The
bulk
of
the
record
amassed
to
date
in
the
R84—l7
docket
generally,
and
most
specifically
Docket
D,
has
related
to
issues
of
technical
feasibility.
As
some
participants
have
noted,
see
e.g.
P.C.
50,
p.2-3,
P.C.
52,
p.
1,
the
record
does
not
contain
sufficient
economic
information
to
support
final
adoption
of any
proposal.
Many
of the
arguments
against
the
Board’s
moving
forward
with
its
own
proposal
at
this
time
are
based
on
a
theory
that
the
Board
should
“wait
and
see”
the
results
of
various
legislative,
regulatory,
and
research
efforts
to
avoid
economically
unreasonable
results.
Much
of the
economic
data
in the
record
at
this
point
is
in
fact
“anecdotal”,
or
“intuitive”
in
nature,
rather
than
hard
data.
One
witness
for WMI,
for
instance,
in response
to a
question
concerning
the
economic
effects
of
the Docket
D
proposed
standards
to
disposal
of
industrial
waste
as
well
as municipal
waste,
commented
that:
I
have
prepared
no
calculations.
I’m
not
aware
that
other
people
in
my
organization
have
done
that.
Our
perspective
and
our
general
philosophy
is
that
the
types
of
management
systems
we
are
advocating
are
the
most
cost
effective
means
to
manage
the
materials
long
term.
(R84—17D,
R.
1730).
Another
commenter,
on the
other
hand,
is
convinced
that:
from
both
a
practical/policy
point
of
view,
as
well
as
a
strictly
legal
point
of
view,
the
IPCB’s
adoption
of
such
a
major
regulatory
overhaul
[of
existing
regulations],
without
a
corresponding
legislative
overhaul
of
applicable
provisions
of
the
[Act],
and
substantial
additional
funding
necessary
to
staff
the
IEPA
sufficiently
to
meet
the
increased
burdens
of
implementing
such
a
86—691
—44—
program,
would
not
only
be
an
act
of
regulatory
suicide,
but
also
an
act
which
in
the
long
run
will
be
determined
to
be
illegal
or
unconstitutional
...
at
least
insofar
as
it
is
made
applicable
to
existing
facilities
with
development
and/or
operating
permits
issued
under
the
old
program.
Additionally,
in
the
short
term,
these
proposals
will
create
an
economic
dysfunction
which
will
make
the
solid
waste
industry
less
attractive
to
sources
of
capital
and
will
result
in
fewer
new
entries
into
the
solid
waste
disposal/treatment
industry
in
Illinois.
Such
a
regulatory
climate
will
not
only
increase
the
overall
cost
of
living
in
Illinois
as
fewer
facilities
will
exist,
which
are
controlled
by
fewer
companies,
it
will
also
severely
restrict
Illinois’
efforts
to
make
the
State’s
economy
attractive
to
both
the
private
and
public
sector
as
a
place
to
locate
or
expand
their
operations.
This
is
particularly
critical
in
the
short
term
as
Illinois
seems
to
be
rebounding
from
the
regional
recession
and
high
unemployment
period
of
the
late
seventies
and
early
eighties.
Long
term
problems
will
involve
an
ever
increasing
inability
on
the
part
of
Illinois
citizens
and
industry
to
attract
capital
to
replace
or
expand
or
maintain
existing
facilities
in
order
to
keep
up
with
any
projected
increase
in
demand
caused
by
the
much
hoped
for
and
anticipated
growth
in
the
region.
(footnote
omitted)
(P.C.
48,
p.
2)
While
NSWMA
has
submitted
some
hard
data
concerning
compliance
costs
generally
(P.C.
47),
much
of
this
data
concerns
potential
costs
of
compliance
with
potential
RCRA
Subtitle
D
regulations.
One
operator
of
an
existing
downstate
landfill
has
provided
certain
cost
projections
at
hearing
and
by
way
of
post
hearing
comments
(R84—17D,
R.
1511—1546,
P.C.
45),
but
the
applicability
and
accurancy
of
these
projected
costs
as
applied
to
that
landfill
or
the
other
145
currently
permitted
landfills
have
not
been
explored.
The
record
developed
to
date
strongly
supports
the
Board’s
intuitive
conclusion
that
imposition
of
more
stringent
landfill
design
and
performance,
and
post—closure
care
standards
will
increase
“up—front,
out
of
pocket”
disposal
costs
for
individuals,
business
and
government.
It
supports
the
further
intuitive
conclusion
that
the
cost
benefits,
by
way,
for
example,
of
avoidance
of
government
and
private
clean—up
costs
of
“Superfund
sites”,
will
be
difficult
to
quantify.
Finally,
it
86—692
—45—
supports
the
conclusion
that
some
fine—tuning
of
these
technically
feasible
proposed
rules
may
well
be
necessary
for
economic
reasons,
but
that
the
record
provides
little
evidence
upon
which
to
base
an
informed
decision.
This
lack
of
data
has
proven
frustrating
to
DENR,
which
has
commented:
It
is
manifest
that
an
EcIS
is
particularly
appropriate
is
this
situation.
The
pending
regulatory
proposals
call
for
a
significant
departure
from
the
means
by
which
Illinois
has
theretofore
managed
its
solid
waste.
It
is
beyond
dispute
that
these
regulatory
changes
will
significantly
impact
every
sector
of
society,
and
every
generator,
hauler,
and
disposer
of
the
waste
stream
in
its
trek
from
“cradle
to
grave”.
One
would
expect
that
under
these
circumstances,
the
affected
participants
would
come
forward
with
information
on
the
economic
impact
of
these
proposals.
Znd
yet,
despite
the
fact
that
there
have
been
nearly
30
hearings
in
this
matter,
there
remains
a
dearth
of
economic
information
on
record.
Indeed,
in
the
December
4
Hearing
Officer
order,
there
is
an
attempt
to
bolster
therecord
regarding
the
economic
effects
of
the
proposals
by
inviting
landfill
operators,
to
provide
cost
estimates
of
waste
disposal
at
their
facilities
—
this
comes
after
three
years
of
proceedings
and
countless
hours
of
testimony.
The
Department
has
been
diligent
in
its
attempt
to
glean
economic
information
from
the
numerous
witnesses
called
to
testify;
however,
the
witnesses
have
been
able
to
provide
little
in
the
way
of
specific
data
useful
to
a
comprehensive
benefit
—
cost,
analysis.
(P.C.
52,
p.
1—2)
The
Board
too
has
been
surprised
that
so
few
members
of
the
affected
community
have
actively
participated
in
this
proceeding.
However,
the
Board
also
notes
that
many
potential
participants
may
have
felt
no
urgency
to
participate
heretofore,
given
the
multiplicity
of
proposals
pending
before
the
Board.
Now
that
the
Board
has
“stopped
the
moving
train”,
potential
participants
will
have
the
incentive,
as
well
as
the
ability,
to
analyze
the
effects
of
the
proposal
on
their
operations
and
to
provide
relevant
information
to
the
Board
and
DENR.
The
Board
further
observes
that
Illinois
Register
publication
of
its
proposal
should
enhance
the
data
collection
86—693
—46—
process:
despite
the
Board’s
publication
of
general
notice
of
the
proposals
and
hearings
in
its
Environmental
Register
and
distribution
of
individual
notices
to
a
mailing
list
of
over
200,
there
have
been
protests
at
hearing
that
notice
of
the
proceeding
has
not
reached
all
potentially
interested
persons.
Given
its
fiscal
constraints,
the
only
vehicle
by
which
the
Board
can
give
notice
of
its
proposal
to
a
more
general
audience
is
by
way
of
Illinois
Register
First
Notice.
Finally,
the
Board
notes
that
DENR
expressed
some
concerns
about
the
effects
of
first
notice
publication
as
it
relates
to
the
time
necessary
to
complete
its
EcIS.
Based
on
the
pendancy
of
four
proposals,
DENR
has
projected
that,
once
a
contract
has
been
let,
that
its
contractor
could
need
12—18
months
to
complete
an
EcIS.
DENR
noted
that
Section
5.01(d)
of
the
Illinois
Administrative
Procedure
Act,
(APA)
Ill.
Rev.
Stat.,
ch.
127,
par.
1005.01(d)
provides
that
“No
rule
...
may
be
adopted
more
than
one
year
after
the
date
the
first
notice
period
commenced,”
and
was
concerned
that
the
one
year
period
would
constrain
its
EcIS
activities.
Dismissal
of
the
prior
proposals,
leaving
only
the
Board’s
proposal
outstanding,
should
alleviate
many
of
DENR’s
concerns.
The
Board
also
notes,
however,
that
the
APA
one
year
period
is
a
constraint
upon
the
Board,
and
not
upon
DENR.
In
the
event
that
the
production
of
the
EcIS,
the
holding
of
the
hearings
required
by
Section
28
of
the
Act,
Board
deliberation,
and
APA
second
notice
review
by
the
Joint
Committee
On
Administrative
Rules
(JCAR)
cannot
all
be
completed
in
a
one
year
period,
the
Board
must,
as
it
has
in
the
past
under
such
circumstances,
cause
the
publication
of
a
second
first
notice
publication
to
restart
the
one
year
timeclock.
In
so
saying,
the
Board
can
only
hope
that
a
repeat
of
First
Notice
will
not
be
necessary.
Anticipated
USEPA
Subtitle
D
Regulation
The
suggestion
that
the
Board
should
defer
action
until
USEPA’s
issuance
of
RCRA
Subtitle
D
regulations
is
in
large
measure
a
two—part
economic
one.
The
first
part
is
that
Illinois
should
wait
for
USEPA
action
and
adopt
regulations
“identical
in
substance”
to
federal
ones,
to
avoid
placing
the
state
at
the
competitive
disadvantage
to
others
which
would
occur
if
Illinois
adopted
more
stringent
regulations.
The
second
part
is
that
it
would
be
administratively
inefficient
to
propose
regulations
which
would
later
need
revision.
As
earlier
noted,
the
timing
of
USEPA’s
release
of
RCRA
Subtitle
D
regulations
is
unknown;
based
on
the
difficulities
USEPA
experienced
in
drafting
Subtitle
C
regulations,
and
the
evidence
in
this
record
regarding
its
Subtitle
D
process,
the
HSWA
deadline
of
March,
1988
may
be
missed.
Anecdotal
information
in
this
record
indicates
that
the
USEPA’s
approach
to
86—694
—47—
the
rules
has
been
in
a
state
of
flux,
so
that
the
form
its
regulations
may
eventually
take
is
unpredictable.
The
General
Assembly
has
not
mandated
that
the
state’s
environmental
agencies
cease
regulatory
activities
pending
issuance
of
federal
non—hazardous
waste
regulations.
It
has
in
fact
issued
contrary
mandates
in,
for
instance,
Section
14.4
of
the
Groundwater
Protection
Act,
which
directs
that
rules
be
proposed
and
adopted
covering
various
solid
waste
management
activities,
and
has
not
precluded
adoption
of
regulations
more
stringent
than
federal
ones.
As
to
revision
of
the
Board’s
proposal,
the
Board
acknowledges
that
revisions
may
be
necessary
if
any
elements
of
this
proposal
(such
as
leachate
recycling)
are
precluded
by
Subtitle
0
regulations,
or
if
USEPA
regulations
contain
required
elements
(such
as
a
bulk
liquids
disposal
ban)
not
contained
here.
The
Board
will
address
any
such
major
inconsistancy
as
quickly
as
they
are
identified
following
promulgation
of
federal
rules.
Consistency
With
The
Groundwater
Protection
Act
The
primary
challenges
asserted
to
the
Board’s
proceeding
with
regulations
at
this
time
are
based
on
the
impending
regulatory
proceedings
mandated
by
the
Groundwater
Protection
Act.
The
Agency
has
stated:
The
Agency
urges
the
Board
to
proceed
with
caution
with
rulemaking
in
this
important
area.
While
it
is
clear
that
the
present
rules
are
woefully
inadequate,
the
Agency
is
concerned
that
the
Board’s
announced
intention
to
adopt
these
rules
piecemeal
may
cause
further
problems
later.
Policies
adopted
in
these
proceedings
with
regard
to
solid
waste
disposal
may
adversely
affect
subsequent
proceedings
regarding
treatment,
storage
and
other
modes
of
dealing
with
solid
wastes;
in
addition,
such
policies
may
be
subject
to
radical
change
due
to
rulemaking
shortly
to
be
conducted
under
the
Groundwater
Protection
Act.
The
Agency
would
prefer
that
comprehensive
rules
be
adopted
for
coherency.
(P.C.
53,
p.
1)
This
is
a
two
part
comment:
one
facet
cautions
against
regulating
only
one
set
in
the
universe
of
waste
management
activities,
and
the
other
cautions
against
regulating
activities
since
the
state’s
groundwater
standards
are
under
review.
86—
695
—48—
As
to
the
first
caution,
in
the
“best
of
all
possible
worlds”,
the
Board,
too,
would
prefer
that,a
comprehensive
set
of
rules
for
all
types
of
facilities
be
adopted
at
one
time.
However,
as
examination
of
the
procedural
history
of
this
proposal
makes
clear,
since
1980
repeated
attempts
by
the
Agency
and
others
to
develop
comprehensive
rules
have
foundered.
The
result
is
that
fifteen
year
old
rules
have
not
been
modernized
for
any
one
type
of
facility
because
of
the
difficulty
of
writing
rules
to
cover
all
types
of
facilities.
The
Board
acknowledges
that,
as
set
out
earlier
in
some
detail,
the
Groundwater
Protection
Act
mandates
the
Agency
by
January
1,
1989
to
propose
regulations
for
certain
on—site
facilities
disposing
of
“special
and
other
wastes
which
could
cause
groundwater
contamination”
as
well
as
other
enumerated
facilities.
(Section
14.4(a))
as
well
as
regulations
for
new
off—
site
disposal
facilities
(Section
14.4(c)),
and
that
it
further
mandates
the
Agency
to
propose
groundwater
quality
standards
six
months
thereafter,
or
by
January
1,
1989.
Assuming
that
the
Agency
meets
its
deadlines
to
propose
regulations,
and
the
Board
meets
its
deadline
to
promulgate
regulations
two
years
after
their
proposal,
a
comprehensive
set
of
facility
design
and
operating
standards
will
not
exist
before
January
1,
1991
and
a
set
of
groundwater
standards
will
not
exist
before
July
1,
1991.
The
Board
does
not
construe
passage
of
the
Groundwater
Protection
Act
as
indicative
of
intent
by
the
General
Assembly
to
frustrate
fruition
of
the
Board’s
pre—existing
regulatory
effort
at
a
date
earlier
than
that
mandated
for
adoption
of
Agency—
proposed
rules.
The
Board
will
proceed
to
propose
these
landfill
regulations;
the
Agency
is,
as
always,
free
to
concentrate
its
efforts
on
proposals
to
fill
other
gaps
in
the
state’s
regulatory
program.
A
second
challenge
made
by
the
Agency,
and
other
major
participants
as
well,
generally
involves
the
groundwater
standards
by
which
facility
performance
is
judged
in
this
proposal.
As
to
the
issue
of
groundwater
standards
themselves,
all
participants
agree
that
there
has
been
no
review
of
the
water
quality
standards
specifically
as
related
to
groundwater,
a
lack
which
the
legislature
has
directed
be
remedied.
All
participants
agree
that
the
Groundwater
Protection
Act
requires
promulgation,
where
possible,
of
numerical
standards
for
discharges
of
listed
contaminants
into
groundwater,
and
that
such
standards
should
apply
to
discharges
from
landfills.
At
this
juncture,
the
issue
then
becomes
whether
any
new
landfill
regulations
should
be
proposed
during
this
three
year
interim
period
pending
review
of
the
groundwater
standards,
and
what
existing
standars
may
properly
be
applied
during
the
interim
period.
86—696
—49—
At
risk
of
oversimplification,
the
groundwater
standards
embodied
in the
Board’s
proposal
for
new
facilities
is
that
any
contaminant
emissions
from
the
facility
will
not
cause
an
increase
in the
levels
of the
background
concentrations
of
indicator
constituents
within
100
years
at
a measuring point
100
feet
from
the
edge
of
the
landfills’
disposal
area
or
at
the
property
boundary.
Constituents
to
be monitored
are
those
which
appear,
or are
expected
to
appear
in
leachate,
and
for
which
the
Board
has
adopted
drinking
water
standards
including
standards
for
discharge to
surface
water,
or
which
may
otherwise
contribute
to
groundwater
pollution.
The streamlined
adjusted
standards
procedure
may
be
used
by
a
facility
to obtain
relaxed
standards
in
two
instances.
First,
where
the
pre—siting
natural
groundwater
quality
is
already
“degraded” below
existing
numerical
standards,
the Board
may
relax
standards
to
any
appropriate
number.
Second,
where
pre—
siting
groundwater
quality
is
better
than
required
by
the
existing
numerical
standards,
the
Board
may relax
the
standard,
but
to
a
number
no
less
stringent
than
existing
standards.
While
a
discharger
would
seek
permission
to degrade
groundwater
by
discharging
contaminants
in excess
of current
standards,
the
procedural
mechanism
for
obtaining such
relief
would
be by
way
of
a general
or
site—specific
rulemaking;
this
is
to
allow
for
participation
by
DENR
in
determining
economic
impacts
on
the
people
of
the
State
of
Illinois
of
the
potential
restriction
of
present
or
future
uses
of
groundwater
which
such
petitions
may
likely
represent.
As
explained
in
some
detail
in the
Background
Report,
the
STS
(pp.
59—60,78)
Recommendation
is
based
on
the
goal
of
the
Clean
Water
Act
that
dischargers
use the
best
available
technology
economically
available
(BACT)
to remove
pollutants
from
the
discharge
regardless
of
the
quality
of
the receiving
water.
In
the
absence
of
groundwater—specific
standards,
the
STS
proposal
incorporates
the
drinking
water
standards
as
well
as
the
surface
water
quality
standards,
as the
minimum
standards,
consistent
with
the
Illinois
Supreme
Court’s
finding
in
and
CIPS
v. PCB,
116
Ill.2d
397,
507
N.E.2d
819,
107
Ill.Dec.
666
(1987),
affg.
(CIPS
v.
PCB,
142
Ill.App.3d
43,
491
N.E.2d
176,
97
Ill.Dec.
362 (4th
Dist
1986)
that
“While
there
are
no
specific
standards
for
groundwater,
groundwater
is
subject
to
existing
general
water
quality
standards”
which
vary
depending
on
the
use
or
potential
use
of
the
water
involved.
The
essence
of the
argument
in
opposition
to regulatory
use
of
this
standard,
even
on an
interim
basis,
is
that
it
will
lead
to
gross
over—design
of
facilities
in
an
attempt
to prevent
migration
into
groundwater
of
constituents
which
have
not
been
proven
harmful
to
groundwater
either
on
a general
or
a
site—
specific
basis.
86—697
—50—
IERG
argues
that
reliance
on
CIPS
is
misplaced
because
the
applicability
of
Section
302
of
the
CWA
to
groundwater
was
never
made
an
issue
in
the
CIPS
court
cases.
By
failing
to
explore
the
possibility
that
the
standards
from
which
it
sought
a
site—specific
rule
change
had
never
actually
applied
to
it,
CIPS
may
have
simply
balanced
the
cost
of
litigating
the
issue
against
the
cost
of
pursuing
the
rule
change
and
chose
the
latter.
One
company’s
failure
to
raise
an
issue
does
not
bar
others
from
pursuing
it.
Nor
does
the
fact
that
CIPS
and
the
IEPA
essentially
stipulated
to
the
standard’s
applicability
on
review
enable
the
Board’s
Scientific/Technical
Section
to
cite
to
the
CIP’S
Illinois
Supreme
Court
case,
supra,
as
having
any
precedential
value.
Even
if
the
issue
had
been
raised
and
argued
before
the
Illinois
Supreme
Court,
the
Board
would
be
free
to
readdress
the
issue
in
a
rulemaking
proceeding
such
as
this
one.
(P.C.
50,
p.
6)
Reminding
the
Board
of
various
findings
in
its
Groundwater
Report*,
IERG
suggested
that
more
reasonable,
if
not
totally
*
Page
ii
——groundwaters
differs
in
many
critical
respects
from
surface
waters,
including
water
quality,
rate
of
movement,
direction
of
flow,
accessibility,
and
use;
these
differences
dicate
differences
in
protection
strategy.
——the
variety
of
compositions
and
uses
of
groundwater
makes
the
objective
of
groundwater
protection
less
readily
identificable
than
that
for
surface
water
protection;
the
groundwater
objective
is
not
likely
to
be
the
same
as
that
for
surface
water...
Page
iii
——existing
ambient
water
quality
standards
are
not
ideally
suited
to
the
task
of
protecting
groundwater.
——ambient
standards
suitable
to
protection
of
groundwaters
are
likely
to
be
significantly
different
from
those
designed
to
protect
surface
waters...
——recommendations
for
the
application
of
either
“general
(continued)
86—698
—51—
appropriate,
interim
standards
at
this
time
would
be
the
Illinois
and
federal
drinking
water
standards.
A
similar
interim
approach
has
been
advocated
by
WMI
and
NSWMA.
The
Board
does
not
consider
it
appropriate
to
readdress
the
issue
of
groundwater
quality
standards
at
this
time.
Even
if
the
existing
regulations
which
are
in
dispute
here
are
at
the
very
least
the
standards
for
discharge
to
surface
water,
as
the
STS
notes
in
its
Background
Report,
the
Board
has
already
determined
that
drinking
water
uses
are
not
the
only
ones
made
of
groundwater
and
are
not
the
only
uses
to
be
protected.
Withdrawals
of
groundwater
for
agricultural
uses,
including
irrigation,
account
for
some
24%
of
current
groundwater
usage
in
Illinois;
drinking
water
standards
alone
may
not
protect
such
uses.
Moreover,
since
natural
groundwater
discharges
occur
at
the
site
of
springs,
streams,lakes
and
wetlands,
application
to
groundwater
of
standards
for
discharge
to
surface
water
cannot
be
deemed
inappropriate
across
the
board.
The
assumption
which
appears
to
underly
many
of
the
objections
to
the
non—degradation
standard
which
is
here
proposed
is
that
the
eventual
outcome
of
regulatory
proceedings
pursuant
to
the
Groundwater
Protection
Act
will
be
a
wholesale
relaxation
of
existing
standards
for
discharges
to
surface
water.
The
Board
cannot
presume
that
such
is
the
case.
As
more
site—specificdata
is
collected
pursuant
to
the
mandates
of
the
Groundwater
Protection
Act,
it
is
clearly
contemplated
that
the
Agency
may
propose
and
the
Board
may
adopt
standards
specifically
tailored
to
specific
areas,
whether
they
be
“setback
zones”
or
“regulated
recharge
areas”,
standards
which
may
well
be
more
restrictive
than
those
in
place
currently.
Moreover,
the
Groundwater
Protection
Act
does
not
explicitly
require
the
Board
to
adopt
any
specific
regulations
and
does
not
explicitly
forbid
the
Board
from
adopting
any
regulations.
In
fact,
that
Act
explicitly
provides
that
it
is
not
intended
to
use”
or
“drinking
water”
standards
to
groundwaters
cannot
be
endorsed
at
this
time:...
Page
iv—lO
From
the
practical
perspective,
the
dissimilarities
between
surface
waters
and
groundwaters
would
suggest
that
the
General
Use
Standards,
in
large
part
conditioned
on
protection
of
habitat
for
aquatic
life
and
for
recreation
uses,
may
not
be
appropriate
to
groundwater
protection...
it
is
possible
that
such
a
determination
would
be
judged
arbitrary
and
capricious
given
the
questionable
applicability
of
aquatic—life
criteria
to
ambient
groundwaters.
86—699
—52--
preclude
the
Board
from
exercizing
its
general
authority
to
adopt
regulations
pursuant
to
Title
VII
of
the
Environmental
Protection
Act.
The
thrust
of
the
Groundwater
Protection
Act
is
to
protect
the
quality
of
water
at
the
supply
intake,
i.e.
the
welihead;
to
construe
that
Act
as
intending
to
forbid
the
Board
from
regulating
a
discharger
so
as
to
protect
other
groundwater
uses
is
absurd.
Section
27(a)
states
“the
generality
of
this
grant
of
authority
shall
only
be
limited
by
the
specifications
of
particular
classes
of
regulations
elsewhere
in
this
Act”.
Examples
of
such
limitations
are
the
exemption
of
certain
sporting
activities
from
noise
regulations
and
the
restraint
on
requiring
Stage
II
vapor
recovery
systems
in
air
regulations
absent
a
federal
mandate.
Insofar
as
the
Groundwater
Protection
Act,
like
any
Act,
establishes
locational
bans
or
constraints,
like
the
setback
zones,
the
proposed
regulations
are
drafted
so
as
to
in
no
way
conflict
with
them.
BOARD
COMMENTS,
AND
REQUEST
FOR
COMMENTS,
CONCERNING
SPECIFIC
RULES
In
this
portion
of
this
Opinion,
the
Board
will
specifically
request
comments,
or
provide
supplemental
comments,
primarily
in
areas
in
which
it
has
amended
the
STS
R84—17
Docket
D
proposal
and/or
questions
whether
the
proposal
should
be
further
modified.
First,
however,
the
Board
wishes
to
specifically
comment
on
a
few
specific
major
elements
of
the
proposal
which
it
has
not
amended.
Generic
Adjusted
Standard
Rule
This
proposal
embodies
two
mechanisms
by
which
articulated
standards
may
be
modified
without
resorting
to
variance
or
rulemaking
procedures.
In
areas
where
it
has
been
possible
to
articulate
equivalent
performance
standards
and
criteria
for
Agency
determinations
of
equivalency,
to
avoid
unlawful
subdelegation
of
authority
to
the
Agency,
the
proposal
leaves
such
modifications
to
the
Agency,
e.g.
modifications
of
cover
requirements
in
Section
811.106(b).
The
proposal
also
provides
for
application
to
the
Board
for
an
adjusted
standard
pursuant
to
Section
28.1
of
the
Act
when,
as
that
Section
requires,
the
Board
has
been
able
to
“specify
the
level
of
justification
required
of
a
petitioner
to
qualify
for
an
adjusted
standard
e.g.
alternative
groundwater
standards
pursuant
to
Section
811.320(b).
IERG
has
suggested
(R84—17D,
Exh.
33,
and
generally
R.
1893—
2009)
that
the
Board
adopt
a
“generic”
adjusted
standards
rule
to
allow
for
modification
of
any
standard
contained
in
Part
811.
Pursuant
to
the
IERG
proposal,
such
standards
are
to
be
granted
86—700
—53--
upon
demonstration
that
the
adjusted
standard“will
result
in
an
equivalent
degree
of
environmental
protection
as
would
the
standards
of
Part
811”.
While
the
Board
is
cognizant
that
adoption
of
this
proposal
would
avoid
rulemaking
delays
which
occur
when
DENR
determines
that
an
EcIS
must
be
performed,
the
Board
does
not
believe
that
this
generic
rule
can
be
lawfully
adopted.
The
Board
construes
Section
28.1
as
requiring
detailed
specification,
in
the
particular
rule
from
which
adjusted
standards
may
be
sought,
of
the
types
of
justification
whichmust
be
submitted
in
identified
areas,
see
e.g.
35
Ill.
Adm.
Code
Section
306.350—306.374
establishing
requirements
for
exceptions
to
the
Board’s
combined
sewer
overflow
regulations.
It
is
the
Board’s
belief
that
Section
28.1
specifically
prohibits
the
type
of
generic
rule
here
advocated.
Comments
on
this
interpretation
are
specifically
invited.
Industry—Specific
Exemptions
Pending
Adoption
of
Industry—
Specific
Regulations
or
Adjusted
Standards
The
records
in
R84—l7
Dockets
B
and
D
contain
considerable
testimony
from
the
foundry
industry
(e.g.
R84—l7D,
R.2006—2099,
Ex.
34—38)
and
the
utility
industry
(e.g.
R84—17B,
R.77—l58,
288—
301,460,516,
Group
Ex.
3,5;
R84—17D,
R.2l68—2275,
Ex.
40).
Each
of
these
industries
has
stated
that
years
of
research
effort
concerning
their
specific
wastestreams
is
coming
to
fruition,
with
the
result
that
each
industry
feels
that
it
can
propose
alternative,
industry—specific,
design
and
operating
standards
for
landfills
disposing
solely
of
such
wastes
on
or
about
July
1,
1989.
Each
industry
has
accordingly
requested
an
exemption
from
these
rules
pending
their
proposal,
and
the
Board’s
promulgation,
of
industry
specific
rules.
The
Board
commends
the
research
efforts
of
each
industry,
as
well
as
the
quality
of
the
testimony
and
data
which
each
has
presented.
The
Board
does
not
question
the
good
faith
estimate
each
has
made
as
to
the
timing
of
completion
of
their
research
efforts.
However,
this
record
contains
little
specific
information
as
to
the
identity
and
status
of
existing
facilities
affected,
or
proposed
facilities
anticipated
to
be
constructed.
Given
this
lack,
the
Board
cannot
determine
the
environmental
effects
of
any
exemption
it
might
grant.
Accordingly,
unless
persuaded
otherwise
by
additional
comments,
the
Board
is
inclined
to
believe
that
these
industries’
situations
are
best
handled
by
variances
from,
rather
than
exemptions
to,
the
proposed
rules.
While
the
Illinois
Steel
Group
(ISG)
has
not
committed
to
making
the
same
type
of
industry
specific
proposal
as
have
the
foundry
and
utilities
industries,
it
has
produced
testimony
suggesting
that
many
of
its
wastes,
e.g.
steel
slags,
should
be
considered
“inert”,
and
has
also
suggested
test
methodologies
for
86—701
—54—
determining
leachate
composition.
(R84—l7D,
R.2ll0—2167,
2276—
2307,
Ex.
39.)
The
proposal
defines
as
“inert”
wastes
whose
leachate
does
not
contain
constituents
in
levels
which
violate
the
existing
drinking
water/discharge
to
surface
water
standards.
ISG
seeks
to
make
the
case
that
the
discharge
to
groundwater
of
certain
constituents
characteristics
of,
for
instance,
its
slag
wastes,
i.e.
increases
of
calcium
and
magnesium
and
associated
hardness
and
pH,
have
no
or
only
benign
impacts
on
groundwater.
Given
the
Board’s
determination
that
it
is
not
appropriate
to
engage
in
wholesale
revision
of
existing
groundwater
standards
in
this
proceeding,
ISG
is
invited
to
initiate
an
appropriate
proceeding.
Proposed
Phased
Closing
of
Units
Within
Two
and
Seven
Years
Part
814
provides
that,
based
on
an
existing
landfill’s
ability
to
meet
interim
standards,
that
initiation
of
closure
could
be
required
within
two
or
seven
years
after
the
effective
date
of
these
proposed
regulations.
Given
the
lack
of
input
from
operators
of
existing
landfills
on
this
issue,
the
Board
is
unsure
how
adoption
of
these
regulations
will
affect
current
estimates
of
the
remaining
landfill
disposal
either
statewide
or
on
a
regional
basis.
Comment
is
accordingly
requested
on
the
appropriateness
and
feasibility
of
the
time
frames
contained
in
this
proposal;
it
is
not
the
Board’s
intention
either
to
precipitate
a
waste
disposal
crisis
or
to
unduly
prolong
a
phase—
out
of
non—conforming
sites.
A
related
concern
has
been
articulated
to
some
extent
by
downstate
landfill
operators
who
have
suggested
that
various
proposed
standards,
e.g.
leachate
collection
and
treatment,
should
be
relaxed
for
small
landfills
to
prevent
them
from
pricing
themselves
out
of
the
disposal
market
with
a
projected
resulting
increase
in
open
dumping
of
waste
in
their
area.
(See,
e.g,
P.C.
45,
R84—170,
R.15l5,15l9,1548)
It
is
axiomatic
that
the
size
of
a
landfill
does
not
dictate
its
potential
for
environmental
harm,
which
relates
instead
to
the
type
of
waste
received
at
the
facility,
the
facility’s
underlying
hydrogeology,
its
design
and
its
operations.
gain,
absent
production
of
data
by
existing
facilities,
small
or
large,
the
Board
has
no
basis
on
which
to
determine
whether
or
how
these
proposed
regulations
could
or
should
be
tailored
generally,
on
a
site—specific
basis,
or
on
some
basis
in
between.
Section
106.410:
Adjusted
Standards
Procedures
The
adjusted
standards
procedures
currently
existing
in
the
Board’s
procedural
rules
were
adopted
by
the
Board
in
the
R86—46
RCRA
Update
proceeding
on
July
16,
1987.
The
sole
change
in
86—702
—55—
these
rules, which were
modelled
on the procedures for CSO
exceptions,
is to
make
them applicable to adjusted standards from
non—hazardous,
as
well
as
hazardous waste regulations.
The
Board
wishes to emphasize a fact which
has been obscured
in
the prior proceedings. The adjusted standards proceeding
need
not
be
an
adversarial one,
as
the procedures allow for the
applicant
to
seek Agency concurrence on its request in advance.
If the Agency
concurs,
a
joint petition
can
be filed. If it does
not, the
applicant
can file a
single petition and contested
issues or
conditions
can be
litigated before the Board.
Section 807.105:
Relation To Other Rules
This is
a
new section. In adopting
35
Ill. Adm. Code Part
700
et
seq.
and codifying old Chapters
7 & 9,
the Board announced
its intent to eventually codify all waste regulations
with
numbers in the 700 series. The Board now believes it
is
impracticable to
do
so, and
intends
to use
numbers in the
800
specifically
series for non—hazardous
directs attention
waste regulations.
to Part 807,
the
As Part
instant
700
new
et.
a•
section is needed to provide a “road map” to
the proposed new
landfill regulations.
The
Agency
(R84—17D,
R.1784—l787)
and
WMI (P.C. 51, P.
24)
expressed
concern regarding the interface
of
the
STS
proposal
as
drafted and the Board’s RCRA
rules.
The
Board believes that
addition of this rule, as well as
modification
of the
definition
of
“solid waste” in Part
810
and modification throughout the
scope
and applicability sections should satisfy these concerns.
If not,
comments should address what further specific
modification is needed.
Part 810:
General Provisions
The
scope
and applicability sections have been amended in
this section, and
throughout the rules,
to
make it clear that the
proposal encompasses only
landfills
which are
not regulated
pursuant to the RCRA
rules.
Some
definitions have been
added:
landfill, land treatment unit, waste pile,
surface impoundment.
Language
for these is drawn from the most recent USEPA Subtitle D
draft
in the
record.
Other definitions
have
been moved from
numbered sections into the rules: new, existing,
contaminated
lea
chate.
Part 811:
General Standards For All Landfills
Subpart A
Section 811.102
Location
Standards
As
explained in
the STS Background
Report
at
pp.
16—17,
the
8 6--
703
—56--
location
standards
are
largely
derived
from
federal
and
corresponding
state
requirements.
To
the
extent
that
compliance
with
various
state
and
federal
acts
will
require
a
“sign’off”
from
Agencies
administering
such
acts,
the
Board
will
specifically
solicit
comments
from
affected
agencies.
In
Section
811.101(c),
the
STS
modified
federal
requiremets
to
include
state
landmarks.
The
Board
further
modifies
the
section
to
include
as
unacceptable
for
landfill
use
areas
which
are
designated
Illinois
Nature
Preserves
by
the
Illinois
Nature
Preserves
Commission.
This
will
provide
some
protection
to
the
Nature
Preserves
system
from
the
threat
of
harm
or
destruction
by
new
facilities.
The
Board
believes
that
the
Illinois
Nature
Preserves
deserve
at
least
as
much
protection
as
national
natural
landmarks
and
other
areas
included
under
811.102.
A
list
of
dedicated
Natural
Preserves
will
be
included
as
an
exhibit
in
R88—7.
The
Board
solicits
comments
on
this
action.
As
the
STS
notes,
various
commenters
have
requested
that
these
regulations
include
a
prohibition
of
landfill
construction
within
the
100
year
floodplain
regardless
of
floodproofing
(e.g.
P.c.
44,46).
The
Board
specifically
requests
additional
comment
on
the
proposal
as
it
relates
to
the
100—year
floodplain,
specifically
noting
the
recent
Illinois
experience
of
the
variability
of
the
contours
of
such
floodplains.
Subpart
C
Section
811.306
Liner
Systems
The
proposal
specifies
a
minimum
liner
thickness
of
three
feet.
(See
STS
Background
Report,
pp.
32—38)
The
current
practice
has
been
to
require
emplacement
of
a
10
foot
liner.
The
Agency
advocated
retention
of
this
requirement
to
avoid
the
piercing
of
the
liner
by
a
long
object,
such
as
a
6—foot
fencepost,
during
initial
waste
placement.
(See
e.g.
R84—l7D,
R.1739—1748).
The
Board
believes
that
this
concern
may
be
obviated
by
the
addition
in
Section
811.321
“Operating
Standards”
of
special
procedures
for
initial
placement
of
the
first
five
feet
of
waste.
A
further
concern
has
been
raised
that
the
three—foot
thick
earthen
liner
might
not
be
emplaced
correctly
because
of
cold
or
rainy
weather
or
operator,
skills
or
occasional
lack
of
supervision.
A
five—foot
thick
liner
has
been
suggested
to
give
a
“factor
of
safety”
should
less
than
ideal
construction
occur
(e.g.
R84—17D,
R.2395).
comment
is
requested
by
the
Board
on
this
alternative
rule.
Section
811.317
Groundwater
Impact
Assessment
86—704
—57—
Section
811.319
Procedures
For
Groundwater
Monitoring
Programs
These
sections
involve
an
issue
which
is
related
to
the
groundwater
standard
issue,
not
previously
addressed
by
the
Board:
the
appropriateness
of
the
use
proposed
here
of
a
contaminant
transport
model.
This
concern
has
been
consistently
expressed
by
WMI
and
NSWMA.
(See
STS
Background
Report,
pp.
59—
69)
The
Board
is
not
persuaded
by comments
heretofore
filed
that
the
use
is
inappropriate,
but
will
entertain
further
comment.
Section
811.319(a)(4)
Organic
Chemicals Monitoring
Program
The
Board
has added
a new
concept
which
was
not
present
in
the
original
STS
proposal,
groundwater
quality
monitoring
for
organic
chemical
contaminants.
This
concept
is
intended
to apply
to
all
facilities
that
accept
putrescible
or chemical
waste
and
that
are new
facilities
or
existing
facilities
that
intend
to
remain
in
operation
for
more
than
seven
years.
This
concept
would
apply
whether
the
facilities
need
a
permit
or
are
exempted
from
permits
under
Section
21(d)
of
the
Act.
-The
rule
provides
that
all
such
facilities
shall
acquire
this
information
within
one
year
of
the
effective
date
of
the
regulations
and
within
one
year
of
the
establishment
of
any
new
monitoring
well.
The
information
must
be
updated
at
least
once
every
five
years
for
every
well.
The
monitoring
requirements
obligate
the
operator
to
analyze
for
at
least
58
organic
chemical
contaminants.
The
United
States
Environmental
Protection
Agency
(“IJSEPA”)
has
established
testing
procedures
for
the
organic
chemical
contaminants
in drinking
water.
USEPA
determined
that
testing
procedures
were
readily
available,
reliable
and
cost
effective
at
approximately
$150
to
$200
per
sample.
50
FR 46902
(November
13,
1985).
The
operator
would
notbe
required
to
use the
specific
testing
protocols
described
by
USEPA,
but
any
alternative
testing
protocols
must
provide
reliable
results
for
at
least
as many
chemicals
to
at
least
low
a
level
of
detection.
The
Board
solicits
comment
on
whether
the
testing
protocols
are
appropriate
for
determining
whether
organic
chemical
contamination
is
occuring
in
the
area
of
the
facility,
as
well
as whether
such
testing
protocols
are
available
and
cost
effective
for
Illinois
facilities.
The
primary
purpose
of the
organic
chemical
testing
requirements
is
to ensure
that
baseline
concentrations
are
established
for
a wide
range
of contaminants.
These
baseline
concentrations,
with
certain
modifications
pursuant
to
Section
8ll.320(d)(l),
would
become
enforceable
water
quality
standards.
ny
subsequent
statistically
significant
increase
in
the
concentration
of any
parameter
which
is
attributable
to
the
facility
would
be
a water
quality
violation.
The
baseline
concentration
for
each
of
the
58
parameters
at
each
well
outside
86•7O5
—59—
Section
813.103
Agency
Decision
Deadline
The
Board
has
revised
subsection
(d)
to provide
that
final
action
is deemed
to
have taken
place
when
the Agency’s
notice
is
signed,
rather
than
when
mailed.
This
change
is proposed
in
response
to Agency
testimony
concerning
administrative
difficulties
under
the current
practice.
(R84—l7D,
R. 1778—80).
Comment
is
solicited.
Section
813.108
Term
of
Permit
The
regulation
specifies
a
five
year
term
of
permit,
consistent
with
terms
of
permits
in other
media
in Illinois.
(See
STS Background
Report,
p.
101) NSWMA
has
presented
testimony
(R.
1491—1508)
suggesting
that
a
10
year term
may
be
preferable
to
eliminate
difficulties
in
funding
post—closure
requirements.
Additional
comment
is solicited.
Section
813.110
Adjusted
Standards
To Engage
In
Experimental
Practices
As described
at
pages 102—103
of the
STS
Background
Report,
the
experimental
practice
procedure
would
be utilized
by an
operator
to avoid
a
“Catch—22”
situation
in which
experimental
technology
could
not
be employed
because
information
demonstrating
that its
use
would
or would
not violate
the
Act or
Board
regulations
could
not
be conclusively
provided
until
after
the
experimental
technology
had in
fact
been used.
While
Landfill,
Inc.,
supra,
makes
it clear
that
the
Agency,
and not
the
Board,
is
the permitting
authority
pursuant
to Section
39(a)
of
the
Act,
it is
also
clear
that the
Agency
may
not
issue
permits
absent
proof
that
the
environmental
standards
established
by
the
Act and
by
the
Board
will be
complied
with.
The
only
procedures
available
for relaxation
of
environmental
standards
are
through
petitions
for variance,
adjusted
standards,
and
site—
specific
rules.
The
Board
believes
that
the
STS
has
correctly
identified
the
adjusted
standard
as the
most
appropriate
procedure
of
the three.
The
Board
also
notes,
based
on this
record,
its belief
that
authorization
of an
experimental
practice
absent
opportunity
for
public
participation
in the
decisionmaking
process
would
hardly
serve
to foster
public
confidence
in
such
authorization.
The
Agency
has
expressed
concerns
(P.C.
53,
p.3—4)
that
it
has no
“up—front”
ability
to
participate
in
the
standard
setting
process,
a
misapprehension
which
the
Board hopes
the
earlier
discussion
of Section
106.410
has laid
to rest.
The
Agency
additionally
questions
whether
the
Board
could
[as
the
rule is
written]
grant
an
“anything
goes”
adjusted
standard.
While
the
Board
hypothetically
could
do
so, just
as
it hypothetically
could
grant
an
“anything
goes”
variance.
Any such
action
would
clearly
be
contrary
to
the
Act
and
would
doubtless
be appealed
by the
86—707
—58--
the
zone of
attenuation
or zone
of
compliance
would be listed
as
part
of the
groundwater
monitoring
program pursuant
to Section
812.317(1).
If
a
water quality
violation
was
detected,
the
organic
chemical
analyses
from
those
wells inside
the
zone
of
attentuation
or
zone
of compliance
would
help
determine
whether
the
facility was
the source
of contamination.
The
Board
specifically
solicits
comments
concerning
this
subsection.
Subpart
G:
Financial
Assurance for Closure
and
Post—Closure
Care
This
Subpart
is
essentially
an amended
version
of
the
existing
Part 807
financial
assurance
rules. As
the amendments
were
not discussed
at
previous
hearings,
comment is
specifically
solicited.
The
Board
has
not
chosen
to
propose
amendments
to,
or repeal
of,
the
Part 807
rules at this
time on
the belief
that these
rules
should remain
intact until
all
existing facilities
have
been
repermitted
under
Part 813
of these proposed
regulations.
Comments on
this strategy
are
solicited.
As
proposed, this
Section
does not
repromulgate
the
financial
assurance
forms currently
contained
in
Appendix
A to
Sections 807.600—807.666.
Instead,
this Subpart
specifies
throughout
that
operators
must
provide financial
assurance
on
“forms
specified by
the Agency”.
Comment
is requested
on the
advisability
of this
proposed
change.
Part
812:
Information
To
Be
Submitted
In A
Permit
Application
There are no
specific
Sections
in this Part
concerning
which
the
Board
specifically
seeks
comment.
Part
813:
Procedural
Permitting
Requirements
This Part has
been
the
subject of
redrafting
by the Board
in
various
areas.
Various
statutory
provisions,
including
reference
to the
prohibition
on Agency
issuance of
permits
without any
necessary
SB172
approvals,
have been included
in
the rules.
There
are two notable
deletions:
the STS
proposed
rules for
“Agency
Review
For
A Complete
Filing” and
“Agency
Concurrence On
Phase
I
and
Phase
II Geohydrological
Investigations”,
which
relates
to
the completeness
review issue.
(See STS
Background
Report,
pp.
99—101)
Pursuant to
the Village
of
Hillside, supra,
the
Board
believes
that it lacks
statutory
authority to
mandate
that the
Agency
employ the
administrative
procedures
suggested
by
the STS.
One effect
of
this
holding,
then, is
that
it
remains in
the
Agency’s
discretion
as
to whether
it
begins technical
review
of
a
permit
application
needing SB172
approval
prior to
its
receipt of
that approval.
86—706
—60—
Agency
on that basis.
The Board
believes
that the
rule as
now
drafted
clearly specifies
what
is to be
contained
in the
petition,
and specifies,
to the extent
practicable,
criteria
for
Board
review. Additional
comments, however,
are
welcome.
Subpart
B
Procedures
Applicable
To
Significant
Modification
of Permits
This Subpart
has
been revised
to make clear
that
authorization
to
operate
a unit must
be obtained
by
way
of
permit
modification.
Subpart
C
Procedures
Applicable
To The
Renewal
of
Permits
A section
has been
added embodying
the language
of
16(a)
of
the APA, providing
that
a landfill operator
who
timely files
an
application for
permit
renewal
may
continue
to
operate under
the
terms of the old
permit
during the
time the application
is being
processed and
any appeals
to the Board
of
Agency
decisions
on
that application
are
being
heard.
Part
814
Interim
Standards For
Existing
Landfills
Subpart
A
General
Requirements
This
Subpart
has been the
subject of
substantial
revision
by
the
Board.
The
primary
purpose
of the revisions
is
to create
a
procedure
for
the orderly
“call in”
and
modification
of existing
permits
consistent
with due
process
requirements.
Various
commenters
(e.g. P.C.
48,49)
have
suggested that
presently
existing “life
of site” permits
cannot
be lawfully
modified,
and
should be “grandfathered”
into
any
new system.
However,
the
Board notes
that existing
Section
807.209(a)
under which
the
permits
were
issued provides
that
“the
Agency
shall revise
any
permit issued
by it
to make the permit
compatible
with
any
relevant new
regulations adopted
by
the Board.”
Section
814.102
Compliance
Date
It is
not the Board’s
intent
to have all
existing facilities
thrown into
a non—compliance
status
immediately
on
passage
of the
new rules.
The
six
month compliance
date ties
into the
notification
deadline
of Section
814.103.
Section
814.103
Notification
To
Agency
of Facility
Status
The
STS
had
proposed
that this
notification
take place
within
two years of
the
effective
date of the
rules.
The Board’s
proposal
requires the
notification
within
six months,
to allow
the Agency
to analyze
the data
and prepare
a prioritized
“call
in” schedule
over
a
four year period.
The
Board solicits
comment
86—708
—61—
on
whether
the
six
month
time
frame
is
an
appropriate
time
frame
in
which
to
expect
compliance.
Section
814.104
Applications
This
section
imposes
a
duty
on
the
operator
to
file
an
application
for
modification
no
later
than
48
months
after
the
effective
date
of
the
rules,
or
at
such
earlier
time
as
the
Agency
calls
in
the
permit.
The
STS
had
chosen
a
42
month
deadline,
which
the
Board
modified
in
response
to
Agendy
testimony
that
a
full
4
year
call
in
period
was
administratively
necessary
to
allow
for
repermitting
of
existing
facilities
within
5
years
(r84—17D,
R.
1781).
Section
814.105
Effect
of
Timely
Filing
The
purpose
of
this
section
is
to
make
clear
that
a
permitee
who
timely
files
both
the
status
notification
and
the
permit
modification
application
is
deemed
in
compliance
with
the
new—
regulations,
and
may
lawfully
continue
operations
under
the
terms
and
conditions
of
its
Part
807
permit
until
1)
such
permit
is
revoked
pursuant
to
any
enforcement
action,
or
2)
a
revised
permit
has
been
issued
and
any
appeals
to
the
Board
thereof
are
exhausted.
P.C.
48
suggests
that
Part
807
permits
cannot
be
modified
unless
a
hearing
has
been
held
by
the
Agency;
(citing
Martell
v.
Mauzy,
511
F.
Supp.
729
N.D.
Ill
1981).
Martell
involved
a
suit
requesting
injunctive
relief
ordering
issuance
of
a
landfill
operating
permit
for
three
disposal
trenches
which
the
Agency
had
denied,
without
prior
hearing,
pursuant
to
Section
39(e)(l)
of
the
Act.
It
was
undisputed
that
the
trenches
had
been
properly
developed;
the
basis
of
the
denial
was
nine
instances
of
alleged,
but
not
adjudicated,
misconduct
on
the
part
of
the
owner.
The
result
of
the
denial
was
a
shut—down
of
the
landfill.
The
District
Court
ordered
issuance
of
the
permit
pending
completion
of
an
adjudicatory
hearing.
The
situation
here
is
completely
distinguishable.
No
existing
facility
which
complies
with
procedural
filing
requirements
would
be
deprived
of
the
opportunity
to
continue
operating
pursuant
to
the
terms
and
conditions
of
its
Part
807
permit,
consistent
with
procedures
established
in
Section
16(b)
of
the
APA
for
the
renewal
of
permits.
The
Board
does
not
believe
that
the
due
process
hearing
to
which
an
operator
is
entitled
prior
to
modification
or
termination
of
rights
conferred
by
an
existing
permit
need
necessarily
be
held
by
the
Agency.
In
IEPA
V.
IPCB,
138
Ill.
App.
3d
550,
486
N.E.
2d
293,
294
(3rd
Dist.
1985),
aff’d.
115
Ill.
2d
47
(1986),
the
Court
observed:
In
a
[landfillj
permit
case,
such
as
this,
the
process
involving
the
EPA
and
the
PCB
is
an
administrative
continuum.
It
became
complete
only
after
the
PCB
had
ruled.
the
EPA
permit
86—709
—62—
denial
did
not
involve
the
issuance
of
detailed
findings
of
fact
and
conclusions
of
law.
EPA
is
only
required
to
give
reasons
for
denial,
the
basis
for
which
the applicant
had
no
opportunity
to
challenge.
WMI
had
no means
of
disputing
any
contrary
evidence
relied
on
by
EPA
until
the
PCB hearing
was
held.
In
short,
as
to
the
EPA
hearing
alone,
there
is
nothing
resembling
a
hearing
where
adversaries
submit
proofs
to
a
neutral
and
detached
decisionmaker.
The
hearing
before
the
PCB,
however,
includes
consideration
of
the
record
before
the
EPA
together
with
the
receipt
of
testimony
and
other
proofs
under
the
full
panoply
of
safeguards
normally
associated
with
a
due
process hearing.
(Cf.,
Borg
Warner
v.
Manuzy,
100
Ill.
App.
3d
862,
427
N.E.
2d 415
(3rd
Dist.
1981)).
Part
815
Reporting
Regulations
For
Landfills
Exempt
From
Permits
As
this
Part
has
been
added
since
the
close
of hearings,
comments
on
the
language are
solicited
generally.
CON
CLU
SI
ON
As
this
rulemaking
enters
a
new
phase,
in
which
the
Board
has
itself
initiated
a
proposal,
the
Board
wishes
to
commend
all
participants
in
the R84—17
proceeding
for
their
thoughtful
testimony
and
comments,
and
to
encourage
their
containued
participation.
At the
same
time,
the
Board
wishes
to
emphasize
to
affected
individuals
and
organizations
who
have
not
previously
explained
their
situations
and
voiced
their
concerns
that
the
time
to focus
on
this
proceeding
is
now,
as
the
Board
intends
to
exercise
all
deliberate
speed
in
final
adoption
of modern
landfill
regulations.
I,
Dorothy
M.
Gunn,
Clerk
of
the
Illinois
Pollution
Control
Board,
by
certi
that
the
above
Opinion
was
adopted on
the
ay
of
,1988,
by
a
vote
of
Dorothy
M.
GAnn,
Clrk
Illinois
Pollution
Control
Board
86—710