ILLINOIS POLLUTION CONTROL BOARD
August 24,
1995
IN THE
MATTER
OF:
)
)
PETITION OF LONE STAR
)
AS 94-15
INDUSTRIES,
INC. FOR
)
(Adjusted Standard-Water)
ADJUSTED STANDARD FROM
)
35 ILL. ADM.
CODE 811.320(d)
(Establishment
of Groundwater
)
Background Concentrations)
)
SAMUEL T. LAWTON, JR.,
of ALTHEIMER
& GRAY, APPEARED ON BEHALF OF
PETITIONER; and,
JOHN J. KIM APPEARED ON BEHALF OF THE ILLINOIS ENVIRONMENTAL
PROTECTION AGENCY.
OPINION AND ORDER OF THE BOARD
(by J. Theodore Meyer):
This matter is before the Board on a petition for an
adjusted standard from the requirements of
35
Ill. Adm.
Code
Subtitle G,
Section 811.320(d)
filed October 4,
1994
by
petitioner,
Lone Star Industries,
Inc.
(LSI).
The Illinois
Environmental Protection Agency
(Agency) filed its Response to
Petition for Adjusted Standard on January
9,
1995 and LSI
submitted its Reply on March
3,
1995.
Hearing was held on April
21, 1995 in Ottawa,
Illinois in which several members of the
public were in attendance1.
Two comments were received during
the post—hearing comment period.
The record
in this matter was
completed on May 19,
1995.
RELIEF REQUESTED
LSI
is seeking an adjusted standard from the background
concentration requirement of groundwater quality standards
pursuant to 35
Iii. Adm.
Code 811.320(d).
(Pet.
at
1.)2
LSI
requests that groundwater standards of Part 620 be applied
instead.
(Tr.
at 131-132.)
The Agency recommends a denial of
1Section
32
of the Act allows citizens of the public to offer comment at
Board hearings.
Pursuant
to Board procedure,
the hearing officer in this case
asked
if anyone from the public wanted to make any statements.
Robert
J.
Riboizi offered public comment on behalf of Area Citizens Representing
Environmental Safety
(A.C.R.E.S.).
2Petitioner’s petition shall be referred
to
as
(Pet.
at
.);
the
Agency’s recommendation shall be referred to
as
(Rec.
at
.); petitioner’s
reply to the Agency’s
recommendation shall be referred
to
as
Reply
at
.);
and,
the hearing transcript shall be referred to as
(Tr.
at ~.)
For
references
to exhibits within an exhibit,
the cite shall
be
(Pet.
at
Exhibit
—
within Exhibit
.)
.
For references
to
the
Incorporated Record,
the cite
shall be
(Inc.
Rec.
at
Exhibit
.).
2
the requested adjusted standard, stating that LSI failed to
provide sufficient technical justification to support
its
position as required by
35
Ill.
Adm.
Code 811.320(b) (2).
(Agency
Br. at 2,3,
Tr.
at
133.)
BACKGROUND
LSI operates a portland cement manufacturing plant and
associated quarry in Oglesby, LaSalle County,
Illinois.
(Inc.
Rec.
at Exhibit
D..)
Purchased by LSI
in
1982,
the plant
is over
100 years old, and employs 105 people.
(Id.)
A by—product of the cement manufacturing process
is cement
kiln dust
(CKD),
a portion of which
is disposed in LSI’s quarry.
(u.)
Although 95
of CKD is returned to the cement process,
some 6,000 tons have been deposited in the quarry in one year.
(~~)
The wasted CKD, which is higher in sodium and potassium
alkalis than recycled CKD, consists of material that appears
naturally in areas rich in limestone deposits.
(Tr.
at 17.)
Occupying eight acres on the southeast bank of the Vermilion
River across from LSI’s plant, the quarry was created from the
company’s prior limestone mining operations.
(Tr.
at 21, Exhibit
2.)
It is bounded by a ledge and precipitous embankment leading
to the river on the north,
a steep hill to the south and east,
and an earthen dam to the west.
(Exhibit
1, page 2,3.)
South of
the quarry is a large area of abandoned surface and underground
limestone mines.
(Exhibit 5.)
Prior to its use as
a CKD landfill,
the empty quarry
collected rainwater and eventually became a pond.
(Tr.
at 21.)
When CKD was first stored in the quarry,
the water became
contaminated with alkali, and the resulting leachate seeped into
the Vermilion River.
(Tr. at 21-22.)
In response to new landfill regulations passed in 1990, LSI
began work to bring its landfill into compliance.
(In the Matter
of Development, Operating and Reporting Requirements for Non-
Hazardous Waste Landfills,
R88—7
(August 17,
1990).)
In its May
20,
1993 Order, the Board granted LSI a variance from certain
regulations, and LSI implemented a compliance plan to eliminate
the migration of leachate beyond the landfill boundaries.
(PCB
92-134, Board Order at l2.)~ This was accomplished by covering
the older part of the landfill with shale, draining most of the
collected rainwater from the remaining landfill area,
and using
the collected rainwater as coolant in the cement manufacturing
3Relief was granted, with certain conditions,
from the following
regulations:
35
Ill. Adm. Code 814.302(a);
811.313; 814.302(b)(1);
811.301(b); 811.314; 811.320(d)811.317;
815.202(a);
815.203(b); 812.316;
815.202(a);
815.203(b);
811.110(d);
and, 811.309(c)(4.
3
process.
(Tr. at 22.)
A shale barrier was created between the
pond and the landfill to prevent further mixing of CKD and any
rainwater.
(Id.)
Finally,
a tile drainage system was placed on
top of the landfill to allow rainwater to drain into the pond to
be used as coolant as well.
(~~)
The landfill has no engineered liner separating the CKD from
the old quarry floor or walls.
(Tr.
at 28.)
The landfill rests
on approximately eight feet of unmined limestone, two feet of
coal,
and several layers of clay, shale and sandstone.
(Tr. at
23,
39.)
Petitioner believes that this topography creates a
natural,
impermeable liner.
(Tr.
at 23,24.)
In 1992 LSI hired environmental engineers to produce a
hydrogeology report for its landfill area.
(Tr. at 52,53.)
The
report relied upon data from 15 monitoring wells:
four which
were located within LSI’s landfill; four which were along its
boundary; six which were situated between the Vermilion River and
the landfill; and,
one which was off-site.
(Pet. at Exhibit
3
within Exhibit 1.)
The report also included a potentiometric map
which was used to explain that surface water flows radially
outward from the landfill, indicating that the landfill is the
highest point in the area,
so that, hydraulically, groundwater
cannot be upgradient.
(Tr.
at 57,78,
Pet. at Exhibit i.)~ The
report concluded that there
is no groundwater upgradient from the
landfill.
(Pet. at Exhibit 1.)
In addition, the report concluded that no aquifer of concern
existed in the area,
and that, due to the impermeability of the
area’s topography,
it is impossible for water to travel
vertically.
(Tr.
at 57,58.)
The second contention implies that,
even if there was an aquifer within the zone of attenuation, no
leachate could travel vertically to impact the aquifer.
Therefore,
it
is inappropriate to determine background
concentrations of groundwater.
(~~)
ADJUSTED STANDARD JUSTIFICATION
The Board’s responsibility in this matter arises from
Section 28.1 of the Illinois Environmental Protection Act
(Act)
which allows the Board to grant adjusted standards modifying the
‘Petitioner used the term “groundwater” interchangeably with other terms
throughout its filings,
exhibits and at hearing,
creating confusion in the
record.
The Act defines groundwater as
“underground water which occurs within
the fluid pressure in the pore space equal to
or greater than atmospheric
pressure.
(415 ILCS 5/3.64.)
Therefore,
for reasons
of clarity,
this
opinion
uses the term “rainwater” to refer to collected water
in the landfill which
petitioner states
is
the result
of precipitation
(Tr.
at
21);
“surface water”
to refer to non—groundwater that travels from one point to another;
and
“leachate” to
refer to water that has come into direct
contact with solid
waste.
(35
Ill. Adm.
Code 810.103.)
4
effect of general rules in specific cases.
(415 ILCS
5/28.1(1992).)
More generally,
the Board’s responsibility in
this matter is based on the system of checks and balances
integral to Illinois environmental governance:
the Board is
charged with the rulemaking and principal adjudicatory functions,
and the Agency
is responsible for carrying out the principal
administrative duties.
The Act provides that a petitioner may request, and the
Board may impose,
an environmental standard that is different
from the standard that would otherwise apply to the petitioner as
the consequence of the operation of a rule of general
applicability.
Such
a standard is called an adjusted standard.
Procedural rules for adjusted standards are found at Section
28.1 of the Act and 35 Ill.
Adm. Code 106, Subpart G.
Where the
Board specifies a
“level of justification” at the time that it
adopts
a rule of general applicability, that level of
justification
is applied to any adjusted standard request filed
pursuant to that rule.
Absent a specified level of
justification, the provisions of Section 28.1(c)
of the Act apply
to a request for adjusted standard.
LSI seeks an adjusted standard from 35
Ill.
Adm. Code
811.320(d).
This section outlines two
levels of justification:
one for groundwater that presently serves,
or in the foreseeable
future will serve, as a source of drinking water; and, one for
groundwater that cannot serve as a source of drinking water.
(35
Ill. Adm. Code 811.320(b).)
The level of justification for
sources of drinking water is addressed specifically
in
35 Ill.
Adm. Code 811.320(b) (2), which states:
For groundwater which contains naturally occurring
constituents which meet the requirements of 35
Ill.
Adm. Code 302.301,
302.304, and 302.305, the Board will
specify adjusted groundwater quality standards no
greater than those of
35 Ill. Adm. Code 302.301,
302.304, and 302.305, upon a demonstration by the
operator that:
(A)
The change
in standards will not interfere
with,
or become injurious
to,
any present or
potential beneficial uses fcr such waters;
(B)
The change
in standards is necessary for
economic or social development, by providing
information including,
but not limited to,
the impacts of the standards on the regional
economy,
social disbenefits,
such as
loss of
jobs or closing of landfills,
and economic
analysis contrasting the health and
environmental benefits with costs likely to
5
be
incurred in meeting the standards; and
(C)
all technically feasible and economically
reasonable methods are being used to prevent
the degradation of the groundwater quality.
The level of justification for sources of non—drinking water is
found at 35
111.
Adin.
Code 811.320(b) (4), which states:
For groundwater which contains naturally occurring
constituents which do not meet the standards of
35 Ill.
Adm. Code 302.301,
302.304,
and 302.305, the Board will
specify adjusted groundwater quality standards upon a
demonstration by the operator that:
(A)
The groundwater does not presently serve as
a
source of drinking water;
(B)
The change in standards will not interfere with,
or become injurious to,
any present or potential
beneficial uses for such waters;
(C)
The change in standards
is necessary for economic
or social development, by providing information,
including, but not limited to, the impacts of the
standards on the regional economy,
social
disbenefits such as loss of jobs or closing of
landfills, and economic analysis contrasting the
health and environmental benefits with costs
likely to be incurred in meeting the standards;
and
(D)
The groundwater cannot presently, and will not in
the future,
serve as a source of drinking water
because:
(i)
It is impossible to remove water
in usable
quantities;
(ii) The groundwater
is situated at a depth or
location such that recovery of water for
drinking purposes
is not technologically
feasible or economically reasonable;
(iii)
The groundwater
is so contaminated that it
would be economically or technologically
impractical
to render that water fit for
human consumption;
(iv) The total dissolved solids content of the
groundwater is more than
3,000 mmg/l and that
water will not be used to serve
a public
6
water supply system;
or,
(v)
The total dissolved solids content of the
groundwater exceeds 10,000 mg/l.
PROPOSED
STANDARD
LSI requests relief from establishing background
concentrations for groundwater due to the unique geology and
hydrogeology of its landfill, and the history of surface and
underground mining that has disturbed the entire area.
LSI
proposes the following language for the adjusted standard:
“Section 811.320(d)
is inapplicable to the landfill
facility owned and operated by Petitioner,
Lone Star
Industries,
Inc.
at Oglesby,
Illinois”.
(Pet.
at 7.)
LSI further proposes that any monitoring at its landfill be
subject to the standards set forth in 35
Ill. Adm. Code
620.440(c).
~
Reply at 4.)
This section provides:
Section 620.440(c)
Groundwater Quality Standards for Class
IV:
Other Groundwater
c)
For groundwater within a previously mined area,
the standards set forth in Section 620.420 must
not be exceeded, except for concentrations of TDS,
chloride,
iron, manganese,
sulfates, or pH.
For
concentrations of TDS,
chloride,
iron, manganese,
sulfates, or pH, the standards are the existing
concentrations.
(35 Ill. Adm. Code 620.440(c))
AGENCY RESPONSE
First, the Agency believes that the correct level of
justification for this matter is
35 Ill. Adm.
Code 811.320(b) (2),
the level for groundwater that presently serves,
or in the future
will serve,
as
a source of drinking water.
As such, the Agency
contends that LSI failed to adequately address the level of
justification required for this Adjusted Standard, and requests
denial on that basis alone.
(Rec.
at 2.)
Secondly,
in its recommendation and at hearing, the Agency
asserts that LSI has not provided sufficient information to
justify the granting of the requested variance.
(Rec. at 2-3,
Tr.
at 133.)
Specifically, the Agency notes that one
potentioinetric map and data from on—site wells only does not
establish the impossibility of determining background groundwater
concentrations.
(Rec.
at Exhibit
1.)
The Agency further
believes that an aquifer
is present in the area,
as evidenced by
7
approximately 16 potable/private wells located in the area
surrounding LSI’s landfill.
(j~)
Therefore,
the Agency
recommends that the request for an adjusted standard from
35 Ill.
Adni. Code 811.320 be denied.
(Rec.
at
5.)
CONCERNED CITIZENS
Roger Riboizi, president of A.C.R.E.S., presented the
group’s concern that,
without constant monitoring,
leachate from
LSI’s landfill will continue to leak into the Vermilion River.
(Tr. at 9.)
Mr. Ribolzi testified that the river is enjoyed by
local residents for fishing and recreational use.
(~.)
A.C.R.E.S. urged LSI to continue prevention measures against the
spread of pollutants from LSI’s landfill.
(Tr. at 10.)
Mr.
Ribolzi requested that LSI continue to monitor its landfill for
the sake of the environment and the citizens of the local
community.
(Tr. at
130.)
DISCUSSION
The major thrust of the Board’s landfill regulations
is
the prevention of groundwater contamination.
To accomplish this,
a facility must establish groundwater quality standards based on
the background concentrations of all monitored chemical
constituents.
(35 Ill.
Adm. Code 811.320.)
Petitioner
is asking
for relief from establishing background concentrations,
stating
that no groundwater exists in the area of its landfill.
For the
reasons set forth below, the Board is not persuaded that LSI met
its burden of proving the non—existence of groundwater
in the
area of its CKD landfill.
Existence of Groundwater or Aquifer of Concern
In examining the record, the Board finds troubling the lack
of reliable data to support LSI’s contention that neither
groundwater nor an aquifer of concern exists.
Regarding
LSI’s
testing for groundwater,
we first notice the failure to provide
testing data from any off-site monitoring wells.
Only one of
LSI’s monitoring wells was located off—site, and no data was ever
provided from this well.
(Exhibit 7,
figure 4-1.)
In
fact,
several wells were either damaged or destroyed,
preventing the
collection of data from them.
(Exhibit 7,
p.5-4.)
LSI did not
prove that it would have been impossible to drill a well in the
unmined areas directly east of LSI’s landfill, within 200 feet of
its service road, thus providing reliable data as to the presence
of groundwater.
(Exhibit 2.)
Secondly, despite LSI’s characterization of the water
collected in its wells as “groundwater”, the Board believes the
data collected from on—site wells only report the characteristics
of either leachate from the landfill or surface water that had
percolated through overburden and into the mines and wells.
The
8
monitoring wells that produced data were all located within the
landfill or on its border.
(Pet.
at Exhibit 2D within Exhibit
1.)
This information does not help determine whether or not
actual groundwater or an aquifer exists in the area.
We are also not convinced that petitioner met its burden of
proving that no aquifer of concern exists within the zone of
attenuation.
Numerous shallow and deep wells exist across the
Vermilion River which provide the town of Oglesby with its water
supply.
(Exhibit
1,
p.5.)
These wells tap into the
Pennsylvanian, Ordovician and Cambrian rocks which include
several aquifers.
~
Alluvial aquifers and shallow wells are
present along the Illinois River as well.
(~~)
Evidence was
not provided to show that these aquifers are not hydraulically
connected to geologic material underlying LSI’s landfill.
Assuming arguendo, that LSI did provide persuasive evidence
of a lack of groundwater in the area of its landfill,
LSI would
still need to demonstrate that any leachate from the landfill
cannot mix with other sources of water.
LSI must prove that
previous detections of leachate travelling off-site into the
Vermilion River will not occur
in the future.
Although data from
the monitoring wells indicate a decrease in the amount of
leachate moving from the landfill, and despite LSI’s commendable
efforts to contain
it,
leachate continues to leave the landfill.
(Exhibit
7,
p.
4—4,405.)
In addition, water has been observed
running through the maze of underground tunnels and emptying into
the Vermilion River.
(Tr. at p.65.)
LSI must demonstrate that
this water is surface water which has not mixed with its CKD
landfill, but simply percolated through the overburden into the
tunnels.
Petitioner must also show that this water is not
leachate seeping through the landfill walls.
Finally, although there is some evidence that vertical
migration of water is minimal, we are not persuaded that the
quarry floor in which the landfill sits
is
impervious to leachate
seepage.
This site experienced dynamite blasting while, being
mined for limestone.
(Tr. at 40.)
Possible cracks or fissures
in the limestone floor could allow leachate to seep out of the
landfill.
Petitioner reasons that no observable drop in the
water level of the lake
is direct evidence that there are no
cracks
in the floor of the landfill.
(Tr.
at 41.)
However,
seepage may not be detected by observing the landfill’s water
level because it may be seeping at a similar rate at which
precipitation enters.
In addition, no evidence was provided that
convinces us that the layers of shale, gravel,
silt,
sand and
clay underneath the landfill are impermeable.
(Pet.
at Exhibit
9
7,
pp. 3~2,3~3.yTherefore,
vertical migration is possible.
The Board notes that it has previously allowed temporary
relief from background concentrations.
(Gallatiri National
Company v.
Fulton County Board and the County of Fulton, PCB 901-
183(January
18,
1991).)
However, Gallatin is distinguishable
from the present matter in that the Board temporarily relieved
the petitioner from background concentration data,
and restricted
the scope
of its decision to 35 Ill. Adm.
Code 812.317(1).
(i~..
at 10.).
In addition, Gallatin’s proposed landfill, although
located in an area previously mined for coal,
had an engineered
liner,
a surrounding area consisting of impermeable clay, and the
landfill was located away from any surface drainage.
(~~)
Therefore, the conditions are not comparable to the present
matter.
Level of Justification
As LSI correctly asserted, the two levels of justification
presume the presence of groundwater in the area at issue.
(Reply
at 4.)
However,
LSI has not answered the threshold question of
whether groundwater or an aquifer of concern was found within the
zone of attenuation.
Therefore,
at this time, the Board finds
that the level of justification was not met
in this matter.
However, we do recognize that, due to the area’s history of
mining, water found within the zone of attenuation has not
served, and likely will not serve, as a source of drinking water.
CONCLUSION
After a careful reading of the record, the Board hereby
denies an adjusted standard from the requirement of establishing
background concentrations for groundwater pursuant to 35
Ill.
Adm. Code 811.320(d).
Petitioner failed to prove the non-
existence of groundwater or an aquifer of concern, thereby
necessitating relief from background
concentration requirements.
This denial does not preclude LSI from filing a new petition for
an adjusted standard,
if circumstances should change.
This opinion constitutes the Board’s findings of fact and
conclusions of law.
5Although petitioner’s witness,
Mr.
Duo Vu, asserted that
a layer of
impermeable blue clay was discovered and documented,
no evidence of the
existence of
a layer of blue clay was found
in the record,
or provided after
hearing.
(Tr.
at 42—44).
10
ORDER
The Board hereby denies Lone Star Industries Inc.’s request
for an adjusted standard from 35
Ill.
Adin.
Code 811.320(d).
IT IS SO ORDERED.
Section 41 of the Environmental Protection Act
(415 ILCS
5/41
(1992)) provides for the appeal of final Board orders within
35 days of the date of service of this order.
The Rule of the
Supreme Court of Illinois establish filing requirements.
(See
also
35 Ill. Adm. Code 101.246, Motions for Reconsideration.)
I, Dorothy Gunn,
Clerk of the Illinois Pollution Control
Board,
hereby certify that the ab~veopinion and order was
adopted on the
~
day of
~
,
1995,
by a vote of
~
~.
~X~?
Dorothy M. G~nn,Clerk
~‘
Illinois Pct~lutionControl Board