1. RECEIVED
      2. PCB 04-88(APPEAL FROM IEPA(DECISION GRANTINGNPDES PERMIT)
      3. NOTICE OF FILING
      4. THIS FILING IS BEING SUBMITTED ON RECYCLED PAPER
      5. PETITIONERS’ MOTION FOR SUMMARY JUDGMENT
      6. Standard of Review
      7. Procedural Background
      8. Argument
      9. 1. Illinois EPA Complied with Anti-Degradation Regulations
      10. Conclusion
      11. The Village ofNew Lenox
      12. CERTIFICATE OF SERVICE
      13. BEFORE THE ILLINOIS POLLUTION CONTROL BO.~&~~’SOFFICE
      14. RESPONSE OF VILLAGE OF NEW LENOX TO PETITIONERS’ STATEMENT OF
      15. RELEVANT FACTS FROM THE AGENCY RECORD
      16. ANSWER:
      17. System. HR 005, 115.
      18. ANSWER:
      19. New Lenox agrees with this fact and notes that its plant is located at 301 North
      20. Cedar Road. HR 005.
      21. ANSWER:
      22. segment of Hickory Creek to which New Lenox will discharge. See HR 371, 699.
      23. ANSWER:
      24. New Lenox agrees with this fact. At the time of the application for expansion at
      25. in New Lenox. The area to be served was within New Lenox’s FPA, and New Lenox
      26. expansion. HR 005.
      27. New Lenox agrees that Illinois EPA reported that Hickory Creek is found on the
      28. entry of 0.87 instead of7.87.
      29. ANSWER:
      30. This statement is a mischaracterization of the comment in this proceeding. New
      31. Comments concerning algae were considered by Illinois EPA, and addressed in its
      32. by the plant. PR 639.
      33. from New Lenox, is the location of a dam. Dams are one aquatic feature that are
      34. associated with algae.
      35. comments were unsworn and not subject to questioning or cross-examination.
      36. ANSWER:
      37. discharge and the latest data is from six years before the permit was issued.
      38. Neither Illinois EPA’s “trigger value” nor a criterion recommended by U.S. EPA
      39. stream conditions.” HR 365. See also PR 639.
      40. Illinois EPA properly weighed Petitioners’ comments, and concluded that there is
      41. these dischargers.
      42. ANSWER:
      43. New Lenox agrees that the results of a grab sample of its effluent were 2.76
      44. 513, 545. As New Lenox’s consultant pointed out, it is misleading to compare
      45. on fourth ofthe upstream total phosphorus. PR. 632-33.
      46. Concentrations of phosphorus in effluent can be highly variable and dependent on
      47. aware of other dischargers upstream and downstream ofNew Lenox.
      48. ANSWER:
      49. New Lenox does not dispute that the Professors made the cited statements.
      50. comparisons. PR 635. The conclusion that there will be “substantial effects on
      51. nutrients to all of these waterbodies.
      52. and uncertain, and Illinois EPA has acknowledged “major knowledge gaps.” HR 356.
      53. that show gas bubble disease in fish from supersaturation. HR 068 and 361.
      54. This conclusory statement is based on an unsworn comment from Petitioners in the
      55. therefore drawing direct conclusions between sites may not be valid. HR 369.
      56. This statement is inaccurate. Illinois EPA requested and received a recent valid
      57. study from New Lenox, performed by its consultant Earth Tech.
      58. Lenox’s consultant. Those differences included the manner in which the MBI was
      59. PR 665; See also 671, 674-75.
      60. Creek. HR 370; PR 019.
      61. minor variations in procedure.
      62. ANSWER:
      63. See Resp. par. 17 and 18. In addition, New Lenox notes that the preferred
      64. relied upon by Illinois EPA.
      65. ANSWER:
      66. This paragraph contains inappropriate characterizations on the state of mind of
      67. reflected in the NPDES Permit, Responsiveness Summary and the Anti-Degradation
      68. Assessment.
      69. The record contains extensive evidence of appropriate Agency deliberations,
      70. permit limit was included in the permit. With respect to the Des Plaines River,
      71. consideration ofpotential impacts would be entirely speculative.
      72. Illinois EPA considered the U.S. EPA method as well as this comment. In its
      73. Twait’s memorandum concerning water quality based effluent limits, Illinois EPA
      74. likely to cause a violation of water quality standard.
      75. New Lenox agrees with this paragraph.
      76. ANSWER:
      77. New Lenox agrees with this paragraph.
      78. ANSWER:
      79. New Lenox disputes that it did not appear at the Public Hearing. The attendance
      80. sheet shows that Mike Turley, the Wastewater Treatment Plant Superintendent, was
      81. informative and meaningful public hearing and comment period, as evidenced by
      82. Petitioners’ extensive participation and voluminous submittals.
      83. ANSWER:
      84. explained in its Responsiveness Summary. HR 352-376.
      85. New Lenox does not dispute the general summary of Petitioners’ comments, but
      86. disagrees that any Petitioners “testified,” as public comments represent unsworn
      87. company in the business of selling land application systems. HR 71.
      88. ANSWER:
      89. New Lenox does not dispute the general summary of Petitioners comments
      90. ANSWER:
      91. cross-examination. New Lenox does not dispute that Mr. Bland made the quoted
      92. Hickory Creek meet the water quality standard for dissolved oxygen. HR 364.
      93. proceeding.
      94. New Lenox does not dispute that Ms. Wentzel made the above comments and
      95. conclusions, although New Lenox disagrees with their content and notes that they
      96. See resp. to par. 26.
      97. ANSWER:
      98. New Lenox does not dispute that Ms. Wentzel submitted the above comments,
      99. Inadequate Consideration ofAlternatives
      100. ANSWER:
      101. New Lenox does not dispute that Ms. Skrukrud submitted the above comments,
      102. include limits on dissolved oxygen, total dissolved solids, and ammonia.
      103. The Village of New Lenox

RECEIVED
CLEf~K’SOFFICE
BEFORE THE ILLINOIS POLLUTION CONTROL
BOAIth~Y252005
DES PLA1NES RIVER WATERSHED
ALLIANCE, LIVABLE COMMUNITIES
ALLIANCE, PRAIRIE RIVERS
NETWORK, and SIERRA CLUB
Petitioners
v.
)
ILLINOIS ENVIRONMENTAL PROTECTION
AGENCY and VILLAGE OF NEW LENOX
Respondents.
PCB 04-88
(APPEAL FROM IEPA
(DECISION GRANTING
NPDES PERMIT)
NOTICE OF FILING
Ms. Dorothy M. Gunn
Illinois Pollution Control Board
James R. Thompson Center
100 West Randolph Street
-
Suite 11-500
Chicago, IL 60601
Albert F. Ettinger, Senior Attorney
Environmental Law and Policy
Center ofMidwest
35
B. Wacker Drive
-
Suite 1300
Chicago, IL 60601
Hearing Officer
Illinois Pollution Control Board
James R. Thompson Center
100 West Randolph Street
-
Suite 11-500
Chicago, IL 60601
PLEASE TAKE NOTICE
that on Wednesday, May 25, 2005, we filed the attached
The Village of New Lenox’s Memorandum ofLaw In Opposition To Petitioner’s Motion
For Summary Judgment
and
Response ofVillage of New Lenox To Petitioners’ Statement
Of Relevant Facts From The Agency Record with
the Clerk ofthe Pollution Control Board, a
copy ofwhich is herewith served upon you.
Respectfully Submitted,
Roy M. Harsch
Sheila H. Deely
GARDNER CARTON & DOUGLAS LLP
191 N. Wacker Drive
-
Suite 3700
Chicago, Illinois 60606
(312) 569-1000
,~e ~
Sheila H. Deely
)
)
)
)
)
)
STATE OF ILLINOIS
Pollution Control Board
)
)
)
)
THIS FILING IS BEING SUBMITTED ON RECYCLED PAPER

RECE~VED
CLERK’S OFFICE
BEFORE THE ILLINOIS POLLUTION CONTROL
BOARD
MAY 252005
DES PLAINES RIVER WATERSHED ALLIANCE,
)
STATE OF ILLINOIS
LIVABLE COMMUNITIES ALLIANCE,
)
Pollution Control
Board
PRAIRIE RIVERS NETWORK, and SIERRA CLUB,
)
)
Petitioners,
)
)
v.
)
PCB04-88
)
(NPDES Permit Appeal)
ILLINOIS ENVIRONMENTAL PROTECTION
)
AGENCY and VILLAGE OF NEW LENOX
)
)
Respondents.
)
THE VILLAGE OF
NEW LENOX’S MEMORANDUM
OF LAW
IN
OPPOSITION TO
PETITIONERS’ MOTION FOR SUMMARY JUDGMENT
The Village of New Lenox urges the Illinois Pollution Control Board to deny the
Petitioners’ Motion for Summary Judgment. The Petitioners’ motion relies on misstatement of
.what the law requires and a selective attention to their own comments in the record, all without
properly considering Illinois EPA’s response or evidence in opposition to those comments.
Petitioners are not entitled to summary judgment.
Standard of Review
In a third party permit appeal, the petitioner is required to show that the permit at issued
would violate the Act or Board regulations.
See Opinion and Order, Village ofLake Barrington
v. Illinois EPA,
PCB
05-59
(April 21, 2005);
Prairie Rivers Network v. Illinois Environmental
Protection Agency,
PCB 01-112 (August 9, 2001), affirmed by
Prairie Rivers Network v. Illinois
Pollution Control Board,
335 Ill. App.3d 391 (4th Dist. 2002). The Board’s review is based on
information before the Agency during the Agency’s statutory review period.
Id.
It is
Petitioners’ burden to establish a
prima facie
case, and only at that point is it necessary for
Illinois EPA to put forth evidence that contravenes the evidence of Petitioners.
See Browning-
CHO2/ 22386522.1

Ferris Industries, Inc. v. Pollution Control Board,
179 Ill. App.3d
598, 534
N.E.2d 616 (2d Dist.
1989).
As the record will show, Petitioners cannot meet their initial burden, but even if they
could, Illinois EPA had ample evidence to support the determinations it made concerning the
limits to be included in the permit, and those limits advocated by Petitioners that were not
necessary to accomplish the purposes ofthe Illinois Environmental Protection Act,
415
ILCS
5/1
et seq..
With respect specifically to summary judgment, this motion is an inappropriate vehicle
for resolution of a third party permit appeal. Summary judgment can only be granted where
there are no disputed issues of fact, and the movant is entitled to judgment as a matter of law.
See
Roger Stone v. Illinois EPA,
PCB 01-68 (January 18, 2001). What Petitioners have done
here is simply excise snippets of statements that may be found in the record and intersperse those
snippets with legal argument. That does not meet the requirement to establish undisputed facts.
The response to Petitioners’ Statement of Facts ought to be enough to defeat their motion. To
the extent the Board may have a different view concerning whether summary judgment may be
granted in a case such as this, New Lenox has responded with the memorandum oflaw.
Procedural Background
In June 2002, the Village of New Lenox applied to expand its treatment plant,
constructed in 1973 and located at 301 North Cedar Road. SOF ¶ 2.’ The plant was then
operating at 85 percent capacity and expansion was necessary to ensure wastewater services
were properly provided for projected development in New Lenox. The area to be served was
within New Lenox’s FPA, and New Lenox had received full approval from the Northeastern
Illinois Planning Commission for its expansion. SOF ¶
4.
Citations refer to New Lenox’s responseto each cited paragraph of Petitioners’ statement of facts.
CHO2/ 22386522.1
2

The plant discharges into Hickory Creek, which is a general use water. Hickory Creek
has a flow of 2.4 cubic feet per second (“cfs”) during critical 7Q10 flow, and is rated a “C”
stream under the Agency’s Biological Stream Characterization (“BCS”) system. SOF ¶ 1.
Hickory Creek segment GG-02 is listed on the Illinois’ impaired waters list, known as the 3 03(d)
list. The potential causes of impairment at the time of listing were nutrients, phosphorus,
nitrogen, salinity/TDS/Chlorides, TDS (chlorides), flow alterations, and suspended solids. The
potential sources associated with the impairment are municipal point sources, combined sewer
overflows, construction, land development, urban runoffYstorm sewers, hydrological/habitat
modification, and flow regulationlmodification. SOF ¶ 4. It is not listed as a biologically
significant water body in the Illinois Natural Survey publication
Biologically Sign~ficant Illinois
Streams,
and does not support any threatened or endangered species. SOF ¶ 1.
On. January
5,
2003, JEPA gave notice that it had made a tentative decision to renew the
NPDES permit issued to the Village ofNew Lenox to discharge to Hickory Creek. SOF ¶ 23.
The draft renewed permit allowed the New Lenox plant to increase its design average flow from
1.54
million gallons per day to 2.5 16 million gallons per day. During the course of the permit
proceedings, New Lenox was asked to and did perform a Water Quality Assessment ofHickory
Creek, which included sampling of Hickory Creek, and a macroinvertebrate survey to assess the
effect of the discharge of aquatic life. SOF ¶ 16-20. New Lenox also reviewed alternatives to
the discharge, including an analysis ofspray irrigation. SOF ¶ 26. Based on these reports and on
other information before Illinois EPA, Illinois EPA was able to complete its antidegradation
assessment and conclude that expansion of the plant could proceed in compliance with
regulatory requirements governing water quality. SOF ¶ 16. After having provided New Lenox
CHO2I
22386522.1
3

with an opportunity to review the proposed conditions ofthe draft NPDES permit, Illinois EPA
issued the draft permit for public notice on January
5,
2003. SOF ¶ 23.
V
Based on the comments that were received, Illinois EPA elected to hold a Public Hearing,
which took place on April 24, 2003. At the hearing, members ofthe public were provided with
and opportunity to comment and ask questions ofthe Illinois EPA staff members involved with
the permit. SOF ¶ 23. New Lenox was present at the Public Hearing, although as the applicant it
did not provide comments to Illinois EPA during the hearing. SOF ¶ 24. In Petitioners
comments, they made a variety of claims and requests, including request for nutrients limits,
copper, ammonia, total dissolved solids. Petitioners commented on algae in Hickory Creek, the
anti-degradation review, urbanization in New Lenox, the macroinvertebrate survey, and other
matters. All of these issues were properly considered by Illinois EPA—to the extent they were
relevant to the NPDES permit review—and were the subject of appropriate deliberation among
Illinois EPA staff members. All comments were ultimately addressed by the Illinois EPA as part
ofthe responsiveness summary or in the conditions ofthe final NPDES permit. SOF ¶ 29.
Illinois EPA issued its final NPDES permit on October 31, 2003. That permit included
new limits on dissolved oxygen, total dissolved solids, and ammonia, which were included to
satisfy concerns raised during the public notice and which New Lenox agreed to accept without
contest. Based on Illinois EPA’s determinations, no limitations were included for nutrients and
copper. SOF ¶ 37.
The Board’s review is heavily dependent on the Agency’s findings of fact here and
conclusions of law as found in its Responsiveness Summary and final NPDES permit, which
differ materially from Petitioners comments and conclusions. Consequently, New Lenox will
address specific public comments as part ofits response to each Petitioner argument.
CHO2/ 22386522.1
4

Argument
1.
Illinois EPA Complied with Anti-Degradation Regulations
As part of the permit review, Illinois EPA conducted an anti-degradation assessment.
Hickory Creek is not on the current list of biologically significant streams compiled by the
Illinois Department ofNatural Resources (“IDNR”), which is one relevant list for purposes of
anti-degradation, and it is not an Outstanding Resource Water. No threatened or endangered
species are present in the stream segment to which New Lenox discharges. See Resp. par. 1.
During the course of these proceedings, Illinois EPA also reviewed the science underlying its
listing of Hickory Creek on the 303(d) list, and concluded that “a revie~vof the causes of
impairment resulted in a new conclusion. Agency biologists now believe that only total
dissolved solids can be implicated as a cause of whatever impairment may exist in this stream
segment outside ofthe immediate area ofthe New Lenox outfall.” Consequently, Illinois EPA
requested that the permit incorporate limits on total dissolved solids, and New Lenox accepted
those limits.
Illinois EPA performed its anti-degradation analysis by reference to standards governing
waters that meet existing uses, and this is the appropriate classification for Hickory Creek. See
PR. 601. Illinois EPA concluded that “at the present time.
. .
the incremental nutrient loading
anticipated to result from this project is not expected to increase algae or other noxious plant
growth, diminish the present aquatic community, or otherwise aggravate existing stream
conditions.” Illinois EPA noted the continued work of the Nutrient Standards Workgroup, and
the possibility that nutrient reduction requirements would be imposed on New Lenox upon
adoption of state standards. PR. 602. Illinois EPA also concluded that alternatives to the
discharge were not feasible, and also noted the economic and social need for the expansion.
CH02/ 22386522.1
5

Petitioner contends that Illinois EPA failed to comply with anti-degradation regulations
because it did not ensure that reasonable controls were put on nutrients. As support for its
argument, Petitioner cites the “High Quality Waters” provision of Illinois Anti-Degradation
Regulations. Mem. 7. This is not the regulatory provision applicable to Hickory Creek. High
Quality Waters are those whose existing quality exceeds the state’s adopted water quality
standards, which is not the case here, and Hickory Creek does not meet this standard. See
Section 302.105(c). Instead, the antidegradation review should be based on the minimum level
ofprotection at Section 302.105(a) applicable to waters that meet existing uses.
Illinois EPA made the determination that no nutrients standards were necessary. With
respect to the uses in Hickory Creek, Petitioners argue that Illinois EPA “at a minimum should
have determined what level of phosphorus and nitrogen removal were economically reasonable
and imposed limits based on that determination.” Mem. 9. Illinois EPA explicitly determined
“the incremental nutrient loading anticipated to result from~this project is not expected to
.
aggravate existing stream conditions.” Illinois EPA completed the regulatory analysis required
under regulations governing antidegradation and considered all the comments made by the
public.
Illinois EPA also considered the nutrient data reported by New Lenox in connection with
its study. New Lenox’s effluent on the day it sampled was 2.76 milligrams per liter of total
phosphorus. The four downstream samples taken as part of the study all showed phosphorus at
values of 1.60 milligrams per liter, 1.63 milligrams per liter, 1.47 milligrams per liter, and 1.52
milligrams per liter. Addressing the available data, Illinois EPA concluded that there was
nothing unusual about stream phosphorus values such as those reported for Hickory Creek.
Further, the Illinois EPA concluded specifically in this case that “the incremental nutrient
CHO2/22386522.1
6

loading anticipated to result from this project is not expected to increase algae or other noxious
plant growth, diminish the present aquatic community or otherwise aggravate existing stream
conditions.”
More importantly, Petitioners’ arguments concerning nutrients beg the question that
regulators and the regulated alike are wrestling with. Illinois EPA and the scientific community
in general have long recognized that the science concerning nutrients and their effect on
waterbodies is both complicated and uncertain, and Illinois EPA has convened a work group to
study the issue of nutrients and develop standards that would be proposed to govern dischargers
in Illinois. Many factors come into play, including the nature of the stream and the discharge.
There is no dispute and the Illinois EPA took into consideration that the existing New Lenox
plant discharges nutrients, and increasing the capacity of the plant will increase the mass of
nutrients, but it will also increase stream flows.
In addition, during the course of the
proceedings, Illinois EPA acknowledged “major knowledge gaps” in the science concerning
nutrients. HR 356. In fact, the Board itself has concluded as much in the opinion concerning the
technology-based interim standard for phosphorus recently proposed by the Board. See Opinion
and Order, R 04-26 (April 7, 2005). Under these circumstances, it would be inappropriate to set
nutrient standards in the context ofan NPDES permit.
The Agency also fully considered the economic and technical feasibility of a range of
alternatives, including spray irrigation at farmland and a golf course, as well as alternative
discharge locations.
PR 403, 634.
Those alternatives were found to be economically
unreasonable and technical unfeasible. With respect to Petitioners’ claim that the acceptance by
other environmental communities of phosphorus limits (see Mem. 10), the records of those
proceedings are more likely to show that those communities accepted the limits not as a
CHO2I 22386522.1
7

consequence of Illinois regulatory requirements but instead as a consequence of the delay and
expense associated with the public’s regulatory involvement in the permit process, including the
right to challenge permits. The record is also likely to show that the acceptance ofpermit limits
by those communities to appease environmental groups, with the goal of allowing the
community projects to proceed in an expeditious manner, has had no discernable impact on the
quality ofthe streams to which those communities discharge.
2.
Illinois EPA’s
Permit Complies with Water
Quality Standards
As part of its determination concerning the permit’s compliance with water quality
standards, Illinois EPA requested and New Lenox voluntarily agreed to accept certain limits.
These limits include dissolved oxygen, total dissolved solids, and ammonia. Illinois EPA also
requested that New Lenox perform a study of the aquatic life in the creek. New Lenox
performed that study, which demonstrated that Hickory Creek has fish populations that are not
impaired by New Lenox’s discharge, and Hickory Creek did not have fish populations indicative
of low dissolved oxygen concentrations. HR 361. Illinois EPA concluded based on relevant data
for 2003 that all measurements in Hickory Creek meet the water quality standard for dissolved
oxygen. HR 364.
Illinois EPA nevertheless included a permit limitation governing dissolved oxygen, and
notwithstanding Illinois EPA’s determination, New Lenox elected not to challenge that permit
limitation. Illinois EPA also recommended limitations for ammonia and total dissolved solids.
Illinois EPA determined, however, that the other limits sought by Petitioners were not warranted
or appropriate. These include limits for nutrients, pH and copper.
CHO2/ 22386522.1
8

a.
Illinois EPA made the determination that no permit limits were necessary to
address “offensive conditions”
Illinois EPA made the determination that no limits were required to address offensive
conditions. To the extent Petitioners claim that algal growth constitutes an offensive condition,
Illinois EPA addressed algae in its Responsiveness Summary, explaining that algae is a vital part
of the aquatic commu~iityand algae growth in itself is not a problem; it is in relation to
dissolved oxygen and the adverse impact on fish that provides context for assessing algae.
Illinois EPA stated that “Streams would be expected to exhibit either one kind of algal growth or
another,” depending on a variety offactors, and “the best measure ofwhether fish are adversely
impacted is to look at the local fish population. Hickory Creek has fish populations that are not
indicative of low dissolved oxygen concentrations.” HR 361.
Further, the Illinois EPA
concluded specifically in this case that “the incremental nutrient loading anticipated to result
from this project is not expected to increase algae or other noxious plant growth, diminish the
present aquatic community or otherwise aggravate existing stream conditions.” PR
565.
So long
as Illinois EPA has appropriately considered Petitioners comments and reviewed information on
the water quality in Hickory Creek, its decision is reasonable and should be upheld.
See Ohio
River Valley Environmental Coalition v. Callaghan,
133 F.Supp.2d 442 (S.D. W. Va. 2001).
Even were Petitioners claims concerning algae as true, it is reasonable for Illinois EPA to
determine that no nutrient limitations were appropriate for New Lenox. Illinois EPA is aware of
other dischargers to the stream as well as conditions in the stream. Under these circumstances, a
solution to any algae problem would be more appropriately imposed stream-wide, rather than
imposing limitations on one discharger not expected to contribute to any existing problem.
See,
e.g., Communities for a Better Environment v. State Water Resources Control Board,
109 Cal.
App.4t’~1089, 1 Cal. Rptr. 3d 76 (Cal 1st Dist. 2003).
CHO2/ 22386522.1
9

It is also worth noting that given the complicated and disputed nature of the science
governing nutrients and their effects, including algae, Illinois EPA has convened a work group to
perform the work necessary to propose scientifically defensible standards for Illinois. In any
case, it is important that any nutrient standards be set in the context ofa rulemaking, not a permit
appeal before the Board. The question of what regulatory limits are appropriate for Illinois is
unresolved and surrounded by scientific uncertainty. Contrary to Petitioners’ arguments, for
Illinois EPA to have set limits on phosphorus in New Lenox’s permit in the absence of a
rulemaking (and a better understanding of the science) would have been a reversible error.
Illinois EPA made the determination that nutrient limitations were not necessary to accomplish
the purposes of the Act. Other state courts have considered this issue and made the finding that
application of such a standard would be rulemaking, requiring compliance with the procedural
requirements governing an agency’s issuance of a rule.
Simpson Tacoma Krafi Co. v.
Washington Dept. of Ecol.,
119 Wash.2d 640, 835 P.2d 1030, 1034-36 (Wash. 1992);
Wisconsin
Elec. Power Co. v. Dept. of Natural Resources,
287 N.W.2d 113 (Wis. 1980). Petitioners’
citation
of PUD No. 1 of Jefferson County v. Washington Dept. ofEcol.,
511 U.S. 700 (1994) is
inapposite, as that case considered imposition of a standard requiring minimum stream flows,
which is easily applied.
V
To the extent it is relevant, Illinois EPA also concluded that no permit limitations were
necessary for pH. Sampling performed by Illinois EPA at the U.S.G.S. stream gauge in Joliet,
approximately seven miles downstream from New Lenox’s discharge point, showed that during
the period of record, average pH was 7.8. PR 640. While there were a handful of pH levels
detected above 9.0 during the extensive time period of this data, Illinois EPA pointed out that in
some environments, a pH over 9.0 is not an unnatural condition. Illinois EPA also stated that its
CHO2/ 22386522.1
10

monitoring station on the lower part of Hickory Creek may not have similar morphology to the
area around New Lenox, and therefore drawing direct conclusions between sites may not be
valid. HR 369. Finally, New Lenox’s pH sampling in connection with its water quality report
showed pH ranging from 6.77 to 8.21 in the vicinity ofNew Lenox’s plant.
b.
Illinois EPA determined that
New
Lenox did not have a reasonable potential
to contribute to violations of copper limits
As part of Illinois EPA’s review ofNew Lenox’s application for expansion, Illinois EPA
also considered whether New Lenox had the reasonable potential to violate water quality
standards for copper. In its Responsiveness Summary, Illinois EPA concluded that for the
chronic standard at issue here, on an average basis, the effluent is not likely to exceed the water
quality standard and therefore would not cause a violation of that standard. HR 363.
Petitioners continue to advocate application of the U.S. EPA’s “reasonable potential to
exceed” analysis, notwithstanding that it is inappropriate for application here and would yield
artificially high results. In Scott Twait’s memorandum concerning water quality based effluent
limits, Illinois EPA specifically considered the U.S. EPA method to assess the “reasonable
potential to violate water quality standards,” that Petitioners advocate. Illinois EPA applied its
policy and decided that it would not use the high multiplier used in U.S. EPA’s method because
that method does not yield valid results when only a small sample population exists. Illinois
EPA also concluded specifically concerning this facility that there was a low risk its effluent
would have high levels ofmetals. PR 509. Illinois EPA’s analysis of the sample results and its
specific consideration ofthe type of facility and the nature of its discharge were the appropriate
analysis to comply with the water quality standard. No permit limit was necessary for copper.
CHO2/ 22386522.1
.
11

Conclusion
The Board must review the Illinois EPA’s decision by deferring to the Agency’s findings
of fact here and conclusions of law, which differ materially from Petitioners arguments in its
motion for summary judgment. Illinois EPA complied with all regulatory requirements in its
issuance of the NPDES permit to New Lenox to allow expansion of its wastewater treatment
facility. Hickory Creek is a general use stream, not a high quality water, and is properly assessed
for purposes of antidegradation by applying regulatory standards to ensure the minimum level of
protection. Illinois EPA properly completed that review by assessing its own information
concerning Hickory Creek, as well as reviewing a Water Quality Assessment that it requested
from New Lenox. New Lenox also provided information on alternatives to the discharge,
including spray irrigation, and Illinois EPA properly concluded that those alternatives were not
feasible. As a result of its review, Illinois EPA requested that the permit incorporate limits on
dissolved oxygen, total dissolved solids, and ammonia. New Lenox accepted those limits.
The Board should also appreciate the complicated and disputed nature ofthe science
governing nutrients and their effects, including algae, and the importance ofsetting those
standards in a reasoned manner that is scientifically defensible. Illinois EPA has convened a
work group to perform the work necessary to propose scientifically defensible standards for
Illinois, and nutrient standards to be set in the context ofa rulemaking, not a permit appeal
before the Board.
Respectfully submitted,
The Village ofNew Lenox
By: ____________________________
One of Its Atto eys
CHO2/22386522.1
12

Roy M. Harsch
Sheila H. Deely
Gardner Carton & Douglas LLP
191 N. Wacker Drive
Suite 3700
Chicago, IL 60606
(312) 569-1000
CHO2I
22386522.1
13

CERTIFICATE OF SERVICE
The undersigned certifies that a copy ofthe foregoing Notice
of Filing and
the
attached
The Village of
New Lenox’s
Memorandum of Law In Opposition To
Petitioner’s Motion For Summary Judgment
and Response
ofVillage of New Lenox To
Petitioners’ Statement Of Relevant Facts From The Agency Record
was filed by hand
delivery with the Clerk ofthe Illinois Pollution Control Board and served upon the parties to
whom said Notice is directed by electronic and regular mail on
Wednesday, May 25, 2005.
~AL~(
CHO1/ 12425982.1

BEFORE THE ILLINOIS POLLUTION CONTROL BO.~&~~’SOFFICE
MAY 25 2005
DES PLAINES RIVER WATERSHED ALLIANCE,
)
LIVABLE COMMUNITIES ALLIANCE
)
rollution
STATE OF
Control
ILLINOIS
Bo
PRAIRIE RIVERS NETWORK, and SIERRA CLUB,
)
)
Petitioners,
)
)
v.
)
PCB04-88
)
(NPDES Permit Appeal)
ILLINOIS ENVIRONMENTAL PROTECTION
)
AGENCY and VILLAGE OF NEW LENOX
..
)
)
Respondents.
)
RESPONSE OF VILLAGE OF NEW LENOX TO PETITIONERS’ STATEMENT OF
RELEVANT FACTS FROM THE AGENCY RECORD
1.
Hickory Creek, a tributary ofthe Des Plaines River which flows in Will County,
was once known for its exceptionally high water quality and biological integrity. Phillip Smith,
a scientist ofthe Illinois Natural History Survey wrote in 1971 that “Prairie and Jackson Creeks
have good species diversity, but Hickory Creek is the outstanding stream in the Des Plaines
River system and contains populations of such unusual species as the northern hogsucker,
rosyface shiner, and slender madtom.” (HR1 15)
ANSWER:
The cited information appears to be a very brief conclusion in an abstract that was
inserted into the record. New Lenox has no reason to agree or disagree with the cited
conclusion, which is of limited relevance given the time.period it references, the absence of
the location along Hickory Creek and data on which it was based, the absence ofthe author
in this proceeding, or other relevant information. However, for regulatory purposes it is
important to note that Hickory Creek is not on the current list of biologically significant
streams compiled by the Illinois Department of Natural Resources (“IDNR”), Natural
History Survey in the publication
Biologically Significant Illinois Streams.
This list is
relevant for purposes of anti-degradation, and IDNR has further concluded that no
threatened or endangered species exist in the vicinity of the segment of Hickory Creek to
CHO2/ 22387197.1

which New Lenox will discharge. See HR 005, 371. Hickory Creek is a general use and is
rated as a “C” stream by Illinois EPA under its Biological Stream Characterization
System. HR 005, 115.
2.
New Lenox Sewage Treatment Plant #1 was built in 1973. (HR 81)
ANSWER:
New Lenox agrees with this fact and notes that its plant is located at 301 North
Cedar Road. HR 005.
3.
Dr. David Bardack, formerly ofthe University ofIllinois at Chicago Circle, wrote
in 1982 that “Studies ofthe Hickory Creek ecosystem are widely recognizedbeyond the Chicago
area. In fact, Hickory Creek has attained the status of a classic biological study area.... As a
relatively unpolluted and unaltered stream with a diversified fauna....” (HR 108)
ANSWER:
New Lenox has no reason to agree or disagree with the cited conclusion, which is of
limited relevance given the time period it references, the absence of the location along
Hickory Creek and data on which it was based, the absence of the author in this
r
proceeding, or other relevant information. Hickory Creek is not on the current list of
biologically significant streams compiled by the Illinois Department of Natural Resources,
L
which is one list that by regulation is relevant for purposes of anti-degradation, and IDNR
has further concluded that no threatened or endangered species exist in the vicinity of the
segment of Hickory Creek to which New Lenox will discharge. See HR 371, 699.
4.
New Lenox Sewage Treatment Plant #1 has been expanded since 1991. (HR
5)
CHO2/ 22387197.1
2

ANSWER:
New Lenox agrees with this fact. At the time of the application for expansion at
issue in this proceeding, the plant was operating at 85 percent capacity, and expansion was
necessary to ensure wastewater services were properly provided for projected development
in New Lenox. The area to be served was within New Lenox’s FPA, and New Lenox
received full approval from the Northeastern Illinois Planning Commission for its
expansion. HR 005.
5.
Hickory Creek is found on the draft 2002 Illinois 3 03(d) list of impaired waters.
“The causes of impairment given
...
at that time were nutrients, phosphorus, nitrogen,
salinity/TDS/Chlorides, TDS (chlorides), flow alterations, and suspended solids. The sources
associated with the impairment are municipal point sources....” (HR
5)
In the Illinois Water
Quality Report 2004, Hickory Creek is listed as impaired with the potential causes ofimpairment
being silver, nitrogen, pH, sedimentationlsiltation, total dissolved solids, chlorides, flow
alterations, physical-habitat alterations, total fecal coliform bacteria, total suspended solids,
excess algal growth, and total phosphorus.
ANSWER:
New Lenox agrees that Illinois EPA reported that Hickory Creek is found on the
draft 2002 Illinois 303(d) list, reportedly based on a study performed in 1991. The selected
quote is misleading in that it omits the numerous other sources generally associated with
the listing. Discovery in this case could be expected to show the basis for the listing, the
additional sources to the stream, and other information relevant to this case. In addition,
Illinois EPA concluded during the permit proceedings that “a review of the causes of
impairment resulted in a new conclusion. Agency biologists now believe that only total
dissolved solids can be implicated as a cause ofwhatever impairment may exist in this
stream segment outside of the immediate area of the New Lenox outfall.” HR 360. New
CHO2/22387197.1
3

Lenox voluntarily agreed to accept a limit in the permit on total dissolved solids. New
Lenox notes that the cited 2004 Water Quality Report was issued after the NPDES permit
challenged in this case was issued. In addition, Illinois EPA has reported that the inclusion
of pH as a potential cause of impairment was a mistake based on an erroneous database
entry of 0.87 instead of7.87.
6.
A number ofwitnesses gave reports of algal blooms in Hickory Creek including
nearby resident Kim Kowalski. (HR 76)
ANSWER:
This statement is a mischaracterization of the comment in this proceeding. New
Lenox agrees that a few commenters reported “algae,” but “algal blooms” have not been
the subject of comment. Further, as pointed out by New Lenox’s consultant, sampling
performed in August 2002 for purposes of the water quality study observed there were no
visible signs of organic growth or over-nutrification at the plant discharge site. PR 515,
633.
Comments concerning algae were considered by Illinois EPA, and addressed in its
Responsiveness Summary. In the Responsiveness Summary, Illinois EPA stated that algae
is a vital part of the aquatic community and algae growth in itself is not problematic; it is
in relation to dissolved oxygen and the adverse impact on fish that provides context.
Illinois EPA stated that “Streams would be expected to exhibit either one kind of algal
growth or another, i.e. planktonic or periphyton” depending on a variety of factors, and
“the best measure of whether fish are adversely impactedj is to look at the local fish
population. Hickory Creek has fish populations that are not indicative of low dissolved
oxygen concentrations.” HR 361. Illinois EPA also concluded based on relevant data for
CHO2/ 22387197.1
4

2003 that all measurements in Hickory Creek meet the water quality standard for dissolved
oxygen. HR 364. Finally, to the extent algae was observed in August, those observations
were more likely due to low flow conditions and solar heating, not to nutrients discharged
by the plant. PR 639.
7.
Jim Bland, Director of Integrated Lakes Management, testified that “I should
comment that as recently as August of this year I saw something unique in-stream, something I
have not seen before. The entirety ofthe stream is covered from Pilcher Park almost all the way
up to Cedar Street with Hydrodictyon and algae on the surface ofit. So here you have a running
stream covered almost completely and a running stream that’s really a very, very viable and
important resource, pretty sadly degraded by the sorts of nutrient discharge that we are seeing.”
(HR 80)
ANSWER:
See response to
par.
6.
Additionally, New
Lenox disagrees that Mr. Bland
“testified,” as his
comments were unsworn and not subject to questioning or cross-
examination. In addition, Pilcher Park, which is located about
two
miles
as
the crow flies
from New Lenox, is the location of a dam. Dams are one aquatic feature that are
associated with algae.
8.
Community resident Brad Salamy testified at the hearing that, “Last summer, and
this was alluded to earlier, the creek was greener than I had ever seen it, a little patch down the
center was liquid, the rest ofit was completely green like you could walk on it.” (HR 82-3)
ANSWER:
V
See response to
par.
6. New Lenox disagrees
that Mr. Salamy “testified,”
as his
comments were unsworn and not subject to questioning or cross-examination.
9.
Phosphorous concentrations are high in the creek. In addition to the IEPA
impaired water data discussed above (~J5),the U.S. Geological Survey database shows that for
the period of ‘92 to ‘97 total phosphorus exceeded Illinois’ EPA trigger value for more than 20
percent of the samples. Illinois EPA’s trigger is approximately eight times higher than the
USEPA’s recommended criterion. Furthermore, data collected in August 2002 by the Village of
CHO2/ 22387197.1
5

New Lenox indicate the total phosphorus instream on that particular day when they sampled was
between 1.49 and 1.63 milligrams per liter. These concentrations are approximately 20 times the
USEPA-recommended criterion and more than twice Illinois EPA’s trigger. (Wentzel Testimony
HR 67)
ANSWER:
This paragraph’s characterization of phosphorus values as “high” in the Creek does
not constitute a fact but merely a characterization by the statement’s author. The cited
data is from Illinois EPA’s samples at U.S.G.S. gauge 05539000 in Joliet, Illinois, which is
published by U.S.G.S. under mutual agreement with Illinois EPA. HR 129, 365. This
monitoring station is located approximately seven miles downstream of New Lenox’s
discharge and the latest data is from six years before the permit was issued.
Neither Illinois EPA’s “trigger value” nor a criterion recommended by U.S. EPA
constitute regulatory standards in Illinois or are relevant here. Illinois EPA’s trigger value
is a tool for ranking streams.
It is based on the
85th
percentile of values recorded for
phosphorus. It has absolutely nothing to do with the impact of phosphorus on a stream or
a cause/effect relationship. Illinois EPA noted that even within the various ecoregions
utilized by U.S. EPA, “the national criteria recommendations are based on statistical
distribution and recurrence frequencies, not direct relationship to detrimental or impaired
stream conditions.” HR 365. See also PR 639.
Illinois EPA properly weighed Petitioners’ comments, and concluded that there is
nothing unusual about stream phosphorus values such as those reported for Hickory
Creek. Illinois EPA is also aware of the other dischargers to the Creek, and their location
both upstream and downstream of New Lenox, and discovery could be expected to address
these dischargers.
10.
Sampling by the applicant’s contractor, Earth Tech, conducted in August of2002
found 2.76 milligrams per liter of total phosphorus in the effluent, almost twice the upstream
CHO2/22387197.1
6

concentration on that day and six times the average over time for that particular stream
(Wentzel Testimony HR 68)
ANSWER:
New Lenox agrees that the results of a grab sample of its effluent were 2.76
milligrams per liter of total phosphorus in the effluent on the date sampled, and notes that
the four downstream samples showed phosphorus at values of 1.60 milligrams per liter,
1.63 milligrams per liter, 1.47 milligrams per liter, and 1.52 milligrams per liter. See PR
513, 545.
As New Lenox’s consultant pointed out, it is misleading to compare
concentrations in the creek and in the plant effluent when the flows are not the same, and
had flows been considered, the total phosphorus from the plant effluent would have been
on fourth ofthe upstream total phosphorus. PR. 632-33.
Concentrations of phosphorus in effluent can be highly variable and dependent on
flows, the time of day and a host of other facts, and a grab sample can be expected to result
in limited information. New Lenox notes that phosphorus is not an acute pollutant, and it
is long-term average values that would be more critical. In addition, the Illinois EPA is
aware of other dischargers upstream and downstream ofNew Lenox.
11.
Comments by Professors David Jenkins and Michael Lemke of the Biology
Department, University ofIllinois at Springfield stated:
Based on the New Lenox August data, the current plant releases an average of 64.7
kg of nitrate+nitrite per day and 16.1 kg oftotal P total phosphorus into Hickory
Creek.
Based on long-term average August flow data from USGS and USGS Schmuhl
Road nutrient analyses, current Hickory Creek nutrient loads upstream from the
WWTP#1 are 151 kg nitrate+nitrite, and 22.7 kg total P.
Therefore, the plant is responsible for 30 of downstream nitrate+nitrite load in
Hickory Creek, and 41 ofthe Hickory Creek total P load.
CHO2/22387197.1
7

As currently planned (and assuming nutrient levels in plant discharge remain the
same), the new plant discharge will release 105.7 kg of nitrate+nitrite per day and
26.3 kg of total P per day into Hickory Creek. Assuming that Hickory Creek flow
will not change for reasons other than the planned extra plant discharge, the new
plant discharge will release 41 ofthe stream nitrate+nitrite load, and 53.7 ofthe
stream P load on an average basis.
More importantly, the same-sized receiving stream will be bearing 170 the levels
ofnitrate+nitrite upstream of the plant, and 216 of the total P levels upstream of
the plant.
These levels of nutrient loading will have substantial effects on
downstream water quality, not only in Hickory Creek, but also the Des Plaines
River and the Illinois River. The Hickory Creek channel will also be receiving
substantially more flow, which will have effects on stream habitat and biota that are
separate from nutrient effects.
Summary of Hickory Creek Water Quality Information, David Jenkins and Michael
Lemke (HR 304-305)
ANSWER:
New Lenox does not dispute that the Professors made the cited statements.
However, the conclusions in these comments are based on questionable or undisclosed
assumptions, and discovery would be necessary to show what support these comments are
based on, mathematically and otherwise. New Lenox’s consultant pointed out several areas
where the Professors used incorrect assumptions, including the flow used and invalid data
comparisons.
PR 635.
The conclusion that there will be “substantial effects on
downstream water quality” in Hickory Creek, the Des Plaines River and the Illinois River
is of very questionable and undisclosed scientific and mathematical support. In any case,
the Illinois EPA considered these comments and
is
aware of point and non-point sources of
nutrients to all of these waterbodies.
12.
Published treatises placed in the record show that elevated nutrient levels cause
impairment ofstreams.
.
“Eutrophication is a fundamental concern in the management of all water
bodies.... There is now also considerable interest in the enrichment of streams
and rivers (see discussion by Dodds and Welch 2000). For example in 1992, the
United States Department of Agriculture National Water Quality Inventory
CHO2/ 22387197.1
8

reported that enrichment and sedimentation were the most significant causes of
water quality degradation in 44
of 1,000,000 km of streams and rivers
surveyed in the US (http://www.usda.gov/stream_restoration).
Management
problems caused by nutrient
enrichment, and associated benthic algal
proliferations, include aesthetic degradation..., loss of pollution-sensitive
invertebrate taxa through smothering of substrata by algae
...,
and degradation of
water quality (particularly dissolved oxygen and pH) resulting in fish kills....”
Biggs, B.J.F. 2000. Eutrophication of streams and rivers: dissolved nutrient-chlorophyll
relationships for benthic algae.
J. North Am. Benthol. Soc.
19:17-3 1. (HR 187)
“Reasons for nutrient criteria include: 1) adverse effects on humans and domestic
animals, 2) aesthetic impairment, 3) interference with human use, 4) negative
impacts on aquatic life, and
5)
excessive nutrient input into downstream systems.”
Dodds, W. K. and E.B. Welch. 2000. Establishing nutrient criteria in streams. .J
North
Am. Benthol. Soc.
19:186-196. (HR 177)
“High algal growth can affect fish distribution by altering the physical (algal mass
accumulation) and chemical (dissolved oxygen, pH) characteristics of the river
system.”
Sabater, S., J. Armengol, E. Comas, F. Sabater, I Urrizalqui, and I. Urrutia. 2000. Algal
biomass in a disturbed Atlantic river: water quality relationships and environmental implications.
Science of the Total Environment.
263: 185-195. (HR 210)
There is a positive correlation between nutrients in streams and algal activity.
“The present analysis suggests that managing nutrient supply could not only
reduce the magnitude of maximum biomass, but also reduce the frequency and
duration ofbenthic algal proliferations in streams.”
Biggs, B.J.F. 2000. (HR 187)
“...
our study indicates that there is a generally positive relationship between Chl
chlorophyll and TP total phosphorus in temperate streams
...“
Van Nieuwenhuyse, E.E. and J.R. Jones. 1996. Phosphorus-chlorophyll relationship in
temperate streams and its variation with stream catchment area.
Can. J. Fish. Aquat. Sci. 53:99-
105. (HR 206)
“If streams are not turbid, preventing maximum benthic chlorophyll levels from
exceeding 200 mg/m2 is reasonable because streams with higher levels are not
aesthetically pleasing, and their recreational uses may be compromised. For
benthic chlorophyll to remain below 200 mg/m2 at the very least, TN should
remain below 3 mg!L and TP below 0.4 mg/L.”
Dodds, W. K. and E.B. Welch. 2000. (HR 184)
CHO2/22387197.1
9

“Photosynthesis and respiration are the two important biological processes that
alter the concentration of oxygen and carbon dioxide. In highly productive
waters, such as slow moving rivers with abundant macrophytes, oxygen is
elevated and carbon dioxide is reduced during the daytime, while the reverse
occurs at night.”
Allan, J. D.,
1995. Stream Ecology: structure andfunction ofrunning waters.
Chapman
& Hall, New York (HR 163)
“Die! (24 h) changes in oxygen concentration provide a means of estimating
photosynthesis and respiration ofthe total ecosystem...”
(Allan, J. D. HR 163)
“Carbon dioxide likewise tends to deviate from atmospheric equilibrium in highly
productive lowland streams where luxuriant growths of macrophytes and
microbenthic algae can result in diel shifts in dissolved C02.... Because of the
interdependence ofCO2 concentration and pH
...,
mid-day pH can increase by as
much as 0.5 units.”
(Allan,J.D. HR 164)
“Dissolved 02 deficit and high pH are perhaps the most severe algal-related
problems affecting the aquatic life-support characteristics of a river or stream.
Deficits of DO can occur when respiration of organic C produced by
photosynthetic processes in the stream exceeds the ability of reaeration to supply
DO.”
(Dodds, W. K. and E.B. Welch. HR 180)
“The contribution of algal biomass~to the die! dissolved oxygen (DO) variability
in rivers is common in systems receiving high nutrient inputs....”
Sabater, S., J. Armengol, E. Comas, F. Sabater, I Urriza!qui, and I. Urrutia. 2000.
(HR216)
V
ANSWER:
New
Lenox agrees that the
state in response to
draft criteria by
U.S.
EPA is moving
forward to develop nutrient standards and has convened a study group that includes
stakeholders from numerous areas, including persons that commented in this proceeding.
New Lenox agrees that published statements were placed in the record by Petitioners, but
they are of limited usefulness since they are not directed at this stream or this effluent, they
CHO2/ 22387197.1
10

are unsworn and unverified, and they are generally more appropriately considered in the
context of setting generally applicable standards for nutrients, not deriving water quality
limits for one discharger along a stream with many dischargers. The provided snippets of
statements from these studies do not change the fact that the science concerning nutrients,
algal growth, dissolved oxygen levels, stream types, and other factors is both complicated
and uncertain, and Illinois EPA has acknowledged “major knowledge gaps.” HR 356.
Further, the Illinois EPA concluded specifically in this case that “the incremental nutrient
loading anticipated to result from this project
is
not expected to increase algae or other
noxious plant growth, diminish the present aquatic community or otherwise aggravate
existing stream conditions.” PR 565. Finally, both Illinois EPA and the Board have
concluded as much with respect to the uncertain science surrounding nutrients in the
opinion concerning the Board’s proposal of a technology-based interim standard for
phosphorus. See Opinion and Order, R 04-26 (April
7, 2005).
13.
It is likely that nutrient discharges from New Lenox WWTP #1 are already
adversely impacting Hickory Creek and that reductions of nutrient discharges are needed to
prevent further impact. (Statement ofProfessors Jenkins and Lemke HR 305)
ANSWER:
See responses
to 11 and
12. This
statement is an unfounded characterization and
conclusion, submitted in an unsworn comment, and
is contrary to Illinois EPA’s
conclusion. The conclusion
does
not explain what the adverse impacts are, and New
Lenox’s studies
and
submissions showed
the opposite. HR 361, 364. Based on the
macroinvertebrate survey performed
by New
Lenox at the request of Illinois EPA at the
location of the discharge, pollution intolerant organisms are present both upstream and
downstream ofthe existing discharge. PR
572.
CHO2/22387197.1
11

14.
The IEPA at the hearing on the draft permit acknowledged that it was “very
possible” that supersaturated oxygen levels found during the daytime hours in Hickory Creek are
due to algae saturation photosynthesis. (HR 67)
ANSWER:
New
Lenox
agrees that Mr.
Bob Mosher of Illinois EPA acknowledged that it
is
“very possible
that algae saturation
photosynthesis
had a part
in
levels of supersaturated
dissolved oxygen levels
during the period of 1979 to
1997” as reported in the
data taken at
the U.S.G.S. stream gauge approximately seven miles in Joliet downstream from
New
Lenox. To put the statement in context, in response to follow up questioning and in the
Responsiveness Summary, Mr. Mosher also stated that he was not aware of any studies
that show gas bubble disease in fish from supersaturation. HR 068 and 361.
15.
Hickory Creek also violated pH standards by exceeding a pH of 9, likely as the
result ofalgal activity. (HR 126)
ANSWER:
This conclusory statement is based on an unsworn comment from Petitioners in the
record. It appears to be derived from Illinois EPA’s sampling at the U.S.G.S. stream gauge
in Joliet, approximately seven miles downstream from New Lenox’s discharge point. New
Lenox’s consultant pointed out that during the period ofrecord, average pH was 7.8, only 3
pH values were 9.0 or higher, with
two
at 9.0 and one at 9.1. PR 640. New Lenox’s pH
sampling in connection with its water quality report showed pH ranging from 6.77 to 8.21
in the vicinity of New Lenox’s plant. Illinois EPA also properly considered its data
concerning pH, and pointed out that in some environments, a pH over 9.0 is not an
unnatural condition. Illinois EPA also stated that its monitoring station on the lower part
of Hickory Creek may not have similar morphology to the area around New Lenox, and
therefore drawing direct conclusions between sites may not be valid. HR 369.
CHO2/22387197.1
12

16.
EPA did not analyze the effects of the existing New Lenox discharge with a
recent valid study. The Antidegradation Assessment Memorandum from Scott Twait to Abe!
Haile, Nov. 26, 2002 states that “The most recent facility related stream survey conducted by the
Agency was on June 10, 1991. The facility related stream survey is not representative of the
stream conditions that exist at this time, since the facility has been expanded since the 1991
facilityrelated stream survey was conducted.” (HR
5)
ANSWER:
This statement is inaccurate. Illinois EPA requested and received a recent valid
study from New Lenox, performed by its consultant Earth Tech.
17.
The applicant’ contractor, Earth Tech, performed a biological study for the
Village of New Lenox (HR 513-519) at EPA’s request (HR 660.5). There is extensive
discussion in the Hearing Record among IEPA staff regarding deficiencies in the Earth Tech
study. (HR 537, HR
556-558,
HR 561, HR 661-698).
ANSWER:
New
Lenox
agrees
that
its
consultant performed a biological study, and
it was
subject to extensive
discussions
and appropriate internal
agency
deliberation about the
information it provided
as well as general discussions about the
manner in which
these
studies
are performed. The conclusion that the study was “deficient” is an inappropriate
characterization, and omits substantial parts of Illinois EPA’s thoughtful and thorough
deliberations. The agency’s deliberations reflect that there are various methodologies for
performing MBIs, and there were initially differences between Illinois EPA staff members’
practice and New Lenox’s consultant, which were addressed by Illinois EPA and New
Lenox’s consultant.
Those differences included the manner in which the MBI was
calculated and the tolerance values assigned to certain species, as well as
procedures,”beyond the staff members”. own familiarity and practice.” Illinois EPA has
also recognized the difficulty of performing an MBI assessment and the variations in
acceptable methods that nevertheless may still not be perfect. For example, one of the
Illinois EPA staff members cited by Petitioners has stated that even its own “bug-sampling
CHO2/22387197.1
13

methods (as they are currently defined) fall short of adequately addressing how to control
for habitat or flow influences on macroinvertebrate samples collected at difference sites.”
PR 665; See also 671, 674-75.
As recognized by Illinois EPA, there
is
no regulatory method to perform the MBI.
See PR 674-75. New Lenox’s consultant was nevertheless able to satisfy Illinois EPA’s
concerns about the study and Illinois EPA made a decision to rely on the study as part of
the information that informed its decision. The consultant revised the MBI values to
accord with the Illinois EPA’s preferred methodology, which produced a relatively minor
difference from the originally calculated MBI. HR 370. Illinois EPA subsequently verified
the validity and acceptability of the survey to characterize the current condition ofHickory
Creek. HR 370; PR 019.
18.
A Sept. 24, 2002 internal EPA email from Howard Essig to Roy Smoger states,
“The macroinvertebrate memo prepared by Earth Tech is one ofthe poorest studies I have seen
in a while.” It is further stated that “Statements made by Earth Tech on page 3 oftheir report are
all without merit. They do not back up any of their statements with data. For example they
attribute differences in taxa between stations to variations in stream flow, dissolved oxygen
levels and habitat types- but they provided no stream flow or dissolved oxygen data.” It is still
further stated in this email that “Earth Tech also indicated that the current baseflow of Hickory
Creek is adequate to dilute the volume discharged from the WWTP. They did not provide any
flow data on Hickory Creek or the New Lenox WWTP to back up this claim.” (HR 666-7)
ANSWER:
See resp. to par. 17. The discussion within
Illinois EPA
is evidence
of proper
internal deliberations in this matter
between various staff members
prior to the
time
Illinois EPA made a decision, and the cited memorandum is evidence of one staff members’
views and comments early in the process. It was not Illinois EPA’s ultimate conclusion
with respect to the study. There were ongoing discussions between New Lenox and Illinois
EPA, and Illinois EPA was ultimately satisfied that the study was sound notwithstanding
minor variations in procedure.
CHO2/22387197.1
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19.
Another internal IEPA memo, the Oct. 9, 2002 Memorandum from Roy Smoger
to Bob Mosher, summarizes the reviews by Smoger, Howard Essig and Mark Joseph ofthe Earth
Tech study and recommends that the study be conducted again. This memo states, “We find it
difficult to judge the validity of the analyses and conclusions because the study used different
collection methods, different taxon-tolerance values, and different criteria for interpreting MBI
scores than those typically used by Illinois EPA. In addition, the report do.es not contain enough
specific information on habitat, water chemistry, and flow.” The memo concludes, “Therefore
we recommend that Earth Tech conduct the survey again following the guidelines listed below.”
(HR
559-560).
ANSWER:
See Resp. par. 17 and 18.
In addition, New Lenox notes that the preferred
procedures and guidelines of certain staff members that reviewed the study have not been
adopted as regulation, and to the extent New Lenox’s consultant used different procedures,
its study was ultimately determined to be sound by Illinois EPA, and is evidence properly
relied upon by Illinois EPA.
20.
A Nov. 25, 2002 email indicates confusion on whether IEPA field staff would
redo the study. (HR 700) A Nov. 26, 2002 email from EPA’s Gregg Good shows EPA’s
decision to ignore the Earth Tech study, stating, “Therefore, forget using the contractor’s bug
study.” On the same day, IEPA referenced the study in the Antidegradation Assessment.
Antidegradation Assessment Memorandum from Scott Twait to Abel Haile, Nov. 26, 2002 (HR
5):
“New Lenox sponsored a macroinvertebrate survey of Hickory Creek at this location in
August 2002. Pollution intolerant organisms were found both upstream and downstream of the
existing discharge.” (HR 562)
ANSWER:
This paragraph contains inappropriate characterizations on the state of mind of
Illinois EPA field staff that are not supported by the record. Illinois EPA did not make a
decision to ignore the Earth Tech study but, having asked for it, utilized and relied on it as
useful and important information for purposes of the Anti-Degradation Assessment. As
explained by Gregg Good in the cited email, Illinois EPA also went back and reviewed the
basis for listing Hickory Creek as “partial impairment,” and determined that the basis for
CHO2/22387197.1
15

the listing was violation of standards governing total dissolved solids.
Illinois EPA
therefore recommended and New Lenox agreed to accept a limitation for total dissolved
solids. Finally, the cited email is evidence of the extensive internal deliberations that
properly occurred. They should not be used as evidence of “confusion,” nor do internal
agency deliberations change the appropriate analysis and conclusions of the Agency
reflected in the NPDES Permit, Responsiveness Summary and the Anti-Degradation
Assessment.
21.
The record does not contain any study of the potential effect of increased
discharges from the plant on Hickory Creek or the Des Plaines River. In an email of September
9,
2002, EPA’s Robert Mosher wrote, “There is no good way to predict what impact the
expansion may have (antidegradation)....” (HR 660.5)
ANSWER:
The record contains extensive evidence of appropriate Agency deliberations,
including by Bob Mosher, concerning the water quality in Hickory Creek and the plant’s
effect on it. After the Agency weighed all of the information before it, it was able to make a
decision that the current cause of impairment in the Creek was total dissolved solids, and a
permit limit was included in the permit.
With respect to the Des Plaines River,
consideration ofpotential impacts would be entirely speculative.
22.
In the reasonable potential analysis for copper done for this permit modification
(Memorandum ofJuly 16, 2002 from Scott Twait to Abel Haile), the concentration ofthe highest
sample was 20.5 ~ig/l while the chronic standard for copper at the hardness level found in
Hickory Creek is 20.6 pg/l. IEPA’s calculation of the reasonable potential for a violation of
water quality standards for copper using the U.S. EPA method revealed that there was a
reasonable potential for the level of copper to be more than double the acute water quality
standard for copper and to exceed the chronic standard by a factor ofover 3.7. (HR 508)
ANSWER:
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16

Illinois EPA considered the U.S. EPA method as well as this comment. In its
Responsiveness Summary, Illinois EPA concluded that for the chronic standard at issue
here, on an average basis, the effluent is not likely to exceed that value. HR 363. In Scott
Twait’s memorandum concerning water quality based effluent limits, Illinois EPA
determined in accordance with Agency policy that it would not use the high multiplier used
in U.S. EPA’s method because that method does not yield valid results when only a small
sample population exists. Illinois EPA also concluded that this facility had been previously
identified as having a low risk for high levels of metals. PR 509. Further, based on Illinois
EPA’s knowledge of other dischargers to the Creek and a known problem with copper in at
least some segments of Hickory Creek, which could be expected to be explored through
discovery, Illinois EPA reasonably concluded that the New Lenox discharge would not be
likely to cause a violation of water quality standard.
23.
On January
5,
2003, IEPA gave notice that it had made a tentative decision to
renew a NPDES permit to New Lenox to discharge into Hickory Creek~ The draft renewed
permit allowed the New Lenox plant to increase its design average flow from 1.54 million
gallons per day to 2.5 16 million gallons per day. (HR
1-15)
ANSWER:
New Lenox agrees with this paragraph.
24.
After reviewing a copy of the draft permit, Petitioners commented through
testimony given at a public hearing held on the draft permit on April 24, 2003 in the New Lenox
Council Chambers. (HR 6 1-87)
ANSWER:
New Lenox agrees with this paragraph.
25.
No one appeared at the hearing on behalf of the applicant, which chose not to
participate in the hearing. (HR 61-87).
ANSWER:
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New Lenox disputes that it did not appear at the Public Hearing. The attendance
sheet shows that Mike Turley, the Wastewater Treatment Plant Superintendent, was
present at the hearing. HR 055. New Lenox was not requested to provide comment at the
hearing, and in light of the fact that the purpose of the hearing is for Illinois EPA to
provide information to the public and accept public comments, this is consistent with the
regulations governing the hearing. As the applicant, under the regulations New Lenox is
not in the same position as a member of the public. The record reflects the extensive
information provided to Illinois EPA prior to the hearing to enable it to hold an
informative and meaningful public hearing and comment period, as evidenced by
Petitioners’ extensive participation and voluminous submittals.
26.
At the hearing, IEPA answered that it had done no studies of alternatives to
allowing the discharge other than to review a study of land treatment done by the applicant’s
contractor and that it had not made any study of the cost ofremoving phosphorus or nitrogen at
the plant. (HR 73-4)
ANSWER:
As noted
by this paragraph and discussed
at the hearing, New Lenox’s consultant
performed an
analysis
of
spray
irrigation either at farmland or on a golf course as
alternatives to the
discharge, and New
Lenox also considered alternative discharge
locations.
PR
403, 634;
HR
372-374.
In addition,
as noted
at the hearing, the
Illinois
Associated of Wastewater
Agencies
(IAWA) at the request of Illinois EPA performed a
study
concerning cost and
efficiency
of nutrient treatment, which was before Illinois EPA
at the time
it made its decision and is consequently properly part of the record. HR 74. All
parties
involved in this proceeding are aware of the content of that study.
27.
In their comments and testimony, Petitioners raised legal and scientific issues
regarding flaws in the draft permit and in IEPA’s consideration ofthe draft permit including:
CHO2/ 22387197.1
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a.
The draft permit allowed discharges ofphosphorus and nitrogen that cause, have a
reasonable potential to cause or contribute to violations of the water quality
standards regarding offensive condition, 35 Ill. Adm. Code 302.203, in violation
of 40 CFR 122.44(d) and 35 Ill. Adm Code 309.141. Nutrients are the likely
cause of algal blooms and other unnatural plant growth that have been reported in
the creek. (HR 68)
b.
Evidence, never disputed in the record, that Hickory Creek now violates state
water quality standards regarding offensive conditions because of algal blooms.
(see ¶IJ 6-9 above)
c.
That the draft permit allowed discharges that may cause, have a reasonable
potential to cause or contribute to violations of state water quality standards
regarding dissolved oxygen, 35 Ill. Adm 302.206, and copper, 35 Ill. Adm. Code
302.208(e) in violation of40 CFR 122.44(d) and 35 Ill. Adm. Code 309.141. (HR
68, HR 265-6)
d.
That the draft permit and the studies and lack of studies that led to the creation of
the draft permit did not comply with Illinois antidegradation rules protecting the
existing uses of the receiving waters. 35 Ill. Adm Code 302.105(a) because
studies were not properly conducted to determine the potential effect of the draft
permit on existing uses of the stream and because IEPA took no steps to
determine if existing recreational uses of the stream might be impacted by the
lack of disinfection of wastewater from the plant in months outside of May
through October. (HR 265, HR 82)
ANSWER:
New Lenox agrees that Petitioners availed themselves of the opportunity to provide
extensive public comment and raised various arguments including those cited in this
paragraph, all of which were fully considered by Illinois EPA. To the extent raised in the
motion, the characterization of these issues as “flaws” in the draft permit constitutes (a) a
legal argument, not a fact and (b) these arguments were rejected by Illinois EPA, as fully
explained in its Responsiveness Summary. HR 352-376.
28.
Further, Petitioners urged that the IEPA take the steps necessary to comply with
35 Ill. Adm. Code 302.105(c). Petitioners presented comments that the alternatives to allowing
the increase in pollution were not reasonably weighed prior to the issuance of the draft permit
and that many of the costs ofproceeding under the draft permit were ignored. William Eyring,
Senior Engineer for the Center of Neighborhood Technology, raised concerns about the social
and economic costs of expanding the plant in the center of the Village. (HR 120-1) Jim Bland
testified that the environmental effects of the kinds of development that would be facilitated by
CHO2/22387197.1
19

the plant expansion were not considered. (HR 78-79, HR 109) Petitioners testified that the
estimated costs of alternatives (e.g. land treatment and land application oftreated wastewater) to
allowing the increased discharge were unreasonably inflated and the costs ofminimizing nutrient
discharges were not considered. Environmental economist Jeff Swano requested
a
life cycle
analysis be performed on all considered alternatives as an appropriate economic assessment of
the costs to provide a better cost-benefit analysis and to provide the public with a costs-per-
treated-volume figure. (HR 70-2)
ANSWER:
New Lenox does not dispute the general summary of Petitioners’ comments, but
Petitioners’ characterization of “the steps necessary to comply with” regulations and its
advice to Illinois EPA concerning same constitutes a legal argument, not a fact. New Lenox
disagrees that any Petitioners “testified,” as public comments represent unsworn
statements by parties not subject to cross examination. New Lenox disputes that these
particular comments are relevant to the extent they concern the “kinds ofdevelopment that
would be facilitated by the plant expansion,” which is a consideration outside the scope of
Illinois EPA’s review of the impact of this particular treatment plant, not the land use
considerations that are properly within the discretion of New Lenox. New Lenox is not
aware of Mr. Swano’s credentials or qualifications as an “environmental economist.” New
Lenox disputes that its estimated cost of alternatives were unreasonably inflated, and notes
that Mr. Swano’s comments concerning land application were not the result of his own
independent analysis but were based on information from Schaffer International, a
company in the business of selling land application systems. HR 71.
29.
Petitioners asked that all technically and economically reasonable measures to
avoid or minimize the extent ofthe proposed increase in pollutant loadings be incorporated into
the permit and that the permit be improved in a number ofrespects including that;
a.
It provide for economically feasible controls on the discharge of nutrients
including phosphorus and nitrogen;
CHO2/ 22387197.1
20

b.
The limits in the permit be improved to prevent discharges that could cause~or
contribute to violations of water quality standards regarding offensive conditions
and dissolved oxygen;
c.
That proper biological studies be conducted to assure that the discharge would not
adversely affect existing uses ofthe stream;
d.
That EPA seriously consider whether the increased discharge was actually
necessary in light ofpotential alternatives; and
e.
That IEPA seriously consider alternatives to allowing the levels of pollutants in
the streams that would be allowed by the draft permit.
(HR 112-3, 120-1, 126, 265-267)
ANSWER:
New Lenox does not dispute the general summary of Petitioners comments
presented by this paragraph. New Lenox believes that Illinois EPA did seriously consider
alternatives in this matter, as noted in its Responsiveness Summary at HR 372-374.
30.
In particular, Jim Bland, an expert on eutrophication, testified on behalf of the
Des Plaines River Watershed Alliance at the public hearing that “Data concerning increased
nutrient loading, especially phosphorus is not included in the proposed permit.... On a long term
basis the proposed increase in discharge will increase the “attached algae” (periphyton that
covers the rocks and bottom rubble that are characteristic ofthis reach (c.f. Ecological Effects of
Wastewater, E.B. Welch). This increase in stream productivity has the capacity to dramatically
alter the character ofthe invertebrate communities downgradient from the STP.” (HR 110)
ANSWER:
New Lenox moves to strike the statement that Mr. Jim Bland
is
“an expert on
eutrophication,” as this has not been established by his comments. Further, New Lenox
disagrees that Mr. Bland “testified” in this case, as he was unsworn and not subject to
cross-examination.
New Lenox does not dispute that Mr. Bland made the quoted
comments, which show a lack of understanding of the relationship between appropriate
permit considerations as opposed to what would be considered in a rulemaking or setting a
TMDL. Illinois EPA fully considered the comments, and stated that “Streams would be
CHO2/22387197.1
21

expected to exhibit either one kind of algal growth or another, i.e. planktonic or
periphyton” depending on a variety of factors, and “the best measure of whether fish are
adversely impactedj is to look at the local fish population. Hickory Creek has fish
populations that are not indicative of low dissolved oxygen concentrations.” HR 361.
Illinois EPA also concluded based on relevant data for 2003 that all measurements in
Hickory Creek meet the water quality standard for dissolved oxygen. HR 364.
31.
In addition, Mr. Bland asked that EPA “Speed up the analysis ofnutrient loading
influences and apply this analysis to the existing permit specification. Document the direct
influences ofphosphorus which already exist at the stream.” (HR 113)
ANSWER:
See resp. to par. 30. New
Lenox
does
not dispute that Mr. Bland made the quoted
comments. New
Lenox notes that Illinois EPA fully
considered
them
as part
of
its permit
proceedings. New
Lenox also notes that Illinois EPA has convened a work group, and this
comment is
more properly directed in the context of that proceeding than a specific permit
proceeding.
32.
In post hearing comments, Beth Wentzel ofthe Prairie Rivers Network stated that
“The literature supports the claim that excess nutrients, nitrogen and phosphorus, can impair
streams by affecting dissolved oxygen concentrations, causing nuisance algal blooms and
causing other problems.” (HR 125) She concluded that “As described at the hearing, the existing
facility discharges nitrogen and phosphorus to Hickory Creek at concentrations that exceed
instream concentrations. According to USGS flow data, Hickory Creek is regularly dominated
by effluent flow. As demonstrated above and through testimony provided by local residents at
the public hearing, there is reasonable potential that instream concentrations cause violations of
water quality standards. Because the discharge from New Lenox STP #1 contributes to these
violations, the existing discharge is illegal and an expansion of the discharge would be illegal.
Prior to issuance of this permit, EPA must determine water quality based effluent limits for
nitrogen and phosphorus that ensure that water quality standards will be satisfied instream.
Alternatively, the applicant must adopt an alternative that does not require discharge ofnutrients
to Hickory Creek.” (HR 126)
ANSWER:
CHO2/ 22387197.1
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New Lenox does not dispute that Ms. Wentzel made the above comments and
conclusions, although New Lenox disagrees with their content and notes that they
constitute a legal conclusion. In any case, Illinois EPA fully considered these comments.
See resp. to par.
5, 6,
9, 10, 11-15.
33.
At the public hearing, Albert Ettinger ofthe Environmental Law & Policy Center
asked the Agency to provide an estimate of the cost of removing phosphorus and the cost of
removing nitrogen from the discharge. (HR 73-4)
ANSWER:
New Lenox does not dispute
that Mr.
Ettinger
made the above request and also
submitted
comments in this proceeding. New Lenox notes that Illinois
EPA
had before
it
the study prepared by the Illinois Association of Wastewater Agencies at the request of
Illinois EPA, which contained information on the cost associated with removing nutrients.
See resp. to par. 26.
34.
Cynthia Skrukrud Ph.D. testified on behalf of the Sierra Club that “using the
standard USEPA method where you use a multiplier to come up with a
95
percent
...
reasonable
potential, the copper suggested that there should be further analysis. But then further in the
memorandum, it’s reported that all copper samples reported were less than the acute and chronic
water quality standards and the conclusion was that no regulation of copper is necessary and no
monitoring beyond routine requirements is needed. My concern is that there were only two
samples taken. And ofthose two samples, I only know what one ofthem was. But one ofthem,
the sample measured 20.5 micrograms per liter. The chronic standard is 20.6 micrograms per
liter. It certainly would seem given that you have only two samples, and you are so close to a
violation ofthe chronic standard there, that I would think that there is a reasonable potential for
violation of the chronic standard, and that because there were
...
so few samples that it needs to
be investigated further.” (HR 70)
ANSWER:
New Lenox does not dispute
that
Ms.
Skrukrud made the above comments and
conclusions, although New Lenox disagrees with their content. See resp. to
par. 22.
CHO2/ 22387197.1
23

35.
In a post-hearing letter and attachments (HR 264-265), Skrukrud wrote:
Reasonable Potential
Analysis to Exceed Water Quality Standards
The USEPA recommended method for Reasonable Potential Analysis is to
use a multiplier to determine the potential to exceed a given standard when
a small number of samples have been collected. It is precisely because so
few data are collected that the multiplier is needed. EPA’s decision to
abandon the method recommended by USEPA in
Technical Support
Document for Water Quality Based Toxics Control
is not acceptable.
IEPA should either use the multiplier in their analysis or require that more
samples be collected
.Yet EPA concludes from this limited data set that there is no need for
additional copper monitoring. If the measured value had been 20.7 ~.tg/l
instead of 20.5, would further investigation have been required? Are we
then to believe that EPA considers 20.5 and 20.7 ~1g/lto be statistically
different? The confusing situation which exists with EPA’s method of
direct comparison of sample values to standards is exactly why the
statistical method recommended by USEPA should be employed.”
ANSWER:
New Lenox does not dispute that Ms. Wentzel submitted the above comments,
although New Lenox disagrees with their content. See resp. to par.
5, 6,
9, 10, 11-15.
36.
Skrukrud further commented:
Inadequate Consideration ofAlternatives
In addition to the other flaws in the antidegradation analysis, the analysis
makes no serious effort to consider alternatives or to rationally weigh
whether the proposed new discharge is socially or economicallynecessary.
Nutrient removal is already required for New Lenox by the Clean Water
Act and Illinois law given that the discharge is plainly causing or
contributing to violations of state narrative water quality standards and
probably state dissolved oxygen standards. Although the Agency is not
now requiring nutrient removal, it concedes that requirements for nutrient
removal are likely to go into effect during the life of the proposed
expansion. It is, thus, unreasonable to decide on the merits of permitting
this expansion without explicit consideration of the costs of nutrient
CHO2/ 22387197.1
24

removal. The Agency wrongly rejects land treatment and other options as
too expensive both by overpricing land treatment and by ignoring
potentially huge future capital and operation costs that will be incurred by
permitting this discharge expansion.” (HR 267)
ANSWER:
New Lenox does not dispute that Ms. Skrukrud submitted the above comments,
although New Lenox disagrees with their content. See resp. to par.
5, 6,
9, 10, 11-15.
37.
On October 31, 2003, Illinois EPA issued the permit that is subject to the current
appeal. The final permit contains some changes from the draft including required levels of
dissolved oxygen in the effluent and a limit on total dissolved solids. The final permit did not
place any limits on the discharge ofphosphorus, nitrogen or copper. (HR 34 1-50)
ANSWER:
New Lenox agrees
that Illinois EPA issued the permit subject to the current appeal
on October
31, 2003.
In
response
to
comments made during the public comment period
and to information before Illinois EPA, the agency recommended and New Lenox agreed to
accept certain limits without challenge. New Lenox notes that it did not challenge the
limits, but this does not mean those limits were not challengeable or were required. They
include limits on dissolved oxygen, total dissolved solids, and ammonia.
38.
The permit set no limit for copper. (HR 343) No explanation appears in the
record as to why the Agency proceeded in conflict with the U.S. EPA recommended method for
determining the reasonable potential to violate the acute copper standard. No study was done
under 35 Ill. Adm. Code 302.102 to develop a mixing zone analysis. Regarding the chronic
standard, the New Lenox Responsiveness Summary states “It is important to remember that this
comment is dealing with reasonable potential to exceed a chronic water quality standard. By
definition, a chronic standard must not be exceeded in the receiving stream by the average of at
least four samples.” (HR 363) Yet there is no discussion of the possibility of requiring more
samples than the two provided.
ANSWER:
New
Lenox
agrees
that no permit limit
was set
for copper.
CHO2/22387197.1
25

39.
The final permit allowed a monthly daily average increase of 82 lbs of CBOD5
and did not place any limit on the discharge of CBOD5 other that the effluent limit of 35 Ill.
Adm. Code.304.120. (HR 342-3)
ANSWER:
New Lenox disagrees
that no permit limit was set for CBOD5. See PR 652, which
shows
the permit does contain a daily average and
a daily maximum value for
CBOD5.
40.
No limits were set for phosphorus or nitrogen. (HR 343) Other than to mention
that a study done by the Illinois Association of Wastewater Agencies (never placed in the record)
indicating that the combined costs of treating nitrogen to an unmentioned level and phosphorus
to the level of0.5 mgIL might cost capital costs of$5.4 million (HR 358), IEPA never discussed
the cost of treating phosphorus. No mention appears in the record of any analysis of the cost,
feasibility or reasonableness of any level of phosphorus treatment alone (without nitrogen
treatment) or ofany level ofphosphorus treatment other than 0.5 mg/L.
ANSWER:
New Lenox agrees that no permit limit was set
for phosphorus or nitrogen. Further,
New
Lenox
disagrees
with the statement that the study performed by the Illinois
Association
of Wastewater Agencies was not part of the record,
as
the record properly
includes everything
before the Illinois EPA at the time it made
its decision.
The
study is
clearly referenced and disclosed by Illinois EPA in the documents filed in this proceeding.
41.
No limits are placed in the permit to prevent violation of the “offensive
conditions” narrative standard. The Responsiveness Summary indicates that the Agency would
only place limits on nutrients in the permit after numeric standards are set. (HR 356) The IEPA
declines to attempt to place limits in the permit to satisfy the narrative standard on plant and
algal growth because “This is a very difficult standard to apply to a permit.” (HR 357)
ANSWER:
New
Lenox
agrees that no limits were placed in
the permit concerning “offensive
conditions.” Further, no limits are required
to address
offensive conditions.
To the extent
Petitioners claim that algal growth constitutes an offensive condition, Illinois EPA
CHO2/ 22387197.1
26

addressed algae in its Responsiveness Summary, explaining that algae is a vital part of the
aquatic community and algae growth in itself
is
not itself a problem;
it
is in relation to
dissolved oxygen and the adverse impact on fish that provides context. Illinois EPA stated
that “Streams would be expected to exhibit either one kind of algal growth or another,”
depending on a variety of factors, and “the best measure of whether fish are adversely
impacted is to look at the local fish population. Hickory Creek has fish populations that
are not indicated of low dissolved oxygen concentrations.” HR 361. Illinois EPA also
concluded based on relevant data for 2003 that all measurements in Hickory Creek meet
the water quality standard for dissolved oxygen. HR 364. Given the complicated and
disputed nature of the science governing algae, both Illinois EPA and the Board have
concluded that a work group is necessary to study the issue of nutrients and proposed
standards that would govern dischargers in Illinois. Further, the Illinois EPA concluded
specifically in this case that “the incremental nutrient loading anticipated to result from
this project is not expected to increase algae or other noxious plant growth, diminish the
present aquatic community or otherwise aggravate existing stream conditions.” PR 565.
Finally, Petitioners do not address the impact of numerous other dischargers to the stream.
Respectfully submitted,
The Village of New Lenox
By:____________
One ofIts Attome~’
Roy M. Harsch
Sheila H. Deely
Gardner Carton & Douglas LLP
191 N. Wacker Drive
Suite 3700
Chicago, IL 60606
(312) 569-1000
CHO2/22387197.1
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