1. ~i~il ~
      2. NOTICE OF FILING
      3. Introduction
      4. and prohibit allowing new pollution that has not been shown to be necessary.
      5. A. The Clean Water Act
      6. B. Illinois Law follows the Clean Water Act.,
      7. Conclusion

~i~il
~
b
~j~~’s
OFFICE
BEFORE THE ILLINOIS POLLUTION CONTROL BOARD
~
15 2~3
‘~
OF
~LLU~1O~S
STA~
~
trot Board
INTERIM PHOSPHORUS EFFLUENT
)
poUut~Ofl
Con
STANDARD, PROPOSED
35
ILL. ADM.
)
R2004-026
CODE 304. 123(G-K)
)
Rulemaking
Water
)
NOTICE OF FILING
PLEASE TAKE NOTICE that the Environmental Law & Policy Center, Prairie Rivers
Network and Sierra Club have filed the attached MEMORANDUM AND TESTIMONY OF
ENVIRONMENTAL LAW & POLICY CENTER, PRAIRIE RIVERS NETWORK AND
SIERRA CLUB IN SUPPORT OF THE ILLINOIS EPA RULE MAKING PROPOSAL.
Albert F. Ettinger (Reg. No. 3125045)
Counsel for Environmental Law & Policy
Center, Prairie Rivers Network, and
Sierra
Club
DATED:
October
15,
2004
Environmental Law & Policy Center
35 East Wacker Drive, Suite
1300
Chicago, IL
60601
312-795-3707

CLERK’S OFF~CE
BEFORE THE ILLINOIS POLLUTION CONTROL BOARD
~
152003
STATE OF ~LUNO~S
tion Con’JO~Bodrd
IN THE MATTER OF:
)
rOuU
)
INTERIM PHOSPHORUS EFFLUENT
)
R2004-026
STANDARD, PROPOSED 35 Iii. Adm.
)
Rulemaking
Water
Code 304.123(g-k)
)
)
MEMORANDUM
AND
TESTIMONY OF ENVIRONMENTAL LAW & POLICY
CENTER,
PRAIRIE RIVERS
NETWORK
AND
SIERRA CLUB IN SUPPORT OF THE
ILLINOIS EPA RULE
MAKING
PROPOSAL
INTRODUCTION:
Environmental Law
& Policy Center ofthe Midwest (ELPC), Prairie Rivers Network and
the Sierra Club strongly support the Illinois EPA proposal to establish an interim rule that will
generally require monthly average permit limits of 1
mg!L total phosphorus fornew or expanded
discharges by major dischargers. The proposal
is extremelymodest and does not provide a long-
term solution to the problem ofnutrient pollution in Illinois waters and waters downstream of
Illinois. Still, adoption ofthe proposal will
serve to reduce the extent to
which the problem gets
worse during the next four years during which numeric nutrient water quality standards are
developed and adopted.
Our submission in support ofthe proposal is in fourparts.
Part I, the Pre-filed Testimony ofAlbert Ettinger, consists essentially ofa legal
memorandum explaining the legal
and regulatory frameworks ofthe proposal. It will be seen
that, while the proposed rule is extremelyhelpful in giving guidance to permit applicants and
permit writers, adoption ofthe proposed rule would not have a major effect on Illinois law.
Dischargers within the Great Lakes Basin have been required to meet the
1
mgIL limit fortwenty
years.
Illinois dischargers less than 25 miles upstream ofa lake or reservoir already must meet a

1 mg/L limit under 35 Iii. Adm. Code 304.123. More generally, given that it unquestionably is
practicable for maj or dischargers to treat wastewater to a level of 1
rng/L or less total
phosphorus, the Illinois antidegradation rule, 35 Iii.
Adm. Code
302.105(c), already requires the
permits that would be affected by the proposed rule to
contain a limit as stringent as
1
mg/L. Still
further, a phosphorus limit should also be required now for manydischargers under 35
Ill. Adm.
Code 302.203
and 35 Ill. Adm. Code 302.206 and 35 Iii. Adm. Code 309.141.
Part II ofthis petition is a description ofthe need for greater controls on phosphorus to
protect Illinois waters. Professor Michael Lemke ofthe University ofIllinois
at Springfield
explains the known effects ofphosphorus pollution and the dangers of allowing unrestricted new
loadings ofphosphorus to be discharged to Illinois rivers, lakes and streams.
In Part III ofthis submission, Beth Wentzel, Watershed Scientist ofPrairie Rivers
Network, discusses existing efforts to
control phosphorus pollution in Illinois and other states. It
will be seen that the proposed monthly average limited of 1
mg/L can be reached affordablyby
Illinois dischargers and that in fact hosts ofdischargers around the country are complying with
much tighter limits. Moreover, many Illinois dischargers are already complying with phosphorus
limits. In addition to discharges controlled by 35
Iii.
Adm. Code 123 (a)
and (b), many Illinois
dischargers intending to have new or increased discharges have already agreed to average, limits
of 1
mg/L total phosphorus. This includes a number ofdischargers that were identified at the
hearing August 30 (Tr.
6) as being potentially affected by this proposal including McHenry,
Piano, Manhattan, Minooka, Bloomingdale, and Lake in the Hills.
In Part IV ofthis submission
to the Board, we propose and explain proposed language
changes to
the proposal. It will be recalled that legal and technical problems in the language used
in the proposal were discussed in the hearing held August 30, 2004. We believe that our

proposed changes
to the agency proposal address all of the substantive and drafting issues that
were brought out in
the hearing and make the proposal stronger and eliminate arguable
inconsistencies between the currently proposed language and
the requirements of the Clean
Water Act and current Board rules.
Finally, it should be pointed out that there is a need for an expedited decision in this
proceeding. Decisions regarding treatment plant design and permits have to be made on an
ongoing basis
and one of the major benefits of adoption of the proposal will be to force
some
dischargers to avoid making investments in equipment that will have to be retrofitted in a few
years.
Albert F. Ettinger (Reg.
No. 3125045)
Counsel for Environmental Law
& Policy
Center, Prairie Ri~iers
Network, and Sierra
Club
DATED:
October
15, 2004
Environmental Law &
Policy Center
35 East Wacker Drive,
Suite
1300
Chicago, IL
60601
312-795-3707

In Re: InterimPhosphorus Effluent LimitR2004-26
Pre-filed Testimony ofAlbert
Ettinger
I am Senior StaffAttorney at the Environmental Law & Policy Center ofthe Midwest
(ELPC) and Water Issues Coordinator and General Counsel for the Illinois Chapter ofthe Sierra
Club. In this proceeding
I represent ELPC, the Sierra Club and Prairie Rivers Network.
I
have
worked in Illinois on matters relating to water pollution and implementation ofthe federal Clean
Water Act as counsel to the Sierra Club since
1982. I am also the principal author ofthe
February 2, 2004 letter (Hearing Exhibit 3) that may have figured in development ofthe interim
phosphorus proposal now before the Board although the proposal does not closely follow the
recommendations made in the letter.
This testimony sets forth the legal principles that support the petition filed by the Illinois
Environmental Protection Agency (IEPA). The testimony also provides the
legal rationale for the
suggestions ofELPC, Prairie Rivers Network and Sierra Club for improving some ofthe
language ofthe IEPA proposal.
Introduction
The Agency’s proposal for an interim monthly average phosphorus effluent limit of 1
mg/L formany new or increased discharges is fullymerited, if not legally required, by existing
law and regulations. The proposal fits well with other Illinois regulations that have been enacted
by the Board to deal with similar situations. The proposed rule addresses several basic goals and
requirements ofthe Clean Water Act and the Illinois Environmental Protection Act.
In particular,
the proposed effluent limitation generally will bring NPDES
permits grantedby IEPA closer to
compliance with federal and state requirements that:
-
permit limits control “all pollutants
...
which will cause, have a potential to
cause, or contribute to an excursion above any State water quality standard,
1

In Re: InterimPhosphorus Effluent LimitR2004-26
including
State
narrative
criteria for water quality” 40 CFR
§ §
1 22.44(d)(1)(i), see
also, 35 Ill.
Adm. Code 304.105,
-
only allow new or increased loadings to Illinois waters if allowing such loadings
is “necessary to accommodate important economic or social development.” 35
Ill.
Adm. Code 302.105(c)(1).
Permits for new or increased discharges not containing a
1
mg/L monthly average limit
forphosphorus generally violate both ofthese bedrock principles ofNPDES
permit writing.
To see how this all fits together, it is helpful to review some ofthe history of the CWA and its
implementation in Illinois.
I.
The Clean Water Act and Illinois
law require that
NPDES permits
control
pollutants that may cause or
contribute to violations ofwater quality standards
and prohibit allowing new pollution that has not been shown to be necessary.
A.
The Clean Water Act
Congress enacted the CWA, 33 U.S.C.
§~
1251-1386, in 1972 to “restore and maintain
the chemical, physical, and biological integrity ofthe Nation’s waters.”
33
U.S.C.
§
125 1(a).
The CWA prohibits any “point
source” from discharging pollutants into waters ofthe United
States unless the source obtains an NPDES permit.
33 U.S.C.
§§
1311(a), 1342., NPDES
is the
initials forthe “National Pollutant Discharge Elimination System.” See 33 U.S.C.
§
1342.
The
Act sets as a national goal that all
discharges be eliminatedby
1985.
33
U.S.C.
§1251(a)(1).
It
was thought that,
while the technology was developed and put in place to eliminate discharges,
municipalities, companies and otherpersons needing to discharge were to obtain NPDES
permits.
Overtime, NPDES limits were to be tightened until discharges were eliminated.’
CWA requires dischargers to
comply with both “technology-based” and “water quality-
based” limitations on pollutant discharges. Permit limitations on the quantity and types of
‘Adler, R.W., Landman, J.C. and Cameron, D.M., The Clean Water Act 20 Years Later, Island Press
(1993)p.
137-39; Rodgers, Jr., W.H., Environmental Law, Second Edition (1994) pp. 361-62.
2

In Re: InterimPhosphorus Effluent LimitR2004-26
pollution permitted
are to
be set according to either technology-based effluent limits or water
quality standard based limits, whichever is more stringent.
33 U.S.C.
§
1311 (b)(1)(C);
see also
Rodgers, Jr., W.H., Environmental Law, Second Edition (1994) p. 352.
Technology-based effluent rules (also known as “effluent limitation guidelines”) are
based on the greatest degree ofeffluent reduction economically achievable for a particular
industry.
EPA has promulgated nationwide technology-based effluent guidelines formany
industries,
see
40 C.F.R. Parts 405 to 499.
When there is no applicable effluent limitation
guideline, the permitting authority must exercise “bestprofessionaljudgment” to set technology
standards for each permit on a case-by-case basis.
33 U.S.C.
§
1342(a)(1)(B); 40 C.F.R.
§
125.3(c).
Publicly owned treatment works are to
meet effluent limits attainable through the
application of “secondary treatment” 33 U.S.C. §~131
1(b) which was to be
specified by U.S.
EPA “within sixty days ofOctober 19,
1972, (and from time to time thereafter).” (33 U.S.C.
§
131 4(d)(a)). Federal regulations, long overdue forreconsideration, define “secondarytreatment.”
40 CFR §133.102
Water quality-based standards
set the water quality goals for specific waterbodies,
40
C.F.R.
§
131.2.
Water quality standards shall provide whenever possible “the protection and
propagation offish, shellfish, and wildlife and provides for recreation in and on the water.”
33
U.S.C.
§
1251(a)(2);
40 C.F.R.
§~
130.3,
131.2.
At a minimum, water quality standards must
include:
(1) the designated use or uses ofa water body (e.g., safe to drink, safe to
swim, safe for
aquatic life, safe for fish consumption); (2) the’water quality criteria necessary to protect the
designated use or uses (expressed as a narrative or numeric standard); and (3) an
“antidegradation policy” consistent with 40 C.F.R.
§
131.12.
See
40 C.F.R.
§
131.6. Further,
“in
designating uses ofa water body and the appropriate criteria for those uses, the
State shall take
3

In Re: InterimPhosphorus Effluent LimitR2004-26
into consideration the water quality standards ofdownstream waters and shall ensure that its
water quality standards provide forthe attainment and maintenance ofthe water quality
standards ofdownstream waters.” 40 CFR
§
131.10(b).
No NPDES permit may be granted that allows discharges that may cause or contribute to
violations of waterquality standards.
40 CFR
§
122.44(d), which implements CWA Section
301(b)(1)(C), explicitly requires that NPDES
permits include restrictions “necessary to achieve
water quality standards
...
including State narrative criteria.” American Paper Institute v. U.S.
Environmental Protection Agency, 996 F.2d 346, 350 (D.C. Cir.
1993). Permit “limitations
must control all pollutants or pollutant parameters (either conventional, nonconventional ortoxic
pollutants) which
...
are or maybe discharged at a level which will cause, have a reasonable
potential to
cause, or contribute to an excursion above any State water quality standard, including
state narrative criteria for water quality.” 40 CFR
§
l22.44(d)(1)(i); see also, 40 CFR
122.4(d)
and (i).
Not only must permit limits protect standards in the waters immediately below the
discharge point, standards must be protected in waters far downstream ofthe discharge, even in
another state.
Arkansas v.
Oklahoma, 503 U.S.
91,
107 (1992);
Naturally, given that the CWA seeks to
restore water quality and eliminate discharges the
circumstances in which new pollution is to be allowed are strictly limited.
Thus,
a key element
ofwater quality standards
is antidegradation policy.
An antidegradation policy is “a policy
requiring that state standards be sufficient to maintain existing beneficial uses ofnavigable
waters, preventing their furtherdegradation.”
PUDNo.
1 ofJefferson County v.
Washington
Dep
‘t
ofEcology,
511
U.S. 700,
705 (1994); Each state mustadopt an antidegradation policy
consistent with 40 C.F.R.
§
131.12, which creates overlapping “tiers” ofprotection.
40 C.F.R.
§
131.12.
At the base, Tier
1
requires the maintenance and protection of “existing
instream
4

In Re: Interim Phosphorus Effluent LimitR2004-26
water uses.”
40 C.F.R.
§
131. 12(a)(1).
Tier 2 adds another layer ofprotection for water quality
by providing that levels ofwater quality better than that needed to meet standards and protect
existing uses,
“shall
be maintained and protected” unless “allowing lower water quality is
necessary
to accommodate
important
economic or social’development in the area in which the
waters are located.”
40 CFR 131.12(a)(2)(emphasis added).2
B.
Illinois Law follows
the Clean Water Act.,
Illinois has adopted the Clean Water Act requirements into its own laws and regulations.
One ofthe provisions ofthe Illinois Environmental Protection Act is a statement that it is the
policy ofthe General Assembly that the Pollution Control Board and IEPA administer the Clean
Water Act in a mannerconsistent with Illinois administering the NPDES permitting
system. 415
ILCS
5/11 (a)(7), (b).
see also,
Peabody Coal Co.
v. Pollution Control Bd., 36 Ill. App.
5,
344
N.E.2d 279, 285
(5th
Dist.
1976)(Illinois statutes and regulations should be read to accord with
the Clean Water Act. ); 415 ILCS
5/13(b)
(Board rules shall be consistent with the Clean Water
Act).3
Following the Environmental Protection Act, the Board has established waterquality
standards and effluent rules that seek, as a minimum, to
comply with the requirements ofthe
Clean Water Act. In Part 302 ofits regulations, the Board has established numeric and narrative
water quality standards that, with some exceptions, track federal criteria or that deviate from
federal criteria only in ways that are supported by a sound scientific rationale.
It has adopted
antidegradation standards that meet federal requirements.
35 Ill. Adm. Code 302.105.
2
Tier 3
adds a third and highest layer of protection for Outstanding National
Resource Waters
(“ONRWs”), for waters designated by a state as waters of“exceptional recreational or ecological
significance.”
40 C.F.R.
§
131.12(a)(3).
5

In Re: Interim Phosphorus Effluent LimitR2004-26
The Board has also
adopted rules for the issuance ofNPDES permits that are designed
with the goal, among other goals, of complying with the Clean Water Act. Most obviously, 35
Ill. Adm. Code 309.14 1
requires that Agency issued permits comply with the technology based
effluent limits required by the Clean Water Act and any other limits required by federal law.
Further, 35 Ill.
Adm. Code 304.105 requires that any effluent or combination ofeffluents be
regulated to insure that there is compliance with all applicable water quality standards in all
receiving or downstream waters that may be affected by the discharge. see In the Matter of:
Petition ofCommonwealth Edison Company for Adjusted Standard from 35 Ill. Adrn. Code
302.211(d) and (e),
AS 96-10 (PCB, October 3,
1996)
In addition, in Part 304 the Board has created a number of effluent rules.
Some ofthese
effluent rules track federally-mandated effluent rules.
For example, the currentphosphorus rule,
itisofar as it requires that “No effluent discharge within the Lake Michigan Basin shall contain
more than 1.0 mg/L ofphosphorus
as P,”
(35
Ill.
Adm.
304.123(a)) is a required federal rule
established as a result ofthe Great Lakes Water Quality Agreement of 1978.
Under the Great
Lakes Water Quality Agreement, all dischargers in the basins ofLake Huron, Lake Michigan and
Lake Superior discharging more than more than
1
million gallon per day have had to
meet a limit
of 1
mg/L for phosphorus. (Exhibit A)
Other ofthe effluent rules in Part 304, like the current JEPA phosphorus proposal, are
hybrid rules designedwith both technological treatment capabilities and protection ofwater
quality standards
in mind.
For example, the current phosphorus rule, insofar as it controls
discharges to lake and reservoirs
(35
Ill. Adm.
Code 304.123(b)), was adopted by the Board,
following consideration ofthe cost ofphosphorus treatment and the effects ofphosphorus on
~Ifthe Illinois
Environmental Protection Act is interpreted or implemented by Illinois in such a manner that it does
not fully implement the letter and policies of the Clean Water Act, Illinois
could lose the
ability to administrate
6

In Re: Interim Phosphorus Effluent LimitR2004-26
lakes, to protect lakes from algal growth and other harmful effects that would cause a violation
ofthe waterquality standards. See In the Matter of: Proposed Amendment to Phosphorus
Effluent Standard, No. 87-6
1990 Ill. Env. Lexis 419 (April
12, 1990)
The Part 304 rules provide rules for permit writers that allow easy formulation ofpermit
limits. In the view ofELPC, Prairie Rivers Network and Sierra Club, these rules have been
abused in cases where, following the effluent rules but not other portions ofthe Board rules,
IEPA permit writers put looser limits in permits when more stringent limits were actually
required to protect water quality standards.4 However, it is certainlybetter that such hybrid
effluent limit rules, developed with technological and water quality considerations in mind, be
used to set some limits on controllable pollution than that there be no limits at all.
II.
Limits on the Discharge of Phosphorus
are needed to prevent violations ofIllinois
water quality standards and comply with antidegradation requirements.
A.
Controls are needed to prevent violations of the water quality standards
regarding offensive
conditions, pH and dissolved oxygen.
Forreasons that are described in greater detail in the testimony ofProfessor Michael
Lemke, controls on phosphorus pollution are needed to prevent conditions in Illinois waters that
violate Illinois water standards.
Generally, U.S. EPA has described the damage caused by excess
nutrients, stating:
Human health problems can be attributed to nutrient enrichment. One serious
human health problem associated with nutrient enrichment is the formation of
trihalomethanes (THMs). Trihalomethanes are carcinogenic compounds that are
NPDES permitting in Illinois. See 40 C.F.R.
123.63.
~Forexample, it is now clear from certain TMDL studies that the effluent limits of35
Ill. Adm. Code
304~.1Z0for
deoxygenatingwastes
are far from adequate to protectIllinois
waters from violations of the dissolved oxygen
standards. By using 35
Ill. Adm. Code
304.120 as a quick and dirty approach to placing controls in permits needed
to prevent violations of DO standards, IEPA in some important cases is permitting pollution that is causing DO
violations. Because there are DO modeling tools that would enable IEPA to do a betterjob, such as the venerable
StreeterPhelps model, IEPA is notjustified in solelyrelying
on
304.120. Still,
the situation is betterwithIEPA
using 304.120 to place
some limits on deoxygenating wastes than it would be if, fmding it hard to calculate limits
for such pollution, IEPA did not putNPDES controls on it at all.
7

In Re: InterimPhosphorus Effluent Limit112004-26
produced when certain organic compounds are chlorinated and bromated as part
ofthe disinfection process in a drinking water facility. Trihalomethanes and
associated compounds can be formed from a variety oforganic compounds
including humic substances,
algal metabolites and algal decomposition products.
The densityof algae and the level of eutrophication in the raw water supply has
been correlated with the production ofTHIMs.
*
*
*
Nutrient impairment can cause problems other than those related to human health.
One ofthe most expensive problems causedby nutrient enrichment is the
increased treatment required for drinking water... Adverse ecological effects
associated with nutrient
enrichment include reductions in dissolved oxygen (DO)
and the occurrence ofHABs (harmful algal blooms). High algal and macrophyte
biomass may be associated with severe diurnal swings in DO and pH in some
waterbodies. Low DO can release toxic metals from sediments contaminating
habitats oflocal aquatic organisms. In addition, low DO can cause increased
availability oftoxic substances like ammonia and hydrogen sulfide, reducing
acceptable habitat for most aquatic organisms, including valuable game fish.
Decreased water clarity (increased turbidity) can cause loss ofmacrophytes and
creation of dense algal mats. Loss ofmacrophytes
and enrichment may alter the
native composition and species diversity ofaquatic communities.5
In addition, nutrients, particularly phosphorus, can cause high pH levels which
themselves can be harmful to
aquatic life. Walter K. Dodds, Freshwater Ecology, Academic
Press (2002) p.
34 1-42.
Phosphorus can
also contribute to blue green algae growth that create a
variety oftoxins.
Ind. Dept. ofEnv. Mgt.,
Water Colunm Fall 2001
Vol.
13 No. 4 (Exhibit B)
Illinois waters that have been monitored for impairments that could have been caused by
phosphorus pollution show that phosphorus is already having a major effect on Illinois waters
even without addition offurther loading ofphosphorus that the Agency proposal is designed to
moderate.
The 1BPA water quality report for 2004 shows that over 100,000 acres ofthe under
150,000 acres of Illinois lakes monitored by JEPA were impaired by “Excessive algal
growth/Chorophyll a” (Exhibit C).
~U.S. Environmental Protection Agency, Nutrient
Criteria, Technical Guidance Manual,
Rivers
and Streams, EPA
-
822-B-00-002 (July 2000) (pp.
4-5,
citations omitted).
8

In Re: Interim Phosphorus Effluent Limit112004-26
IEPA does not really study, or studies only indirectly, adverse river conditions likely to
be caused by phosphorus pollution.
6
Nonetheless, JEPA in its 2004 water quality reporthas
listed phosphorus as a potential cause ofimpairments ofnumerous river miles, including sections
ofthe Illinois, Wood and Mississippi Rivers, which are, of course, downstream ofnumerous
Illinois dischargers ofphosphorus and other sources ofphosphorus. (Exhibit
C)7
However,
recent studies show that algal blooms are causing violations ofDO and pH standards in dammed
pools in
the Fox River. See
Victor Santucci Jr. and Stephen R. Gephard, Fox River Fish Passage
Feasibility Study, http://www.co.kane.il.us/kcstorm/dams/fishpssg/final.pdf.,
pp. 42-54. (Exhibit
D)
Earlier with regard to the Fox
River, the Illinois
Natural History Surveywrote of the effect of
elevated phosphorus levels on the Fox:
High nutrient inputs and still-water environments createdby the
numerous channel dams situated along the entire main stem ofthe Fox River in
Illinois promote excessive algal growths.
Very high phosphorus levels appear
to promote and sustain massive algal blooms along the Fox River.
Pronounced algal growth will continue to produce fluctuating DO levels
behind the low channel dams unless significant reduction in phosphorus levels
occurs.8
By creating algal blooms and blooms ofcyanobacteria (a.k. a. “blue green algae”),
nutrients cause a host- ofproblems for Illinois drinking water, recreational uses and aquatic life.
Phosphorus
is known to cause violation ofat least three Illinois water quality standards:
-
302.203 which states that “Water ofthe State shall be free from sludge or bottom
deposits, floating debris, visible oil, odor, plant or algal growth, color or turbidity ofother
than natural origin,”
6
IEPA does not measure excessive algal growth in rivers or streams and, astheBoard has heard in R04-25, does not
normally measure dissolved oxygen levels at the time of day at which violations of the DO standards are
likelyto be
found.
~‘
There
is also evidence that phosphorus,
as
well
as nitrogen, is contributing to the “dead zone” in the Gulfof
Mexico.
(ExhibitE)
8
Illinois
State Water Survey, Considerations
in Water Use Planning for the Fox River, Contract Report
586
(September
1995)
pp. 100,
104,
113,
120,122.
(Exhibit F)
9

In Re: Interim Phosphorus Effluent LimitR2004-26
-
302.204 which provides that pH shall be within the range of
6.5
to 9.0
except for natural
causes,
and
-
302.206 Dissolved Oxygen.
Although it is well aware that phosphorus discharges can cause or contribute to violations
ofthe three water quality standards
in Illinois waters, IEPA does not now generally limit
phosphorus discharges on the grounds that Illinois does not currently have numeric nutrient
standards. However, issuing permits that ignore the effect ofnutrients on algal
growth, dissolved
oxygen
levels and pH does not comply with the federal and
state requirements
that NPDES
permits
control all pollutants that may cause or contribute
to a violation of state numeric
or
narrative
water quality standards.
IEPA has now proposed
a
1
mg!L
effluent limit for new or increased discharges of
phosphorus.9 This would basicallybe a step toward limiting the extent to which the problems
caused by phosphorus in Illinois waters
and waters downstream ofIllinois will get worse during
the period that numeric phosphorus standards are developed.
Even for limiting the extent to ‘which things will get worse during the interim, the IEPA
proposal is
a
very
modest step. In a similar situation in which it was known that phosphorus was
harming the Great Lakes but the
exact
extent ofthe
controls
needed were
unknown,
the United
States and Canada
agreed on
1
mg/L
phosphorus limits
on
both
new
and
existing dischargers to
the Lake Michigan
basis and
on a
0.5
mg/L limit
for new
and existing dischargers
to
LakeErie
~Section
39(a) of
the Illinois Environmental Protection Act clearly places the burden
on
the
applicant to offer
“proof’
that its proposed permit “will not cause the a violation ofthis Act or of
regulations
thereof.”
Permits that allow discharges that
may
cause or contribute
to violations of
water
quality
standards violate 40 CFR 122.44(d) and the Illinois regulations that incorporate
those federal
requirements.
35
Ill. Adm. Code 309.141.
Accordingly, the Agency should not
grant NPDES permits
for
discharges without proofby
the applicant
that the discharge will
not
cause
or contribute to violations of
state
dissolved oxygen standards
and other standards.
10

In Re: Interim Phosphorus Effluent LimitR2004-26
and Lake Ontario.
In areas ofthe country where nutrients arebeing seriously addressed, limits
well below
0.5
mg/L are common. (see Testimony ofBeth Wentzel)
Moreover, given that the
U.S.
EPA 2000 and 2001
criteriadocuments for nutrients
suggest that Illinois numeric
phosphorus standards should be under .08
mg/L, an effluent limit of 1.0 mg!L should be seen
as
a very conservative step
even by those with hopes that the final Illinois water quality standards
will be
a substantial multiple ofthe U.S. EPA criteria.
B. Antidegradation requires that new or increase discharges be limited to 1
mg/L of phosphorus or less.
The Agency’s proposal is limited to new or increased discharges. Such discharges are
already subject to antidegradation regulations. Under the antidegradation regulations, lowering of
water quality may only be allowed if it is necessary to
accommodate important economic or
social development. 40 CFR
131.12;
35 Ill.
Adm. Code 302.105(c).
Treatment alternatives must
be considered. See 35 Ill. Adm.
Code 302.105(f)(1)(D) because a lowering ofwater quality is not
necessary if it can practicably be avoided.
As statedby 35 Ill.
Adm. Code
1 05(c)(2)(B)(iii), before a new or increased loading may
be allowed all “technically and economicallyreasonable measures to
avoid or minimize the
extent ofthe proposed increase in pollutant loading” must be incorporated.
U.S.
EPA in its
~WaterQuality
Standards Handbook
(4th
Edition 1994) explained:
Lowering
water quality is allowedonly
in a few extraordinary
circumstances where the economic
and social need for the activity
clearly outweighs the benefit ofmaintaining water quality above
that required for “fishable/swimmable” water, arid both cannot be
achieved. The burden of demonstrationon the individual proposing
such activity will be very high. In any case, moreover, the existing
use must be maintained and the activity shall not preclude the
maintenance ofa “fishable swimmable” level ofwater quality
protection. (p. 4-7)
11

In Re: InterimPhosphorus Effluent Limit112004-26
New or increased discharges ofphosphorus, then, are only permissible to the extent it is
necessary for dischargers to discharge more than a monthly average of 1
mg/L ofphosphorus.
It
is clear, however, that it is never necessary for the dischargers covered by the proposed IEPA
effluent limit to discharge more than
1
mg/L phosphorus. As detailed in the testimony ofBeth
Wentzel, dischargers throughout the Great Lakes Basin, very large numbers of dischargers across
the country and numerous Illinois
dischargers have met
suchlimits, in some cases for decades,
without stifling their economic orsocial development.
Particularly as limited to relatively large
dischargers, the Agency proposal adds little
to existing antidegradation requirements and
adoption ofthe Agency proposal by the Board willnot create significant new legal requirements
for Illinois dischargers. The main role ofthe new effluent rule will be to clarify forpermit writers
and permit applicants that phosphorus limits at least as tight as
1
mg/L will be required. (see
August 30, 2004 Tr.
54-55).
Conclusion
The IEPA phosphorus effluent limit proposal in general is supported by the provisions of
the Clean Water Act and the Illinois Environmental Protection Act. In furthertestimony,
language is proposed that would improve the proposal by clarifying its language and assuring
that it cannot be read to violate the basic federal and
state rules that NPDES permits must
comply with the antidegradation policy and cannot allow discharge ofpollutants that would
cause or contribute to the violation ofnumeric or narrative water quality standards.
12

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