Illinois Division of the Izaak Walton League
-
Illinois Council of Trout Unlimited
National Wildlife Federation
-
Natural Resources Defense Council
Prairie Rivers Network
REC
E I
VED
Re:
Comments on Proposed New 35 ILL . ADM
. CODE 225, Control of Emissions from
Large Combustion Sources (Mercury) ; R06-25
Dear Honorable Members of the Board ;
The undersigned organizations wish to express our support for the proposed rule filed
with the Illinois Pollution Control Board by the Illinois Environmental Protection Agency, as
amended and including the Ameren and Dynegy proposals ("the rule")
. We believe this rule is
necessary to protect the health of the citizens of Illinois, as well as the health of our fish and
wildlife populations, and is both technologically feasible and cost effective
.
First and foremost, adoption of this rule is critical to protecting the health of Illinois
citizens, especially our children
. Every year, thousands of pounds of mercury pollution are
emitted by coal fired power plants in Illinois
. Many experts have submitted comments to the
Board that detail the health impacts of mercury, but in short, it is a neurotoxin that passes
through the placenta and poisons fetal brain development
. Every day, thousands of developing
fetuses, newborns and young children are exposed to mercury when pregnant and nursing
women eat contaminated fish, or children eat fish themselves
. Six to ten percent of women of
childbearing age in the U .S
. are estimated to have mercury levels high enough to put their
developing children at increased risk for developmental problems from mercury poisoning
. That
translates to more than 100,000 women of childbearing age in Illinois whose blood mercury
levels may exceed the federal recommended limit
.
Further, coal fired power plants in Illinois have resulted in severe mercury hot spots in
some areas of the state
. The southern Great Lakes experience one of the highest deposition rates
in the U.S
. In this region, local and regional sources are the main cause of elevated mercury
concentrations, with the great majority of mercury contamination coming from coal fired powers
plants
. In fact, coal plants produce 71% of the mercury pollution in Illinois and 60% in the Great
Lakes states as a whole .
As a result, fish in Lake Michigan and all Illinois waterways are contaminated with
mercury
. So much so, that the Illinois Department of Public Health has issued "fish advisories"
warning sensitive populations
-
and particularly pregnant women, women of childbearing age
and children -
to limit their consumption of certain species of predator fish from every lake, river
and stream in the State .'
September 20, 2006
SEP 2 0 2006
Office of the Clerk
Illinois Pollution Control Board
100 West Randolph
Chicago, IL 60601
~%
STATE
O
Control
ec~
Bod
At the same time, mercury in fish is not just a threat to the health of those who consume
it
. There is mounting evidence that mercury levels in fish can affect their ability to reproduce, as
well as survive, endangering the health of fish populations themselves
. Recent research has
documented mercury effects on fish (at what could be considered more typical environmental
exposure levels) that include lower reproductive success due to decreased spawning and
increased embryo mortality 2;
altered sex hormones
; and increased vulnerability because of
particularly
adverse effects
high
on
levels
development
of mercury
and
occursdifficulty
4.
Of
schoolingall
freshwater
.3
Death
fish
has
species
occurred
studied,
when
walleye
exposure
(a
to
popular
Studies
Great
in the
Lakes
Great
sport
Lakes
fish)
have found
on average
that the
have
walleye
some of
have
the
a
highest
high energetic
mercury levels
rate and
documentedconsume
.
mercury
more fish
levels
and therefore
have been
more
shown
mercury
to reduce
compared
juvenile
to other
growth
species
rates
of
.
5
predator fish
. These elevated
Scientists have also found high levels of mercury in yellow perch in the Great Lakes
which is of concern given the importance of these fish as prey for many other species of fish and
wildlife6.
Studies have also shown that elevated levels of mercury in largemouth bass-another
popular sport fish in Illinois and an important food source for many species of wildlife-have
altered hormone profiles, indicating that mercury may be affecting the health of these fish
.
Much research has been done on the impacts of mercury on wildlife species as well
.
Studies have shown that many species of birds that live in and along rivers, lakes and wetlands
and
implications
feed on fish
for their
or other
healthaquatic
. Documented
prey also
impacts
accumulate
of elevated
mercury
mercury
in their
levels
systems
in
with
birds
seriousinclude
lower reproductive success due to fewer smaller eggs, lower hatch rates, altered chick behavior
and lower survival rates, and decreased nest attendance
s ; behavior abnormalities
; and
neurological and physiological problems such as tremors, difficulty flying, walking and standing,
reduced feeding and weight loss, wing and leg weakness, spinal cord degeneration, and disrupted
hormone levels
.`' A wide range of birds around the country, including bald eagles, egrets and
terns, have been found to have elevated levels of mercury, and loons tested in the Great Lakes
and elsewhere have often been found to have very high mercury levels because of their long lives
and their diets made up largely of fish
. 10
impacting
Mercury
many other
effects
species
are not
of
limited
wildlife
to fish
including
and shore
mammals
birds,
such
howeveras
mink,
. This
bats
pollutant
and riveris
also
otters-the latter being of particular concern in Illinois where endangered river otters are
beginning to make a come back in the wild
. The effects on mammals range from physiological
problems such as impaired sensory and motor skills, to reproductive problems
.
"
Effects, which
we
lifewill
.
not detail here, have also been noted in amphibians and reptiles, songbirds, and marine
Healthy fish and wildlife populations play an important role in the Illinois economy, The
most recent survey conducted by the US Fish and Wildlife Service indicates that more than 4
.5
million people participated in wildlife-associated recreation activities in Illinois in 2001,
including fishing, hunting, and bird watching
. Expenditures for these activities in just one year
included $595 million for fishing, $450 million for hunting, and $814 million for wildlife
watching (defined as observing, feeding, and photographing wildlife)
.
12
Given these important
benefits to our economy, it makes sense to eliminate a source of pollution that could have
significant negative impacts on a wide range of fish and wildlife in the state .
By regulating the leading source of mercury pollution in Illinois
- coal fired power plants
-
we can reduce mercury exposure and the resulting health effects of that exposure for humans
and fish and wildlife
. Studies show a direct relationship between reducing mercury deposition
and reducing mercury levels in fish and conclude that reducing emissions of mercury lowers
mercury concentrations in fish, regardless of contributions from natural or foreign sources
. In a
2002 study in Wisconsin for example, researchers correlated a decrease in atmospheric mercury
loading into a Wisconsin lake with a 30% reduction in fish tissue mercury concentrations after
only six years .
13
Another study in Florida showed that a reduction in local atmospheric mercury
emissions led to a decline of more than 80% of mercury contamination in fish and wildlife
.
14
Reducing mercury pollution and deposition in Illinois would likely have similar benefits, and
thereby reduce the risks for human exposure and the associated public health impacts, as well as
the risks for fish and wildlife populations.
While federal rules have been adopted by the Bush administration to regulate mercury
emissions, they are inadequate to address the problem of mercury contamination in Illinois
. Not
only are the federal rules less stringent in their requirements for reducing levels of mercury
emissions despite the availability of technology to achieve greater reductions, but the rules will
also perpetuate mercury hot spots like those in Illinois by allowing coal plants to continue using
older technology and also purchase the right to continue polluting at high levels rather than
installing equipment to clean up their plants and protect our health and environment
. The Illinois
rule is needed to provide those protections that the federal rules lack
.
The Illinois rule as drafted, including amendments and Ameren's and Dynegy's
proposals, is sound and will be effective
. First, states such as Georgia, Maryland, Massachusetts,
Michigan, Minnesota, New Jersey and Pennsylvania, among others, have adopted or initiated
proposals that would go beyond the federal rules and require mercury reductions from power
plants similar to those in the Illinois proposed rule, demonstrating that this rule is reasonable and
the bases for it are sound
.
Second, the IEPA and proponents made the necessary showing at the hearings and in
filings that the rule is both technically feasible and economically reasonable
. Specifically, the
technology for controlling mercury in accordance with the requirements of the rule is readily
available. Activated carbon injection
("ACI"), with brominated or halogenated sorbents where
appropriate, has been shown to achieve 95-percent capture rates in short-term tests for all ranks
of coal burned in Illinois
. Where 90% is not achievable with ACI alone, other pollution control
options can be used to achieve 90%, including controls for other pollutants that provide
additional mercury reductions .
The technology is also economically reasonable
. The reductions required by the proposed
rule could be achieved while costing Illinois residential consumers only $0
.69 more per month,
on average. Commercial businesses would pay about $5
.82 more on average, while the average
industrial bill would increase $305
.47 monthly
. The cost of ACI per unit is less than one million
dollars .
Finally, there is sufficient flexibility in the rule for operators to choose a compliance
pathway that is appropriate for them in terms of both means and timing of achieving the
necessary reductions
. The flexibility built into the rule includes
: 1) the initial averaging period,
2) the output based standard, 3) the temporary technology-based standard, and 4) Ameren and
Dynegy's proposed multi-pollutant standard
. Moreover, Ameren and Dynegy's support for the
rule demonstrates that facilities within the state of Illinois can achieve the required reductions
contained in the proposed rule in a cost-effective manner
. In fact, Dynegy has already
committed, as part of a recent settlement agreement, to installing this equipment at its Oakwood
plant by 2007 with a goal of at least 90% reduction in mercury emissions
. Clearly, they believe
the reductions proposed in the rule are attainable .
For all of these reasons, our organizations support the proposed rule, believe it is
necessary to protect public health and the environment in Illinois, and encourage the Board to
vote in favor of it .
Sincerely,
Terry Fanning, President
Illinois Division of
Ed Michael, Vice Chair
Illinois Council of Trout Unlimited
the Izaak Walton League
Andy Buchsbaum, Director
Laurel O'Sullivan
Great Lakes Natural Resources Center
National Wildlife Federation
Great Lakes Campaign Coordinator
Natural Resources Defense Council
Jean Flemma, Executive Director
Prairie Rivers Network
Illinois Department of Public Health, Sport Fish Consumption Advisory, 2006
.
Fathead
2 Drevnick,
MinnowsPE
and
.
Sandheinrich,
Environmental Science
MB
. 2003,
and
Effects
Technology,
of Dietary
37
:4390-4396Methylmercury
.
on Reproductive Endocrinology of
Reproduction
Hammerschmidt,
of
CR,
Fathead
Sandheinrich,
Minnows, Environmental
MB, Wiener, JG,
Science
and Rada,
and Technology
JG
. 2002
.
36Effects
:877-883of
Dietary
.
Methylmercury on
effects
Matta, MB,
of methylmercury
Linse, J, Cairncross,
or aroclor
C,
1268
Francendese,
on Fundulus
L,
heteroclitusand
Kocan, RM
.
.
Environmental
2001
. Reproductive
Toxicology
and transgenerational20
:327-335 .
Fishery
Dawson
Bulletin
MA. 198280
:389-392
. Effects
.
of Long-Term Mercury Exposure on Hematology of Striped Bass, Morone saxatilis
.
Hara, TJ, Law, YMC, and Macdonald, S . 1976
. Effects of mercury and copper on the olfactory response in rainbow
trout, Salmo gairdneri
. Journal of the Fisheries Research Board of Canada 33
:1568-1573 .
Webber, HM and Haines, TA
. 2003
. Mercury effects on predator avoidance of behavior of forage fish, golden
shiner
. Environmental Toxicology and Chemistry 22 :1556-1561 .
° Matta et al, 2001 .
s Mathers, RA and Johansen, PH . 1985
. The effects of feeding ecology on mercury accumulation in walleye and
pike in Lake Simcoe
. Canadian Journal of Zoology 63 :2006-2012
.
Friedmann, AS, Watzin, MC, Brinck-Johnsen, T, and Leiter, JC
. 1996, Low levels of dietary mercury inhibit growth
and gonadal development in juvenile walleye
. Aquatic Toxicology 35 :265-278 .
6
Kamman, NC et al
. 2005 . Mercury in freshwater fish of northeast North America
- a geographic perspective based
on fish tissue monitoring data bases
. Ecotoxicology 14 :163-180 .
Friedmann, AS, Costain, EK, MacLatchey, DL, Stanley, W, and Washuta, EJ
. 2002
. Effect of mercury on general
and reproductive health of largemouth bass from three lakes in New Jersey
. Ecotoxicology and Environmental
Safety 52
:117-122 .
Kamman et al. 2005 .
s DeSorbo, CR and Evers, DC
. 2006
. Evaluating exposure of Maine's Bald Eagle population to mercury
: Assessing
impacts on productivity and spatial exposure patterns
. Erpot BRI 2006-02
. Biodiversity Research Institute, Gorham,
Maine .
Evers, DC, Taylor, KM, Major, A, Taylor, RJ, Poppenga, RH, and Scheuhammer, AM
. 2003
. Common loon eggs as
indicators of methylmercury availability in North America
. Ecotoxicology 12 :69-81
.
Frederick, PC, Hylton, BA, Heath, JA, and Spalding, MG
. 2004
. An historical record of mercury contamination in
southern Florida as inferred from avian feather tissue
. Environmental Toxicology and Chemistry 23
:1474-1478 .
Schwarzbach, SE, Albertson, JD, and Thomas, CM . 2006
. Effects of predation, flooding and contamination on
reproductive success of California clapper rails in San Francisco Bay
. Auk 123 :45-60 .
° Heath, JA and Frederick, PC
. 2005
. Relationships among mercury concentrations, hormones, and nesting effort of
White Ibises in the Florida Everglades . Auk 122 : 255-267
.
Spalding, MG et al . 2000
. Histologic, neurologic, and immunologic effects of methylmercury in captive Great
Egrets . Journal of Wildlife Diseases 36
:423-435 .
10
Evers, DC, Kaplan, JD, Meyer, MW, Reaman, PS, Major, A, Burgess, N, and Braselton, WE
. 1998 .
Bioavailabilty of environmental mercury measured in Common Loon feathers and blood across North America
.
Environmental Toxicology and Chemistry 17 :173-183 .
Meyers, MW, Evers, DC, Hartigan, JJ, and Rasmussen, PS
. 1998
. Patterns of common look mercury exposure,
reproduction, and survival in Wisconsin
. Environmental Toxicology and Chemistry 17
:184-190 .
Scheuhammer, AM, Atchison, CA, Wong, AHK, and Evers, DC
. 1998
. Mercury exposure in breeding common
looks in Central Ontario, Canada
. Environmental Toxicology and Chemistry 17
:191-196 .
Scheuhammer, AM, Perrault, JA and Bond, DE . 2001
. Mercury, Methylmercury, and Selenium Concentrations in
Eggs of Common Loons from Canada
. Environmental Monitoring and Assessment 72 :79-94
.
Evers et al. 2003 and 2005
.
mercury
2411
Basu,
:1444-1450on
N,
neurochemical
Klenavic,
.
K,
receptor-binding
Gamberg, M, O'Brien,
characteristics
M
., Evans,
in
D,
wild
Scheuhammer,
mink
. Environmental
AM, and Chan,
Toxicology
HM
. 2005a
and ChemistryEffects
of
mercury
Basu, N,
on
Scheuhammer,
neurochemical
A,
receptors
Grochowina,
in wild
N,
river
Kelnavic,
ottersK,
.
Evans,
Environmental
D.,
O'Brien,
Science
M,
and
and
Toxicology
Chan, HM .
3920056:3585-3591
. Effects
.
of
CanadaMierle,
:
G,
Variation
Addison,
in age,
EM,
sex,
MacDonald,
and locationKS
and
. Environmental
Joachim, DG
.
Toxicology
2002
. Mercury
and
levels
Chemistry
in tissues
19
:3044-3051of
otters
.
from Ontario,
Environmental
Facemire, CF, Gross,
Health
TS,
Perspectives
and Guillette,
103 SupplLJ
. 1995.4:79-86
. Reproductive
.
impairment in Florida panthers
: nature or nurture?
12 US Fish and Wildlife Service
. 2001
. National Survey of Fishing, Hunting, and Wildlife-Associated Recreation
.
13 Hrabik, TR and Watras, CJ
. 2002
. Recent declines in mercury concentrations in a freshwater fishery
: Isolating the
Total
effects
Environment
of de-acidification
297.1-3
:229-37and
decreased
.
atmospheric mercury deposition in Little Rock Lake
. The Science of the
Cycling
14
Florida
in
Department
Southern Floridaof
Environmental
: An Approach
Protectionfor
Conducting
. Integrating
a Total
Atmospheric
Maximum Daily
Mercury
Load
Deposition
Analysis
with
for
Aquatican
Atmospherically Derived Pollutant, (October 2002, Revised 2003) 88-99
.