Economic
Cost of Mercury/Toxic Metals Emissions in Florida 6-1-07
High
levels of mercury have been found in the rain throughout Florida and the U.S.(42,11),
resulting in accumulation of mercury in the environment, water bodies, fish,
wildlife, and people of Florida. Approximately 30 % of Floridians tested for
mercury in 2 studies had dangerous levels of mercury body burden(32).
The
largest sources of emissions have been found to be coal power plants and incinerators(11). The
level of mercury in rain ranged from 1.3 to 81.2 nanograms
per liter depending on location and weather conditions, with an average of
12.6. This resulted in average annual deposition
of about 17.6 micrograms of mercury per square meter, much higher than the U.S.
EPA health criteria to prevent harm to wildlife and humans (42,43). The Electric
Power Research Institute(38) and other studies have found that only ˝ gram of
mercury is required to contaminate all predator fish in a 10 acre lake to the
extent that fish consumption warnings are required, and enough mercury is being
released into the environment of Florida to raise levels in all predator fish
to such a level. From past monitoring
and laboratory experiments, it is projected that another significant source of mercury
in the environment is from temperate/boreal forest fires and from all
biomass burning(51). "The
combustion of litter and green
vegetation under controlled burn conditions resulted in essentially complete
release of mercury contained in fuel. This is different and higher than
releases reported for some coal and biomass burning. Highest mercury
concentrations were found in litter, reflecting accumulation of dry and wet
deposition mercury over growing seasons. A suggested regional difference in
mercury concentrations in vegetation coincides with the known highest dry/wet
deposition rates in the US northeast and northwest. Mercury is emitted almost
exclusively as elemental mercury (TGM, >95%) and thus joins the global pool.
..." (51)
____________________________
Another
significant source of mercury in Florida water bodies is dental amalgam. Dental
amalgam is documented by medical lab tests to be the largest source of
mercury in most people with several amalgam fillings, and the largest source of
mercury in sewers and sewer sludge
, and thus a significant source of mercury in fish and wildlife. Since mercury vaporizes continuously at room
temperature, mercury in sewer sludge outgases and there are significant air
mercury emissions from crematoria.
The majority of lakes and rivers in Florida
tested and thousands in other states have been documented to have dangerous
levels of mercury and other toxic metals accumulating in sediments and in the
fish and food chain (3,6,9,10,11,28,36). Health warnings have been issued against
eating fish in the hundreds of lakes or
rivers affected(9,36,6), as well as against eating sharkmeat
caught throughout Florida or several
types of saltwater fish from areas of the Florida East Coast or Panhandle Gulf
Coast due to dangerous levels of mercury in the fish (28,29,33,36). Florida commercial fishermen sold 6.8
million pounds of sharkmeat in 1989, 36% of the U.S.
total. Over 1/3 of the shark meat tested
in Florida has been found to have dangerous levels of mercury(33).
Twenty seven other commercially important coastal fish or seafoods have dangerous levels of mercury
according to experts and tests(28,36).
High levels of toxic metals have been found in shellfish in many areas
of the state (36,28).
This represents a major economic cost to both Florida and the U.S.
The level of mercury emissions of
Florida coal plants and incinerators prior to the addition of improved emission
controls (over 4 tons per year (20)), as well as the current levels of
emissions appear to be far above the level required for depositions over large
areas of Florida to be above the level previously documented to be sufficient
to bioaccumulate to dangerous levels in fish (20,38,11,42,43). There
is consensus among researchers that the main source of the mercury in lakes is
from air emissions, with the largest sources being municipal incinerators,
medical waste incinerators, and coal plants in most areas
(6,9,11,29,31,34-39,20). Emission
levels had been found to be increasing since the 1900s with the largest
increases in since the 1940s(30,35,39). Toxic levels of aluminum and other toxic
metals also appear to be the main factor adversely affecting fish and other
organisms in lakes or streams that are becoming acidic throughout the U.S. Florida has the most acidic lakes in the
U.S. Commercial fishermen and the sportsfishing sector have already been seriously adversely
affected. There is also consensus that
acidity and acid pollutants are major factors in the level of toxic metals
getting into fish and the food chain (6,11,35,46). Mercury emissions from incinerators have been
significantly reduced in recent years due to a requirement to improve emission
controls. However mercury and other toxic levels in ash have likely thus
increased, making the ash more toxic than before.
According to the Fla. Fish & Wildlife Commission(40,41), the freshwater(bass) fishery in Fla. is
responsible for over $1 billion in direct sales per year to the Florida economy
in 1990 . According to a 1980 survey of sports fishermen by
the U.S. Fish and Wildlife Service(40), there were over 23 million freshwater
fishing trips by sports fishermen with the average trip spending $26.79 on
bait, tackle, gas for boats, and lodging alone. This $615 million would have
been only a portion of the total value of the fishery, which would be at least
double that amount now for all freshwater fishing expenses affected. Over half of the fishery has been affected by
health warnings and studies have indicated a decline of approx. 20 % in fishing
in areas studied that have well publicized advisories. The adverse publicity has affected the entire
state. This means a loss of approx. $400
million in reduced expenditures on freshwater fishing trips and equipment each
year alone. If 50% of the estimated 40
million pounds of bass caught and eaten in Florida each year during the early
1980s are now not eaten and had their economic value subtracted at $1 per pound due
to the hazardous levels of mercury, this would
be $20 million in reduced value of bass meat. This would not include the other types of
freshwater fish affected which would add at least $10 million more. Over 1 million acres of streams and lakes are
affected by health advisories in Fla., with the affected areas producing
approx. 20 harvestable bass(> 10 inches) per acre
per year. This alternative calculation
of the value of the bass gives 20 million bass affected in affected areas and at an average of 1.5
pounds per bass(40) gives 35 million pounds of bass affected. At $1per pound this would give $35
million. Thus the direct impact on the
Fla. freshwater and saltwater fisheries appears to be over $445 million, not
counting any indirect economic effects or adverse health effects on people
eating such fish.
A study by the Florida Fish and Wildlife
Conservation Commission found that direct sales and taxes related to saltwater fishing were over $4.4
billion per year(41), representing over 3 million anglers(45,42). If a 20%
reduction in economic value similar to the one found for fresh water fish
warnings were assumed, this would amount to $880 million in losses per
year. Counting shark meat alone, over 2
million pounds of salt water fish per year are estimated to be contaminated
with dangerous levels of mercury alone, and at $1.50 per pound would give at
least $3 million, not counting adverse health effects. Since it has been found
that most Florida saltwater commercial species have dangerous levels of
mercury, the total losses are likely many times this amount. There have likely been at least this much in
additional losses in
lower amounts of saltwater fish and shellfish being eaten due to
the adverse publicity.
The
U.S. Center for Disease Control(CDC) and other federal agencies rank toxic
metals as the number one environmental health threat to children, adversely
affecting millions of children in the, U.S. each year(1-4,7-11,18). According to an EPA assessment, the toxic metals
mercury, lead, arsenic, cadmium, chromium, and nickel are all ranked in the top
12 toxics having the most adverse health effects on the U.S. public based on
toxicity and current exposure levels(2).
EPA and CDC indicate that over 3 million children have their health
significantly adversely affected or learning ability significantly adversely
affected by lead in drinking water, mercury in fish, or other toxic metals from
emissions(1-4,7,8,18). Evidence
indicates that over 60,000 children are born each year with neurodevelopmental
impairment due to methylmercury(4,18). As noted,
emissions are the main source of mercury in lakes and streams and acid
pollutants are a major factor in the level of mercury or other toxic metals in
fish and of lead or cadmium in drinking water(11,20,9).
Some persons have
been diagnosed with mercury poisoning from saltwater fish, as
well as from freshwater fish. Studies (36,32) have also found that the level in
most large predator species on the Gulf Coast is higher than levels found to
adversely affect health(25) with mercury contamination being pervasive along
the whole coastal area, and that people who eat Gulf Coast fish at least once
per week usually have dangerous levels of mercury(36,32). 29% of a coastal
sample from Florida, Alabama, and Mississippi ate fish at least once per week(36,32). Thus would indicate that over 1 million
Floridians likely have dangerous levels of mercury exposure. A U.S. CDC study found that it is likely that
well over 1000 Florida babies per year have received exposures sufficient to
cause developmental disabilities(4,18,36).
Based on large numbers of medical studies
and government assessments of these studies, it appears that over 1 million
Floridians likely have significant developmental or adverse health effects
related to mercury(or other toxic metals)(18,32,36,1-4,7,25). If a very conservative estimate of the
average annual cost per person having a significant adverse learning disability
or health effect were estimated at
$3,000, the annual health cost due to
mercury or toxic metals would be over $3
billion per year. Florida appears
to be one of the states most adversely affected(9-11,28,36)
and health authorities believe mercury exposure from fish is the most
significant source.
Mercury, lead, aluminum, and other toxic
metals have been found to be accumulating in forest floors at levels high
enough to cause forest declines and diebacks in some areas of Europe and the
Eastern U.S(5). Both inorganic and
methyl mercury are toxic to spruce seedlings at levels of 0.4 to 0.5 ppm. Many areas of
Europe have passed this point in cumulative mercury buildup and some areas of
the Eastern U.S. are approaching this level(5). Toxic metals have also reached levels in
food crops in Europe documented to be
causing health problems, and vegetables cannot be grown in some regions or eaten safely in grown in
other regions. Levels are building up in
the food chain in the U.S.-especially in urban/industrial areas(39,36) and
including areas in south Florida with documented high deposition levels(29,36).
Gov’t studies have found that mercury deposited on
soil has mercury methylated to methylmercury
by soil bacteria of which some is transferred to crops and some is outgased when the sun shines to later come down in rain(50). This
represents another large potential economic loss, as well as from health
effects.
High levels of mercury have been found to
evaporate from fly ash piles at temperatures higher than 70 degrees F. Temperatures above 86 degrees would likely
produce levels of mercury in the vicinity violating EPA ambient air guidelines(11,12).
This could cause health effects on site, as well as being a regional
mercury source. Florida ash piles can
reach 140 degrees in the summer(11), and ash piles of
plants using lime to control sulfur often get much hotter than this due to
hydration. Additionally, mercury from
ash piles that is land spread or landfilled has been
found by government studies to be methylated to
highly toxic methyl and di-methyl mercury and be outgassed, being a factor in the high levels found in rain througout Florida(36,11).
The coal and ash piles from coal plants or
incinerators contain large amounts of toxic metals(as
well as dioxins, furans,etc.) which can affect both
ground and surface water, as well as considerable particulate and toxic air
emissions. Widespread serious health
effects have been documented for plant
workers working with ash at the facility or ash piles(11). This has been confirmed both in Florida and
other states with ash piles. A coal
plant with scrubbers per megawatt of power generated produces about 308 tons of
fly ash, 77 tons of bottom ash, and 364 tons of flue gas desulfurization waste
for landfilling- all containing toxic metals and
other toxic constituents(13). Many coal ash laboratory tests have found
cadmium and arsenic at levels considered hazardous per EPA RCRA standards(13). Many toxic constituents from coal combustion
waste disposal sites have been detected in both on-site and off-site ground
water and surface water. Where the depth to groundwater is less than 30 feet,
"there is a reasonably high potential that leachate
will reach groundwater" unless extensive precautions are taken(13). The high
PH that often characterizes Western coal tends to cause the release of harmful
toxic metals such as arsenic, selenium, and manganese. In Florida, radionuclides,
mercury, and other toxic metals have been found in sediments and the food chain
in rivers and bays near coal and ash piles.
The average cost of disposing of hazardous
waste in the Midwest is $210 per ton(26). The Dept. of Environmental Regulation reports
that the cost of recent contracts in Florida has ranged between $250 and $360
per ton, including transportation and taxes.
Assuming that a conservative $250 per ton is the public cost of
disposing of fly ash(or of related health effects),
that $100 per ton is the cost of disposing of bottom ash, and $50 per ton is
the cost of disposing of desulfurization waste
gives a total cost of ash disposal per MW of coal plant power of (308 x
$250 + 77 x $100 + 364 x $50) = $102,900 per year. Assuming a 70 % capacity factor gives 6132
megawatt-hours per MW of power. Thus the
ash disposal cost would be 1.7 cents per kwh.
The ash from incinerators contains more
toxic metals, and other toxics such as dioxins or furans, than coal ash; most incinerator
fly ash tested has been shown to be toxic under EPA toxicity standards and much
is in a soluble form(14, 15, 21-24). The
metals most commonly failing the toxicity test are cadmium and lead, but high
levels of mercury, arsenic, and chromium have also been found(24). Some states already require ash to be tested
and disposed of as toxic waste. Tests by the State of New York showed more than
half of its incinerator waste tested was "hazardous" and all waste in
New York will be disposed of in hazardous waste sites or special sites with
additional precautions(19a). Bottom ash has also been found to have
relatively high levels of toxics(24). The toxics in ash has been documented to have
widespread and serious health effects on those working with the ash at
facilities, and the health effects on the public from trace metals and dioxins
have been shown to be higher than for the traditional pollution emissions
normally considered(16). Ash disposal
has also been found to face much higher cost than normal landfilling
due to: abrasive impact on equipment & tires, corrosive effect on
equipment, unworkability when wet, and health effects
on workers(19b).
Many researchers think ash disposal and pollution cleanup from ash pile
toxics will become increasingly expensive.
The 160 MSW incinerators operating in
the U.S. produce about 8 million tons of ash each year containing, by rough
estimate, some 18,000 tons of lead, over 50 tons of mercury, plus lesser
quantities of other potent toxins such as cadmium, arsenic and dioxin.[ Assuming the 8 million tons are 90% bottom ash containing 2000 ppm lead and 10% fly ash containing 4000 ppm lead](23).
Ash containing 2000 ppm lead is contaminated
at a level more than 5 times as high as the "level of concern" EPA
recently set for lead in soil.
Hazardous
waste can cost up to $300 per ton for burial at a legally-designated hazardous
waste dump. Judi Enck of the New York Public Interest
Research Group estimates that ash can be placed in an "ash monofill" for only $70 or $80 per ton(23).
A 1000 ton per day mass burn incinerator at
76% capacity produces 25 megawatts
of
power and 138 million kwh per year, along with 100
tons of fly ash and 200 tons of bottom ash per day. At $100 per ton for fly ash disposal(26,23) and $50 per ton for bottom ash disposal, the
total disposal cost would be $7,300,000 per year. This gives a cost of 5.3 cents per kwh.
Florida utilities burned 33,654,000 tons
of coal in 1999(27). Based on the EPA
estimate of .21 ppm mercury in Eastern coal, this
would give approx. 7
tons of mercury in the coal burned in Florida per year. The mercury not emitted in the flue or from
the ash piles would end up in the ash pile, which would be highly toxic. Fla. utilities burned 56.3 million barrels of
oil in 1999, and using EPA estimates for .06 ppm
mercury in residual oil and .4 ppm in distillate oil,
would give approx. 0.62 tons of mercury in oil burned by Fla. utilities. Based on current technology it appears
likely that the majority of such mercury was emitted directly or indirectly.
Similarly
municipal solid waste incinerators were projected to burn approx. 5.8 million
tons of garbage in 1991, with an average mercury content of 2 ppm
according to EPA data. This would give a
content of approx. 10 tons of mercury, much of which would be emitted.
Currently more tons are burned with a lower mercury level but the total amount
may be similar. FDEP estimates of MSW
incinerator mercury emissions are lower due to additional emission controls
added a few years ago . But high levels of mercury and toxic metals
would be in the ash. Based on this and
previous studies by the Dept. of Environmental Regulation, it is assumed that
coal power plants are responsible for approx. 25 % of Florida mercury emissions
and MSW incinerators for 10% of mercury emissions. Fla. coal plants generated 78,413,000,000
kilowatt hours of electricity in 1999 and MSW incinerators generated
2,684,000,000 kwh of
electricity. If economic cost due to
mercury(and other toxic metals) emissions is assumed to be $1251 million
per year, with coal plants responsible for 25% of emissions and MSW
incinerators for 10% of emissions, then the economic cost related to coal plant
emissions would be 0.4 cents per kwh of electricity
generated. Likewise for MSW
incinerators, the economic cost would be 4.7 cents per kwh generated.
So the total metals related environmental cost for coal plants would be
approx. 2.1 cents per kilowatt-hour, while the corresponding cost for municipal
incinerators would be 12.9 cents per kilowatt-hour. Since biomass plants are
generally less efficient than coal plants and often have less effective
controls, biomass plant mercury emission cost may be somewhat similar to those
for coal plants, but it would also depend on the mercury deposition levels and
patterns in the area of the fuel source and whether litter from tree cutting is
also burned.
REFERENCES
(1) US. Dept. of Health, ATSDR, www.atsdr.cdc.gov/toxfaq.html ; & U.S.
EPA, Lead in your drinking water, 1993, www.epa.gov/safewater/Pubs/lead1.html; & U.S. Centers for Disease Control,
Childhood lead poisoning in the U.S. 1997,
www.cdc.gov/nceh/programs/lead/guide/1997/pdf/chapter1.pdf &
Screening Young Children for Lead Poisoning. Atlanta, GA:Centers for Disease Control and
Prevention, 1997. & Neilke HW, Reagan PL, Soil is an important
pathway of human lead exposure. Environ
Health perspect 1998, 106:217-29.;
& www.intelihealth.com/IH/ihtIH/WSIHW000/333/8895/339795.html
(2)
ATSDR/EPA Priority List for 2005: Top 20 Hazardous
Substances, Agency for Toxic Substances and Disease Registry,U.S.
Department of Health and Human Services,
www.atsdr.cdc.gov/clist.html;
&
(b) U.S. EPA, Region I, 2001, www.epa.gov/region01/children/outdoors.htm
(3)
U.S. Geological Survey, The Occurrence of Mercury
in the Fishery Resources of the Gulf of Mexico; http://mo.cr.usgs.gov/gmp/hg.cfm
&, Estuarine Research
Federation
http://erf.org/user-cgi/conference_abstract.pl?conference=erf2001&id=4 ; & http://gill.tamug.tamu.edu/Projects/Articles/hgreport.pdf
& (b)SFWMD, 2003 Everglades Consolidated Report, Appendix
2B-4: Preliminary Report on Florida Bay
Mercury
http://www.sfwmd.gov/org/ema/everglades/consolidated_03/ecr2003/appendices/app2b-4.pdf
and © Florida DOH Mercury
Saltwater Fish Advisories, 2004
www.doh.state.fl.us/environment/hsee/fishconsumptionadvisories/MEFG.htm
& D.H.Adams,
R.H.McMichael, Florida Marine Research Institute,
Technical Reports, Mercury Levels in Marine and Estuarine Fishes of Florida,
2001; & Mercury in Marine
Fish, Florida Fish & Wildlife
Conservation Commission, http://capmel.com/Mercury_in_fish.htm
(4) Science
News, Methylmercury’s toxic toll. July 29, 2000, Vol 158, No.5,
p77; & National Research Council, Toxicological
Effects of Methylmercury, National Acadamy Press, Wash, DC, 2000; & U.S. Centers for
Disease Control, Mar 2001, Blood and Hair Mercury Levels in Young
Children and Women of Childbearing Age
--- United States, 1999
www.cdc.gov/mmwr/preview/mmwrhtml/mm5008a2.htm
(5) Proceedings, International
Conference on Mercury as an Environmental Pollutant, Gavle, Sweden June 11-13,
1990.
(6) United States Environmental Protection Agency, Office of Water, June
2003, The National Listing of Fish and Wildlife Advisories: Summary of 2002
Data, EPA-823-F-00-20,www.epa.gov/waterscience/fish/ ; & U.S. EPA, Office
of Water, Mercury Update: Impact on Fish Advisories-Fact Sheet,
http://www.epa.gov/ost/fish/mercury.html;
& J.Raloff,
"Mercurial Risks from Acids' Reign", Science News, March 9,1991;
& J Raloff, Why the
mercury falls, Science News, V 163, Feb 1;
(7)
National Academy of Sciences, National Research Council, Committee on
Developmental Toxicology, Scientific Frontiers in Developmental Toxicology
and Risk Assessment, June 1, 2000,
313 pages; & Evaluating
Chemical and Other Agent Exposures
for Reproductive and Developmental
Toxicity Subcommittee on Reproductive and Developmental Toxicity, Committee on Toxicology, Board on
Environmental Studies and Toxicology, National Research Council National Academy Press, 262 pages, 6 x 9, 2001; & National Environmental Trust (NET), Physicians for Social Responsibility
and the Learning Disabilities
Association of America, "Polluting
Our Future: Chemical Pollution in the U.S. that Affects Child Development and
Learning" Sept 2000;
http://www.safekidsinfo.org
(8) U.S. Enviromental Protection Agency, Hazardous Air Pollutant
Hazard Summary Fact Sheets, EPA: In Risk Information System, 1998,
www.epa.gov/grtlakes/seahome/mercury/src/ways.htm; & EPA spokesman, U.S.News &
World Report, “In the Air that
they Breathe”, Science &
News, 12-20-99. & U.S. Environmental Protection Agency(EPA),
1996, "Integrated Risk Information System,
National Center for Environmental Assessment, Cincinnati, Ohio(&
webpage);& EPA spokesman, U.S.News & World Report, “Kids at Risk”(cover
story), 6-19-2000;
(9) Florida Department of Health, Bureau of Environmental Toxicology,
Health Advisories for Mercury in Florida Fish
2004, http://www.doh.state.fl.us/environment/community/fishconsumptionadvisories/Fish_consumption_guide.pdf
; & FDEP, Toxic metal levels in Florida
shellfish, 1990; & Mercury Studies in the Florida Everglades, http://sflwww.er.usgs.gov/publications/fs/166-96/
; & Tom Atkeson,
Florida Dept. of Environmental Protection Mercury Coordinator, "Mercury in Florida's Environment",
Aug 18,1994;
(10)
Forrest Ware, Game & Freshwater Fish Commission, "Results of Tests
for Mercury in Florida Bass",
1990.
(11) "Environmental and Health Effects of Toxic Metals
& the Relationship to Acid Pollutants and Incineration",
1999(annotated bibliog.) www.myflcv.com/tm98.html
(12)
S.E. Lindberg, "Emission and Deposition of Atmospheric Mercury
Vapor", in lead,
mercury, cadmium, and Arsenic in the
Environment, John Wiley & Sons,
Ltd, NY, 1987.
(13)
U.S. EPA, Waste from the Combustion of Coal Power Plants, Report to Congress, Feb
1988.
(14)U.S.
EPA, Municipal Waste Combustion Study, Report to Congress,
EPA/530-5w-87-021a, June 1987.
(15)
Congressional Office of Technology Assessment, Facing America's Trash, OTA-0-424, USGPO, Oct 1989.
(16) Radian Corporation/U.S.EPA, Assessment of Health Risks
Associated with Municipal Waste Combustion Emissions, EPA/530-SW-87-02, 1989
(17) Journal of Chromatography, Vol
389,1987,pp 127-137 & Dr. Barry
Commoner, in Remote Access Chemical
Hazards Electronic Libray(RACHEL), Hazardous
Waste News, No. 45, Oct 5,1987 &
Science, Vol 237, Aug 14, 1987, pp754-756.
(18) Effects of Toxic Metals on Learning Ability and Behavior ,2005, www.flcv.com/tmlbn.html
(annotated bibliog.-over 250
references)
(19)
(a)Wall Street Journal, Oct 13, 1987. & (b) The Sentinel, Rome, N.Y., July
1986.
(20) KBN Engineering
and Applied Sciences, Inc. Mercury
Emissions to the Atmosphere in Florida, Final Report, Aug 1992, prepared for FDEP; & (b) “Estimated Florida mercury emissions from coal-burning power
plants” EWG,
www.ewg.org/reports/mercuryfalling/Florida.pdf
(21) RACHEL'S
HAZARDOUS WASTE NEWS #390 May 14, 1994 http://www.ejnet.org/rachel/rhwn390.htm & RACHEL'S HAZARDOUS WASTE NEWS #391 ---May 26, 1994--- http://www.ejnet.org/rachel/rhwn391.htm & RACHEL'S ENVIRONMENT & HEALTH
WEEKLY #457 ---August 31, 1995--- http://www.ejnet.org/rachel/rehw457.htm
(22)
U.S. Bureau of Mines, Bulletin 683, "Resource Recovery from Municipal
Waste" , & U.S. EPA, Region III, Environmental News, Oct
31,1984.; & Waste Age, Feb 1981,
p66-68.
(23)
RACHEL'S HAZARDOUS WASTE WEEKLY #403, 1994, www.ejnet.org/rachel/rehw403.htm
; & RACHEL Hazardous Waste News, No. 22, April 27, 1987;
& Environmental Pollution(Series A) 38,pp339-360, 1985.
(24)
Environmental Tests on Incineration Wastes, Environmental Health Perspectives,
59,pp159-162, 1985.
(25) (a) J. Hightower, “Methylmercury
Contaminmation in Fish: Human Exposures and Case
Reports," Environmental Health
Perspectives; Nov 1, 2002; & (b) A Oskarsson et al, Swedish National Food Administration,
Mercury levels in hair from people eating large quantities of Swedish
freshwater fish. Food Addit Contam
1990; 7(4):555-62; & (c)
Preventive Medicine February 2002;34:221-225; &(d) Dickman
MD; Leung KM, "Hong Kong subfertility links to
mercury in human hair and fish", Sci Total
Environ, 1998,214:165-74; & Mercury and organochlorine
exposure from fish consumption in Hong Kong. Chemosphere 1998
Aug;37(5):991-1015; &(e) Y.Kinjo et al,
"Cancer mortality in patients exposed to methyl mercury through fish
diet", J Epidemiol, 1996, 6(3):134-8; & (f) Choy C et al, Seafood consumption linked to infertility,
BJOG: An International Journal of Obstetrics & Gynaecology
2002 109:1121-5; &(g) J.T. Salonen et al, "Intake of mercury from fish and the
risk of myocardial infarction and cardiovascular disease in eastern Finnish
men", Circulation, 1995; 91(3):645-55; & Wisconsin Bureau of Public
Health, Imported seabass as a source of mercury
exposure: a Wisconsin Case Study, Environ Health Perspect
1995, 103(6): 604-6;
(26)
City of Chicago official, in New York Times, 11-17-92.
(27)
Florida Public Service Commission, Statistics of the Florida Electric Utility
Industry, 1999.
(28)Florida
Mackerel Mercury Warning; Florida Dept. of Environmental Regulation,
www.myflorida.com/chdcollier/health_alerts/health_alerts.htm#_Hlt516549004;
& Florida Marine Species Mercury Warning for Species in some water bodies
(Spanish mackerel, Ladyfish, Gafftop sailcat, Crevelle Jack, Spotted
sea trout-eat only one serving per month)
ftp://ftp.dep.state.fl.us/pub/labs/assessment/mercury/health/fha951006.pdf
& FDEP, Toxic metal levels in
Florida shellfish, 1990.
(29)
U.S. EPA, in Florida Environments, May 1994.
(30)
Brian Rood, Univ. of Florida study for Dept.of
Environmental Protection,
Tallahasse Democrat, June 6, 1994.
(31) J. Raloff, "Mercurial
Airs: Tallying Who's to Blame", Science News, 2-19-94; & Dr.S.Sundlof, Univ. of Florida Vetinary
College, Florida Environements, Oct 1993.
(32) Mobile Register, Mercury Series(Aug 2001 to
Mar 2002): Mercury Taints Seafood
www.al.com/specialreport/?mobileregister/mercuryinthewater.html
; & An
Investigation of Factors Related to Levels of Mercury in Human Hair, Environmental
Quality
Institute, October 01, 2005,
www.greenpeace.org/raw/content/usa/press/reports/mercury-report.pdf
www.greenpeace.org/usa/assets/binaries/addendum-to-mercury-report
http://www.consumeraffairs.com/news04/2006/02/mercury_sport_fish.html
(33)
Dr. Robert Hueter, Mote Marine Laboratory Center for
Shark Research, Sarasota Florida, July 19, 1994; & Tallahassee
Democrat, High Mercury Levels in Shark Meat, May 13,1991.
(34)
Compliance Stratigies Review, Fieldstom
Publications, Vol 5, No.12, 6-6-94.
(35) E.B.Swain et al, Minnesota
Pollution Control Agency, "Mercury in Fish from Northeastern Minnesota Lakes and
Historical Trends, Environemental Correlates,
Potential Sources", Journal of the Minn. Academy of Sciences, Vol Vol 55, No 1, 1989,p103-109; & "Increasing Rates of Atmospheric
Mercury Deposition in Midcontinental North America", Science, V257, Aug
7,1992; & Minnesota Pollution Control Agency, "Strategies for Reducing
Mercury in Minnesota" June 1994.
(36) Mercury in Florida freshwater and saltwater fish,
levels, sources, health effects, www.myflcv.com/fishhg.html
(37) E.A.Nater et al,
"Regional Trends in Mercury Distribution Across the Great Lakes States", Nature, Vol
348, July 9, 1992.
(38)
Electric Power Research Institute. Mercury in the
Environment. Electric EPRI Journal 1990; April,p5.
& Electric Power Research Institute, EPRI
Technical Brief:"Mercury in the
Environment", 1993; & Weiner,
JG et al, 1990, Partitioning and bioavailablity of
mercury in an experimentally acified lake,
Environmental Toxicology and Chemistry, Vol 9:
909-918.
(39)
J.O.Nriagu, "Global Metal Pollution- Poisoning
the Biosphere", Environment, Vol 32, No. 7,
Sept, 1990.
(40)
Florida Game and Freshwater Fish Commission, Office of Information
Services, 1993.
(41) Florida Fish & Wildlife Conservation Commission; Fish
and Wildlife Recreation Creates Huge Economic Boom for Florida, January 19,
2001 CONTACT: David Harding (850) 487-3794
www.floridaconservation.org/whatsnew/2001/econdata-st.html &
American Sportfishing
Association, U.S. Fish & Wildlife Service, Wash. D.C.,
Economic Impact of Fishing in Florida,
1996.
http://floridafisheries.com/updates/econ-2.html
(42) National Wildlife
Federation, Cycle of Harm: Mercury’s Pathway from Rain to Fish in the
Environment, May, 2003,
www.nwf.org/nwfwebadmin/binaryVault/CycleOfHarm111.pdf; & (b) NADP/Mercury Deposition Network, Total Mercury
Concentration, 2001; & Total Mercury Wet Deposition , 2001
(43) Water Quality Criterion for
the Protection of Human Health: Methylmercury, United States Environmental Protection
Agency, Office
of Water 4304
EPA-823-F-01-001, January 2001,
(44) Chronic Health Effects of Mercury
Toxicity, www.myflcv.com/indexa.html
(45)U.S. Fish and Wildlife Service, 2001, National Survey of
Fishing, Hunting, and Wildlife-Associated Recreation, Oct 2002.
(46)Effects of Acid Rain on Florida, www.myflcv.com/newar.html
(47)Agency for Toxic Substances and Disease Registry, U.S.
Public Health Service , Toxicological
Profile for Mercury",March 1999; & Apr 19,1999
Media Advisory, New MRLs for toxic
substances, MRL: elemental mercury vapor/ inhalation/chronic & MRL: methyl
mercury/oral/acute; &
http://atsdr1.atsdr.cdc.gov:8080/97list.html ;
(48) Steskal V & Windham B, Developmental Effects of Prenatal and
Neonatal Mercury Exposure, 2002,
(49)Florida Panther Interagency Committee, Status Report: Mercury Contamination in Florida
Panthers, Dec 1989, & C.F.Facemire
et al, “Reproductive
impairment in the Florida Panther”, Health
Perspect,1995,
103 (Supp4):79-86; & Jagoe CH, 1998, Mercury in Alligators in the Southeastern
U.S.,
Science of the Total Envirnonment, 213:255-262, & Esley
RM, Mercury levels in alligator meat in south
Louisiana, 1999, Bull Environ Contam Toxicol, 63: 598-603;
& High Mercury in Wading Birds; & High
Mercury in Florida alligators
hppt://everglades.fiu.edu/taskforce/precursor/chapter10.html; & (17.6)
Osowski SL, 1995, The decline of mink in Georgia, North Carolina, and S.
Carolina: the Role of
Contaminants, Env Contam and Toxicol, 29:418-423;
& Sepulveda MS et al, 1999, Effects
of mercury
on health and first-year survival of
free-ranging great eggrets from southern Florida,
Archives Environ
Contam
and Toxicol, 37:369-376; & M.Maretta et al, "Effect of mercury on the epithelium
of the fowl
testis", Vet Hung 1995, 43(1):153-6.
(50)(a) Lindberg, S.G., et al.Oak
Ridge National Laboratory,
2001. Methylated mercury species in
municipal waste landfill gas sampled in Florida, USA. Atmospheric Environment 35(Aug):4011-15.;
& Lindberg, S.G. et al, Airborne Emissions of mercury from municipal solid
waste: measurements from 3 Florida landfills, JAWMA, 2002 ; & (c)Methyl Mercury Contamination and Emission to the
Atmosphere from Soil Amended with Municipal Sewage Sludge, Anthony Carpi et al,
U.S. Dept. of Energy Oak Ridge National Lab(ORNL), Journal Environ. Quality
26:1650-1655 (1997); & ORNL, Sunlight-mediated Emission of
Elemental Mercury from Soil Amended with Sewerage Sludge, Env
Sci & Tech, 31(7):2085-91; &Press
Release: ORNL finds green plants
fertilized by sewer sludge emit organic and inorganic mercury, www.ornl.gov/Press_Releases/archive/mr19960117‑01.html
(51) Friedli HR, Radke LF, Lu JY
(2001). Mercury in smoke from biomass
fires.
Geophysical Research Letters (28:17, p.3223-3226).
(52) Externalities related to biomass
plants. www.myflcv.com/biomass.html