You will need Adobe Acrobat Reader to view the files on this page. See EPA's PDF page to learn more about PDF and for a link to the free Acrobat Reader.
Fish Contaminants
Health Concerns from fish consumption

The Great Lakes Fish Monitoring and Surveillance
Program (GLFMSP) consists of two separate programs, the Open Lakes Trend
Monitoring Program and the Emerging Chemical Surveillance Program. The
Sport Fish Fillet Monitoring Program was recently eliminated. The Open Lake
Trend Monitoring Program was designed to examine the health of fish and
fish-consuming wildlife through trend analysis while the Emerging Chemical
Surveillance Program has been designed to screen for emerging chemicals in
fish tissue according to their persistent, bioaccumulative, and/or toxic
chemical
properties to help identify chemicals to be added to
the Open Lakes Trend Monitoring Program and to inform State Fish Advisory
Programs.
Open Lakes Trend Monitoring
Program - This
component is directed at monitoring contaminant trends in the open waters of
the Great Lakes (using fish as biomonitors), and assessing the overall
effects of toxics on fish and fish consuming
wildlife . The program provides
for collection and analysis of lake trout (walleye in Lake Erie) from each
of the Great Lakes. Fish samples are collected in the fall of the year,
using fish of similar size to reduce the impact of size variation on
contaminant trend data. Fish samples are then analyzed for several
different contaminants, including PCBs, toxaphene, chlordanes, nonachlors,
and other organochlorine compounds. Whole fish
are analyzed , including parts not usually eaten
by humans, such as the liver and bones, because wildlife consume the entire
fish. Contaminants,
such as PCBs, toxaphene, chlordanes,
nonachlors, and other organochlorine compounds are routinely monitored in
Great Lake’s top predator fish. Emerging contaminants, such as PBDEs were
recently added to the list of contaminants to be analyzed.
Contaminant concentrations in the Great Lakes are
decreasing. However, the rate of decrease varies from lake to lake due
to differences in lake size and historical contaminant input. In
addition, direct comparison of contaminant
concentrations across lakes is not possible as the Great Lakes Fish
Monitoring Program’s Open Lakes Trend Monitoring Program was designed to
analyze fish of similar size, rather than of the same age.
The age of fish affects the contaminant body burden concentration and
the rate of uptake is affected by the rate of growth of the fish. Other
factors, such as forage base, lipid (fat) content, and gender also
affect the contaminant body burden of the fish. For example, a Lake
Michigan lake trout may be the same size and contain the same amount of
lipid and have a completely different contaminant body burden that a
Lake Ontario lake trout of the same size and lipid content. For this
reason, only general chemical concentration patterns can be observed.
This is especially true for Lake Erie, where walleye are collected as
the top predator fish instated of lake trout. Lake Erie’s fish have the
fastest growth rate of the five Great Lakes.
Emerging Chemical Surveillance Program
is directed at screening for emerging chemicals in fish tissue according to
their persistent, bioaccumulative, and/or toxic chemical properties. This
program has utilized samples collected for the Open Lakes Monitoring Program
and mega composites from each lake (representing all samples from a given
lake) to determine the presence of a contaminant of interest in top predator
fish, help identify and guide State and Federal monitoring programs in the
development of their analyte lists and priority setting, and to inform the
Open Lakes Monitoring Program to allow for the incorporation of contaminants
of concern into the routine analyte list. Retrospective analysis may be
conducted upon on archived samples if a chemical of interest is identified.
Prioritization for Emerging Chemicals to be included in this portion of the
program are identified in a number of ways.
-
Broad Scan analysis of Open Lake Monitoring Program samples
-
Identification of new, possible PB&T substances important in the Great Lakes region by screening of chemicals in commerce (PDF) (24 pp. 284 kb)
-
Priority Chemicals identified by State Fish Advisory Programs
Sport Fish Fillet Monitoring Program - This component of the program was recently eliminated to allow for the analysis of emerging chemicals, see above. It was directed at monitoring potential human exposure to contaminants through consumption of popular sport fish species. The inclusion of coho and chinook salmon in this program also provided a snapshot of contaminant concentrations across the Great Lakes in fish of consistent age, complementing the size-based data collected in the open lakes component. The program provided for the collection of skin-on fillets from coho or chinook salmon (or rainbow trout, if neither was available) by the Great Lakes states. Fish samples were then analyzed for several different contaminants, including PCBs, toxaphene, chlordanes, nonachlors, and other organochlorine compounds. Emerging contaminants, such as PBDEs were recently added to the list of contaminants to be analyzed. All samples collected for this program have been archived and may be available for additional research. All data produce is available through the Great Lakes Environmental Database.
Information gained from the game fish fillet monitoring program
cannot be used to determine trends in contaminants and cannot
be used to set fish advisories. All eight Great Lakes states and
the Great Lakes tribes
issue their own fish consumption advice
. PCB concentrations
in coho salmon from this program can be compared to a standardized fish
advisory protocol, the
Protocol for a Uniform Great Lakes Sport
Fish Consumption Advisory
, developed by the eight Great Lakes states to assess potential human
exposure to PCBs through sport fish consumption. Although not
intended as fish consumption advice, information from this program can
assess the extent to which PCBs accumulate in coho salmon tissue in each
of the Great Lakes.
Great Lakes Fish Monitoring Program Analyte List
|
Analyte |
MDL, ng/g |
|
PCB congeners |
0.002 – 1.0 |
|
PCB co-planars |
0.002 – 1.0 |
|
Hexachlorobenzene |
1 |
|
Octachlorostyrene |
0.83 |
|
δ-BHC (Lindane) |
0.606 |
|
α-BHC |
4.7 |
|
Dieldrin |
0.44 |
|
Heptachlor epoxide b |
0.52 |
|
Cis-chlordane |
1.814 |
|
Trans-chlordane |
0.488 |
|
Cis-nonachlor |
1.95 |
|
Trans-nonachlor |
1.48 |
|
Oxychlordane |
1.94 |
|
pp,-DDT |
0.66 |
|
pp,-DDE |
0.74 |
|
pp,-DDD |
0.52 |
|
Endrin |
2.86 |
|
Mirex (Lake Ontario only) |
1.52 |
|
Toxaphene&homologs |
24.6 |
|
PBDEs |
0.001 – .10 |
|
Hg |
0.521 |
|
Fraction lipid |
5% |
|
*PCDD/Fs |
0.3 - 25 |
|
*PCNs |
0.2 – 6.0 |
|
*Dacthal |
1.0 |
|
*PBB-153 |
0.1 - .2 |
|
*PFOS |
0.5 |
*A scan for specified list of additional analytes, such as perfluorinated compounds, musk fragrances, APEs, pharmaceuticals and other personal care products (pseudo-persistence), other flame retardants, etc., will be conducted.
![[logo] US EPA](http://www.epa.gov/epafiles/images/logo_epaseal.gif)