FUNDAMENTAL CHANGES IN LAKE HURON AND THE ST. CLAIR RIVER: ROLE OF INVASIVE SPECIES CHANGING FISH COMMUNITIES AND PCB DYNAMICS
DAVID JUDE UNIVERSITY OF MICHIGAN
DAVID JUDE UNIVERSITY OF MICHIGAN OUTLINE -LAKE HURON TROPHIC - - PowerPoint PPT Presentation
FUNDAMENTAL CHANGES IN LAKE HURON AND THE ST. CLAIR RIVER: ROLE OF INVASIVE SPECIES CHANGING FISH COMMUNITIES AND PCB DYNAMICS DAVID JUDE UNIVERSITY OF MICHIGAN OUTLINE -LAKE HURON TROPHIC CASCADE -ST CLAIR FISH COMMUNITY CHANGES -PCB
DAVID JUDE UNIVERSITY OF MICHIGAN
PLANTS REDUCED PHOSPHORUS INPUTS
August 20, 1965
2 4 6 8 10 12 14 16 18 20 66 68 70 72 74 76 78 80 82 84 86 88 90 92 94 96 98 00 02
Year Effluent Total Phosphorus Concentration (mg/L)
1970 Polymer and Pickle Liquor Feeding Facilities Added
1971
Michigan Limits Phosphorus in Cleaning Agents to 8.7% 1973-1976 Construction of Aeration Facilities 1977 Michigan's Phosphorus Detergent Ban 1979-80 Implementation of Alternative Sludge Removal Process
1981
Consistent Secondary Treatment
(Data Source: DWWTP)
! COW ! MCDONALDS
Phytoplankton (Algae) Zooplankton Pelagic Fish Benthic Fish Diporeia
Phytoplankton (Algae) Zooplankton Pelagic Fish Benthic Fish Diporeia Zebra/Quagga Mussels Energy Shunt
THROUGH THE FOOD WEB AFFECTING:
TP
TDP
500 1000 1500 2000 2500
1996 1997 1998 1999 2007
Huron Spring (cells/ml)
1000 2000 3000 4000 5000 6000 7000 8000 9000
1996 1997 1998 1999 2007
Huron Summer (cells/ml)
50000 100000 150000 200000 250000 300000 350000 400000 450000
1996 1997 1998 1999 2007
Huron Spring (µm³/ml)
50000 100000 150000 200000 250000 300000 350000 400000
1996 1997 1998 1999 2007
Huron Summer (µm³/ml) Other/unidentified Dinoflagellates Euglenoids Blue-greens Cryptophytes Greens Chrysophytes Pennate diatoms Centric diatoms
Lake Huron comparison of pre-2000 and 2007 phytoplankton data. Data are presented for spring (left) and summer (right) sampling events based on cell density (top) and biovolume (bottom).
among trophic levels.
Daphnia Bosmina Cyclopoid copepod Diaptomid copepod Limnocalanus
Cladocerans Copepods
50000
2000
10000
2001
50000
2001
10000
2002
50000
2002
10000
2003
50000
2003
10000
2004
50000
2004
10000
2005
50000
2005
10000
2007
50000
2007
10000 Northern Lake Huron Central Lake Huron Southern Lake Huron
2008
50000 Northern Lake Huron Central Lake Huron Southern Lake Huron
2008
Rotifers Other Cladocerans Nauplii Native Predatory Cladocerans Invasive Predatory Cladocerans Immature Cyclopoids Immature Calanoids Holopedium Dreissenid Veligers Daphnia Bosminids Adult Cyclopoids
Lake Huron Biomass (ug/m3)
Left panel = Spring Right panel = Summer
Alewife Limnocalanus too deep Bloater (whitefish larger, lake herring similar)
1994/95
2000 2005
Diporeia spp.
Density (per m2 x 103) 0 3 6 9 12 15
94% Decline in 10 Years
0 3 6 9 12 15 0 3 6 9 12 15 Density (per m2 x 103) Density (per m2 x 103)
Preyfish populations in Lake Huron (USGS fall bottom trawl survey)
50 100 150 200 250 300 350
Biomass (kilotonnes)
round goby troutperch stickleback sculpin bloater rainbow smelt alewife
Data courtesy Ed Roseman, USGS GLSC
1 9 7 3 1 9 8 1 1 9 8 9 1 9 9 7 2 005
Ye a r
5 0 1 00 1 5 0 2 00 2 5 0 3 00 3 5 0 4 00 4 5 0 5 00
Lak e- wi de bi
as ( k t )
B l oat er S l i m y scul pi n D eepw at er scul pi n R ai nbow sm el t A l ew i f e N i nespi ne st i ckl eback
VERY SCARCE
PROBABLY EXTINCT IN LAKE HURON
RESURGENCE IN ES, WL, LT, AND LH
DAVID JUDE UNIVERSITY OF MICHIGAN
ROUND AND TUBENOSE GOBIES HAD DETRIMENTAL EFFECTS ON BENTHIC SPECIES
MADTOMS, LOGPERCH
IN ST CLAIR RIVER
5 10 15 20 25 30 35 40 45 % COMPOSITION
5 10 15 20 25 30 35 40 R GOBY L PERCH R BASS SPOTTAIL EMERALD S Y PERCH SM BASS T.-PERCH MISC % COMPOSITION
5 10 15 20 25 30 35 40 45 R GOBY L PERCH ALEWIFE C DARTER R BASS N MADTOM R DARTER
% COMPOSITION
(N=1,454)
a similar proportion of catch: about 40%
ENDANGERED SPECIES
SPECIES): 4% TO NEAR 0
3% TO NEAR 0
3% TO NEAR 0
RESULTS
AND ST. LOUIS RIVER, DULUTH, MINN
AOCs
100 200 300 400 500 600 700 800 900 PCBS (NG/G WW)
ST CLAIR RIVER PCBs IN THE FOOD WEB, 1999
20 40 60 80 100 120 140 160 180 200 PCBs (NG/G WW)
ST CLAIR RIVER PCBS IN THE FOOD WEB, 1999
20 40 60 80 100 120 140
ZEBRA M PSEUDOF AMPHIPOD CRAYFISH R GOBIES S M BASS PCBs (NG/G WW) FOOD WEB COMPONENT
50 100 150 200 250 300 350 400 450 PHYTO B.ALGAE ZM PSEUDO AMPHI CRAYFIS RG SB NG/G (WW) FOOD WEB COMPONENTS
CALUMET RIVER FOOD WEB PCBs, 1999
2000 4000 6000 8000 10000 12000 PHYTO B.ALGAE ZM-FP PSEUDO AMPHI RG-FP - 80 SBC-348 SB-415 PCBS (NG/G WW) FOOD WEB COMPONENT
RAISIN RIVER PCBs FOOD WEB, 1999
500 1000 1500 2000 2500 3000 3500 RAISIN CALUMET ST CLAIR PCBs (NG/G WW)
PCBs IN ZEBRA MUSSELS FROM VARIOUS RIVERS, 1999
500 1000 1500 2000 2500 3000 3500 4000 4500 5000 RAISIN CALUMET ST CLAIR PCBs (NG/G WW) RIVERS
PCBs IN AMPHIPODS FROM VARIOUS RIVERS, 1999
500 1000 1500 2000 2500 3000 3500 4000 4500 5000 RAISIN CALUMET ST CLAIR SAG RIV ST LOUIS PCBs (NG/G WW) RIVERS
PCBs IN ROUND GOBIES FROM VARIOUS RIVERS, 1999
500 1000 1500 2000 2500 3000 RAISIN CALUMET ST CLAIR RAISIN C PCBs (NG/G WW) RIVERS
PCBs IN SMALLMOUTH BASS FROM VARIOUS RIVERS, 1999
ZM-SMB FOOD WEB AS A DELISTING CRITERIA
RIVER NEEDS MORE REHABILITATION, WHILE OTHERS ARE CONSIDERABLE LESS
LIKE LAKE SUPERIOR
LAKE HURON- WL, ES, LT, LH
HAVE CHANGED: RG,NM:LP,RB:CD,RD,MS,AL,TN
CONDUCIVE TO PCB UPTAKE IN SMB