PUBLIC HEALTH ASSESSMENT
BAY CITY MIDDLEGROUNDS
BAY CITY, BAY COUNTY, MICHIGAN
| Chemical | Date | Maximum Concentration (ppb) |
Reference | Comparison Value (ppb) | |
| upstream | downstream | ||||
| 1,4-dichlorobenzene | 1988 | | 0.38 | 15 | 75MG, carcinogen |
| 1989 | ND (10) | ND (10) | 1 | ||
| 1992 | ND (10) | ND (10) | 3 | ||
| 1,2,4-trichlorobenzene | 1988 | | 0.041 | 15 | 100R |
| 1989 | ND (10) | ND (10) | 1 | ||
| 1992 | ND (10) | ND (10) | 3 | ||
| arsenic | 1989 | 3 | 3 | 1 | 3E, 0.02C |
| 1992 | ND (6) | ND (6) | 3 | ||
| barium | 1988 | | 39 | 15 | 700R |
| 1989 | 190 | 290 | 1 | ||
| 1992 | 32.7J | 33.2J | 3 | ||
| chromium | 1989 | 2 | 1 | 1 | 10,000R (III) 50R, 3C (VI) |
| 1992 | ND (3) | 3.4J | 3 | ||
| lead | 1989 | ND (1) | ND (1) | 1 | 15PL, carcinogen |
| 1992 | 3 | 3.2 | 3 | ||
| manganese | 1992 | 31.2 | 34.6 | 3 | 50R |
| PCBs (total) | 8/89 | 0.0032 | 0.0104 | 21 | 0.2E, 0.005C |
| 1989 | ND (0.1) | ND (0.1) | 1 | ||
| 1992 | ND (1) | ND (1) | 3 | ||
| zinc | 1989 | 17 | 12 | 1 | 3,000R |
| 1992 | ND (4) | 4.3J | 3 | ||
Only chemicals that were detected are listed
Bolded chemicals exceed comparison values.
J Estimated Concentration: below Contract Required Detection Level, but above
Instrument Detection Limit
ND Not Detected (with detection limit)
= Not Reported
(III) For chromium(III)
(VI) For chromium(VI)
carcinogen Carcinogen (proven, probable, or possible) but no CREG available
Comparison Value Bases
E ATSDR Environmental Media Evaluation Guides (EMEGs)
R ATSDR Reference Dose Media Evaluation Guides (RMEGs), calculated from U.S.
EPA Reference Dose, assuming child ingestion
C ATSDR Cancer Risk Evaluation Guides (CREGs), for 1 x 10-6 estimated excess
cancer risk (a significant additional risk of developing cancer is taken to be one additional case of
cancer in a population of 1 million people experiencing the exposure)
PL U.S. EPA Proposed Action Level for Lead in Drinking Water
MG U.S. EPA Safe Drinking Water Act Maximum Contaminant Level Goal
| Location | Dissolved PCBs (ppt) |
Total PCBs (ppt) |
| Shiawassee River Mouth | 0.7 | 5.0 |
| Tittabawassee River Mouth | 1.6 | 3.8 |
| Downstream of Saginaw WWTP | 1.5 | 1.7 |
| (Middleground Island) (no samples collected) | ||
| Upstream of GMC-CPC (Bay City) | 2.9 | 10.4 |
| Between CPC and Bay City WWTP | 4.6 | 17.6 |
| Midway between Bay City WWTP and mouth | 5.2 | 17.2 |
| Saginaw Bay | 1.0-1.7 | 4.8-5.6 |
Reference: 21
WWTP Waste Water Treatment Plant
Comparison Values (drinking water, in ppt): 200 (EMEG), 5 (CREG)
| Location | Concentration Range (ppm) |
| Above Saginaw | 0.019-0.11 |
| Above G.M. Saginaw Foundry | 0.018-0.14 |
| Saginaw, between Foundry and WWTP | 0.16-0.17 |
| Below Saginaw WWTP | 0.14-0.26 |
| Between Saginaw and Bay City | 0.024-0.089 |
| West Channel | 0.050-0.22 |
| East Channel | 0.024-0.31 |
| Between Middlegrounds Island and G.M. Plant | 0.030-0.17 |
| Below Bay City G.M. Plant | 0.024-0.56 |
| Below Bay City WWTP | 0.13-0.71 |
| Essexville | 0.12-1.6 |
| Saginaw River Mouth | 0.090-0.60 |
| Saginaw Bay | 0.0012-0.17 |
Reference: 21
WWTP Waste Water Treatment Plant
Comparison Values (soil, in ppm): 0.04 (EMEG), 0.09 (CREG)
| Location | Concentration Range (ppm) |
| Between Middlegrounds Island and G.M. Plant | 0.0058-4.2 |
| Below Bay City G.M. Plant | 0.21-1.9 |
| Below Bay City WWTP | 0.021-4.0 |
| Saginaw River Mouth | 0.0023-0.84 |
| Saginaw Bay | 0.0012-0.18 |
Reference: 21
WWTP Waste Water Treatment Plant
Comparison Values (soil, in ppm): 0.04 (EMEG), 0.09 (CREG)
| Chemical | Date | Maximum Concentration (ppm) |
Reference | Comparison Value (ppm) | |
| upstream | downstream | ||||
| acenaphthylene | 1992 | ND | 0.16J | 3 | NA |
| benzo(a)anthracene | 1992 | 0.12J | 2.4 | 3 | carcinogen |
| benzo(a)pyrene | 1992 | 0.12J | 1.7 | 3 | 0.1C |
| benzo(g,h,i)perylene | 1992 | ND | 0.51 | 3 | NA |
| benzo(b)fluoranthene | 1992 | 0.19J | 2.6 | 3 | carcinogen |
| benzo(k)fluoranthene | 1992 | 0.061J | 0.91 | 3 | carcinogen |
| chrysene | 1992 | 0.15J | 2.3 | 3 | carcinogen |
| dibenzo(a,h)anthracene | 1992 | ND | 0.13J | 3 | carcinogen |
| indeno(1,2,3-c,d)pyrene | 1992 | ND | 0.71 | 3 | carcinogen |
| 2-methylnaphthalene | 1992 | ND | 0.2J | 3 | NA |
| naphthalene | 1992 | ND | 0.46 | 3 | NA |
| phenanthrene | 1992 | 0.15J | 4 | 3 | NA |
| carbazole | 1992 | ND | 0.66 | 3 | NA |
| dibenzofuran | 1992 | ND | 0.36 | 3 | NA |
| PCBs | 1992 | ND | 0.87 | 3 | 0.04E, 0.09C |
| gamma-BHC | 1992 | ND | 0.01 | 3 | 0.6E, carcinogen |
| delta-BHC | 1992 | 0.001J | 0.0038 | 3 | NA |
| 1,3-dichlorobenzene | 1992 | ND | 0.056J | 3 | NA |
| 1,4-dichlorobenzene | 1992 | ND | 0.23J | 3 | carcinogen |
| 4-methylphenol | 1992 | ND | 0.039J | 3 | carcinogen |
| arsenic | 1989 | 16 | 39 | 1 | 0.6E, 0.4C |
| 1992 | 7 | 21.2 | 3 | ||
| barium | 1989 | 100 | 170 | 1 | 100R |
| 1992 | 60.3 | 130 | 3 | ||
| beryllium | 1989 | 0.4 | 0.8 | 1 | 10R, 0.2C |
| 1992 | 0.65J | 0.81J | 3 | ||
| chromium | 1989 | 21 | 47 | 1 | 2,000R (III) 10R, 60C (VI) |
| 1992 | 19.8 | 60.7 | 3 | ||
| cobalt | 1989 | 5 | 7 | 1 | NA |
| 1992 | 5.7J | 7.3J | 3 | ||
| copper | 1989 | 19 | 35 | 1 | NA |
| 1992 | 16 | 43.8 | 3 | ||
| lead | 1989 | 17 | 32 | 1 | carcinogen |
| 1992 | 28.7J | 123 | 3 | ||
| manganese | 1992 | 198 | 339 | 3 | 300R |
| vanadium | 1992 | 16.B | 18.4B | 3 | NA |
| zinc | 1989 | 220 | 290 | 1 | 600R |
| 1992 | 78.3 | 283 | 3 | ||
Only chemicals that were detected are listed
Bolded chemicals exceed comparison values.
ND Not Detected
J Estimated Concentration: below Contract Required Detection Level, but above
Instrument Detection Limit
(III) For chromium(III)
(VI) For chromium(VI)
NA None Available
carcinogen Carcinogen (proven, probable, or possible) but no CREG available
Comparison Value Bases
E ATSDR Environmental Media Evaluation Guides (EMEGs)
R ATSDR Reference Dose Media Evaluation Guides (RMEGs), calculated from U.S.
EPA Reference Dose, assuming child ingestion
A U.S. EPA Drinking Water Lifetime Health Advisory
C ATSDR Cancer Risk Evaluation Guides (CREGs), for 1 x 10-6 estimated excess
cancer risk (a significant additional risk of developing cancer is taken to be one additional case of
cancer in a population of 1 million people experiencing the exposure)
| Chemical | Date | Maximum Concentration (ppm) |
Reference | MDCH Level of Concern (ppm) | |||
| Carp | Walleye | ||||||
| Whole fish | Skin-off fillets | Whole fish | Skin-on fillets | ||||
| cadmium | 1986 | 0.05 | 0.01 | ND (0.01) | ND (0.01) | 22 | 0-5.5(17) |
| chromium | 1986 | ND (0.1) | ND (0.1) | 0.13 | ND (0.1) | 22 | 1(17) |
| copper | 1986 | 1.8 | 0.8 | 0.6 | 0.5 | 22 | 10-100(17) |
| lead | 1986 | 0.14 | ND (0.1) | ND (0.1) | ND (0.1) | 22 | 0.5-10(17) |
| mercury | 1986 | ND (0.1) | 0.11 | ND (0.1) | 0.3 | 22 | 0.5(18) |
| 1992 | | 0.2 | | | 24 | ||
| PCBs (total) | 1986 | 16.2 | 19.2 | 4 | 0.6 | 22 | 2(19) |
| 1992 | | 24.7 | | | 24 | ||
| zinc | 1986 | 116 | 27 | 12.7 | 7.2 | 22 | 30-1,000(17) |
| dieldrin | 1992 | | 0.108 | | | 24 | 0.3(19) |
| hexachlorobenzene | 1992 | | 0.014 | | | 24 | 0.2-0.5(17) |
| octachlorostyrene | 1992 | | 0.1 | | | 24 | NA |
| 4,4'-DDD | 1992 | | 0.729 | | | 24 | 5(19),(20) |
| 4,4'-DDE | 1992 | | 1.73 | | | 24 | |
| 4,4'-DDT | 1992 | | 0.044 | | | 24 | |
| chlordane (total) | 1992 | | 0.41 | | | 24 | 0.3(19) |
| heptachlor epoxide | 1992 | | 0.039 | | | 24 | 0.3(19) |
NA No Level of Concern
= Not sampled or not analyzed
| Area | Incidence Rate | Death Rate |
| Bay County | 403.5 | 179.9 |
| Michigan | 412.3 | 180.8 |
Reference: 57
| Year | Zip Code 48706 | Zip Code 48708 | Age-Adjusted Incidence Rate | |||||||
| # Obs. | # Exp. | SMR | # Obs. | # Exp. | SMR | 48706 | 48708 | Bay County | Michigan | |
| 1990 | 219 | 202.3 | 1.08 | 129 | 149.5 | 0.86 | 432.5 | 351.8 | 416.7 | 397.0 |
| 1991 | 225 | 211.7 | 1.06 | 133 | 156.4 | 0.85 | 439.4 | 347.2 | 400.5 | 415.7 |
| 1992 | 223 | 214.0 | 1.04 | 170 | 158.4 | 1.07 | 429.2 | 424.9 | 409.9 | 420.2 |
| 1993 | 219 | 201.9 | 1.08 | 154 | 149.2 | 1.03 | 427.6 | 391.5 | 395.0 | 398.2 |
| 1990-3 | 886 | 829.9 | 1.07a | 586 | 613.5 | 0.96 | 432.2g | 378.9 | 405.7 | 407.8 |
Reference: 58
# Obs. Cases diagnosed between 1990 and 1993 and reported to the Michigan Department of Community Health, Office of the State Registrar and Division of Health Statistics by December 31, 1994.
# Exp. Calculated by applying the age- and sex- specific incidence rates for white Michigan residents to the age- and sex-specific Zip Code area population estimates.
Age-adjusted rates are computed by the direct method, using as the standard population the age distribution of the total population of the United States as enumerated in 1970. Rates are per 100,000 in the specific group. Zip Code area populations for 1990 were used for 1990-1993.
County and State rates are for white residents only.
a Ratio of observed to expected cases was significantly higher than 1.0 (p < 0.05).
g Age-adjusted Zip Code area rate is significantly greater than state rate (p < 0.05).
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