Contaminated Sediments Program
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Sediment Assessment and Remediation Report
Tables
Table 1
Black River Sample Stations and Sample Types*
| River Mile | Location | Sampling Type |
| 0.3 | Harbor mouth at boat gas station | S, LT |
| 0.5 | Ust. Erie St. Dst. Kobe | LT, FT |
| West bank | ||
| 2.4 | Kobe (dst dredging) | S, LT, FT |
| East bank, lake side of Turning Basin | ||
| 2.5 | East bank, Turning Basin | LT |
| 2.9 | Ust Turning Basin, West Bank of Kobe | S, LT, D |
| 3.6-4.8 | Kobe area. Broad area sampling for snails | D |
| 4.6 | West Bank of Kobe near coal pile | S |
| 4.9 | Mouth of French Creek | LT, FT |
| 2.5 (Tributary) | Kline Ditch:tributary of French Creek | |
| @ RM 3.9 | D | |
| 5.2 | Ust. Kobe and French Creek | S, LT, Ft, D |
| 8.3 | St. Rt. 254 | D |
| 9.8 | Ford Rd. (Dst. Elyria WWTP) | S, LT |
| 11.6 | Spring Valley Country Club | |
| (Ust. Elyria WWTP) | S, LT,FT, D | |
| 15.0 | Dst. confluence East and West Branches at Cascade Park | LT, FT, D |
| 18.9 (east Br) | Ust. Grafton (East Fk, East Branch) | LT, FT |
| Not Applicable | Field Laboratory Controls | Ft |
| Laboratory Controls | LT | |
| Sampling Codes: | S-sediment chemistry by Ohio EPA and USGS LT-laboratory sediment toxicity FT-field (in situ) toxicity (water and sediment) D-DNA fingerprinting of snails |
|
In Situ Exposures on the Black River, Fall 1997
| Black River--In situ Survivals | |||||
| September 29-October 2, 1997 | |||||
| Hotel cont. | 0.3 Mi (U) | 0.3 mi (L) | 0.5 Mi (U) | 0.5 Mi (L) | |
| H. azteca | 10 | 0 | 9 | 7 | 10 |
| 10 | 9 | 0 | 10 | 7 | |
| 10 | 0 | 7 | 6 | 8 | |
| 10 | 9 | 5 | 8 | 8 | |
| Ave. surviv | 10 | 4.5 | 5.25 | 7.75 | 8.25 |
| % surviv | 100 | 45 | 52.5 | 77.5 | 82.5 |
| St. dev. | 0 | 5.1962 | 3.8622 | 1.7078 | 1.2583 |
| Coeff. var | 0 | 115.470054 | 73.5659062 | 22.0364533 | 15.2521908 |
| C. tentans | 9 | 6 | 6 | 6 | 8 |
| 10 | 8 | 10 | 6 | 6 | |
| 9 | 10 | 8 | 8 | 10 | |
| 9 | 8 | 11 | 9 | 8 | |
| Ave. surviv | 9.25 | 8 | 8.75 | 7.25 | 8 |
| % surviv | 92.5 | 80 | 87.5 | 72.5 | 80 |
| St. dev. | 0.5 | 1.6330 | 2.2174 | 1.5 | 1.6330 |
| Coeff. var | 5.4054 | 20.4124 | 25.3412 | 20.6897 | 20.4124 |
| P. promelas | 10 | 9 | 6 | 0 | 10 |
| 10 | 10 | 10 | 0 | 10 | |
| 10 | 10 | 10 | 9 | 9 | |
| 10 | 3 | 9 | 7 | 10 | |
| Ave. surviv | 10 | 8.000 | 8.750 | 4 | 9.75 |
| % surviv | 100 | 80.000 | 87.500 | 40 | 97.5 |
| St. dev. | 3.8622 | 1.8930 | 1.8930 | 0.5 | 3.3665 |
| Coeff. var | 38.6221 | 23.6621 | 21.6339 | 12.5000 | 34.5282 |
| C. dubia | 9 | 11 | 5 | ||
| 10 | 10 | 7 | |||
| 10 | |||||
| 9 | |||||
| Ave. surviv | 9.25 | 10.5 | 6 | ||
| % surviv | 92.5 | 105 | 60 | ||
| St. dev. | 0.9574 | 0.7071 | 1.4142 | ||
| Coeff. var | 10.3506 | 6.7344 | 23.5702 | ||
| 2.4 (U) | 2.4 (L) | 5.2 (U) | |||
| H.azteca | 5 | 7 | 5 | ||
| 10 | 9 | ||||
| 10 | 9 | ||||
| 10 | 11 | ||||
| Ave. surviv | 5 | 9.25 | 8.5 | ||
| % surviv | 50 | 92.5 | 85 | ||
| St. dev. | NA | 1.5 | 2.5166 | ||
| Coeff. var | NA | 16.2162162 | 29.6071939 | ||
| C. tentans | 9 | 10 | 10 | ||
| 9 | 10 | ||||
| 9 | 10 | ||||
| 8 | 7 | ||||
| Ave. surviv | 9 | 9 | 9.25 | ||
| % surviv | 90 | 90 | 92.5 | ||
| St. dev. | 0 | 0.8165 | 1.5 | ||
| Coeff. var | 0.0000 | 9.0722 | 16.2162 | ||
| P. promelas | 0 | 9 | 7 | ||
| 7 | 10 | 9 | |||
| 10 | 9 | ||||
| 10 | 8 | ||||
| Ave. surviv | 3.5 | 9.75 | 8.25 | ||
| % surviv | 35 | 97.5 | 82.5 | ||
| St. dev. | 0.5 | 4.6904 | 1.8930 | ||
| Coeff. var | 14.2857 | 48.1068 | 22.9451 | ||
| C. dubia | 8 | ||||
| 7 | |||||
| Ave. surviv | 7.5 | ||||
| % surviv | 75 | ||||
| St. dev. | 0.7071 | ||||
| Coeff. var | 9.4281 | ||||
| 5.2 (L) | 15.0 Mi | 18.9 Mi | |||
| H.azteca | 7 | 10 | 7 | ||
| 5 | 9 | 9 | |||
| 10 | 10 | 10 | |||
| 9 | 7 | 11 | |||
| Ave. surviv | 7.75 | 9 | 9.25 | ||
| % surviv | 77.5 | 9 | 9.25 | ||
| St. dev. | 2.2174 | 1.4142 | 1.7078 | ||
| Coeff. var | 28.6110424 | 15.713484 | 18.4629744 | ||
| C. tentans | 8 | 9 | 7 | ||
| 10 | 8 | 8 | |||
| 9 | 10 | 10 | |||
| 11 | 8 | 10 | |||
| Ave. surviv | 9.5 | 8.75 | 8.75 | ||
| % surviv | 95 | 87.5 | 87.5 | ||
| St. dev. | 1.2910 | 0.9574 | 1.5 | ||
| Coeff. var | 13.5894 | 10.9420 | 17.1429 | ||
| P.promelas | 6 | 9 | 10 | ||
| 9 | 10 | 10 | |||
| 10 | 2 | 8 | |||
| 10 | 10 | 5 | |||
| Ave. surviv | 8.75 | 7.75 | 8.25 | ||
| % surviv | 87.5 | 77.5 | 82.5 | ||
| St. dev. | 1.8930 | 2.3329 | 0.9574 | ||
| Coeff. var | 21.6339 | 30.4891 | 11.6052 | ||
| C. dubia | 9 | 11 | 10 | ||
| 9 | |||||
| Ave. surviv | 9 | 11 | 10 | ||
| % surviv | 90 | 110 | 100 | ||
| St. dev. | 0.0000 | 0.0000 | 0.0000 | ||
| Coeff. var | 0.0000 | 0.0000 | 0.0000 | ||
| U=upper level-water L=Lower level-sediment ***Chamber mesh broken |
|||||
Laboratory Sediment Toxicity
on the Black River, Fall 1997
| October 31, 1997-November 10, 1997 | |||||
| 0-2 cm | 8-10 cm | 0-2 cm | |||
| Florissant | 18.9 Mi (EB) | 0.3 Mi (U) | 0.3 Mi (L) | 0.5 Mi (U) | |
| H.azteca | 8 | 7 | 1 | 6 | 7 |
| 7 | 7 | 3 | 5 | 5 | |
| 5 | 8 | 3 | 5 | 5 | |
| 7 | 7 | 6 | 6 | 6 | |
| Ave.surviv | 6.75 | 7.25 | 3.25 | 5.5 | 5.75 |
| % surviv | 84.375 | 90.625 | 40.625 | 68.75 | 71.875 |
| St. dev. | 1.26 | 0.50 | 2.06 | 0.58 | 0.96 |
| Coeff. var | 18.64 | 6.90 | 63.43 | 10.50 | 16.65 |
| C. tentans | 8 | 10 | 7 | 3 | |
| 10 | 7 | 6 | 3 | ||
| 9 | 10 | 7 | 6 | ||
| 8 | 8 | 6 | 7 | ||
| Ave.surviv | 8.75 | 8.75 | 6.5 | 4.75 | 0 |
| % surviv | 87.5 | 87.5 | 65 | 47.5 | 0 |
| St. dev. | 0.96 | 1.50 | 0.58 | 2.06 | |
| Coeff. var | 10.94 | 17.14 | 8.88 | 43.40 | |
| 8-10 cm | 0-2 cm | 8-10 cm | 0-2 cm | 8-10 cm | |
| 0.5 Mi (L) | 2.4 Mile (U) | 2.4 Mile (L) | 2.5 Mile (U | 2.5 Mile (L) | |
| H.azteca | 8 | 10 | 6 | 6 | 2 |
| 7 | 8 | 3 | 2 | 2 | |
| 7 | 7 | 4 | 2 | 0 | |
| 6 | 6 | 6 | 2 | 2 | |
| Ave.surviv | 7 | 7.75 | 4.75 | 3 | 1.5 |
| % surviv | 87.5 | 96.875 | 59.375 | 37.5 | 18.75 |
| St. dev. | 0.82 | 1.71 | 1.50 | 2.00 | 1.00 |
| Coeff. var | 11.66 | 22.04 | 31.58 | 66.67 | 66.67 |
| C. tentans | 8 | 6 | 10 | 6 | |
| 6 | 8 | 8 | 7 | ||
| 4 | 5 | 6 | 10 | ||
| 10 | 6 | 8 | 7 | ||
| Ave.surviv | 0 | 7 | 6.25 | 8 | 7.5 |
| % surviv | 0 | 70 | 62.5 | 80 | 75 |
| St. dev. | 2.58 | 1.26 | 1.63 | 1.73 | |
| Coeff. var | 39.89 | 20.13 | 20.41 | 23.09 | |
| 0-2 cm | 8-10 cm | 0-2 cm | 8-10 cm | 0-2 cm | |
| 2.9 Mile (U) | 2.9 Mile (L) | 4.6 Mile (U) | 4.6 Mile (L) | 5.2 Mile (U) | |
| H.azteca | 5 | 6 | 8 | 6 | 7 |
| 8 | 3 | 8 | 6 | 8 | |
| 4 | 5 | 5 | 7 | 8 | |
| 7 | 9 | 7 | 6 | 8 | |
| Ave.surviv | 6 | 5.75 | 7 | 6.25 | 7.75 |
| % surviv | 75 | 71.875 | 87.5 | 78.125 | 96.875 |
| St. dev. | 1.83 | 2.50 | 1.41 | 0.50 | 0.50 |
| Coeff. var | 30.43 | 43.48 | 20.20 | 8.00 | 6.45 |
| C. tentans | 7 | 4 | 7 | ||
| 6 | 7 | 8 | |||
| 4 | 5 | 7 | |||
| 7 | 5 | 8 | |||
| Ave.surviv | 0 | 0 | 6 | 5.25 | 7.5 |
| % surviv | 0 | 0 | 60 | 52.5 | 75 |
| St. dev. | 1.41 | 1.26 | 0.58 | ||
| Coeff. var | 23.57 | 23.97 | 7.70 | ||
| 8-10 cm | |||||
| 5.2 Mile (L) | 9.8 Mi | 11.6 Mi | 15.0 Mi | ||
| H.azteca | 5 | 6 | 6 | 8 | |
| 6 | 7 | 6 | 8 | ||
| 7 | 7 | 5 | 2 | ||
| 8 | 11 | 6 | 8 | ||
| Ave.surviv | 6.5 | 7.75 | 5.75 | 6.5 | |
| % surviv | 81.25 | 96.875 | 71.875 | 81.25 | |
| St. dev. | 1.29 | 2.22 | 0.50 | 3.00 | |
| Coeff. var | 19.86 | 28.61 | 8.70 | 46.15 | |
| C. tentans | 10 | 3 | 8 | 1 | |
| 8 | 4 | 8 | 6 | ||
| 7 | 6 | 9 | 3 | ||
| 6 | 6 | 7 | 2 | ||
| Ave.surviv | 7.75 | 4.75 | 8 | 3 | |
| % surviv | 77.5 | 47.5 | 80 | 30 | |
| St. dev. | 1.71 | 1.50 | 0.82 | 2.16 | |
| Coeff. var | 22.04 | 31.58 | 10.21 | 72.01 | |
| October 31, 1997-November 10, 1997 | |||||
| 0-2 cm | 8-10 cm | 0-2 cm | |||
| Florissant | 18.9 Mi (EB) | 0.3 Mi (U) | 0.3 Mi (L) | 0.5 Mi (U) | |
| H.azteca | 0.0628571 | 0.18714 | 0.138 | 0.08 | 0.06 |
| 0.0542857 | 0.30143 | 0.076 | 0.14667 | 0.145 | |
| 0.044 | 0.252 | 0.102 | 0.08 | 0.12 | |
| 0.1222 | 0.19 | 0.10667 | 0.07333 | 0.12667 | |
| Ave.dry wt | 0.708357 | 0.236425 | 0.1056675 | 0.95 | 0.1129175 |
| St. dev. | 0.04 | 0.05 | 0.03 | 0.03 | 0.04 |
| Coeff. var | 49.55 | 23.54 | 24.07 | 36.41 | 32.61 |
| C. tentans | 1.7025 | 1.95 | 1.32986 | 0.46333 | |
| 1.782 | 2.33143 | 1.364 | 0.658 | ||
| 1.3025 | 1.535 | 0.94714 | 0.838333 | ||
| 1.6725 | 2.03 | 1.91833 | 0.515 | ||
| Ave. dry wt | 1.614875 | 1.9616075 | 1.4055825 | 0.6186658 | 0 |
| St. dev. | 0.21 | 0.33 | 0.40 | 0.17 | |
| Coeff. var | 13.21 | 16.74 | 28.31 | 27.16 | |
| 8-10 cm | 0-2 cm | 8-10 cm | 0-2 cm | 8-10 cm | |
| 0.5 Mi (L) | 2.4 Mile (U) | 2.4 Mile (L) | 2.5 Mile (U | 2.5 Mile (L) | |
| H.azteca | 0.115 | 0.1075 | 0.05 | 0.06167 | 0.095 |
| 0.23333 | 0.1025 | 0.03 | 0.06 | 0.125 | |
| 0.07714 | 0.10714 | 0.0975 | 0.195 | 0.22 | |
| 0.08667 | 0.85 | ||||
| Ave. dry wt | 0.128035 | 0.10571333 | 0.065625 | 0.10555667 | 0.1466667 |
| St. dev. | 0.07 | 0.00 | 0.03 | 0.08 | 0.07 |
| Coeff var | 56.25 | 2.63 | 47.42 | 73.38 | 44.49 |
| C. tentans | 0.942 | 1.4667 | 1.181 | 1.11429 | |
| 1.44375 | 1.83 | 0.83125 | 1.24714 | ||
| 1.00143 | 3.33333 | 0.92167 | 0.915 | ||
| 0.93667 | 1.00333 | 0.575 | 1.544 | ||
| Ave. dry wt | 0 | 1.0809625 | 1.9083325 | 0.87723 | 1.2051075 |
| St. dev. | 0.24 | 1.01 | 0.25 | 0.26 | |
| Coeff. var | 22.54 | 52.84 | 28.51 | 21.90 | |
| 0-2 cm | 8-10 cm | 0-2 cm | 8-10 cm | 0-2 cm | |
| 2.9 Mile (U) | 2.9 Mile (L) | 4.6 Mile (U) | 4.6 Mile (L) | 5.2 Mile (U) | |
| H.azteca | 0.112 | 0.09667 | 0.1475 | 0.8833 | 0.09286 |
| 0.04125 | 0.188 | 0.08375 | 0.12833 | 0.10375 | |
| 0.1175 | 0.01 | 0.098 | 0.10143 | 0.06429 | |
| 0.09054 | 0.09889 | 0.11 | 0.10167 | 0.12125 | |
| Ave. dry wt | 0.0903225 | 0.9839 | 0.1098125 | 0.10494 | 0.0955375 |
| St. dev. | 0.03 | 0.07 | 0.03 | 0.02 | 0.02 |
| Coeff. var | 38.44 | 73.87 | 24.88 | 16.00 | 25.01 |
| C. tentans | 1.85429 | 1.58571 | 1.5574 | ||
| 2.08333 | 1.822 | 1.72 | |||
| 1.284 | 2.3675 | 1.76514 | |||
| 3.5075 | 1.55375 | ||||
| Ave. dry wt | 0 | 0 | 2.18228 | 1.92507 | 1.6486575 |
| St. dev. | 0.95 | 0.40 | 0.11 | ||
| Coeff. var | 43.31 | 20.83 | 6.67 | ||
| 8-10 cm | |||||
| 5.2 Mile (L) | 9.8 Mi | 11.6 Mi | 15.0 Mi | ||
| H.azteca | 0.09 | 0.114 | 0.0725 | 0.15375 | |
| 0.02667 | 0.0917 | 0.215 | 0.08125 | ||
| 0.08 | 0.09 | 0.0725 | 0.09 | ||
| 0.11375 | 0.1756 | 0.195 | 0.11875 | ||
| Ave. dry wt | 0.077605 | 0.1178 | 0.1388 | 0.1109 | |
| St. dev. | 0.04 | 0.04 | 0.08 | 0.03 | |
| Coeff. var | 47.40 | 33.98 | 55.45 | 29.50 | |
| C. tentans | 1.81 | 0.8167 | 1.28625 | 0.82 | |
| 2.335 | 0.915 | 1.425 | 1.795 | ||
| 1.86 | 0.7533 | 1.18111 | 1.08333 | ||
| 2.375 | 0.575 | 1.47571 | 2.885 | ||
| Ave. dry wt | 2.095 | 0.765 | 1.342 | 1.6458 | |
| St. dev. | 0.30 | 0.14 | 0.13 | 0.92 | |
| Coeff. var | 14.38 | 18.70 | 9.98 | 56.09 | |
|
Table 4 RAPD Genetic Similarity in the Snail, Physella gyrina, on the Black River, Fall 1997 |
|
| Station (River Mile) | Mean Genetic Similarity (Std. Dev.) |
| 2.9 | 0.821 (0.043) |
| 3.6-4.8 | 0.810 (0.045) |
| 5.2 | 0.853 (0.048) |
| Tributary (2.5) of French Creek (4.9) |
0.882 (0.041) |
| 15.0 | 0.815 (0.061) |
| 18.9 (East Br.) | 0.831 (0.042) |
Table 5
In Situ Exposures in the Black River, Spring 1998
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Table 6
Concentrations of organic compounds in sediments from the
Black River, 1997 All concentrations in ug/kg
| 11.60 | 9.81 | 5.20 | 4.80 | 2.90 | 2.90 dup |
2.32 | 0.42 | |
| Semi-volatile Organics | ||||||||
| Benzo(a)anthracene (56-55-3( |
<0.5 | <0.5 | <0.7 | <0.9 | 0.8 | <0.7 | 1.6 | <0.7 |
| Benzo(a)pyrene (50-32-8) |
<0.5 | <0.5 | <0.7 | <0.9 | 0.8 | <0.7 | 1.7 | <0.7 |
| Benzo(b)fluoranthene (205-99-2) |
<0.5 | <0.5 | <0.7 | 0.9 | 0.9 | 0.7 | 12.0 | <0.7 |
| Benzo(g,h,i)perylene (191-24-2) |
<0.5 | <0.5 | <0.7 | <0.9 | <0.8 | <0.7 | 1.7 | <0.7 |
| benzo(k)fluoranthene (207-08-9) |
<0.5 | <0.5 | <0.7 | <0.9 | <0.8 | <0.7 | 1.5 | <0.7 |
| bis (2-ethylhexyl) phthalate (117-81-7) |
<0.5 | <0.5 | 0.7 | 1.2 | <0.8 | <0.7 | <0.7 | 1.5 |
| Chrysene (218-01-9) |
0.6 | <0.5 | 0.7 | 1.1 | 1.1 | 1.0 | 2.0 | <0.7 |
| Fluoranthene (206-44-0) |
1.1 | 0.8 | 1.2 | 1.7 | 2.0 | 1.6 | 2.2 | <0.7 |
| Indeno(1,2,3-cd)pyrene (193-39-5) |
<0.5 | <0.5 | <0.7 | <0.9 | 0.8 | <0.7 | 1.8 | <0.7 |
| 3 & 4 Methylphenol (106-44-5) |
<0.5 | <0.5 | <0.7 | 1.9 | 1.1 | 1.3 | <0.7 | <0.7 |
| Naphthalene (91-20-3) |
<0.5 | <0.5 | <0.7 | <0.9 | <0.8 | <0.7 | 0.7 | <0.7 |
| Phenanthrene (85-01-8) |
0.7 | 0.6 | <0.7 | <0.9 | 1.2 | 0.9 | 1.0 | <0.7 |
| Pyrene (129-00-0) |
1.0 | 0.7 | 1.0 | 1.4 | 1.6 | 1.4 | 1.7 | <0.7 |
| Volatile Organics | ||||||||
| Acetone (67-64-1) |
<0.7 | <0.6 | <0.8 | 0.1 | <0.13 | 0.1 | <0.9 | <0.9 |
| Toulene (108-88-3) |
<0.6 | <0.5 | <0.6 | <0.9 | 1.0 | 1.0 | <0.7 | <0.7 |
| Organochlorine Pesticides and PCB's | ||||||||
| 4,4'-DDE (72-55-9) |
<5.7 | <4.9 | <7.1 | 10 | <7.6 | <7.8 | <7 | <7.4 |
| 4,4'-DDT (50-29-3) |
<5.7 | <4.9 | <7.1 | 9.8 | <7.6 | <7.8 | <7 | <7.4 |
| PCB-1254 (11097-69-1) |
99 | 45 | 41 | <45 | 58 | 68 | <35 | <37 |
| PCB-1260 (11096-82-5) |
<28 | <24 | <35 | <45 | 46 | <39 | <35 | <37 |
Table 7
Sediment sample particle size characteristics, concentrations (mg/kg dry
weight) of heavy metals and percent total organic carbon for the sediments
of the Black River Study Area,
1996 and 1997a.
| River Mile |
Particle Size Characteristics |
Percent TOC |
Percent Solids |
Arsenic | Barium | Cadmium | Chromium |
| Black River | |||||||
| 0.19b | Sand/Silt | 2.0 | 45.6 | NA | 79.7 | 3.4 | 26.3 |
| 0.42 | Sand/Silt | 1.9 | 54.8 | 8.73 | 231 | 1.3 | 23.6 |
| 2.32 | Silt/Sand | 1.9 | 52.6 | 16.5 | 174 | 10.4c | 63.2 |
| 2.90 | Silt/Sand | 1.9 | 44.8 | 9.25 | 136 | 3.69 | 45.4 |
| 4.80 | Silt/Sand | 2.2 | 39.8 | 15.6 | 274 | 4.94 | 74.1 |
| 5.20 | Sand/Silt | 1.4 | 52.8 | 9.77 | 153 | 3.41 | 45.4 |
| 5.80b | Sand/Silt | 1.2 | 56.5 | NA | 40.2 | 3.1 | 22.5 |
| 9.81 | Sand | 1.3 | 73.8 | 9.79 | 71.9 | 5.06 | 60.3 |
| 11.60 | Sand/Silt | 1.1 | 68.4 | 10.5 | 102 | 60.5 | 55.9 |
| W. Branch Black River | |||||||
| 19.6b | Sand/Silt | 0.5 | 69.4 | NA | 22.8 | 0.1 | 5.4 |
| E. Branch Black River | |||||||
| 11.40b | Sand/Silt | 1.0 | 43.1 | NA | 52.8 | 0.2 | 10.1 |
| 18.90 | Sand | 0.5 | 85.6 | 6.13 | 62.6 | <0.0882 | 15 |
| 30.00b | Sand/Silt | 1.0 | 58.8 | NA | 58.3 | 0.2 | 9.8 |
| 32.50 | Sand | 0.3 | 84.0 | 4.03 | 28.8 | 0.114 | <13.7 |
| Willow Creek | |||||||
| 2.90 | Sand | 1.1 | 76.8 | 9.29 | 98 | 0.23 | 15.3 |
| French Creek | |||||||
| 3.20b | Sand | 0.1 | 68.7 | NA | 15.9 | 0.4 | 4.9 |
| 6.10b | Sand | 0.2 | 69.7 | NA | 22.0 | 0.2 | 4.7 |
| Key to data: Non-elevated; Slightly elevated; Elevated; Highly elevated; Extremely elevatedd | |||||||
| a Samples collected in 1997 unless otherwise noted. b Samples collected in 1996 c Exceeds Ontario severe effect level (Persuad, et al., 1993) d Data comparisons are made to Ohio EPA reference sites except for mercury for which Illinois stream data are used for comparison (Illinois EPA, 1984) |
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DRAFT
River Mile
Copper
Iron
Lead
Mercury
Nickel
Zinc
Black River
0.19b
248.4c
120,830
35.9
0.129
29.8
757.3
0.42
20.8
24,900
100
0.0506
<28.6
137
2.32
39.9
57,100
67.4
0.166
35.6
402
2.90
40.6
26,900
50.3
0.224
34.9
171
4.80
52.87
37,000
56.2
0.0925
51.1
245
5.20
35.6
24,700
40.2
0.0756
35.6
158
5.80b
131.6
65,957
23.4
0.0852
21.9
430.5
9.81
48.7
17,100
39.3
0.116
33.7
126
11.60
48.7
29,300
30.3
0.196
36.9
134
W. Branch
Black River
19.60b
7.1
11,324
5.9
<0.0301
9.4
36.3
E. Branch
Black River
11.40b
36.8
46,666
10.9
0.0320
15.9
149.9
18.90
11.5
18,400
<17.6
0.0507
<17.6
43.2
30.00b
8.0
16,480
10.1
0.0357
16.5
50.1
32.50
<4.58
8,390
<18.3
<0.0192
<18.3
42.6
Willow Creek
2.90
11.7
16,300
26
<0.0282
<20.4
63.8
French Creek
3.20b
41.8
47,624
7.8
0.0232
10.9
221.0
6.10b
38.7
15,802
10.1
<0.0216
9.9
78.9
Key to data: Non-elevated; Slightly elevated;
Elevated; Highly elevated; Extremely elevated
a Samples collected in 1997 unless otherwise noted.
b Samples collected in 1996
c Exceeds Ontario severe effect level (Persuad, et al., 1993)
d Data comparisons are made to Ohio EPA reference sites except for
mercury for which Illinois stream data are used for comparison
(Illinois EPA, 1984)
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