The range, mean, and standard deviations of the analytical parameters arc given by county in Table 1 and the overall values arc given in Table 2. A statistical analysis of the data showed that there were significant differences between counties for sonic parameters, and these are shown in Table 3. There were no consistent trends toward higher metals in one county vs. another. Sonic metals were significantly higher in one or more counties while other metals were highest in other counties. While there were significant differences in metal levels between the counties studied, these differences are small compared to the amounts of heavy metals that are commonly added to the soil in sewage sludges. The overall means in Table 2 are probably adequate as estimates of background heavy metal levels for the state.
Partial correlations between the analytical parameters are presented in Table 4. Only those correlations that were significant at the 0.01 level arc included. DTPA extractable Cd, Cu, and Zn were correlated with the total amounts of those metals but similar correlations for Ph and Ni were not significant. An examination of the data in Table 2 shows that all of the cadmium was DTPA extractable while 11.6, 13.7, 5.0, and 2.4% of the total Cu, Ph, Ni, and Zn, respectively, were extracted by DTPA. Soil pH was negatively correlated with DTPA Ni and Zn, and total P was positively correlated with lead.
Table 5 compares the total metal levels found for Ohio soils with other literature values. The values are quite consistent except those for chromium which were much lower in the Ohio and Minnesota studies than those reported by Allaway (1) or Baker and Chesnin (2).
Background hcavy metal concentrations can be useful in determining if a soil has been contaminated by metals. Values greater than two or three times the mean background levels should be indicative of metal contamination. This study did not idcntify any major regional differences in soil heavy metal concentrations which would indicate areas where metal levels were naturally higher than others; however, the present study did not attempt to cover all soil parent material regions in the state.
TABLE 1. Background Analyses by County of pH, Nutrients (µg/g), and Heavy Metals (µg/g). | |||||
---|---|---|---|---|---|
Number of Samples | Mean | Standard Deviation | Minimum | Maximum | |
CLARK | |||||
pH | 0 | ||||
Bray PI | 0 | ||||
Total P | 0 | ||||
TKN* | 0 | ||||
Total K | 0 | ||||
DTPA Cu | 0 | ||||
Cd | 0 | ||||
Pb | 0 | ||||
Ni | 0 | ||||
Zn | 0 | ||||
Total Cu | 15 | 14 | 2 | 11 | 19 |
Cd | 15 | < 0.1 | 0.1 | BDL*** | 0.1 |
Pb | 15 | 14 | 1 | 11 | 16 |
Ni | 15 | 15 | 2 | 11 | 18 |
Zn | 15 | 61 | 9 | 47 | 87 |
Cr | 15 | 12 | 6 | 6 | 23 |
*Total Kjefdahl nitrogen. ***Below detection limit. | |||||
TABLE 1 cont. Background Analyses by County of pH, Nutrients (µg/g), and Heavy Metals (µg/g). | |||||
Number of Samples | Mean | Standard Deviation | Minimum | Maximum | |
DEFIANCE | |||||
pH | 0 | ||||
Bray Pl | 0 | ||||
Total P | 0 | ||||
TKN | 0 | ||||
Total K | 1 | 10500 | 10500 | 10500 | |
DTPA Cu | 8 | 3.2 | 1.2 | 1.9 | 4.9 |
Cd | 8 | 0.88 | 1.22 | 0.14 | 3.61 |
Pb | 8 | 2.5 | 0.7 | 1.9 | 4.2 |
Ni | 8 | 1.5 | 0.6 | 0.7 | 2.6 |
Zn | 8 | 2.3 | 1.4 | 0.7 | 4.8 |
Total Cu | 17 | 23 | 5 | 14 | 30 |
Cd | 15 | 0.4 | 0.7 | BDL | 2.9 |
Pb | 17 | 15 | 3 | 9 | 21 |
Ni | 17 | 22 | 5 | 10 | 32 |
Zn | 17 | 79 | 17 | 47 | 103 |
Cr | 15 | 18 | 4 | 11 | 23 |
*Total Kjefdahl nitrogen. ***Below detection limit. | |||||
TABLE 1 cont. Background Analyses by County of pH, Nutrients (µg/g), and Heavy Metals (µg/g). | |||||
Number of Samples | Mean | Standard Deviation | Minimum | Maximum | |
FRANKLIN | |||||
pH | 0 | ||||
Bray PI | 0 | ||||
Total P | 0 | ||||
TKN | 0 | ||||
Total K | 2 | 7000 | 54 | 7000 | 7000 |
DTPA Cu | 2 | 2.8 | 0.8 | 2.3 | 3.4 |
Cd | 2 | 0.10 | 0.01 | 0.09 | 0.11 |
Pb | 2 | 2.0 | 0.2 | 1.9 | 2.1 |
Ni | 2 | 1.3 | 0.5 | 0.9 | 1.7 |
Zn | 2 | 1.5 | 0.3 | 1.3 | 1.7 |
Total Cu | 61 | 19 | 0.3 | 13 | 30 |
Cd | 61 | 0.1 | 0.1 | BDL | 0.8 |
Pb | 61 | 17 | 3 | 10 | 26 |
Ni | 61 | 18 | 4 | 12 | 29 |
Zn | 61 | 77 | 16 | 48 | 138 |
Cr | 59 | 12 | 3 | 5 | 22 |
TABLE 1 cont. Background Analyses by County of pH, Nutrients (µg/g), and Heavy Metals (µg/g). | |||||
Number of Samples | Mean | Standard Deviation | Minimum | Maximum | |
MADISON | |||||
pH | 0 | ||||
Bray Pl | 0 | ||||
Total P | 0 | ||||
TKN | 0 | ||||
Total K | 0 | ||||
DTPA Cu | 0 | ||||
Cd | 0 | ||||
Pb | 0 | ||||
Ni | 0 | ||||
Zn | 0 | ||||
Total Cu | 4 | 19 | 2 | 17 | 21 |
Cd | 4 | 0.1 | 0.1 | BDL | 0.3 |
Pb | 4 | 17 | 1 | 15 | 18 |
Ni | 4 | 20 | 4 | 14 | 23 |
Zn | 4 | 73 | 5 | 67 | 79 |
Cr | 4 | 12 | 2 | 10 | 15 |
TABLE 1 cont. Background Analyses by County of pH, Nutrients (µg/g), and Heavy Metals (µg/g). | |||||
Number of Samples | Mean | Standard Deviation | Minimum | Maximum | |
MEDINA | |||||
pH | 17 | 6 | 0 | 5 | 7 |
Bray Pl | 17 | 22 | 13 | 8 | 54 |
Total P | 20 | 590 | 120 | 400 | 1010 |
TKN | 19 | 2200 | 2100 | 1100 | 7900 |
Total K | 25 | 6300 | 1300 | 4200 | 8700 |
DTPA Cu | 25 | 1.9 | 1.4 | 0.9 | 7.7 |
Cd | 25 | 0.10 | 0.04 | 0.03 | 0.20 |
Pb | 25 | 2.7 | 0.3 | 1.9 | 3.2 |
Ni | 25 | 0.6 | 0.3 | 0.3 | 1.7 |
Zn | 25 | 1.2 | 0.3 | 0.7 | 2.0 |
Total Cu | 40 | 17 | 5 | 11 | 37 |
Cd | 40 | 0.2 | 0.2 | BDL | 0.6 |
Pb | 40 | 23 | 8 | 11 | 39 |
Ni | 40 | 20 | 4 | 13 | 29 |
Zn | 40 | 75 | 10 | 54 | 95 |
Cr | 15 | 7 | 1 | 4 | 9 |
TABLE 1 cont. Background Analyses by County of pH, Nutrients (µg/g), and Heavy Metals (µg/g). | |||||
Number of Samples | Mean | Standard Deviation | Minimum | Maximum | |
MUSKINGUM | |||||
pH | 6 | 6 | 1 | 5 | 7 |
Bray Pl | 6 | 26 | 13 | 9 | 39 |
Total P | 6 | 560 | 110 | 390 | 710 |
TKN | 6 | 1500 | 400 | 1100 | 2100 |
Total K | 6 | 4900 | 500 | 4200 | 5400 |
DTPA Cu | 6 | 1.3 | 0.6 | 0.7 | 2.5 |
Cd | 6 | 0.09 | 0.05 | 0.06 | 0.19 |
Pb | 6 | 3.3 | 2.4 | 1.7 | 7.9 |
Ni | 6 | 0.6 | 0.5 | 0.2 | 1.5 |
Zn | 6 | 2.1 | 2.3 | 0.5 | 6.6 |
Total Cu | 6 | 16 | 2 | 13 | 19 |
Cd | 6 | 0.3 | < 0.1 | 0.2 | 0.4 |
Pb | 6 | 33 | 3 | 28 | 36 |
Ni | 6 | 25 | 4 | 20 | 29 |
Zn | 6 | 74 | 10 | 65 | 92 |
Cr | 0 | ||||
TABLE 1 cont. Background Analyses by County of pH, Nutrients (µg/g), and Heavy Metals (µg/g). | |||||
Number of Samples | Mean | Standard Deviation | Minimum | Maximum | |
PICKAWAY | |||||
pH | 0 | ||||
Bray Pl | 0 | ||||
Total P | 0 | ||||
TKN | 0 | ||||
Total K | 18 | 6300 | 1300 | 3900 | 9800 |
DTPA Cu | 18 | 2.3 | 0.6 | 1.3 | 3.7 |
Cd | 18 | 0-12 | 0.03 | 0.09 | 0.20 |
Pb | 18 | 2.5 | 0.7 | 1.5 | 3.9 |
Ni | 18 | 1.1 | 0.4 | 0.6 | 2.4 |
Zn | 18 | 2.3 | 2.4 | 1.0 | 11.2 |
Total Cu | 96 | 20 | 5 | 12 | 36 |
Cd | 96 | 0.2 | 0.2 | BDL | 1.0 |
Pb | 96 | 17 | 3 | 11 | 27 |
Ni | 96 | 17 | 5 | 9 | 38 |
Zn | 96 | 74 | 14 | 47 | 130 |
Cr | 78 | 11 | 3 | 5 | 20 |
TABLE 2. Background Analyses for All Farms for pH, Nutrients (µg/g), and Heavy Metals (µg/g). | |||||
---|---|---|---|---|---|
Number of Samples | Mean | Standard Deviation | Minimum | Maximum | |
pH | 23 | 6.4 | 0.48 | 4.7 | 7 |
Bray PI | 23 | 23 | 13 | 8 | 54 |
Total P | 26 | 580 | 120 | 390 | 1010 |
TKN | 25 | 2100 | 1800 | 1100 | 7900 |
Total K | 52 | 6300 | 1400 | 3900 | 10500 |
DTPA Cu | 59 | 2.2 | 1.2 | 0.7 | 7.7 |
Cd | 59 | 0.21 | 0.50 | 0.03 | 3.61 |
Pb | 59 | 2.6 | 0.9 | 1.5 | 7.9 |
Ni | 59 | 0.9 | 0.5 | 0.2 | 2.6 |
Zn | 59 | 1 8 | 1.6 | 0.5 | 11.2 |
Total Cu | 239 | 19 | 5 | 11 | 37 |
Cd | 237 | 0.2 | 0.3 | BDL | 2.9 |
Pb | 239 | 19 | 5 | 9 | 39 |
Ni | 239 | 18 | 5 | 9 | 38 |
Zn | 239 | 75 | 15 | 47 | 138 |
Cr | 186 | 12 | 4 | 4 | 23 |
TABLE 3. Differences in the Total and DTPA Extractable Heavy Metal Contents of Farm Soils by County. | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|
Total | DTPA | |||||||||
CU | Cd | Pb | Ni | Zn | CU | Cd | Pb*** | Ni | Zn*** | |
µg/g | ||||||||||
Clark | 14c* | < 0.1c | 14d | 15b | 79a | ** | ||||
Defiance | 23a | 0.4a | 15dc | 22a | 61b | 3.2a | 0.88a | 1.50 | ||
Franklin | 19b | 0.1bc | 17c | 18b | 77a | 2.8ab | 0.10b | 1.3a | ||
Madison | 19bc | 0.Ibc | 17dc | 20ab | 73ab | ** | ||||
Medina | 17c | 0.2b | 23b | 20ab | 75a | 1.9b | 0.10b | 0.6b | ||
Muskingum | 16c | 0.3ab | 33a | 25ab | 74ab | 1.3b | 0.09b | 0.6b | ||
Pickaway | 20b | 0.2b | 18c | l7b | 74a | 2.3ab | 0.12b | 1.1a | ||
*Means in each vertical column with the same letter are not significantly different at the 0.05 level. **DTPA extractable heavy metals were not measured in Clark and Madison counties. ***There were no significant differences between counties for DTPA Pb and Zn. |
TABLE 4. Partial Correlation Coefficients for All Parameters at the 0.01 Level of Significance. | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Total | DTPA | ||||||||||||
pH | Total P | Cu | Cd | Pb | Ni | Zn | Cr | Cu | Cd | Pb | Ni | Zn | |
pH | -0.57 | -0.77 | |||||||||||
Total P | 0.69 | ||||||||||||
Total Cu | 0.29 | 0.66 | 0.67 | 0.57 | 0.83 | 0.65 | |||||||
Cd | 0.29 | 0.30 | 0.32 | 0.31 | 0.19 | 0.94 | |||||||
Pb | 0.69 | 0.30 | 0.40 | 0.28 | 0.29 | -0.35 | |||||||
Ni | 0.66 | 0.32 | 0.40 | 0.69 | 0.52 | ||||||||
Zn | 0.69 | 0.31 | 0.28 | 0.69 | 0.37 | 0.51 | 0.52 | 0.56 | |||||
Cr | 0.57 | 0.19 | 0.29 | 0.52 | 0.37 | ||||||||
DTPA Cu | 0.83 | 0.94 | 0.51 | 0.73 | 0.40 | ||||||||
Cd | 0.94 | ||||||||||||
Pb | |||||||||||||
Ni | -0.57 | 0.65 | -0.35 | 0.52 | 0.73 | 0.53 | |||||||
Zn | -0.77 | 0.56 | 0.40 | 0.53 |
TABLE 5. Comparison of Ohio Background Heavy Metal Soil Concentrations with Published Values from Other Areas. | ||||||||
---|---|---|---|---|---|---|---|---|
Ohio | Allaway | Baker and Chesnin (2)* | Dowdy et al. (4)** | |||||
Mean | Range | Mean | Range | Mean | Range | Mean | Standard Deviation | |
Total Metal Concentration (ug/g) | ||||||||
Cd | 0.2 | 0-2.9 | 0.06 | 0.01-7 | 0.5 | 0.01-0.70 | 0.39 | 0.17 |
Cu | 19 | 11-37 | 20 | 2-100 | 20 | 2-100 | 23 | 4 |
Cr | 12 | 4-23 | 100 | 5-3000 | 200 | 5-1000 | 39 | 29 |
Ni | 18 | 9-38 | 40 | 10-1000 | 40 | 5-500 | 18 | 10 |
Pb | 19 | 9-39 | 10 | 2-200 | 10 | 2-200 | ||
Zn | 75 | 47-138 | 50 | 10-300 | 50 | 10-300 | 60 | 14 |
*Numerous sources worldwide. **Background levels from uncontaminated soils in Minnesota. Ranges were not given. |