Contamination Assessment and Potential Human Health Risks of Heavy Metals in Urban Soils from Grand Forks, North Dakota, USA
Abstract
:1. Introduction
2. Materials and Methods
2.1. Study Area
2.2. Sample Collection and Processing
2.3. Physicochemical Characteristics and Elemental Analysis
2.4. Estimation of Pollution Index
2.4.1. Enrichment Factor (EF)
2.4.2. Contamination Factor (Cf)
2.4.3. Geoaccumulation Index (Igeo)
2.4.4. Ecological Risk (Ei) and Potential Ecological Risk Index (RI)
2.5. Statistical Analysis
2.6. Human Health Risk Assessment of Heavy Metals
3. Results and Discussion
3.1. Chemical Characteristics
3.2. Metal Levels and Comparison with Worldwide Reported Levels and Guidelines
3.3. Principal Component Analysis (PCA)
3.4. Ecological Risk Assessment
3.5. Health Risk Assessments
4. Conclusions
Author Contributions
Funding
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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Mn | Fe | Co | Ni | Cu | Zn | As | Pb | Hg | Cr | Cd | Tl | pH | EC | TDS | ||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Park Soils | Min | 560.2 | 14,120 | 5.608 | 17.89 | 12.58 | 62.35 | 6.265 | 9.315 | 0.028 | 10.95 | 0.524 | 0.228 | 6.35 | 128.3 | 85.5 |
Max | 1129 | 24,209 | 8.801 | 32.34 | 21.84 | 104.5 | 12.20 | 51.63 | 0.179 | 33.34 | 0.809 | 0.440 | 7.03 | 1417 | 945.0 | |
Mean | 818.3 | 21,011 | 6.849 | 23.63 | 17.23 | 79.99 | 8.965 | 17.20 | 0.062 | 24.28 | 0.665 | 0.365 | 6.75 | 336.1 | 223.1 | |
SD | 137.2 | 2089 | 0.790 | 3.181 | 2.438 | 8.955 | 1.356 | 9.657 | 0.034 | 4.059 | 0.069 | 0.042 | 0.21 | 337.1 | 222.6 | |
Residential Soils | Min | 452.0 | 16,965 | 5.376 | 17.00 | 13.17 | 68.91 | 5.514 | 9.773 | 0.037 | 19.53 | 0.527 | 0.293 | 6.54 | 134.4 | 89.8 |
Max | 1114 | 24,056 | 8.064 | 31.40 | 22.53 | 89.79 | 11.99 | 31.36 | 0.111 | 27.56 | 0.809 | 0.473 | 7.05 | 1024 | 683.0 | |
Mean | 783.5 | 20,896 | 6.708 | 24.80 | 17.38 | 81.58 | 9.147 | 14.67 | 0.060 | 23.62 | 0.670 | 0.377 | 6.70 | 281.9 | 187.9 | |
SD | 191.3 | 2454 | 0.914 | 4.772 | 2.793 | 7.965 | 2.000 | 6.262 | 0.021 | 3.017 | 0.100 | 0.059 | 0.15 | 293.2 | 195.5 |
As | Cd | Co | Cr | Cu | Fe | Hg | Mn | Ni | Pb | Tl | Zn | Acid Mixture | |||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Park soil | 8.97 | 0.67 | 6.85 | 24.28 | 17.23 | 21,011 | 0.06 | 818.3 | 23.63 | 17.20 | 0.37 | 79.99 | HNO3 + HCl | PS * | |
Residential soil | 9.15 | 0.67 | 6.71 | 23.62 | 17.38 | 20,896 | 0.06 | 783.5 | 24.80 | 14.67 | 0.38 | 81.58 | HNO3 + HCl | PS * | |
Jiaozuo city, China | 55.81 | - | 20.21 | 51.80 | 20.36 | - | - | 460.77 | 34.43 | 27.56 | - | 84.21 | HNO3 + HCl + HF + HClO4 | [80] | |
Karachi, Pakistan | - | - | - | 9.6 | 33.3 | 908.4 | - | - | - | 42.1 | - | 99.5 | HNO3 + HClO4 | [83] | |
Caserta, Italy | 15.8 | 0.7 | 9.4 | 14.7 | 36 | 27,900 | 0.084 | 980 | 12.8 | 68 | 1.55 | 116.4 | HNO3 + HCl | [84] | |
Isfahan city, Iran | 16.17 | 2.17 | 13.15 | 80.57 | 92.75 | - | - | - | 61.65 | 179.97 | - | 470.36 | HNO3 + HCl | [85] | |
Ghaziabad, India | - | 0.4 | - | 288 | 122 | 21,433 | - | 386 | 147 | 147 | - | 187 | HNO3 + HCl + H2O2 | [86] | |
Yerevan, Armenia | 0.776 | - | 13.7 | 122 | 103 | 36,400 | 0.115 | 776 | 61.9 | 110 | - | 262 | X-ray fluorescence | [87] | |
Shanghai, China | 8.3 | 0.3 | - | 115.3 | 40.4 | - | 0.2 | - | 37.4 | 45.0 | - | 144.8 | HNO3 + HF + HClO4 | [88] | |
Thiva, Greece | - | 0.67 | 99 | 285 | 26 | 44,600 | - | 946 | 1777 | 30 | - | 78 | HNO3 + HCl | [89] | |
Hualpén, Chile | 3 | - | 15 | 15 | 24 | - | - | - | 33 | 6 | - | 918 | HNO3 + HCl | [90] | |
Lisbon, Portugal | 5.3 | - | 13.0 | 38 | 37 | 21,000 | 0.36 | 337 | 43 | 89 | - | 97 | HNO3 + HCl | [91] | |
Niger, Nigeria | - | 1.779 | - | 12.39 | 41.88 | 2038 | - | 211.1 | 42.54 | 915.8 | - | 63.37 | HNO3 | [92] | |
Chicago, USA | 19.55 | - | 11 | 71 | 150 | 33,000 | 0.64 | 583 | 36 | 397 | - | 397 | HNO3 + HCl + HF + HClO4 | [93] | |
Baltimore, USA | - | 1.06 | 15 | 72 | 45 | 23,495 | - | 472 | 27 | 231 | - | 141 | HNO3 + HCl + H2O2 | [94] | |
Oslo, Norway | 5.48 | 0.41 | 9.98 | 32.5 | 31.7 | 21,582 | 0.13 | 486 | 28.4 | 55.6 | - | 160 | HNO3 | [95] | |
Darkhan, Mongolia | 5.3 | 0.19 | 9.05 | 35 | 19.5 | - | - | - | 27.5 | 21.5 | - | 68.5 | HNO3 + HCl + HF | [96] | |
Comparison with International Guidelines | |||||||||||||||
California Human Health (SSLs) | Residential | 0.07 | 1.7 | 660 | 17 | 3000 | - | 18 | - | 1600 | 150 | 5 | 23,000 | - | [97] |
Commercial/industrial | 0.24 | 7.5 | 3200 | 37 | 38,000 | - | 180 | - | 16,000 | 3500 | 63 | 100,000 | - | [97] | |
Dutch Soil Guidelines | Background concentration | 29 | 0.8 | 9 | 100 | 36 | - | 0.3 | - | 35 | 85 | 1 | 140 | - | [98] |
Intervention value | 55 | 12 | 240 | 380 | 190 | - | 10 | - | 210 | 530 | - | 720 | - | [98] | |
Max. permissible concentration (MPC) | 34 | 1.6 | 33 | 100 | 40 | - | 2.2 | - | 38 | 140 | 1.3 | 160 | - | [99] | |
Canadian Soil Quality Guidelines | Residential/parkland | 12 | 10 | - | 64 | 63 | - | 6.6 | - | 50 | 140 | 1 | 200 | - | [100] |
Spanish Government recommendations | Regulatory guidance values | 24 | 30 | - | 230 | 800 | - | 7 | 390 | 1560 | 270 | 3 | 11,700 | - | [101] |
RA Government, 2005 | 10 | 2 | - | 90 | 132 | - | 2.1 | 1500 | 80 | 65 | - | 220 | - | [87] |
PC 1 | PC 2 | PC 3 | |
---|---|---|---|
Eigenvalue | 7.04 | 1.26 | 1.02 |
Total variance (%) | 58.6 | 10.5 | 8.50 |
Cumulative eigenvalue | 7.04 | 8.29 | 9.31 |
Cumulative variance (%) | 58.6 | 69.1 | 77.6 |
Mn | 0.81 | 0.01 | −0.30 |
Fe | 0.90 | 0.06 | 0.21 |
Co | 0.94 | −0.02 | −0.14 |
Ni | 0.86 | 0.11 | −0.33 |
Cu | 0.84 | −0.08 | −0.17 |
Zn | 0.78 | −0.10 | 0.46 |
As | 0.51 | 0.49 | −0.20 |
Pb | 0.48 | −0.66 | 0.29 |
Hg | 0.04 | 0.63 | 0.60 |
Cr | 0.85 | −0.22 | 0.17 |
Cd | 0.79 | 0.33 | 0.02 |
Tl | 0.89 | −0.03 | 0.06 |
Adults | Children | |||||
---|---|---|---|---|---|---|
RfD/RDA (mg/kg/day) | Conc. | HQing | CRing | HQing | CRing | |
As | 0.0003 | 9.01 | 4.11 × 10−2 | 6.17 × 10−6 | 3.84 × 10−1 | 1.44 × 10−5 |
Cd | 0.001 | 0.67 | 9.13 × 10−4 | 1.16 × 10−7 | 8.52 × 10−3 | 2.70 × 10−7 |
Co | 0.02 | 6.81 | 4.67 × 10−4 | 4.36 × 10−3 | ||
Cr | 0.003 | 24.1 | 1.10 × 10−2 | 5.51 × 10−6 | 1.03 × 10−1 | 1.28 × 10−5 |
Cu | 0.04 | 17.3 | 5.91 × 10−4 | 5.52 × 10−3 | ||
Hg | 0.0003 | 0.06 | 2.80 × 10−4 | 2.62 × 10−3 | ||
Mn | 0.14 | 809.6 | 7.92 × 10−3 | 7.39 × 10−2 | ||
Ni | 0.02 | 23.9 | 1.64 × 10−3 | 1.53 × 10−2 | ||
Pb | 0.004 | 16.6 | 5.67 × 10−3 | 6.43 × 10−8 | 5.29 × 10−2 | 1.5 × 10−7 |
Tl | 0.00008 | 0.37 | 6.30 × 10−3 | 5.88 × 10−2 | ||
Zn | 0.3 | 80.4 | 3.67 × 10−4 | 3.43 × 10−3 | ||
HI | 7.63 × 10−2 | 7.12 × 10−1 |
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Saleem, M.; Sens, D.A.; Somji, S.; Pierce, D.; Wang, Y.; Leopold, A.; Haque, M.E.; Garrett, S.H. Contamination Assessment and Potential Human Health Risks of Heavy Metals in Urban Soils from Grand Forks, North Dakota, USA. Toxics 2023, 11, 132. https://doi.org/10.3390/toxics11020132
Saleem M, Sens DA, Somji S, Pierce D, Wang Y, Leopold A, Haque ME, Garrett SH. Contamination Assessment and Potential Human Health Risks of Heavy Metals in Urban Soils from Grand Forks, North Dakota, USA. Toxics. 2023; 11(2):132. https://doi.org/10.3390/toxics11020132
Chicago/Turabian StyleSaleem, Muhammad, Donald A. Sens, Seema Somji, David Pierce, Yuqiang Wang, August Leopold, Mohammad Ehsanul Haque, and Scott H. Garrett. 2023. "Contamination Assessment and Potential Human Health Risks of Heavy Metals in Urban Soils from Grand Forks, North Dakota, USA" Toxics 11, no. 2: 132. https://doi.org/10.3390/toxics11020132