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Bioavailability of Heavy Metals and Polycyclic Aromatic Hydrocarbon in Long-Term Sewage-Drained Soils of Tamil Nadu


Affiliations
1 Department of Environmental Science, Tamil Nadu Agricultural University, Coimbatore 641 003, India
2 Department of Soil Science and Agricultural Chemistry, Tamil Nadu Agricultural University, Coimbatore 641 003, India
3 Department of Bioenergy, Tamil Nadu Agricultural University, Coimbatore 641 003, India
4 Department of Agricultural Entomology, Tamil Nadu Agricultural University, Coimbatore 641 003, India
 

Heavy metals and organic contaminants are reported in sewage discharged sites. Screening and assessment of their toxic concentration in soils of the discharged sites of major cities in Tamil Nadu, India have been carried out in the present study. The major cities included Coimbatore (Ukkadam; U), Madurai (Avanaiyapuram; A), Tiruchirappalli (Rettamalai; R), Nesapakkam (N) and Koyambedu (K) Chennai Corporation. The total aquaregia-extractable concentrations of cadmium, chromium, lead and nickel were measured and found to be highest in U, followed by A, R, N and K. Their potential bioavailabilities were quantified in the following order: Cd – N > U > K > R > A; Cr – N > A > K > R > U; Pb – N > K > R; U > A; Ni – N > K > R > U > A. Bioavailable Factor was found to be highest for Cd in U (2.9%–83%) followed by Cr in N (1.1%–62.3%) and Ni in (1.70%– 52.7%) N. With regard to organic contamination, the major pesticides belonged to 13 organochlorine, 10 organophosphate and 8 synthetic pyrethroids reported below detectable concentration. Among the 16 US EPA priority poly aromatic hydrocarbon (PAHs) only 15 were detected. However, PAHs were found to be less than the permissible concentration for soils (0.3 mg kg–1) in sewage-contaminated sites. The results show that there is potential risk of transfer of heavy metals to higher trophic level of the food chain.

Keywords

Heavy Metals, Health Risk, Polycyclic Aromatic Hydrocarbon, Sewage Contamination.
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  • Strauss, M. and Blumenthal, U., Human waste use in agriculture and aquaculture: utilization practice and health perspectives. IRCWD Report 09/90, International Reference Centre for Waste Disposal, Duebendorf, Germany, 1990.

  • https://www.cpursehero.com/file/33493434/chp-19-water-pollution-India-An-Economic-Appraisalpdf/

  • http://www.worldometers.info/world-population/india-population/

  • Anon., National Agricultural Technological Project report on ‘use of urban and industrial effluent in agriculture’, Central Soil Salinity Research Institute, Karnal, 2004.

  • Sengupta, A. K., WHO Guidelines for the safe use of wastewater, excreta and grey water. In National Workshop on Sustainable Sanitation, New Delhi, 19–20 May 2008, http://www.whoindia.org/LinkFiles/WasteWater_Management_WHO Guidelines for_the_safe_use_of_wastewater, excreta_use_of_wastewater, excreta and greywater.pdf.

  • Datta, A., Schmeits, J. L., Amin, N. S., Lau, P. J., Myung and Kolodner, R. D., Checkpoint-dependent activation of mutagenic repair in Saccharomyces cerevisiae pol3-01 mutants. Mol. Cell. 2000, 6(3), 593–603.

  • Yadav, S. K. Subhash Babu, M. K. Yadav, Kalyan Singh, G. S. Yadav and Suresh Pal, A., Review of organic farming for sustainable agriculture in northern India. Int. J. Agron., 2002; Article ID 718145; http://dx.doi.org/10.1155/2013/718145.

  • Rattan, R. K., Datta, S. P., Chhonkar, P. K., Suribabu, K. and Singh, A. K., Long-term impact of irrigation with sewage effluents on heavy metal content in soils, crops and groundwater – a case study. Agric., Ecosyst. Environment., 2005, 109, 310–322.

  • Preciado, C., Jiménez-Cartagen, D. C., Matamoros, V. and Bayona, J. M., Screening of 47 organic micro contaminants in agricultural irrigation waters and their soil loading. Water Res., 2011, 221–231; doi:10.1016/j.watres.2010.07.050.

  • Wild, S. R., Berrow, M. L. and Jones, K. C., The persistence of polynuclear aromatic hydrocarbons (PAHs) in sewage sludge amended agricultural soils. Environ. Pollut., 1991, 72(2), 141– 157; https://doi.org/10.1016/0269-7491(91)90064.

  • Andrews, R. J., Lloyd, J. W. and Lerner, D. N., Sewage sludge disposal to agriculture and other options in the UK. In Groundwater Contaminants and their Migration (eds Mather, J. et al.), Geological Society of London, Special Publications, 1998, vol. 128, pp. 63–74.

  • Rogers, H. R., Organic contaminants in sewage sludge. Occurrence and fate of synthetic organic compounds in sewage and sewage sludge – a review. Water Research Centre Report, 1987, PRD 1539-M.

  • Wilson, S. C., Duarte-Davidson, R. and Jones, K. C., Screening the environmental fate of organic contaminants in sewage sludges applied to agricultural soils: the potential for downward movement to groundwaters. Sci. Total Environ., 1996, 185, 45–57.

  • Chung, N. J., Cho, J. Y., Park, S. W., Park, B. J., Hwang, S. A. and Park, T. I., Polycyclic aromatic hydrocarbons in soils and crops after irrigation of wastewater discharged from domestic sewage treatment plants. Bull. Environ. Contamin. Toxicol., 2008, 81, 124–127.

  • Li, X. J., Li, P. J., Lin, X., Gong, Z. Q., Fan, S. X., Zheng, L. and Verkhozin, E. A., Spatial distribution and sources of polycyclic aromatic hydrocarbons (PAHs) in soils from typical oil sewage irrigation area, northeast China. Environ. Monit. Assess., 2008, 143, 257–265.

  • Cai, Q. Y., Mo, C. H., Wu, Q. T., Zeng, Q. Y. and Katsoyiannis, A., Occurrence of organic contaminants in sewage sludge from eleven wastewater treatment plants, China. Chemosphere, 2007, 68(9), 1751–1762.

  • ATSDR, Toxicological profile for polycyclic aromatic hydrocarbons. US Department of Health and Human Service, Agency for Toxic Substances and Disease Registry, USA, 1995.

  • Fernández-Alba, A. R., European Union proficiency test for pesticides in fruits and vegetables for screening methods 02 (EUPTFVSM-02).

  • Kim, K. H., Jahan, S. A., Kabir, E. and Brown, R. J., A review of airborne polycyclic aromatic hydrocarbons (PAHs) and their human health effects. Environ. Int., 2013, 60, 71–80; doi:10.1016/ j.envint.2013.07.019.

  • IARC, International Agency for Research on Cancer, Some nonheterocyclic polycyclic aromatic hydrocarbons and some related exposures. In IARC, Monographs Evalat. Carcinoge. Risks Hum., 2010, 92, 765–771.

  • Khan, S. Aijun, L., Zhang, S., Hu, Q. and Zhu, Y. G., Accumulation of polycyclic aromatic hydrocarbons and heavy metals in lettuce grown in the soils contaminated with long-term wastewater irrigation. J. Hazard. Mater., 2008, 152, 506–515.

  • Zhang, S. et al., Uptake and translocation of polycyclic aromatic hydrocarbons (PAHs) and heavy metals by maize from soil irrigated with wastewater. Sci. Rep., 2017, 7, 12165; doi:10.1038/ s41598-017-12437-w.

  • Wu, W., Huang, H., Ling, Z., Yu, Z., Jiang, Y., Liu, P. and Li, X., Genome sequencing reveals mechanisms for heavy metal resistance and polycyclic aromatic hydrocarbon degradation in Delftia lacustris strain LZ-C Wenyang. Ecotoxicology, 2016, 25(1), 234– 247; doi:10.1007/s10646-015-1583-9.

  • Huang, H. et al., A novel Pseudomonas gessardii strain LZ-E simultaneously degrades naphthalene and reduces hexavalent chromium. Bioresour. Technol., 2016, 207, 370–378.

  • Xiao, J., Guo, L., Wang, S. and Lu, Y., Comparative impact of cadmium on two phenanthrene-degrading bacteria isolated from cadmium and phenanthrene co-contaminated soil in China. J. Hazard. Mater., 2010, 174, 818–823.

  • Thavamani, P., Malik, S., Beer, M., Megharaj, M. and Naidu, R., Microbial activity and diversity in long-term mixed contaminated soils with respect to polyaromatic hydrocarbons and heavy metals. J. Environ. Manage., 2012, 99, 10–17.

  • Kuppusamy, S., Thavamani, P., Megharaj, M. and Naidu, R., Biodegradation of polycyclic aromatic hydrocarbons (PAHs) by novel bacterial consortia tolerant to diverse physical settings – assessments in liquid- and slurry-phase systems. Int. Biodeterior. Biodegrad., 2016, 108, 149–157.

  • Kathavarayan, V., Avudainayagam, S., Doraisamy, P. and Chandraseharan, C. N., Chemical immobilization of lead in long term sewage irrigated soil. J. Agric. Sci. Technol., 2012, 14, 449–458.

  • Chitdeshwari, T., Savithri, P. and Mahimai Raja, S., Effect of sewage bio-solids compost on biomass yield of amaranths and heavy metal availability. J. Indian Soc. Soil Sci., 2002, 50, 480– 484.

  • Musharafia, A. S. K., Mahmoud, I. Y. and Al-Bahry, S. N., Heavy metal pollution from treated sewage effluent. APCBEE Proc., 2013, 5, 344–348.

  • Chary, S. N., Kamala, C. T. and Raj, D. S. S., Assessing risk of heavy metals from consuming food grown on sewage irrigated soils and food chain transfer. Ecotoxicol. Environ. Saf., 2008, 69, 513–524.

  • Black, C. A., Evans, D. D. Ensminger, L. E. White, J. L., Clark, F. E., Dinauer, R. C., Methods of soil Analysis. Part 2. Chemical and Microbiological Properties, American Society of Agronomy, Madison, Wisconsin, USA, 1965.

  • Avudainayagam, S., Megharaj, M., Owens, G., Kookana, R. S., Chittle Borough, D. and Naidu, R., Chemistry of chromium in soils with particular emphasis on tannery waste contaminated sites: a review. Rev. Environ. Contamin. Toxicol., 2003, 178.

  • de Carvalho Damasceno, O. I., Reis, C., Reis, E. L., Bellato, C. R. and Fidêncio, P. H., Assessment of bioavailability of heavy metals after vermicomposting in the presence of electronic waste. Rev. Bras. Cienc. Solo, 2015, 39, 1786–1795.

  • Walkley, A. and Black, I. A., Estimation method for determination of soil organic matter and a proposed modification of the chromic acid titration method. Soil Sci., 1934, 37, 29–33.

  • EPA US, Environmental Protection Agency, United State. Method 8270C: Semivolatile organic compounds by gas chromatography/ mass spectrometry (GC/MS). SW-846, Test methods for eva luating solid waste, physical/chemical methods. United States Environmental Protection Agency, Washington, DC, 1996.

  • Malarkodi, M., Krishnasamy, R., Kumaraperumal, R. and Chitdeshwari, T., Characterization of heavy meal contaminants soils of coimbatore in Tamil Nadu. J. Agron., 2007, 6(1), 147– 151.

  • Chlopecka, A., Bacon, J. R., Wilson, M. J. and Kay, J., Heavy metals in the environment. J. Environ. Qual., 1996, 25, 69–79.

  • Ramos, L., Hernandez, L. M. and Gonzales, M. J., Sequential fractionation of copper, lead, cadmium and zinc in soil from or near Donana national park. J. Environ. Qual., 1994, 23, 50–57.

  • Bashir, F., Tariq, M., Khan, M. H. Khan, R. A. and Aslam, S., Fractionation of heavy metals and their uptake by vegetables growing in soils irrigated with sewage effluent. Turk. J. Eng. Environ Sci., 2014, 38, 1–10.

  • Fytianos, K., Katsianis, G., Triantafyllou, P. and Zachariadis, G., Accumulation of heavy metals in vegetables grown in an industrial area in relation to soil. Bull. Environ. Contam. Toxicol., 2001, 67, 423–430.

  • Somasundaram, J. et al., Accumulation of few heavy metals in sewage sludges, soils and plants of coimbatore, Tamil Nadu (India). J. Environ. Sci. Eng., 2012, 54(1), 13–29.

  • Sara, P. B. K., Megharaj, M., Juhasz, A. L., Sethunathan, N. and Naidu, R., Chromium–microorganism interactions in soils: remediation implications. Rev. Environ. Contam. Toxicol., 2003, 178, 93–164.

  • Khan, A. G., Kuek, C., Chandhry, T. M., Khoo, C. S. and Hayes, W. J., Role of plants, mycorrhizae and phytochelators in heavy metal contaminated land remediation. Chemosphere, 2000, 41, 197–207.

  • Pendias, K. A. and Pendias, H., Trace Elements in Soils and Plants, CRC Press, New York, USA, 2001.

  • Arnesen, A. K. M. and Singh, B. R., Plant uptake and DTPAextractability of Cd, Cu, Ni and Zn in a Norwegian alum shale soil as affected by previous addition of dairy and pig manures and peat. Can. J. Soil Sci., 1999, 78, 531–539.

  • Elliot, H. A., Liberati, M. R. and Huang, C. P., Competitive adsorption of heavy metals by soils. J. Environ. Qual., 1986, 15, 214–219.

  • Wang, N., Li, H. B., Long, J. L., Cai, C., Dai, J. L. Zhanga, J. and Wanga, R. Q., Contamination, source, and input route of polycyclic aromatic hydrocarbons in historic wastewater-irrigated agricultural soils. J. Environ. Monit. 2012, 14, 3076.

  • Finžgar, N., Tlustoš, P. and Leštan, D., Relationship of soil properties to fractionation, bioavailability and mobility of lead and zinc in soil. Plant Soil Environ., 2007, 53(5), 225–238.

  • Duan, L., Naidu, R., Thavamani, P., Meaklim, J. and Megharaj, M., Managing long-term polycyclic aromatic hydrocarbon contaminated soils: a risk-based approach. Environ. Sci. Pollut. Res. 2013, 12, 8927–8941; doi:10.1007/s11356-013-2270-0.

  • Coover, M. P. and Sims, R. C., The effect of temperature on polycyclic aromatic hydrocarbon persistence in an unacclimated agricultural soil. Hazard. Waste Hazard. Mater., 1987, 4, 1.

  • Mackay, D., Shiu, W. Y., Ma, K. and Lee, S. C., Handbook of Physical-Chemical Properties and Environmental Fate for Organic Chemicals, CRC Press, Vol. I, 2006.

  • EPA US, Environmental Protection Agency, United State. Provisional guidance for quantitative risk assessment of polycyclic aromatic hydrocarbons. Development, 1993, 1–28.


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  • Bioavailability of Heavy Metals and Polycyclic Aromatic Hydrocarbon in Long-Term Sewage-Drained Soils of Tamil Nadu

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Authors

Veeramani Kathavarayan
Department of Environmental Science, Tamil Nadu Agricultural University, Coimbatore 641 003, India
S. Avudainayagam
Department of Environmental Science, Tamil Nadu Agricultural University, Coimbatore 641 003, India
K. Sara Parwin Banu
Department of Environmental Science, Tamil Nadu Agricultural University, Coimbatore 641 003, India
N. Chandrasekharan
Department of Soil Science and Agricultural Chemistry, Tamil Nadu Agricultural University, Coimbatore 641 003, India
S. Karthikeyan
Department of Bioenergy, Tamil Nadu Agricultural University, Coimbatore 641 003, India
K. Bhuvaneswari
Department of Agricultural Entomology, Tamil Nadu Agricultural University, Coimbatore 641 003, India
P. T. Ramesh
Department of Environmental Science, Tamil Nadu Agricultural University, Coimbatore 641 003, India

Abstract


Heavy metals and organic contaminants are reported in sewage discharged sites. Screening and assessment of their toxic concentration in soils of the discharged sites of major cities in Tamil Nadu, India have been carried out in the present study. The major cities included Coimbatore (Ukkadam; U), Madurai (Avanaiyapuram; A), Tiruchirappalli (Rettamalai; R), Nesapakkam (N) and Koyambedu (K) Chennai Corporation. The total aquaregia-extractable concentrations of cadmium, chromium, lead and nickel were measured and found to be highest in U, followed by A, R, N and K. Their potential bioavailabilities were quantified in the following order: Cd – N > U > K > R > A; Cr – N > A > K > R > U; Pb – N > K > R; U > A; Ni – N > K > R > U > A. Bioavailable Factor was found to be highest for Cd in U (2.9%–83%) followed by Cr in N (1.1%–62.3%) and Ni in (1.70%– 52.7%) N. With regard to organic contamination, the major pesticides belonged to 13 organochlorine, 10 organophosphate and 8 synthetic pyrethroids reported below detectable concentration. Among the 16 US EPA priority poly aromatic hydrocarbon (PAHs) only 15 were detected. However, PAHs were found to be less than the permissible concentration for soils (0.3 mg kg–1) in sewage-contaminated sites. The results show that there is potential risk of transfer of heavy metals to higher trophic level of the food chain.

Keywords


Heavy Metals, Health Risk, Polycyclic Aromatic Hydrocarbon, Sewage Contamination.

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DOI: https://doi.org/10.18520/cs%2Fv117%2Fi3%2F448-459