Protecting Groundwater for Health - Scientific background

Page 151

Chemicals: Health relevance, transport and attenuation

131

wastewater treatment facilities play a key role in the introduction of EDCs into surface water and groundwater (Drewes and Shore, 2001). The transport of EDCs to groundwater depends on their hydrophobicity and degradability. The majority of highly potent compounds such as steroids are hydrophobic and degradable. Degradation rates of EDC compounds depend on temperature, soil characteristics and their molecular weights (IUPAC, 2003). The potential risk related to an uptake of individual EDCs present in wastewater affected groundwater by humans does not appear to be very significant. The small data set about the fate of EDCs (such as natural and synthetic hormones, surfactants and pesticides) during percolation through the soil and aquifer and the lack of toxicity data on long-term exposure of low concentrations makes it at present impossible to finally assess the impact of EDCs in groundwater on human health. However, contaminated groundwater may be impacted by a mix of different compounds, which could additively impose endocrine disrupting effects.

4.8

REFERENCES

Ahmed, F.M., Ali, M.A. and Adeel, Z. (2001) Technologies for Arsenic Removal From Drinking Water, BUET, Dhaka. Alaerts, G.J., Khouri, N. and Kabir, B. (2001) Strategies to mitigate arsenic contamination in water supply. In United Nations Synthesis Report on Arsenic in Drinking Water, www.who.int/water_sanitation_health/dwq/en/arsenicun8.pdf (accessed April 29. 2005). Albu, M.A., Morris, L.M., Nash. H. and Rivett, M.O. (2002) Hydrocarbon contamination of groundwater at Ploiesti, Romania. In: Sustainable Groundwater Development (eds. K.M. Hiscock, M.O. Rivett and R.M. Davison), pp. 293-301, Geological Society Special Publication No. 193, London. Allen-King, R.M., Ball, W.P. and Grathwohl, P. (2002) New modeling paradigms for the sorption of hydrophobic organic chemicals to heterogeneous carbonaceous matter in soils, sediments, and rocks. Advances in Water Resour., 25, 985-1016. Appelo, C.A.J. and Postma, D. (1993) Geochemistry, Groundwater and Pollution, Balkema, Rotterdam. Araya, M., Chen, B., Klevay, L.M., Strain, J.J., Johnson, L., Robson, P., Shi, W., Nielsen, F., Zhu, H., Olivares, M., Pizarro, F., Haber, L.T. (2003) Confirmation of an acute no-observedadverse-effect and low-observed-adverse-effect level for copper in bottled drinking water in a multi-site international study. Regul. Toxicol. Pharmacol. 38, 389-399. Ashley, R.P. (1998) Foreseeability of environmental hazards: the implications of the Cambridge Water Company case. In: Groundwater Contaminants and their Migration, (ed. J. Mather), pp. 23-26, Special Publication 128, Geological Society, London. Bailey, K., Chilton, J., Dahi, E, Lennon, M. and Jackson, P (In Press) Fluoride in Drinking Water. WHO Drinking-water Series. IWA Publishing, London. Barceloux, D.G. (1999) Selenium. J. Toxicol. Clin. Toxicol., 37(2), 145-172. Barker, J.F., Patrick, G.C. and Major, D. (1987) Natural attenuation of aromatic hydrocarbons in a shallow sand aquifer. Ground Water Monitor Review 7(4), 64-71. Barnard, C., Daberkow, S., Padgitt, M., Smith, M.E. and Uri, N.D. (1997) Alternative measures of pesticide use. Sci. Total Environ., 203, 229-244. Barnes, C.J. Jacobson, G. and Smith, G.D. (1992) The origin of high-nitrate groundwaters in the Australian arid zone. J. Hydrology, 137, 181-197. Bedient, P.B., Rifai, H.S. and Newell, C. (1999) Ground Water Contamination: Transport and Remediation, 2nd edn, Prentice-Hall, New Jersey.


Issuu converts static files into: digital portfolios, online yearbooks, online catalogs, digital photo albums and more. Sign up and create your flipbook.