Maximum likelihood mixture estimation to determine metal background values in estuarine and coastal sediments within the European Water Framework Directive

• Published in: The Science of the total environment 2006-11, Vol.370 (2-3), p.278-293
• Main Authors: RODRIGUEZ, J. G, TUEROS, I, BORJA, A, BELZUNCE, M. J, FRANCO, J, SOLAUN, O, VALENCIA, V, ZUAZO, A
• Format: Article
• Language: English
• Subjects: Applied sciences; Arsenic - analysis; Earth sciences; Earth, ocean, space; Engineering and environment geology. Geothermics; Exact sciences and technology; Geologic Sediments - analysis; Guidelines as Topic; Likelihood Functions; Metals, Heavy - analysis; Pollution; Pollution sources. Measurement results; Pollution, environment geology; Seawater; Soil and sediments pollution; Spain; Water Pollutants, Chemical - analysis; Water Pollution - legislation & jurisprudence; Water Pollution - prevention & control
• ISSN: 0048-9697; 1879-1026
• DOI: 10.1016/j.scitotenv.2006.08.035

Some of the recently derived European Directives, such as the Water Framework and Marine Strategy, have, as ultimate aims, to achieve concentrations of hazardous substances in the marine environment near background values. Hence, the determination of natural background levels, in marine sediments, is highly relevant. The present study proposes the use of the maximum likelihood mixture estimation (MLME) to determine regional background levels and upper threshold of metal concentration, with the Basque Country as a case study (with a data set of 575 samples, from estuarine and littoral areas, including both intertidal and subtidal sediments). The heuristic procedure is applied with unimodal data distributions (Cd, Cr, Fe and Ni) and the mixture density estimations, based upon maximum likelihood, are carried out with polypopulational data distributions (As, Cu, Mn, Hg, Pb and Zn). The upper limits of the distribution are proposed, as the limits between 'High Status' and 'Good Status' (according to the Water Framework Directive terminology). The regional upper limits were 0.45 microg g(-1) for Cd, 71 microg g(-1) for Cr, 53,542 microg g(-1) for Fe, 57 microg g(-1) for Ni, 24 microg g(-1) for As, 64 microg g(-1) for Cu, 447 microg g(-1) for Mn, 0.27 microg g(-1) for Hg, 66 microg g(-1) for Pb, and 248 microg g(-1) for Zn. The results from this study can assist further in the determination of sediment reference conditions, to assess chemical status, within the above-mentioned directives; likewise, it will be studied as a useful methodology in determining regional metal backgrounds in other European countries.