Polycyclic musk fragrances in the aquatic environment.

The polycyclic musk fragrances, mainly 1,3,4,6,7,8-hexahydro-4,6,6,7,8,8-hexamethylcyclopenta(g)-2-ben zopyrane (HHCB) and 7-acetyl-1,1,3,4,4,6-hexamethyltetrahydronaphthalene (AHTN) are synthetic musk fragrances which are used in almost all scented consumer products, such as perfumes, cosmetics and laundry detergents. Concerning their chemical structures the polycyclic musks are indane and tetraline derivatives highly substituted mainly by methyl groups. Their production has been increased continuously during the last years with a world-wide production volume today of about 6000 t/year. After their application in private households they are dumped via the sewage treatment plants into the aquatic environment. In this review the analysis of polycyclic musk compounds in environmental samples is shortly presented and all published data of polycyclic musk compounds in water, sediment, suspended particulate matter (SPM), sewage sludge, and biota are summarized and discussed. The highest HHCB and AHTN concentrations were analysed in water (maximum concentrations: 6 microg HHCB/l, 4.4 microg AHTN/1) and sludge (maximum concentrations: 63 mg HHCB/kg dry matter, 34 mg AHTN/kg dry matter) from sewage plants, and in fish (maximum concentrations: 159 mg HHCB/kg lipid, 58 mg AHTN/kg lipid) from sewage ponds. In all other samples from different aquatic ecosystems these chemicals were unequivocally detected in varying concentrations dependent on the distance to sewage treatment plants. Even in marine water samples from the German Bight HHCB and AHTN could be quantified at the lower ng/l level. Very often HHCB and AHTN formed the major organic contaminants, in all samples their concentrations exceeded those of musk xylene and musk ketone. Also several by-products and impurities of the commercial polycyclic musks were analysed in river and waste water samples in not negligible amounts. The apparently ubiquitous distribution of polycyclic musks in the aquatic environment demonstrates the persistence and lipophilicity of these pollutants. The high log K(ow) values of HHCB and AHTN (5.7-5.9) do not directly correlate with their relatively low bioconcentration factors (BCFs) derived from fish experiments, this discrepancy may be explained by a particular metabolism in fish. There are indications of a possible species dependent metabolisation. For a general risk assessment of this new group of environmental pollutants besides the missing toxicological data, further studies on the distribution of the polycyclic musk fragrances including their by-products in the aquatic environment, on possible degradation processes in sediment/sludge as well as on the metabolism in fish are urgently needed.