Molecular markers of sewage in the ocean, namely, coprostanol, linear alkylbenzenes (LABs) and trialkylamines (TAMs) have been determined in pollution sources (i.e. wastewaters, sewage sludges, river water and sediments), seawater and sediments collected in bays (Tokyo and Guanabara) and in the open sea (western Mediterranean and southern California, Pacific Ocean). The TAM concentrations found in wastewater and sewage sludge are of the same order of magnitude as coprostanol and one order of magnitude higher than LABs. The correlation between coprostanol and TAM concentrations in wastewater (r 2 = 0.89, n = 7) demonstrates a similar urban source. In enclosed bays, TAMs exhibited the highest concentrations presumably attributable to their higher stability than other molecular markers investigated. In open sea transects, the distribution of LABs in surficial sediments is consistent with their enrichment in the colloidal fraction of wastewaters causing a concentration maxima in sediments farther from the source than the other molecular markers. Furthermore, TAMs and LABs enabled us to trace long-range transport of pollution from land-based sources to the open ocean due to their stability in a variety of depositional environments.Source-specific and conservative molecular markers are needed for the assessment of anthropogenic pollution in the marine environment. Coprostanols (5p(H)-cholestan-3|3-ol and 5p(H)-cholestan-3ot-ol, Figure 1) have traditionally been used for this purpose [7][8][9][10]. However, the stability of these compounds under oxic conditions is believed to be limited [9], and in situ formation can occur under strongly anoxic conditions [77]. In order to improve the source specificity, we have defined several indices based on the epimeric 5a(H)/5p(H) ratio of stanols and stanones which are useful for slightly to moderately polluted areas [72]. On the other hand, Venkatesan and Kaplan have used