The analysis of hexachlorobenzene, hexachlorocyclohexanes, polychlorobiphenyls, and DDTs in muscle of fish from high mountain lakes shows that a proportion of their concentration variance depends on fish age and lake altitude. Interestingly, the magnitude of this share corresponds linearly with the log-transformed vapor pressure (Vp) of the organochlorine compounds (OC). Thus, the distributions of OC with Vp < 10(-2.5) Pa are mostly determined by these two variables. Altitude gradients mainly respond to temperature differences, involving concentration increases of 25-150 times between 8.7 and -2.3 degrees C. The age effect encompasses concentration increments of 2.4-7.8 for average lake differences between 2 and 13 yr. However, both effects are independent since no correlation between fish age and lake altitude is observed. Fish liver concentrations exhibit the same pattern, but the correlations are only significantfor age, suggesting thatthe temperature trend is more related to long-term accumulation than episodic intake. The temperature effect is independent from compound origin. In addition, the sites situated at highest altitude, those most distant from possible ground pollution sources, are the most polluted. The results can be explained by condensation effects such as those described for the latitudinal trends that support the global distillation theory. However, in the high altitude lakes a temperature-dependent amplification mechanism, probably related to low metabolism and respiration at lowtemperatures, enhances OC accumulation in fish beyond the increases predicted from theoretical condensation and solubilization enthalpies. The observed temperature dependence suggests that a general remobilization of OC accumulated in high mountain areas could take place as a consequence of the general warming of these areas anticipated in the climatic change studies.

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Individual polybromodiphenyl ethers (PBDEs) were investigated in liver and muscle tissue of trout from 11 high mountain lakes in Europe and one in Greenland. Trouts in these lakes [brown trout (Salmo trutta), brook trout (Salvelinus fontinalis) and arctic char (Salvelinus alpinus)] are important sentinel species because they are located in the top of the food chain and pollution can only reach these ecosystems by atmospheric transport. The major PBDE congeners were BDE 47 and BDE 99, followed by BDE 100, BDE 153, BDE 154, and BDE 28. These compounds were found in all the samples examined. Their average concentrations [110-1300 and 69-730 pg g(-1) wet weight (ww) in liver and muscle or 2400-40000 and 2900-41000 pg g(-1) lipid weight (lw), respectively] were in the lower range when compared with those of fish from other less remote locations. The highest levels of PBDEs in liver and muscle are found in Lochnagar, Scotland: 11000 and 1200 pg g(-1) ww, respectively (366 000 and 177000 pg g(-1) lw, respectively). Male specimens exhibited higher PBDE concentrations in liver than female. The concentrations of most PBDEs in liver were correlated with fish age (p < 0.01) and, inversely, with condition factor (p < 0.01). Muscle PBDE concentrations did not correlate with age, and only some congeners showed significant positive correlations with condition factor (p < 0.05). The main differences between species were found in the accumulation of the more abundant PBDEs, brook trout showing the highest concentrations in muscle and the lowest in liver. No correlation between the occurrence of these compounds in high mountain fish and altitude, latitude, or temperature was observed. This fact and the lack of correlation between muscle concentrations and age suggest that the fluxes of PBDEs arriving at high mountain lakes are still not constant. In view of the present use of these compounds, they are probably increasing.

Atmospheric concentrations and deposition fluxes of PCDD/F and PCB have been evaluated over a 1-year period in a Mediterranean coastal lagoon (Etang de Thau, France). Indicative PBDE air concentrations in the hot season are also reported in this work. ∑2,3,7,8-PCDD/Fs and ∑18PCBs (gas+particulate) air concentrations ranged from 67 to 1700 fg m(-3) and from 13 to 95 pg m(-3), respectively whereas ∑8PBDEs (gas+particulate) summer time levels varied from 158 to 230 pg m(-3). The PCDD/F and PCB atmospheric occurrence over Thau lagoon and subsequent inputs to the surface waters are determined by an assemble of factors, being the seasonality of atmospheric concentration, the air mass origin and meteorological conditions important drivers. Total (wet+dry) ∑2,3,7,8-PCDD/Fs and ∑18PCBs deposition fluxes to Thau Lagoon waters are 117 and 715 pg m(-2)d(-1), respectively.