This study consisted of a 10-day whole sediment toxicity test with the chironomid Chironomus riparius and a 28-day sediment toxicity test with the oligochaete Tubifex tubifex at seven sites to assess the quality of the River Lambro (Italy), one of the most contaminated rivers of the Po Basin. Endpoints measured were survival and growth for chironomids and cocoon deposition and development of young worms for tubificid oligochaetes. Responses were evaluated in relation to the occurence of organic micropollutants (PCBs, DDT, HCB, and HCH) representative of the industrial and agricultural contamination of the area. Though survival of the organisms remained unaffected, sublethal effects were observed at all sites. The sediment sampled at the farthest upstream site differed from the control only in the number of cocoons deposited by the worms. Both test species in the next three sediments, where concentrations of PCB and DDT were in the range 21.9-39.5 ng g(-1) DW and 0.6-1.3 ng g(-1) DW, respectively, experienced greater toxicity in terms of growth and reproduction. Contamination was particularly high in the site closest to Milan, where the river receives untreated urban and industrial discharges. Levels of total PCBs and total DDT here were up to two orders of magnitude higher than those found at the other sampling locations, and chironomid growth and the reproductive endpoints of tubificids were significantly lower than in the control and the other sites. The test results for the next two stations showed improvement relative to that of Milan, although contamination was still evident. Sublethal effects were in agreement with the measured concentrations of the principal persistent organic pollutants and should be included as part of environmental monitoring efforts as a basis for assessing the recovery of the river.
The present study reports the results of an interlaboratory analysis of selected labile pesticides: trichlorfon, fenamiphos, ethofumesate, phenmedipham, bromofenoxim, chosen among priority compounds, indicated by a European Commission Report as lacking valid analytical procedures. Most of these compounds show stability problems both in solution and during analysis. Each participating laboratory developed methods for the analysis of these compounds and then used the obtained procedure to analyze samples spiked solutions of the five above mentioned pesticides, each in an unknown concentration. Using a different approach, cartridges loaded with samples spiked with the same pesticides were prepared and analyzed for the interlaboratory exercise.
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