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Acute and sublethal toxicity of the organochlorine insecticide lindane to the amphipod crustacean Hyalella azteca was investigated. Acute experiments were conducted for a maximum test exposure period of 240 h with adult and neonate H. azteca. Median lethal concentrations (LC50s) determined for adult Hyalella included a 48-h LC50 of 47.6 &mgr;g/L and 240-h LC50 of 26.9 &mgr;g/L. For neonate H. azteca 24-, 48-, and 240-h LC50s were 29.5, 14.8, and 9.8 &mgr;g lindane/L, respectively. Neonate H. azteca were approximately three times more sensitive than adults. Two sublethal toxicity bioassays were developed based on the direct and indirect disruption of the precopulatory or mate guarding behavior of Hyalella. This reproductive behavior is readily quantifiable and of ecological significance as it is a vital component of the mating success of the species. The direct disruption bioassay examined the separation of precopulatory pairs maintained in control water and a range of lindane concentrations during a 24-h exposure period. Median separation times (ST50s) were determined and the LOEC was 24.4 &mgr;g lindane/L. The indirect disruption bioassay consisted of a test exposure period of just 4 h after which an invertebrate anesthetic solution was administered to induce separation of precopulatory pairs. The LOEC was 17.3 &mgr;g lindane/L, suggesting that the indirect precopulatory separation bioassay was comparable to the 24-h direct separation study. Both bioassays are rapid, relatively simple to perform, and have yielded effect concentrations that correspond with LC50 values determined using adult and neonate H. azteca life stages over more prolonged lindane exposures. Following some modification, these behavioral bioassays may be suitable for use in the hazard evaluation of sediments and for deployment as in situ toxicity tests.

Trace organic contaminant (TrOC) studies in Australia have, to date, focused on wastewater effluents, leaving a knowledge gap of their occurrence and risk in freshwater environments. This study measured 42 TrOCs including industrial compounds, pesticides, and pharmaceuticals and personal care products by liquid chromatography tandem mass spectrometry at 73 river sites across Australia quarterly for 1 yr. Trace organic contaminants were found in 92% of samples, with a median of three compounds detected per sample (maximum 18). The five most commonly detected TrOCs were the pharmaceuticals salicylic acid (82%, maximum = 1530 ng/L), paracetamol (also known as acetaminophen; 45%, maximum = 7150 ng/L), and carbamazepine (27%, maximum = 682 ng/L), caffeine (65%, maximum = 3770 ng/L), and the flame retardant (2-chloroethyl) phosphate (44%, maximum = 184 ng/L). Pesticides were detected in 28% of the samples. To determine the risk posed by the detected TrOCs to the aquatic environment, hazard quotients were calculated by dividing the maximum concentration detected for each compound by the predicted no-effect concentrations. Three of the 42 compounds monitored (the pharmaceuticals carbamazepine and sulfamethoxazole and the herbicide simazine) had a hazard quotient >1, suggesting that they may be causing adverse effects at the most polluted sites. A further 10 compounds had hazard quotients >0.1, indicating a potential risk; these included four pharmaceuticals, three personal care products, and three pesticides. Most compounds had hazard quotients significantly <0.1. The number of TrOCs measured in this study was limited and further investigations are required to fully assess the risk posed by complex mixtures of TrOCs on exposed biota.

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