Toxicity of Sediment-Associated Pesticides to <Emphasis Type="Italic">Chironomus dilutus</Emphasis> and <Emphasis Type="Italic">Hyalella azteca</Emphasis>

Two hundred sediment samples were collected and their toxicity evaluated to aquatic species in a previous study in the agriculturally dominated Central Valley of California, United States. Pyrethroid insecticides were the main contributors to the observed toxicity. However, mortality in approximately one third of the toxic samples could not be explained solely by the presence of pyrethroids in the matrices. Hundreds of pesticides are currently used in the Central Valley of California, but only a few dozen are analyzed in standard environmental monitoring. A significant amount of unexplained sediment toxicity may be due to pesticides that are in widespread use that but have not been routinely monitored in the environment, and even if some of them were, the concentrations harmful to aquatic organisms are unknown. In this study, toxicity thresholds for nine sediment-associated pesticides including abamectin, diazinon, dicofol, fenpropathrin, indoxacarb, methyl parathion, oxyfluorfen, propargite, and pyraclostrobin were established for two aquatic species, the midge Chironomus dilutus and the amphipod Hyalella azteca. For midges, the median lethal concentration (LC₅₀) of the pesticides ranged from 0.18 to 964 μg/g organic carbon (OC), with abamectin being the most toxic and propargite being the least toxic pesticide. A sublethal growth endpoint using average individual ash-free dry mass was also measured for the midges. The no–observable effect concentration values for growth ranged from 0.10 to 633 μg/g OC for the nine pesticides. For the amphipods, fenpropathrin was the most toxic, with an LC₅₀ of 1–2 μg/g OC. Abamectin, diazinon, and methyl parathion were all moderately toxic (LC₅₀s 2.8–26 μg/g OC). Dicofol, indoxacarb, oxyfluorfen, propargite, and pyraclostrobin were all relatively nontoxic, with LC₅₀s greater than the highest concentrations tested. The toxicity information collected in the present study will be helpful in decreasing the frequency of unexplained sediment toxicity in agricultural waterways.     

Acute Toxicity of Methyl-Parathion in Wetland Mesocosms: Assessing the Influence of Aquatic Plants Using Laboratory Testing with <Emphasis Type="Italic">Hyalella azteca</Emphasis>

Methyl-parathion (MeP) was introduced into constructed wetlands for the purpose of assessing the importance of distance from the source of contamination and the role of emergent vegetation on the acute toxicity to Hyalella azteca (Crustacea: Amphipoda). A vegetated (90% cover: mainly Juncus effuses) and a nonvegetated wetland (each with a water body of 50 × 5.5 × 0.2 m) were each exposed to a simulated MeP storm runoff event. H. azteca was exposed for 48 h in the laboratory to water samples taken from the wetlands at a distance of 5, 10, 20, and 40 m from the pesticide inlet 3 h, 24 h, 96 h, and 10 days following application. Methyl-parathion was detected throughout the nonvegetated wetland, whereas the pesticide was only transported halfway through the vegetated wetland. A repeated-measure three-way analysis of variance (ANOVA) using time, location, and vegetation indicated significantly lower toxicity in the vegetated wetland. Furthermore, the mortality decreased significantly with both increasing distance from the inlet and time (48-h LC₅₀ ± 95% CI: 9.0 ± 0.3 g/L). A significant three-way interaction of time × vegetation × location confirmed higher toxicity at the inlet area of the nonvegetated wetland immediately after contamination. Significant linear regressions of maximum mortality (independent of time) versus distance from the pesticide inlet indicated that 44 m of vegetated and 111 m of nonvegetated wetland would reduce H. azteca mortality to 5%. These results suggest that vegetation contributes to reduced MeP effects in constructed wetlands.     

Effects of Copper in Flooded Florida Agricultural Soils on <Emphasis Type="Italic">Hyalella azteca</Emphasis>

This study examined the uptake and effects of copper (Cu) from flooded agricultural soils to epibenthic amphipods (Hyalella azteca) using 10-day sediment toxicity tests. Soils were collected from 10 citrus agricultural sites in South Florida. One sediment toxicity test was conducted with one flooding of the 10 soils, and based on the results of this test a second sediment toxicity test was conducted with 4 of the soils, after four 14-day flooding and four 14-day drying intervals over 4 months. Sediment toxicity tests were conducted under flow-through conditions using U.S. EPA methodology. Effects on survival, dry weight, and whole-body Cu concentrations of H. azteca were determined. Cu concentrations in overlying water and sediment of both sediment toxicity tests exceeded regulatory criteria for aquatic organisms. Although survival of H. azteca was not consistently affected from the first to the second sediment toxicity tests, dry weight was consistently reduced and related to Cu concentrations in soil, overlying water, and pore water. Furthermore, whole-body tissue Cu concentrations were significantly higher in H. azteca in all 10 soil-water treatments in the first sediment toxicity test and in all 4 soil-water treatments in the second sediment toxicity test compared to controls. Whole-body tissue concentrations and effects on dry weight were related to Cu exposures in soil, overlying water, and pore water. In these managed soil-water systems, small fish consuming H. azteca with high concentrations of Cu may be at risk.     

Evaluation of Bioaccumulation and Photo-induced Toxicity of Fluoranthene in Larval and Adult Life-Stages of <Emphasis Type="Italic">Chironomus tentans</Emphasis>

Laboratory sediment tests were conducted to evaluate the bioaccumulation and photo-induced toxicity of fluoranthene in larval and adult life-stages of the midge, Chironomus tentans. In the first of 2 experiments, fourth-instar and adult C. tentans exposed to spiked sediments (204 g fluoranthene/g dry weight) were collected for determination of fluoranthene tissue concentrations and toxicity after ultraviolet (UV) radiation treatment in the absence of sediment (water-only). Fluoranthene tissue concentrations in larvae collected after a 72-hour exposure period were 7 times greater than concentrations in adults collected on emergence from the same spiked sediments. Fluoranthene-exposed adults were tolerant of UV exposure (100% survival after 7 hours), whereas larvae were sensitive (0% survival after 1 hour). In the second experiment, C. tentans larvae were exposed for 96 hours to 2 sediment treatments (170 and 54 g fluoranthene/g dry weight), after which fluoranthene tissue concentrations were determined and UV exposures conducted under water-only versus sediment conditions. Exposure to UV radiation, in conjunction with sediment, provided larvae with significant protection from photo-induced toxicity compared with the water-only exposure. Adults that emerged from the 2 sediment treatments were also analyzed for fluoranthene tissue residues and exposed to UV radiation. Fluoranthene tissue residues were higher in adult female than in adult male midges, but exuviae from both sexes contained higher fluoranthene concentrations than whole-body tissue, thus demonstrating that the molting process is a possible detoxification mechanism. Consistent with the greater tissue residue concentrations, female midges demonstrated a significant decrease in survival under UV exposure compared with male midges. These studies indicated that both the burrowing behavior of the larvae and the elimination of fluoranthene in molted exuviae are protective mechanisms against photo-enhanced PAH toxicity in this species.     

Toxicity of Chiral Pesticide <Emphasis Type="Italic">Rac-</Emphasis>Metalaxyl and <Emphasis Type="Italic">R-</Emphasis>Metalaxyl to <Emphasis Type="Italic">Daphnia magna</Emphasis>

Chirality in pesticides has become a challenge because of enantiomers’ different toxicities to non-target organisms. Acute and chronic toxicities of Rac-metalaxyl and R-metalaxyl to Daphnia magna were determined and compared. The 48-h LC50 for Rac- and R-metalaxyl to Daphnia magna were 51.5 and 41.9 mg/L. In a 14-day chronic test, the lowest-observed-effective concentration (LOEC) and no-observed-effective concentration (NOEC) of Rac-metalaxyl were 2 and 1 mg/L, respectively, whereas those of R-metalaxyl were 1 and 0.1 mg/L. Body length, days-to-first-brood and number of broods per female were significantly (p < 0.05) affected by R-metalaxyl at >1.0 mg/L, but affected by Rac-metalaxyl at ≥2.0 mg/L.     

Effects of Pentachlorophenol on <Emphasis Type="Italic">Galba pervia</Emphasis>, <Emphasis Type="Italic">Tubifex sinicus</Emphasis> and <Emphasis Type="Italic">Chironomus plumousus</Emphasis> Larvae

The 24-h median lethal concentrations of pentachlorophenol to Chironomus plumousus, Tubifex sinicus and Galba pervia were 0.302, 0.977 and 0.293 mg/L, respectively. Bioconcentration factors of C. plumousus, T. sinicus and G. pervia to pentachlorophenol were 108, 367 and 85 at 0.02 mg/L pentachlorophenol, respectively. As pentachlorophenol concentration increased, the G. pervia egg hatching rates became lower, and the total hatched time became longer. Pentachlorophenol teratogenesis was demonstrated by observing the deformation of C. plumousus larvae mentum.     

Characterization of Acute and Chronic Toxicity of DBP to <Emphasis Type="Italic">Daphnia magna</Emphasis>

As a commonly used phthalate compound, di(n-butyl) phthalate (DBP) is an emerging group of polyvinyl chloride plasticizers. The acute toxicity of DBP has been extensively studied using the aquatic indicator organism, Daphnia magna. However, little is known about chronic and transgenerational toxicity of DBP. In this study, acute LC₅₀ values were 3.04 mg/L (24 h) and 2.55 mg/L (48 h). Chronic toxicity tests in the case of maternal exposure to DBP revealed that DBP had negligible effects on growth and reproduction of F3 generation of D. magna, although the growth rate of body length and the intrinsic rate of increase were prominently reduced, to a pretty small extent. At specific concentrations, DBP generated beneficial effects on the parental generation of D. magna and no obvious impacts on the F1 generation. This study showed that maternal exposure to DBP did not cause any transgenerational effects on D. magna.     

<Emphasis Type="Italic">Hyalella azteca</Emphasis> (Saussure) Responses to Coldwater River Backwater Sediments in Mississippi,USA

Sediment from three Coldwater River, Mississippi backwaters was examined using 28 day Hyalella azteca bioassays and chemical analyses for 33 pesticides, seven metals and seven PCB mixtures. Hydrologic connectivity between the main river channel and backwater varied widely among the three sites. Mortality occurred in the most highly connected backwater while growth impairment occurred in the other two. Precopulatory guarding behavior was not as sensitive as growth. Fourteen contaminants (seven metals, seven pesticides) were detected in sediments. Survival was associated with the organochlorine insecticide heptachlor.     

Enantioselective Chronic Toxicity of Fipronil to <Emphasis Type="Italic">Ceriodaphnia dubia</Emphasis>

Fipronil is a phenylpyrazole pesticide that has greatly increased in popularity in recent years. As a chiral molecule, fipronil is released into the environment as a 1:1 mixture (called a racemate) of its two enantiomers. Previous toxicity work has indicated that the enantiomers of fipronil exhibit significantly different levels of acute toxicity to the nontarget organism Ceriodaphnia dubia. In this work we examine the chronic effects of the pure enantiomers and racemate on the survival, development, mobility, and reproduction of C. dubia adults and the survival and mobility of their offspring. Based on 8-day trials, the (+) enantiomer of fipronil showed a significantly greater reduction in the number of offspring (LOEC = 2 μg/L) than either the racemate (LOEC = 15 μg/L) or the (−) enantiomer (LOEC = 30 μg/L). The (+) enantiomer was also shown to be significantly more toxic to neonates born during the course of the experiment (LC50₂₄ = 18.1 μg/L, LC50₄₈ = 10.3 μg/L) than the racemate (LC50₂₄ = 33.3 μg/L, LC50₄₈ = 30.3 μg/L), but only after 48 h. Both the (+) enantiomer and the racemate were significantly more toxic to C. dubia than the (−) enantiomer (LC50₂₄ = 65.2 μg/L, LC50₄₈ = 50.1 μg/L) at both time points. Qualitative mobility data followed a similar trend, with the (+) enantiomer causing greater impairment in mobility at low concentrations. These data imply that the (−) enantiomer has less impact on the reproductive success of C. dubia than either the (+) enantiomer or the racemate. Enantiomerically pure or enriched formulations of (−) fipronil may reduce impacts to the nontarget organism C. dubia.     

Accumulation and Chronic Toxicity of Uranium Over Different Life Stages of the Aquatic Invertebrate <Emphasis Type="Italic">Chironomus tentans</Emphasis>

Limited data are available on the effects of uranium (U) exposures on benthic macroinvertebrates, something that would be needed before national or provincial water quality guidelines could be developed. The goal of this study was to evaluate chronic U toxicity and accumulation in the aquatic invertebrate Chironomus tentans. Test organisms were exposed to three aqueous U concentrations (40, 200, and 1,000 μg/L) and an untreated control. Larval growth, adult emergence, and U tissue concentrations at different life stages were evaluated. The measured no-observed-effect concentration (NOEC) and lowest-observed-effect concentration (LOEC) for growth of C. tentans larvae after 10 days of U exposure were 39 and 157 μg/L, respectively. At U concentrations >157 ug/L, there was reduced larval growth of 30% to 40%, which corresponded to reduced adult emergence of 40% to 60%. Despite significant delays in time to adult emergence, there were no significant effects on reproductive output of successfully emerged adults. The F₁ generation C. tentans larvae that were never directly exposed to U, but originated from adult males and females exposed to U during their immature life stages, displayed a significant decrease in 10-day growth that was similar to that observed for the F₀-exposed larvae. This suggests that the environment of the parental generation can significantly influence the development of the next generation through environmentally induced parental effects. Uranium accumulated in C. tentans immature stages was partially excreted during molting and metamorphosis to the adult stage. However, the elimination of U was not complete and some was still measured in adult midges. Consequently, a minor transfer of U from the aquatic to the terrestrial environment could be expected to occur.     

Acute and Chronic Copper Toxicity to a Saltwater Cladoceran <Emphasis Type="Italic">Moina monogolica</Emphasis> Daday

The objective of this study was to evaluate the sensitivity of a saltwater cladoceran Moina monogolica Daday to copper toxicity. Acute and chronic toxicity tests were conducted according to the American Society for Testing and Materials (ASTM) guidelines. The 24- and 48-h LC(50)s and their 95% confidence intervals (CIs) were calculated as 154.21 (135.50-182.05) microg Cu/L and 106.07 (99.77- 112.36) microg Cu/L , respectively, based on measured copper concentrations. When compared with different phyla or classes of estuarine organisms, M. monogolica had moderate sensitivity and was suitable to be used as an indicator organism in the Changjiang estuary. Eight end points of longevity, number of broods, brood size, total reproduction, time to first brood, intrinsic rate of natural increase (r(m)), net reproductive rate (R(0)), and mean generation time (T) used to evaluate chronic effects were affected at chronic copper concentrations. Comparisons of chronic effects showed that toxicity mechanisms of dissolved copper are different from those of dietary exposure. The EC(20)s, EC(50)s, and their 95% CIs of end points were calculated using linear regression equations. The geometric mean generated the maximum-acceptable-toxicant concentration of 6.74 microg Cu/L between the no-observed-effect concentration of 5.06 and the lowest-observed-effect concentration of 8.99 microg Cu/L for brood size, total reproduction, r(m), and R(0), and 12.1 microg Cu/L between 8.99 and 16.29 microg Cu/L for longevity and number of broods as the end points, respectively. The EC(20) of R(0) appeared to be the most sensitive at 3.82 microg Cu/L among the end points. Results showed that aquatic organisms were possibly negatively affected at sites of higher copper concentrations in the Changjiang estuary. Further research is needed to evaluate the direct or indirect effects of copper more comprehensively to protect aquatic organisms and their habitats in the Changjiang estuary.