Drivers of copper sensitivity in copepods: A meta-analysis of LC50s.

Copper is both an essential trace element and a potent pesticide. The use of copper as an antifoulant has increased in the last decades in line with the expanding aquaculture and shipping industries. In aquatic environments, it also affects non-target taxa. One of which are copepods, which constitute the central link in the marine food web. Despite their ecological importance, there are no systematic reviews of the lethal concentration range and drivers of copper toxicity in this taxon. Here, we combined literature data from 31 peer-reviewed articles recording the Lethal Concentration 50 (LC50) for copper in copepods and the experiments' respective environmental, developmental, and taxonomic parameters. The LC50 is a traditional endpoint for toxicity testing used in standardized toxicity testing and many ecological studies. In total, we were able to extract 166 LC50 entries. The variability in the metadata allowed for a general analysis of the drivers of copper sensitivity in copepods. Using a generalized additive modeling approach, we find that temperature increases copper toxicity when above approximately 25℃. Counter to our expectations; salinity does not influence copper sensitivity across copepod species. Unsurprisingly, nauplii are more susceptible to copper exposure than adult copepods, and benthos-associated harpacticoids are less sensitive to copper than pelagic calanoids. Our final model can predict sensible specific-specific copper concentrations for future experiments, thus giving an informed analytical approach to range testing in future dose-response experiments. Our model can also potentially improve ecological risk assessment by accounting for environmental differences. The approach can be applied to other toxicants and taxa, which may reveal underlying patterns otherwise obscured by taxonomic and experimental variability.

Pesticide effects on the abundance of springtails and mites in field mesocosms at an agricultural site.

The use of pesticides to protect crops often affects non-target organisms vital to ecosystem functioning. A functional soil mesofauna is important for decomposition and nutrient cycling processes in agricultural soils, which generally have low biodiversity. To assess pesticide effects on natural soil communities we enclosed intact soil cores in situ in an agricultural field in 5 cm wide mesocosms. We used two types of mesh lids on the mesocosms, allowing or preventing migration of mesofauna. The mesocosms were exposed to the insecticide imidacloprid (0, 0.1, 1, and 10 mg/kg dry soil) and left in the field for 20 days. Overall, regardless of lid type, mesocosm enclosure did not affect springtail or mite abundances during the experiment when compared with undisturbed soil. Imidacloprid exposure reduced the abundance of both surface- and soil-living springtails in a concentration-dependent manner, by 65-90% at the two highest concentrations, and 21-23% at 0.1 mg/kg, a concentration found in some agricultural soils after pesticide application. Surface-living springtails were more affected by imidacloprid exposure than soil-living ones. In contrast, neither predatory nor saprotrophic mites showed imidacloprid-dependent changes in abundance, concurring with previous findings indicating that mites are generally less sensitive to neonicotinoids than other soil organisms. The possibility to migrate did not affect the springtail or mite abundance responses to imidacloprid. We show that under realistic exposure concentrations in the field, soil arthropod community composition and abundance can be substantially altered in an organism-dependent manner, thus affecting the soil community diversity.

Recovery of cholinesterase activity in the earthworm Eisenia fetida Savigny following exposure to chlorpyrifos.

Organophosphorus (OP) insecticides inhibit cholinesterase activity, an essential process in the nervous system of most animals. Re-establishment of active enzymes is slow and depends on elimination of the insecticide from the body followed by two lengthy processes: Reactivation and/or biosynthesis of new enzymes. Earthworms (Eisenia fetida) were exposed to either clean or chlorpyrifos-containing (240 mg/kg) soil for 48 h. After transfer to clean soil, we monitored two cholinesterases (E1 and E2) and chlorpyrifos content of the earthworms for 12 weeks. After 14 to 21 d of recovery, the exposed and control worms were indistinguishable in terms of appearance and behavior. Chemical analysis showed a rapid elimination of chlorpyrifos from the earthworms, with only minor levels detected after one week. The activities of E1 and E2 were measured spectrophotometrically in whole specimen homogenates using acetylthiocholine as the substrate. Carbaryl, which selectively inhibits E1, was used to discriminate the enzyme activities. Mean +/- standard error of mean of E1 and E2 activity in the controls immediately after exposure were 1.57 +/- 0.18 nanokatal (nkat)/mg protein (n = 3) and 0.95 +/- 0.07 nkat/mg protein, respectively, and 0.48 +/- 0.07 nkat/mg and 0.45 +/- 0.06 nkat/mg, respectively, in exposed worms. After three weeks, E1 had regained an activity comparable to the controls, whereas E2 remained depressed throughout the 12-week monitoring period. The non- or late recovery of E2 makes this enzyme a potential biomarker candidate for previous OP insecticide exposure in Eisenia fetida, provided the protocol for measurements is improved and standardized.