Chlorinated flame retardants, particularly dechlorane plus (DP), were widely used in commercial applications and are ubiquitous in the environment. A total of seven species of aquatic organisms were collected concurrently from the region of a chemical production facility in Huai’an, China. DP and structurally related compounds including mirex, dechloranes 602, 603, 604, chlordene plus (CP), DP monoadduct (DPMA), and two dechlorinated breakdown products of DP, decachloropentacyclooctadecadiene (anti-Cl10-DP) and undecachloropentacyclooctadecadiene (anti-Cl11-DP), were detected in these aquatic organisms. Nitrogen stable isotope ratios were also measured to determine the trophic levels of the organisms. Trophic magnification factors (TMFs) for these chemicals were calculated with values ranging from 1.0 to 3.1. TMFs for CP, mirex, anti-DP, and ∑DP were statistically greater than 1, showing evidence of biomagnification in the food web. Concentration ratios of anti-Cl11-DP to anti-DP showed a significant relationship with trophic level, implying that anti-Cl11-DP had a higher food-web magnification potential than its precursor. The biota-sediment accumulation factors and TMFs for DP demonstrated stereoselectivity, with syn-DP having a greater bioaccumulation potential than anti-DP in the aquatic environment.

Predicting food web responses to climate change can be difficult because of the potentially complex interplay between co-occurring climate variables and multiple interacting species across trophic levels. The large majority of research in this field has focused on understanding the effects of single climate variables on species at one or two trophic levels, implicitly assuming that simultaneous shifts across multiple climate variables will have additive effects on food web dynamics. We constructed a tri-trophic food web model and varied temperature, CO2, and water availability both alone and in concert to test this assumption. We found that population biomass does indeed respond additively across trophic levels when temperature, CO2, and water availability all increase simultaneously to moderate levels; however, if water availability decreases, like in a drought scenario, all three trophic levels respond antagonistically. We also found that interaction effect magnitude is highly dependent on temperature and water availability. Decreases in water availability led to 54–74% declines in population biomass across trophic levels when temperatures were within normal organismal operating ranges, but dry conditions coupled with high temperatures led to the extinction of the highest trophic level. Our results suggest that studying simplified versions of climate change and food webs will not be sufficient to predict the responses of real ecological systems. Therefore climate change ecology experiments and models must incorporate more complexity into their structure.

Nanomaterials of various shapes and dimensions are widely used in the medical, chemical, and electronic industries. Multiple studies have reported the ecotoxicological effects of nanaoparticles when released in aquatic and terrestrial ecosystems; however, information on the toxicity of silver nanowires (AgNWs) to freshwater organisms and their transfer through the food webs is limited. In the present study, we aimed to evaluate the toxicity of 10- and 20-μm-long AgNWs to the alga Chlamydomonas reinhardtii, the water flea Daphnia magna, and the zebrafish and study their movement through this three-species food chain using a variety of qualitative and quantitative methods as well as optical techniques. We found that AgNWs directly inhibited the growth of algae and destroyed the digestive organs of water fleas. The results showed that longer AgNWs (20μm) were more toxic than shorter ones (10μm) to both algae and water fleas, but shorter AgNWs were accumulated more than longer ones in the body of the fish. Overall, this study suggests that AgNWs are transferred through food chains, and that they affect organisms at higher trophic levels, potentially including humans. Therefore, further studies that take into account environmental factors, food web complexity, and differences between nanomaterials are required to gain better understanding of the impact of nanomaterials on natural communities and human health.