Comparing the Impacts of Sediment‐Spiked Cadmium on Chironomidae Larvae in Laboratory Bioassays and Field Microcosms and the Implications for Field Validation of Site‐Specific Threshold Concentrations. (7th July 2021)

• Record Type: Journal Article
• Authors: Liu, Zhihong; Zhang, Chi; Xin, Zhuohang; Tai, Peidong; Song, Changchun; Deng, Xin
• Is Part Of: Environmental toxicology and chemistry. Volume 40:Number 9(2021)
• Page Start: 2450
• Page End: 2462
• Publication Date: 2021-07-07
• Subjects: Benthic macroinvertebrates -- Cadmium -- Sediment toxicity -- Water quality criteria; Pollution -- Environmental aspects -- Periodicals; Environmental chemistry -- Periodicals; 615.902
• DOI: 10.1002/etc.5073
• Languages: English
• ISSNs: 0730-7268

Abstract

Abstract: Information on the effects of pollutants in sediments at an ecosystem level to validate current and proposed risk‐assessment procedures is scarce. The most frequent criticism of these procedures is that responses of surrogate species in the laboratory are not representative of responses of natural populations. A tiered approach using both laboratory and microcosm exposures (96‐h and 21‐d laboratory bioassays and a 3‐mo field microcosm) was conducted to compare the impacts of sediment‐spiked cadmium on the mortality, development, and abundance of Chironomidae larvae. The 96‐h and 21‐d lethal concentrations of sediment‐spiked Cd to 50% of the species Chironomus riparius were estimated to be 201.07 and 172.66 mg/kg, respectively. In the 21‐d laboratory bioassay, the endpoints, including the development rate and emergence ratio, were compared, and the lowest‐observed‐effect concentration (LOEC) values were 325.8 and 10.7 mg/kg, respectively. The abundance, richness, and biomass of field‐collected larvae were compared among the different treatments in the field microcosm, and it was found that the order of sensitivities using different endpoints was biomass (2.6/5.2 mg/kg of no‐observed‐effect concentration/LOEC) > diversity (10.7/21.2 mg/kg) > abundance (41.2/82.7 mg/kg). The toxicity values based on lethal/sublethal changes in the laboratory bioassays might not fully protect field organisms against damage from chemicals, such as Cd, unless an assessment factor of 5 is used. These findings highlight the need to conduct field validation of criteria/guidelines before they are introduced to protect organisms/ecosystems in the field and provide a preliminary template for future field validation of criteria elsewhere. Environ Toxicol Chem 2021;40:2450–2462. © 2021 SETAC