Abstract

Introducing biomarkers into monitoring programs requires understanding of their responses in relation to higher-level biological effects as well as modulating effects of confounding environmental factors. We evaluated relationships between the general toxicity biomarkers (acetylcholinesterase [AChE], lysosomal membrane stability [LMS], oxygen radical absorbance capacity [ORAC]) and reproductive performance (fecundity and embryo aberrations) in the amphipod Monoporeia affinis in the Baltic Sea. To further link biomarker response to contaminant (PCBs, PAHs and metals) levels in the surrounding sediments as well as environmental factors (salinity, bottom depth and total organic carbon in sediments [TOC]), correlation and partial least square regression (PLSR) analyses were applied. The observed contaminants levels were frequently elevated for heavy metals and PAHs, but not PCBs. In the amphipod populations, female ORAC values were positively related to the occurrence of females carrying malformed or membrane-damaged embryos and to the percentage of such embryos in their broods, but also to the fecundity. Female AChE activity was negatively related to the frequency of the membrane-damaged embryos, and positively to the frequency of embryos with arrested development in the broods. Moreover, higher AChE activity and ORAC values in the females occurred at elevated concentrations of metals and PAHs, while there was a negative correlation between embryo ORAC and some PCB congeners. The PLSR models explained over 80% of the variation in the female ORAC and AChE values by variation in contaminant concentrations in combination with environmental variables. Specifically, CB180 and PAM4,9 were identified as negative predictors for ORAC, whereas many PAHs and some metals were positive predictors. The AChE activity was positively related to some metals and negatively to PCBs. In the PLSR models, environmental factors had significant modulating effects, with positive effect of salinity on female ORAC and AChE, and negative effect of TOC on the AChE. The LMS data were less informative, with no apparent relation to any of the contaminants. Linking subcellular responses to the reproduction effects facilitates environmental stress assessment and understanding of the response mechanisms, but also calls for more experimental and field data providing a mechanistic understanding to these linkages.

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