Timothy R. Gleason

Risks of Endocrine-Disrupting Compounds to Wildlife: Extrapolating from Effects on Individuals to Population Response

Although this manuscript has been technically reviewed at AED and cleared for publication, it has not be subjected to Agency level review and therefore does not necessarily reflect the views of the U.S. EPA. Mention of trade names, products, or services does not convey, and should not be interpreted as conveying, official U.S. EPA approval, endorsement, or recommendation. Much of the research conducted on the effects of endocrine disrupting compounds (EDCs) has been focused on effects at the individual or subindividual level. The challenge from the point of view of ecological risk assessment is to determine effects on populations and higher levels of biological organization. While there have been some notable cases where field studies were used to demonstrate effects of EDCs on exposed populations in the wild, there has been relatively little research addressing the quantitative linkage between effects at the individual level and effects at the population level. The present study provides an example of linking markers of endocrine effects to indicators of population level effect using basic population models and published data for a fish species often used in laboratory studies, the fathead minnow (Pimephales promelas). Additionally, the relation between life history strategy and stressor response is explored using population models for two bird species, European kingfisher (Alcedo atthis) and least tern (Sterna antillarum browni), with markedly different life history strategies. As these examples demonstrate, populations of species that have different life history strategies can respond differently to a stressor producing responses of similar type and magnitude at the individual level. Matrix population models represent quantitatively the life history strategy of an organism and provide a framework for exploring the risks that EDCs pose to wildlife populations.

Evolutionary and Ecological Effects of Multi-Generational Exposures to Anthropogenic Stressors

Biological and ecological responses to stress are dictated by duration and frequency, as well as instantaneous magnitude. Conditional compensatory responses at the physiological and behavioral levels, referred to as ‘acclimation’, may mitigate effects on individuals experiencing brief or infrequent periods of moderate stress. However, even modest stress over extended periods may reduce the fitness of some or all exposed individuals. In this way, specific stress that persists over multiple generations will increase probabilities for extinction of populations composed of sensitive individuals. For populations whose members demonstrate variance and heritability for stressor response, this selective loss of sensitive individuals may result in populations dominated by resistant individuals. The formation of these ‘adapted’ populations may be considered an ecological compensatory mechanism to multi-generational stress. Paradoxically, the biological costs to individuals of toxicity and physiological acclimation may result in obvious signs of stress in affected wildlife populations while the costs of genetic adaptation may be more covert. It is important to consider such costs because recent evidence suggests that anthropogenic stressors have acted as powerful selection agents that have modified the composition of wildlife populations subjected for successive generational exposures to specific stressors. This essay focuses on a case study where adaptation has been demonstrated in fish populations with a history of chronic exposure to persistent, bioaccumulative and toxic environmental contaminants. Because the magnitude, breadth and long-term outcomes of such changes are unknown, ecological risk assessments that are limited in focus to short-term exposures and consequences may seriously underestimate the ecological and evolutionary impacts of anthropogenic stressors.

Biological responses of the sea urchin, Arbacia punctulata, to lead contamination for an estuarine ecological risk assessment

An estuarine ecological risk assessment for thePortsmouth Naval Shipyard (PNS) Kittery, ME, wasconducted utilizing the U.S. EPAs Framework forEcological Risk Assessment (ERA). As part of theanalysis phase of the ERA, laboratory studies wereconducted to develop quantitative exposure-responserelationships for lead (Pb), a key contaminant ofconcern for PNS, in order to evaluate the role of Pbin the ecological stress observed near PNS, and toestimate the probability of ecological risk associatedwith Pb contamination at the site. Biological effectsof exposure to Pb via sediment or diet were evaluatedusing several life stages of the sea urchin, Arbacia punctulata. This strategy was employedbecause echinoderm species, including A.punctulata, are amenable to laboratory testing andhave been used frequently to assess the toxicity ofestuarine waters and sediments. In addition, lifestage-specific biological effects could be comparedand integrated into projections of population-levelresponses to Pb. Results indicated that adult seaurchins accumulated Pb in direct proportion toexposure medium Pb concentration, whether exposureoccurred via sediment or diet. High Pb concentrationsreduced survival and gamete production in females, buthad no effect on the viability of produced gametes. Aqueous Pb exposure concentrations that producedadverse effects on adult sea urchin survival andreproduction were also directly toxic to early lifestages. In addition to their utility for this ERA,these results have applicability for the prediction ofbiological effects or the retrospective analysis ofcausal relationships at other estuarine sites.

A Resilience Framework for Chronic Exposures: Water Quality and Ecosystem Services in Coastal Social-Ecological Systems

Abstract Water quality degradation is a chronic problem which influences the resilience of a social-ecological system differently than acute disturbances, such as disease or storms. Recognizing this, we developed a tailored resilience framework that applies ecosystem service concepts to coastal social-ecological systems affected by degraded water quality. We present the framework as a mechanism for coordinating interdisciplinary research to inform long-term community planning decisions pertaining to chronic challenges in coastal systems. The resulting framework connects the ecological system to the social system via ecological production functions and ecosystem services. The social system then feeds back to the ecological system via policies and interventions to address declining water quality. We apply our resilience framework to the coastal waters and communities of Cape Cod (Barnstable County, Massachusetts, USA) which are affected by nitrogen over-enrichment. This approach allowed us to design research to improve the understanding of the effectiveness and acceptance of water quality improvement efforts and their effect on the delivery of ecosystem services. This framework is intended to be transferable to other geographical settings and more generally applied to systems exposed to chronic disturbances in order to coordinate interdisciplinary research planning and inform coastal management.

Projecting population-level response of purple sea urchins to lead contamination for an estuarine ecological risk assessment

As part of an ecological risk assessment casestudy at the Portsmouth Naval Shipyard (PNS), Kittery,Maine, USA, the population level effects of leadexposure to purple sea urchin, Arbaciapunctulata, were investigated using a stage-classifiedmatrix population model. The model divided the lifehistory of A. punctulata into five classes,incorporating both, the developmental stages of thisspecies and the endpoints from a laboratory bioassay. Finite population growth rate (λ) was themetric relating population level impact to leadexposure. An inverse relationship was observed betweenlead tissue residues in A. punctulata andλ. Bioassay treatments which resulted insignificant impacts on fertilization success and zygoteviability did not translate into significant effects onλ, unless those treatments also negativelyimpacted adult survival. These results paralleled theelasticity (relative sensitivity) analysis of themodel, which indicated that λ was mostsensitive to adult and subadult survival and wasrelatively insensitive to fecundity, fertilizationsuccess, or zygote survival. Model results indicatedthat the environmental lead levels observed at PNSshould not pose significant ecological risk to seaurchin populations. Additionally, the model resultsindicated that impacts to the early life stagesroutinely used in toxicity testing do not necessarilytranslate directly into impacts at the populationlevel.