# Arsenic in Shallow Unstratified and Seasonally Stratified Urban Lakes: Mobility, Bioaccumulation and Ecological Toxicity

> **NIH NIH P42** · UNIVERSITY OF WASHINGTON · 2020 · $314,648

## Abstract

PROJECT SUMMARY 
Arsenic, a priority Superfund contaminant, neurotoxin, and carcinogen, is a ubiquitous metalloid contaminant 
polluting many urban freshwater ecosystems. However, the human health and ecological implications of this 
contamination are unclear due to an incomplete understanding of arsenic bioavailability in urban waters, which 
are typically affected by eutrophication. The objective of the proposed project is to quantify spatiotemporal 
patterns and primary drivers of arsenic mobility, bioavailability and ecological toxicity in urban lakes. The 
South-Central Puget Sound Lowland region offers an exceptional environment to study the human and 
environmental health impacts of urban metal(loid)-impacted freshwater ecosystems because it contains an 
array of densely populated lakes with arsenic-contaminated waters that display a wide range of redox 
behaviors: seasonally stratified and anoxic to well-mixed and oxic. Although elevated levels of arsenic usually 
occur in anoxic waters at the bottom of thermally-stratified lakes during the summer, at least one lake in the 
study region maintains elevated aqueous arsenic concentrations under oxic conditions. This situation raises 
questions about the physical and geochemical processes controlling arsenic chemistry in oxic waters of 
shallow, unstratified lakes, and also about the resulting bioavailability of arsenic to aquatic life, including fish. 
Due to limitations that anoxia poses for aquatic organisms, the typical coincidence of elevated arsenic and 
anoxic conditions may act to minimize biological exposure to arsenic, whereas shallow, unstratified lakes may 
enhance exposure to arsenic contamination. Within this context, the proposed project will pursue three specific 
aims: (1) determine the physical and biogeochemical conditions that promote arsenic mobilization from 
sediments and maintain elevated aqueous concentrations within shallow, unstratified oxic lakes, (2) identify the 
physical and chemical factors that control arsenic bioaccumulation through a lake food web in both stratified 
and unstratified lakes, and (3) assess ecological toxicity of arsenic within both stratified and unstratified lakes 
using established and novel molecular biomarkers (identified using RNA-Sequencing technology) indicating 
arsenic injury. We hypothesize that arsenic contamination in oxic waters of unstratified lakes is promoted and 
maintained by inputs of nutrients and organic matter, and that arsenic bioaccumulation and toxicity is 
enhanced in oxic unstratified lakes compared to seasonally stratified lakes. We will achieve our aims by linking 
measurements of physical, chemical and biological lake properties with investigations of arsenic 
bioaccumulation and ecological toxicity. Our proposed research is innovative because of its combined 
biogeochemical and eco-toxicological approach and its use of novel toxicogenomic methods to identify 
molecular biomarkers of arsenic injury. Our project i...

## Key facts

- **NIH application ID:** 9895797
- **Project number:** 5P42ES004696-32
- **Recipient organization:** UNIVERSITY OF WASHINGTON
- **Principal Investigator:** Rebecca B Neumann
- **Activity code:** P42 (R01, R21, SBIR, etc.)
- **Funding institute:** NIH
- **Fiscal year:** 2020
- **Award amount:** $314,648
- **Award type:** 5
- **Project period:** — → —

## Primary source

NIH RePORTER: https://reporter.nih.gov/project-details/9895797

## Citation

> US National Institutes of Health, RePORTER application 9895797, Arsenic in Shallow Unstratified and Seasonally Stratified Urban Lakes: Mobility, Bioaccumulation and Ecological Toxicity (5P42ES004696-32). Retrieved via AI Analytics 2026-05-23 from https://api.ai-analytics.org/grant/nih/9895797. Licensed CC0.

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