David Walters, PhD
Dr. David Walters is a Supervisory Research Ecologist at the Columbia Environmental Research Center.
David has been a research ecologist with the USGS since 2008. Prior to that, he was an ecologist for the U.S. EPA, National Exposure Research Laboratory for 6 years. He is a freshwater ecologist with broad training in stream ecology, human impacts on aquatic ecosystems, and ecotoxicology. His current research topics include food webs and contaminant flux, aquatic-riparian linkages, stream fish ecology, land use and climate change, and invasive species.
Current Projects/Areas of Interest
- Riparian indicators of contaminant exposure at Great Lakes Areas of Concern (AOCs)
We are investigating contaminant flux from aquatic to nearby terrestrial (riparian) shoreline habitats. In particular we use riparian spiders (many of which feed almost exclusively on adult aquatic insects) to characterize contamination at these sites and to evaluate the effectiveness of their remediation. - Leaky rivers: Nutrient retention and productivity in Rocky Mountain streams under alternative stable states
This project investigates how the volume of wood and log jams have declined in Rocky Mountain streams since European settlement, how the loss of wood affects stream geomorphology, communities, nutrient cycling, and productivity, and what management actions can be taken to restore lost ecosystem functions. - Mechanisms for metal uptake and trophic transfer in stream and riparian food webs in mineralized landscapes
We are investigating how metals in streams (derived from natural geologic sources as well as mines) are transferred from streams to riparian zones and how this contamination alters ecological linkages between these systems. This work combines large-scale field studies with mesocosm experiments to better understand processes driving the patterns we observe in nature. - “Metal webs” for the Grand Canyon
We are developing quantitative food webs to measure metal flux (mercury, selenium, and other trace metals) in the Colorado and Little Colorado rivers in Grand Canyon. These studies will identify key pathways of metal exposure to important fish species, such as the endangered humpback chub. - Consequences of climate change for alpine lake-stream networks and native fishes in the southern Rocky Mountains
This project investigates the importance of alpine lakes in the ecology of native cutthroat trout and how lakes could mitigate the negative effects of rising temperatures on these threatened populations.
Education and Certifications
Ph.D. Ecology, University of Georgia (UGA), 2002
M.S. Conservation Ecology, UGA, 1997
B.A. Anthropology, UGA, 1991
Science and Products
Aquatic pollution increases use of terrestrial prey subsidies by stream fish
Mercury and selenium accumulation in the Colorado River food web, Grand Canyon, USA
Methylmercury bioaccumulation in stream food webs declines with increasing primary production
Turbidity alters pre-mating social interactions between native and invasive stream fishes
The natural sediment regime in rivers: broadening the foundation for ecosystem management
Metamorphosis alters contaminants and chemical tracers in insects: implications for food webs
Metamorphosis enhances the effects of metal exposure on the mayfly, Centroptilum triangulifer
Cross-ecosystem impacts of stream pollution reduce resource and contaminant flux to riparian food webs
Barriers impede upstream spawning migration of flathead chub
Effects of a chronic lower range of triclosan exposure to a stream mesocosm community
Emergence flux declines disproportionately to larval density along a stream metals gradient
Assessing ongoing sources of dissolved-phase polychlorinated biphenyls in a contaminated stream
Non-USGS Publications**
**Disclaimer: The views expressed in Non-USGS publications are those of the author and do not represent the views of the USGS, Department of the Interior, or the U.S. Government.
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Aquatic pollution increases use of terrestrial prey subsidies by stream fish
Stream food webs are connected with their riparian zones through cross-ecosystem movements of energy and nutrients. The use and impact of terrestrial subsidies on aquatic consumers is determined in part by in situ biomass of aquatic prey. Thus, stressors such as aquatic pollutants that greatly reduce aquatic secondary production could increase the need for and reliance of stream consumers on terrAuthorsJohanna M. Kraus, Justin F. Pomeranz, Andrew S. Todd, David M. Walters, Travis S. Schmidt, Richard B. WantyMercury and selenium accumulation in the Colorado River food web, Grand Canyon, USA
Mercury (Hg) and selenium (Se) biomagnify in aquatic food webs and are toxic to fish and wildlife. The authors measured Hg and Se in organic matter, invertebrates, and fishes in the Colorado River food web at sites spanning 387 river km downstream of Glen Canyon Dam (AZ, USA). Concentrations were relatively high among sites compared with other large rivers (mean wet wt for 6 fishes was 0.17–1.59 μAuthorsDavid M. Walters, E.J. Rosi-Marshall, Theodore A. Kennedy, W.F. Cross, C.V. BaxterMethylmercury bioaccumulation in stream food webs declines with increasing primary production
Opposing hypotheses posit that increasing primary productivity should result in either greater or lesser contaminant accumulation in stream food webs. We conducted an experiment to evaluate primary productivity effects on MeHg accumulation in stream consumers. We varied light for 16 artificial streams creating a productivity gradient (oxygen production =0.048–0.71 mg O2 L–1 d–1) among streams. TwoAuthorsDavid Walters, D.F. Raikow, C.R. Hammerschmidt, M.G. Mehling, A. Kovach, J.T. OrisTurbidity alters pre-mating social interactions between native and invasive stream fishes
Environmental degradation can result in the loss of aquatic biodiversity if impairment promotes hybridisation between non-native and native species. Although aquatic biological invasions involving hybridisation have been attributed to elevated water turbidity, the extent to which impaired clarity influences reproductive isolation among non-native and native species is poorly understood. We examinAuthorsGregory J. Glotzbecker, Jessica L. Ward, David M. Walters, Michael J. BlumThe natural sediment regime in rivers: broadening the foundation for ecosystem management
Water and sediment inputs are fundamental drivers of river ecosystems, but river management tends to emphasize flow regime at the expense of sediment regime. In an effort to frame a more inclusive paradigm for river management, we discuss sediment inputs, transport, and storage within river systems; interactions among water, sediment, and valley context; and the need to broaden the natural flow reAuthorsEllen E. Wohl, Brian P. Bledsoe, Robert B. Jacobson, N. LeRoy Poff, Sara L. Rathburn, David M. Walters, Andrew C. WilcoxMetamorphosis alters contaminants and chemical tracers in insects: implications for food webs
Insects are integral to most freshwater and terrestrial food webs, but due to their accumulation of environmental pollutants they are also contaminant vectors that threaten reproduction, development, and survival of consumers. Metamorphosis from larvae to adult can cause large chemical changes in insects, altering contaminant concentrations and fractionation of chemical tracers used to establish cAuthorsJohanna M. Kraus, David M. Walters, Jeff S. Wesner, Craig A. Stricker, Travis S. Schmidt, Robert E. ZuelligMetamorphosis enhances the effects of metal exposure on the mayfly, Centroptilum triangulifer
The response of larval aquatic insects to stressors such as metals is used to assess the ecological condition of streams worldwide. However, nearly all larval insects metamorphose from aquatic larvae to winged adults, and recent surveys indicate that adults may be a more sensitive indicator of stream metal toxicity than larvae. One hypothesis to explain this pattern is that insects exposed to elevAuthorsJeff S. Wesner, Johanna M. Kraus, Travis S. Schmidt, David M. Walters, William H. ClementsCross-ecosystem impacts of stream pollution reduce resource and contaminant flux to riparian food webs
The effects of aquatic contaminants are propagated across ecosystem boundaries by aquatic insects that export resources and contaminants to terrestrial food webs; however, the mechanisms driving these effects are poorly understood. We examined how emergence, contaminant concentration, and total contaminant flux by adult aquatic insects changed over a gradient of bioavailable metals in streams andAuthorsJohanna M. Kraus, Travis S. Schmidt, David Walters, Richard B. Wanty, Robert E. Zuellig, Ruth E. WolfBarriers impede upstream spawning migration of flathead chub
Many native cyprinids are declining throughout the North American Great Plains. Some of these species require long reaches of contiguous, flowing riverine habitat for drifting eggs or larvae to develop, and their declining populations have been attributed to habitat fragmentation or barriers (e.g., dams, dewatered channels, and reservoirs) that restrict fish movement. Upstream dispersal is also neAuthorsDavid M. Walters, Robert E. Zuellig, Harry J. Crockett, James F. Bruce, Paul M. Lukacs, Ryan M. FitzpatrickEffects of a chronic lower range of triclosan exposure to a stream mesocosm community
Triclosan (5-chloro-2-(2,4-dichlorophenoxy)phenol) is an antimicrobial found in consumer soaps and toothpaste. It is in treated wastewater effluents at low part per billion concentrations, representing a potentially chronic exposure condition for biota inhabiting receiving streams. A naturally colonized benthos was created using flow-through indoor mesocosms. Then the benthic communities were doseAuthorsC.T. Nietch, E.L. Quinlan, J. Lazorchak, C. Impellitteri, D. Raikow, David M. WaltersEmergence flux declines disproportionately to larval density along a stream metals gradient
Effects of contaminants on adult aquatic insect emergence are less well understood than effects on insect larvae. We compared responses of larval density and adult emergence along a metal contamination gradient. Nonlinear threshold responses were generally observed for larvae and emergers. Larval densities decreased significantly at low metal concentrations but precipitously at concentrations of mAuthorsTravis S. Schmidt, Johanna M. Kraus, David M. Walters, Richard B. WantyAssessing ongoing sources of dissolved-phase polychlorinated biphenyls in a contaminated stream
Few studies assess the potential of ongoing sources of “fresh” polychlorinated biphenyls (PCBs) to aquatic systems when direct discharge to the environment has been eliminated. In the present study, the authors used single-layered, low-density polyethylene samplers (PEs) to measure total PCB concentrations, congener profiles, and enantiomeric fractions (EFs) in a contaminated stream and to provideAuthorsViet D. Dang, David M. Walters, Cindy M. LeeNon-USGS Publications**
Wanty, R.B., L.S. Balistrieri, J.S. Wesner, D.M. Walters, F. Podda, G.De Giudici, C. Stricker, T.S. Schmidt, J.M. Kraus, P. Lattanzi, R.E. Wolf, and R. Cidu. 2015. What zinc isotopes might tell us about biological uptake in systems contaminated with heavy metals. Procedia Earth and Planetary Sciences 13:60-63.Dang, V.D., D.M. Walters, and C. M Lee. 2012. Historical changes in polychlorinated biphenyls (PCBs) contaminated sediments in Twelvemile Creek, South Carolina (USA). Amer. J. Env. Sci. 8:11-15.Walters, D.M., et al. 2010. Mercury contamination in fish in mid-continent great rivers of the United States: Importance of species traits and environmental factors. Env. Sci. Tech. 44:2947-2953.Walters, D.M., A.H. Roy, and D.S. Leigh. 2009. Environmental indicators of macroinvertebrate and fish assemblage integrity in urbanizing watersheds. Ecol. Ind. 9:1222-1233.Rashleigh, B., M.C. Barber, and D.M. Walters. 2009. Foodweb modeling for polychlorinated biphenyls (PCBs) in the Twelvemile Creek Arm of Lake Hartwell, South Carolina, USA. Ecol. Mod. 220:254-264.Johnson, B.R., K.M. Fritz, K.A. Blocksom, and D.M. Walters. 2009. Larval salamanders and channel geomorphology are indicators of hydrologic permanence in forested headwater streams. Ecol. Ind. 9:150-159.Walters, D.M., et al. 2008. Red shiner invasion and hybridization with blacktail shiner in the upper Coosa River, USA. Bio. Inv. 10:1229-1242.Walters, D.M., et al. 2008. The dark side of subsidies: Adult stream insects export organic contaminants to riparian predators. Ecol. App. 18:1835-1841.Walters, D.M. et al. 2008. Influence of trophic position and spatial location on polychlorinated biphenyl (PCB) bioaccumulation in a stream food web. Env. Sci. Tech. 42:2316-2322.Fritz, K.M., B.R. Johnson, and D.M. Walters. 2008. Physical indicators of hydrologic permanence in forested headwater streams. Jour. Nor. Amer. Benth. Soc. 27:690-704.Rybczynski, S.M., D.M. Walters, et al. 2008. Comparing the trophic position of stream fishes using stable isotope and gut contents analyses. Eco. Freshw. Fish 17:199-206.Walters D.M., et al. 2007. Reach-scale geomorphology affects organic matter and consumer δ13C in a forested Piedmont stream. Freshw. Bio. 52:1105-1119.Walters, D.M., D.S. Leigh, M.C. Freeman, B.J. Freeman, and C.M. Pringle. 2005. Effect of urbanization on fish assemblages and habitat quality in a Piedmont river basin. Pages 69-86 in Brown, L. R., R. M. Hughes, R. Gray, and M. R. Meador (eds), Effects of Urbanization on Stream Ecosystems. AFS, Symposium 47, Bethesda, Maryland.Walters, D.M., et al. 2003a. Geomorphology and fish assemblages in a Piedmont river basin, USA. Freshw. Bio. 48:1950-1970.Walters, D.M., et al. 2003b. Urbanization, sedimentation, and the homogenization of fishes in the Etowah River Basin, Georgia Piedmont, USA. Hydrobiologia 494:5-10.Walters, D.M. and B.J. Freeman. 2000. Distribution of Gambusia (Poeciliidae) in a southeastern river system and the use of fin ray counts for species identification. Copeia 2000:555-559.Kraus, J. M., Schmidt, T. S., Walters, D. M., Wanty, R. B., Zuellig, R. E. and Wolf, R. E. (2014), Cross-ecosystem impacts of stream pollution reduce resource and contaminant flux to riparian food webs. Ecological Applications, 24: 235–243. doi: 10.1890/13-0252.1**Disclaimer: The views expressed in Non-USGS publications are those of the author and do not represent the views of the USGS, Department of the Interior, or the U.S. Government.
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