Presentation is loading. Please wait.

Presentation is loading. Please wait.

Mercury cycling and bioaccumulation in streams in Oregon, Wisconsin, and Florida Mark E. Brigham 5 th National Monitoring Conference San José, California.

Similar presentations


Presentation on theme: "Mercury cycling and bioaccumulation in streams in Oregon, Wisconsin, and Florida Mark E. Brigham 5 th National Monitoring Conference San José, California."— Presentation transcript:

1 Mercury cycling and bioaccumulation in streams in Oregon, Wisconsin, and Florida Mark E. Brigham 5 th National Monitoring Conference San José, California May 7-11, 2006 U.S. Department of the Interior U.S. Geological Survey

2 Mercury: A leading water-quality impairment Data source: EPA 303(d) list ( http://oaspub.epa.gov/waters/national_rept.control ) Mercury: ~ 6,000 Metals impairments ~ 2,100 Fish consumption advisories >8,100 impaired waters

3 Factors that control mercury levels in fish After: Mumley & Abu-Saba, WEF National TMDL Science and Policy Conference Proceedings, Nov. 13-16, 2002 Hg(II)  MeHg

4 Willamette Basin Hudson River Basin Lake Erie Basin Santee Basin Georgia-Florida Coastal Plain Western Lake Michigan Drainages Long Island- New Jersey Reference stream Urban stream USGS NAWQA mercury study areas

5 Sites span gradient of wet Hg deposition

6 Settings Urban sites –Presumed higher loading; proximity to many sources –Not targeted to point sources! –Enhanced runoff –Disturbed ecosystems Reference sites – Low-moderate Hg loading – Not “control” for urban sites – Natural runoff pathways – Minimally disturbed ecosystems

7 Comparison of Basin Sizes

8 Reference settings: streams range from high-topographic gradient / low organic carbon…

9 …to low-gradient, high-carbon streams

10 Main study components: THg, MeHg, and related measures in: Stream water filtered & particulate phases Precipitation aquatic food web Hg +2 MeHg Sediment & pore water

11 Aqueous methylmercury (MeHg) is a major control on mercury bioaccumulation Hg in forage fish (μg/g wet wt.) [mean of N ≈ 24 at each site] Aqueous MeHg (ng/L) [mean of N ≈ 35 at each site]

12 Stream sediment geochemistry 1.Characterize channel substrate. 2.Detailed geochemical measures: Concentrations: MeHg, THg, carbon, S, etc. Rates: –Methylation: Hg(II)  MeHg –Demethylation: MeHg  Hg(II), Hg° –Sulfate reduction: SO 4 -2  S -2

13 Sediment methylation rate and MeHg concentration strongly relate to texture & organic content 0 50 100 150 200 250 0102030405060 Loss On Ignition (% dry weight) Methylation rate (from 203 Hg experiment) (ng g dry sed -1 d -1 ) y = 4.36x + 9.7 R 2 = 0.95 Evergreen Oak Creek Pike Creek

14 Stream sediment characterization Fines Mixed sand & fines Sand Gravel & cobble Simplified channel cross section Substrate characterization sampling points

15 Transect Sediment & porewater geochemistry sampling Sand Fines Sand & fine mixture

16 Large range in dominant channel substrate (grain size; organic content) 0 10 20 30 40 50 60 70 80 90 100 L. Wekiva Santa Fe St. Mary's Beaverton Lookout Evergreen Oak Cr. Pike R. Percent of channel substrate Sand High organic - Fine High org-Sand/Fine Larger than sand Low organic - Fine

17 MeHg in sediment (spatially weighted) unrelated to stream-water MeHg 0 0.1 0.2 0.3 0.4 St MarysL WekivaSanta FePikeEvergr.Oak CrLookoutBeaver. Mean aqueous MeHg (ng/L) 0 1 2 3 4 5 6 7 8 9 Florida sitesWisc. sites Oregon sites Sediment MeHg (ng/g dry sed) Note extremes

18 Fluvial MeHg yield unrelated to stream-sediment methylation rate Fluvial MeHg yield (μg/m 2 /year) Sediment methylation rate (spatially weighted; potential rate from 203 Hg experiment, μg/m 2 /year)

19 Summary & Implications (1) Aqueous MeHg is strongly related to fish-Hg concentrations. –Therefore, efforts to better understand MeHg production and transport are important for ecosystem management

20 Summary & Implications (2) Sediment MeHg unrelated to fluvial MeHg concentration and yield. Evidence suggests stream sediments play weak role in MeHg mass balance –Demethylation – high in sandy sediments. –Methylation – high in organic-rich sediments. –Difficult to scale isotope experiments to mass-balance context. It’s the watershed—Thursday’s presentation.

21 Future directions: Move toward more complete mass balance: --Net role of sediments & periphyton --Dry deposition? Evasion? --Watershed retention / delivery / methylation Integrate with model development Intensive study area

22 Acknowledgments USGS: Dennis Wentz, Barb Scudder, Lia Chasar, Amanda Bell, Michelle Lutz, Dave Krabbenhoft, Mark Marvin- DiPasquale, George Aiken, Robin Stewart, Carol Kendall, Bill Orem, Rod DeWeese, Jeff Isely, and many others… USGS: NAWQA and several other programs USEPA: support for periphyton study MDN site support: Wisconsin DNR, Oregen DEQ, Forest Service, US Fish & Wildlife Service, St. John’s River Water Management District (Florida), USGS NAWQA Menomonie Indian Tribe of Wisconsin


Download ppt "Mercury cycling and bioaccumulation in streams in Oregon, Wisconsin, and Florida Mark E. Brigham 5 th National Monitoring Conference San José, California."

Similar presentations


Ads by Google