Date: Thu, 4 Mar 1999 09:59:06 -0700
Subject: Trace Element News v.4 -- Mercury
From: Dennis Helsel 
To: nawqa_97pc@srv1rvares.er.usgs.gov,
    nawqa_91pc@srv1rvares.er.usgs.gov,
    nawqa_94pc@srv1rvares.er.usgs.gov
Cc: "John S Zogorski, Supervisory Hydrologist, Rapid City, SD" ,
    "Robert J Gilliom, Supv. Hydrologist, Sacramento, CA" ,
    "Jeffrey D Stoner, Supervisory Hydrologist, Denver, CO" ,
    "Carol A Couch, Hydrologist, Norcross, GA" ,
    "Alan H Welch, Hydrologist, Carson City, NV" ,
    "Peter C VanMetre, Project Chief, Hydrol(RGEG), Austin, TX" ,
    "Lawrence R Deweese, Fish and Wildlife Biologist, Denver, CO" ,
    "David P Krabbenhoft, Research Hydrologist (GeoChem), Middleton, WI" ,
    "Edward Callender, Hydrologist, Reston, VA" ,
    "Terry M Short, Physical Scientist, Menlo Park, CA" ,
    "Michael T Koterba, Hydrologist, Baltimore, MD" ,
    "Dennis A Wentz, Willamette NAWQA Chief, Portland, OR" ,
    "William G Brumbaugh, Research Chemist, Columbia, MO" ,
    "Timothy L Miller, Chief, NAWQA, Reston, VA" ,
    "William G Wilber, National Synthesis Coordinator, Reston, VA" ,
    "Jeffrey T Armbruster, Asst. Reg. Hydr.-NAWQA, Norcross, GA" ,
    "Michael C Yurewicz, Asst. Reg. Hydrol.-NAWQA, Reston, VA" ,
    "Ivan C James II, Asst. Reg. Hydrologist-NAWQA, Denver, CO" ,
    "Marc A Sylvester, Asst. Reg. Hydrologist-NAWQA, Menlo Park, CA" ,
    reg.wqspecs@srv1rvares.er.usgs.gov,
    "Wayne W Lapham, Hydrol(Geol) GW Spec, Reston, VA" ,
    "Larry R Shelton, Hydro Tech, Sacramento, CA" ,
    "Robert M Hirsch, Chief Hydrologist, Reston, VA" 

Mercury in Streambed Sediments
Trace Element Synthesis News v.4

Call or email for copies of previous TE news blurbs:
v.1   Trace Element Synthesis Staffing and plans   2/10/99
v.2   Changes to TE lab methods for bed sediments  2/19/99
v.3   Well Selection for Subunit Surveys           2/26/99

-----------------------------------------------
Status of NAWQA / Toxics Program pilot study:
Mercury in Fish, Water and Streambed Sediments

Twenty-one NAWQA study units participated in collecting fish, water and
streambed sediment samples at the end of FY98 as a pilot study for a
national mercury survey in those media, focusing on the characteristics
which enhance methyl mercury production.  Results of the water and sediment
samples have been completed.  Analyses of fish are being performed now, a
joint effort between WRD (Krabbenhoft and others) and BRD (Bill Brumbaugh
and others).  Dave Krabbenhoft is presenting current results at the USGS
Toxics Program meeting on Monday, March 8.  A summary is below for your
information.  More information is available in the paper which Dave has
sent to each of the study units participating in the project.  For more
detail on the results, contact Dave Krabbenhoft [dpkrabbe] AFTER March 8.
For general information on Trace Element Synthesis, contact Dennis Helsel
[dhelsel].



A National Pilot Study of Mercury Contamination of Aquatic Ecosystems along
Multiple Gradients

SUMMARY OF RESULTS

A national scale pilot study to examine relations of total Hg (HgT) and
methyl mercury (MeHg) in water, sediment and fish was conducted in the
summer and fall of 1998.  Samples were collected at 106 sites from 21 study
units across the United States, including Alaska and Hawaii (see attached
figure sites.jpg).  Sites were selected to provide a diverse array of
environmental settings, water chemistry, and Hg loading. Wetland density
was the single most important basin-scale factor correlated with MeHg
production.  At low concentrations, MeHg production generally increases
with increasing tatal Hg in the sediment.  But at high total Hg
concentrations (>1,000 nanograms per gram; ng/g) in sediment there was
little evidence of increasing MeHg production with increasing total Hg.  An
atmospheric Hg accumulation index (AHA) was developed for differentiating
areas where atmospheric Hg deposition was the dominant Hg source from areas
with significant on-site sources.  Four study basins along the east coast
of the United States had the greatest methylation efficiency, as reflected
by the MeHg/HgT ratio in sediments  (see attached figure AHA.jpg).
Nationwide, sub-basins characterized as mixed agriculture and forest cover
types had the highest methylation efficiency, whereas areas affected by
mining had the lowest efficiency.

Study Units participating in the pilot:
ACAD, ALMN, CKIB, DELR, GRSL, LINJ, LTEN, MIAM, MOBL, NECB, NROK, NVBR,
OAHU, SACR, SANA, SANT, SOFL, TRIN, UCOL, UIRB, YELL

Study Units with greatest % of mercury in seds as MeHg:
SANT, SOFL, NECB, LINJ

Study Units with highest atmospheric deposition rates:
NECB, LINJ, SOFL, DELR, ALMN

Study Units where atmospheric deposition is dominant source (low AHA):
SOFL, LINJ, DELR, SANT

Study Units with dominant local sources of total mercury (high AHA) --
(proposed source in parentheses):
NVBR, NROK, GRSL, CKIB, SACR, UCOL (mining)
OAHU   (volcanic emissions)

Study Units with highest % of wetlands in basins sampled (data not
available for 5 study units):
SOFL, LINJ, NECB, SANT

Average Me/Tot Hg ratios in bed sediment, by land-use group and % wetlands:

Group          Me/Tot Hg     ave % Wetland
Ag/Forest         8%             20%
Background        2%              8%
Agriculture       2%              3%
Urban             1%              6%
Mining            0.1%            1%

Map showing the twenty study units participating in the Hg pilot study (76Kb, JPEG)

Plot of mercury ratios (26Kb, JPEG)

--------------------------------------------------------------
   Dennis R. Helsel                    Ph:  (303) 236-2101 x227
   Trace Element National Synthesis    Fax: (303) 236-4912
   U.S. Geological Survey
   PO Box 25046, MS-415                dhelsel@usgs.gov
   Denver, CO   80225