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Historical
Trends of Metals in the Sediments of San Francisco Bay, California:
Core
data from San Pablo Bay, Grizzly Bay, Richardson Bay, and
Central Bay
by Michelle I. Hornberger,
Samuel N. Luoma, Alexander van Geen, Christopher Fuller, and
Roberto Anima, USGS
based on article published in
Marine
Chemistry, 1999. V. 64, pp 39-55.
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Methods: Sample
Locations
Preliminary analyses of 0.6N HCl-extractable
metals were conducted on 14 cores from a group of 273 gravity
cores collected in 1990 and 1991. Detailed analyses were conducted
on six of the 14 cores and, for comparison, on one core from
Tomales Bay. Tomales Bay is 45 km north of San Francisco Bay
and is neither industrialized nor urbanized, although there
is a small, inactive mercury mine in its watershed. The six
cores from San Francisco Bay included replicate cores from
two major regions of the Bay. All six had bimodal depth profiles
of HCl -extractable metal concentrations (higher concentrations
in the near surface sediments than at depth) and were from
locations of net sediment deposition, as indicated by differences
in bathymetry between 1955 and 1990 (Ogden Beeman & Assoc.,
1992)
Core RB92-3 was collected at the mouth of
Richardson Bay, a 2-km wide, wind-protected embayment near
the mouth of San Francisco Bay. A ship building facility was
operational during World War II within Richardson Bay; otherwise,
local sources of contaminants are minimal. Richardson Bay
sediments should integrate contamination from both North and
South Bay (Krone, 1979), but are probably also strongly influenced
by marine processes (Conomos, 1979). Cores CB90-9 and CB90-12
were from Central Bay which is also strongly influenced by
marine inputs (Conomos, 1979). In addition, these sites are
approximately 6 km from the Alcatraz Island dredge spoil dumping
site, where dredging waste has been deposited since 1975 (AHI
and Williams Associates, 1990). Three cores from further landward
in the estuary were analyzed in detail; two from San Pablo
Bay (SP90-2 and SP90-8) and one from the Grizzly Bay arm of
Suisun Bay (GB90-6). Together these are termed North Bay cores.
Water chemistry and sediment transport in these locations
are influenced by inputs from the San Joaquin and Sacramento
Rivers (Conomos, 1979). Salinities less than 1 can occur during
the highest river flows; low flow salinities are typically
17 to 24 in northern San Pablo Bay. Previous studies have
documented enriched concentrations of Cr, Ni, V, Cu, and Cd
in water and bivalves in Suisun and northern San Pablo Bay
as a result of a variety of industrial discharges (Flegal
et al., 1991; Abu-Saba and Flegal, 1995; Brown and Luoma,
1995).
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