『Abstract
Seasonal (Spring and Summer 2002) concentrations of dissolved
(<0.22μm) trace metals (Ag, Al, Co, Cu, Mn, Ni, Pb), inorganic
nutrients (NO3, PO4,
Si), and DOC were determined in groundwater samples from 5 wells
aligned along a 30 m shore-normal transect in west Neck Bay, Long
Island, NY. Results show that significant, systematic changes
in groundwater trace metal and nutrient composition occur along
the flowpath from land to sea. While conservative mixing between
Neck Bay water and the groundwaters explains the behavior of Si
and DOC, non-conservative inputs for Co and Ni were observed (concentration
increases of 10- and 2-fold, respectively) and removal of PO4 and NO3 (decreases to about
half) along the transport pathway. groundwater-associated chemical
fluxes from the aquifer to the embayment calculated for constituents
not exhibiting conservative behavior can vary by orders of magnitude
depending on sampling location and season (e.g. Co, 3.4×102−8.2×103μmol
d-1. Using measured values from different wells as
being representative of the true groundwater endmember chemical
composition also results in calculation of very different fluxes
(e.g., Cu, 6.3×103μmol d-1(inland, freshwater
well) vs. 2.1×105μmol d-1(seaward well,
S = 17 ppt)). This study suggests that seasonal variability and
chemical changes occurring within he subterranean estuary must
be taken into account when determining the groundwater flux of
dissolved trace metals and nutrients to the coastal ocean.』
1. Introduction
2. Methods
3. Results and discussion
3.1. Temporal and spatial variations in groundwater composition
3.2. Geochemical behavior of dissolved constituents in the WNB
subterranean estuary
3.2.1. Constituents with conservative mixing distribution
3.2.2. Constituents exhibiting non-conservative removal
3.2.3. Constituents exhibiting non-conservative input
3.2.4. Constituents with variable trends not clearly related
to fresh-saline mixing
3.3. Calculation of SGD-derived chemical fluxes
3.3.1. Total volume flux
3.3.2. Flux of conservative constituents
3.3.3. Flux of constituents exhibiting non-conservative input
in the subterranean estuary
3.3.4. Flux of constituents exhibiting non-conservative removal
in the subterranean estuary
3.3.5. Flux of constituents with variable trends
4. Summary
Acknowledgements
References