Arsenic speciation and accumulation in evapoconcentrating waters of agricultural evaporation basins.
To sustain agricultural productivity, evaporation basins (or ponds) have been widely used for the disposal of agricultural drainage in areas requiring subsurface drainage in the San Joaquin Valley of California, USA. The drainage water contains elevated concentration of trace elements including selenium (Se) and arsenic (As). Unlike Se, little information is available about As, a potentially high risk element. The objective of this study was to characterize the chemical behavior of As and acquire data for better understanding of biogeochemical processes and conditions affecting As fate in evaporation ponds. The study site was a 726 ha evaporation basin facility (containing 10 cells with water flowing in series) in the hydrologically closed Tulare Basin of California. We examined water chemistry, As concentration and speciation along the water flow path between cells as well as within the cells. Arsenic concentrations in the water increased linearly with Cl(-), a conservative ion from evapoconcentration. Reduced As species as arsenite [As(III)] and organic arsenic (org-As) also increased with increases in Cl(-) and salinity. Water samples with elevated EC (i.e., towards the end of flow path) had high dissolved organic matter, low dissolved oxygen, and elevated sulfide concentrations, indicating the development of reducing conditions. We hypothesize that such changes could facilitate the reduction of arsenate [As(V)] to As(III) and org-As. Elevated As in sediment profiles indicate a solid phase sink mechanism, but not significant enough to remove and reduce As concentrations in the water columns. These findings help us better define the processes that affect As in drainage facilities and contribute to our understanding of how As behaves in other regions of the world that have similar climatic and hydrogeochemical conditions.
Gao
S
S
Water Management Research Unit, USDA-ARS, Parlier, CA 93648, USA. sgao@fresno.ars.usda.gov
Ryu
J
J
Tanji
K K
KK
Herbel
M J
MJ
D000383:Agriculture / Q000379:methods*; D001149:Arsenates / Q000032:analysis; D001151:Arsenic / Q000032:analysis / Q000737:chemistry*; D001152:Arsenicals / Q000032:analysis; D018053:Arsenites / Q000032:analysis; D002101:Cacodylic Acid / Q000032:analysis; D002712:Chlorides / Q000032:analysis; D019015:Geologic Sediments / Q000032:analysis; D008670:Metals / Q000032:analysis; D010084:Oxidation-Reduction; D012643:Selenium / Q000032:analysis; D013431:Sulfates / Q000032:analysis; D014865:Waste Disposal, Fluid / Q000379:methods*; D014874:Water Pollutants, Chemical / Q000032:analysis / Q000737:chemistry*
D001149:Arsenates; D001152:Arsenicals; D018053:Arsenites; D002712:Chlorides; D008670:Metals; D013431:Sulfates; D014874:Water Pollutants, Chemical; D002101:Cacodylic Acid; D012643:Selenium; C020300:monomethylarsonic acid; C015001:arsenite; D001151:Arsenic; C025657:arsenic acid