Concentrations of naturally occurring arsenic in ground water vary regional
ly due to a combination of climate and geology. Although slightly less than
half of 30,000 arsenic analyses of ground water in the United States were
less than or equal to 1 mu g/L, about 10% exceeded 10 mu g/L. At a broad re
gional scale, arsenic concentrations exceeding 10 mu g/L appear to be more
frequently observed in the western United States than in the eastern half.
Arsenic concentrations in ground water of the Appalachian Highlands and the
Atlantic Plain generally are very low (less than or equal to 1 mu g/L), Co
ncentrations are somewhat greater in the Interior Plains and the Rocky Moun
tain System. Investigations of ground water in New England, Michigan, Minne
sota, South Dakota, Oklahoma, and Wisconsin within the last decade suggest
that arsenic concentrations exceeding 10 mu g/L are more widespread and com
mon than previously recognized.
Arsenic release from iron oxide appears to he the most common cause of wide
spread arsenic concentrations exceeding 10 mu g/L in ground water. This can
occur in response to different geochemical conditions, including release o
f arsenic to ground water through reaction of iron oxide with either natura
l or anthropogenic (i.e., petroleum products) organic carbon. Iron oxide al
so can release arsenic to alkaline ground water, such as that found in some
felsic volcanic rocks and alkaline aquifers of the western United States.
Sulfide minerals are both a source and sink for arsenic. Geothermal water a
nd high evaporation rates also are associated,vith arsenic concentrations g
reater than or equal to 10g/L in ground and surface water, particularly in
the west.