Human development along the land-seawater interface is considered to have s
ignificant environmental consequences. Development can also pose an increas
ed human health risk. In a rapidly developing coastal region we investigate
d this phenomenon throughout a series of five estuarine watersheds, each of
which differed in both the amount and type of anthropogenic development. O
ver a four-year period we analyzed the abundance and distribution of the en
teric pathogen indicator microbes, fecal coliform bacteria and Escherichia
coli. We also examined how these indicator microbes were related to physica
l and chemical water quality parameters and to demographic and land use fac
tors throughout this system of coastal creeks. Within all creeks, there was
a spatial pattern of decreasing enteric bacteria away from upstream areas,
and both fecal coliform and E. coli abundance were inversely correlated wi
th salinity. Turbidity was positively correlated with enteric bacterial abu
ndance. Enteric bacterial abundance was strongly correlated with nitrate an
d weakly correlated with orthophosphate concentrations. Neither fecal colif
orms nor E. coli displayed consistent temporal abundance patterns. Regardle
ss of salinity, average estuarine fecal coliform abundance differed greatly
among the five systems. An analysis of demographic and land use factors de
monstrated that fecal coliform abundance was significantly correlated with
watershed population, and even more strongly correlated with the percentage
of developed land within the watershed. However, the most important anthro
pogenic factor associated with fecal coliform abundance was percentage wate
rshed-impervious surface coverage, which consists of roofs, roads, driveway
s, sidewalks, and parking lots. These surfaces serve to concentrate and con
vey storm-water-borne pollutants to downstream receiving waters. Linear reg
ression analysis indicated that percentage watershed-impervious surface are
a alone could explain 95% of the variability in average estuarine fecal col
iform abundance. Thus, in urbanizing coastal areas waterborne health risks
can likely be reduced by environmentally sound land use planning and develo
pment that minimizes the use of impervious surface area, while maximizing t
he passive water treatment function of natural and constructed wetlands, gr
assy swales, and other "green" areas. The watershed approach used in our st
udy demonstrates that the land-water interface is not restricted to obvious
shoreline areas, but is influenced by and connected with landscape factors
throughout the watershed.