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GeoRef Categories
Era and Period
Date
Availability
Escherichia
Preparation and Antibacterial Properties of Carvacrol-loaded Composite Microcapsules via Palygorskite-Stabilized Pickering Emulsions Available to Purchase
Noninvasive Quantification of Green Fluorescent Protein Labeled Escherichia coli in a Dynamic Capillary Fringe by Fluorescence Intensity Available to Purchase
Oxygen Transfer in a Fluctuating Capillary Fringe: Impact of Microbial Respiratory Activity Available to Purchase
Application of Reactive Transport Modeling to Growth and Transport of Microorganisms in the Capillary Fringe Available to Purchase
Transport of Antibiotic Resistance Plasmids in Porous Media Available to Purchase
Physicochemical Factors Influencing the Preferential Transport of Escherichia coli in Soils Available to Purchase
Intra-Aggregate Pore Structures and Escherichia coli Distribution by Water Flow within and Movement Out of Soil Macroaggregates Available to Purchase
Sampling Escherichia coli and Total Coliforms using Stainless Steel Suction Lysimeters Available to Purchase
Water-quality characteristics and contaminants in the rural karst-dominated Spring Mill Lake watershed, southern Indiana Available to Purchase
The Spring Mill Lake watershed is located in the Mitchell Plateau, a karst area that developed on Mississippian carbonates in southern Indiana. Spring Mill Lake is a reservoir built in the late 1930s and is located in Spring Mill State Park. Within the park, groundwater from subsurface conduits issues as natural springs and then flows in surface streams to the lake. From 1998 to 2002, surface and subsurface hydrology and water quality were investigated to determine the types and sources of potential contaminants entering the lake. Water samples collected during base flow and a February 2000 storm event were analyzed for selected cations, anions, trace elements, selected U.S. Environmental Protection Agency (EPA) primary and secondary drinking-water contaminants, nitrogen isotopes, suspended solids, Escherichia coli , and pesticides. All of the water samples met the EPA drinking-water standards for inorganic constituents, except those collected at five sites in August 1999 during a drought. Nitrate nitrogen (NO 3 -N) concentrations were highest during base-flow conditions and displayed a dilutional trend during peak-flow periods. The NO 3 -N concentrations in water samples collected during the 2001 spring fertilizer applications tended to increase from early to late spring. All of the δ 15 N values were low, which is indicative of either an inorganic source or soil organic matter. Storm discharge contained increased concentrations of total suspended solids; thus, storms are responsible for most of the sediment accumulation in the lake. E. coli levels in 24% of the samples analyzed contained a most probable number (MPN) greater than 235/100 mL, which is the maximum acceptable level set for recreational waters in Indiana. E. coli does appear to be a potential health risk, particularly at Rubble spring. The sources of E. coli found at this spring may include barnyard runoff from a horse barn or wastes from a wastewater treatment facility. The pesticides atrazine, metolachlor, acetochlor, and simazine were detected during the spring of 2001. Atrazine, metolachlor, ace-tochlor, and simazine are used to suppress weeds during corn and soybean production. Additional sources of atrazine and simazine may result from application to right-of-ways, orchards, and managed forest areas.