The late Mr. Henry H. Bisbee and son-"running" a Michigan trout stream-near Ludington?

verso: (Mr. B. and family were well-known Ludington residents who left the city over forty years ago to go South, and finally West. He was the James St. jeweller and incidentally an outstanding humorist among his friends. He was a brother-in-law of the late Dr. Josiah Strong, formerly of Greenwich, Conn., sociologist and friend of Theo Roosevelt.) signed: B.M. Willson 389 Orange St. New Haven, Conn.

A bank-operated traveling-block cableway for stream discharge and sediment measurements /

Includes bibliographical references (p. 14).

The book of the Axe: containing a piscatorial description of that stream and historical sketches of all the parishes and remarkable places upon its banks.

Facsimile reprint of 4th ed., rewritten and greatly enlarged., London, Longman, Green, Reader & Dyer, 1875.

Assessment of effects of altered stream flow characteristics on fish and wildlife.

Performed for the Western Energy and Land Use Team, Office of Biological Services, Fish and Wildlife Service, U. S. Dept. of the Interior.

Evaluation of the cost effectiveness of the 1983 stream-gaging program in Kansas /

Bibliography: p. 56-57.

Cost-effectiveness of the U.S. Geological Survey stream-gaging program in central Florida /

Bibliography: p. 86-89.

Cost effectiveness of the U.S. Geological Survey's stream-gaging program in Illinois /

Tables.

Urban land runoff as a factor in stream pollution,

Cover title.

Marine and stream terraces of the southeast coastal plain of the Dominican Republic,

Mode of access: Internet.

Quantifying ice-shelf basal melt and ice-stream dynamics using high-resolution DEM and GPS time series

Thesis (Ph.D.)--University of Washington, 2016-06

Quantifying potential nitrogen removal by denitrification in stream sediments at a regional scale

Potential denitrification rates were measured using the acetylene block method, in sediments collected from streams in the sub-tropical, south-east Queensland region of Australia. Our aim was to estimate how much nitrogen could be removed from lotic systems by denitrification at the regional scale. Denitrification measured at 65 sites in August and September from a catchment of 22700 km(2) was extrapolated to all streams and rivers in the region based on the sediment area available for denitrification. Denitrification rates ranged between 4 and 950 mumol N m(-2) h(-1), with most sites having rates below 150 mumol N m(-2) h(-1). Based on these results, the current study estimates that a total of 305 t of nitrogen could be denitrified per year from all streams and rivers in the region, representing 6% of the total annual nitrogen load from surrounding land use. During baseflow conditions, when nitrogen loads to streams are low, the proportion of nitrogen removed through denitrification would be substantially higher, in some cases removing 100% of the nitrogen load. It is proposed that denitrification is an important process maintaining low concentrations of dissolved inorganic nitrogen under baseflow conditions and is therefore likely to enhance nitrogen limitation of primary production in this region.

Benthic metabolism as an indicator of stream ecosystem health

We tested direct and indirect measures of benthic metabolism as indicators of stream ecosystem health across a known agricultural land-use disturbance gradient in southeast Queensland, Australia. Gross primary production (GPP) and respiration (R-24) in benthic chambers in cobble and sediment habitats, algal biomass (as chlorophyll a) from cobbles and sediment cores, algal biomass accrual on artificial substrates and stable carbon isotope ratios of aquatic plants and benthic sediments were measured at 53 stream sites, ranging from undisturbed subtropical rainforest to catchments where improved pasture and intensive cropping are major land-uses. Rates of benthic GPP and R-24 varied by more than two orders of magnitude across the study gradient. Generalised linear regression modelling explained 80% or more of the variation in these two indicators when sediment and cobble substrate dominated sites were considered separately, and both catchment and reach scale descriptors of the disturbance gradient were important in explaining this variation. Model fits were poor for net daily benthic metabolism (NDM) and production to respiration ratio (P/R). Algal biomass accrual on artificial substrate and stable carbon isotope ratios of aquatic plants and benthic sediment were the best of the indirect indicators, with regression model R-2 values of 50% or greater. Model fits were poor for algal biomass on natural substrates for cobble sites and all sites. None of these indirect measures of benthic metabolism was a good surrogate for measured GPP. Direct measures of benthic metabolism, GPP and R-24, and several indirect measures were good indicators of stream ecosystem health and are recommended in assessing process-related responses to riparian and catchment land use change and the success of ecosystem rehabilitation actions.