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Export coefficient models have been widely used to study non-point source pollution.
The layer of export coefficient was related to each spatial unit and those coefficients were determined.
Models include a bulk runoff-concentration load calculation, an export coefficient model, and land-use specific runoff and loads.
However, there has been little discussion about applying non-point source pollution and export coefficient modeling to design sampling points for monitoring.
Crop-specific (oat, wheat, corn, alfalfa, and fallow) export coefficient values were generally on par with those typically reported in the literature.
Simple export coefficient models and statistical models also require extensive primary watershed attribute information and further they cannot address seasonal patterns of nutrient delivery.
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The second half of Table 3 displays the intra-bloc parts and components export coefficients.
The export coefficients were derived from literature sources as well as calibration using the hydrology and water quality data.
An approach has been developed based on the mass balance of the pollutant to determine the export coefficients of different land use types (Ding et al., 2010).
The objectives were to: (i) examine spatial and temporal characteristics of fecal bacteria loading during the growing season from five subwatersheds, and (ii) develop areal fecal indicator organism export coefficients for rural landscapes.
Stream SRP, NO3-N and TN concentrations (geometric-mean) increased linearly with per cent of pasture in watersheds, whereas N and P export coefficients increased exponentially with pasture land use.
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