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To mimick the patchy distribution of sewage sludge, NP-contaminated sewage sludge pellets were distributed in noncontaminated soil and F. fimetaria were exposed to it.
The equations of velocity distribution of sewage are, respectively, v+ = 2.5 ln y+ + 5.7, v+ = 5.11 ln y+ − 3.22, and v+ = y+ in turbulence, intermediate, and laminar current zone in circle pipe.
Nano-particle loadings from households to rivers were simulated considering household connectivity to sewerage, sewage treatment efficiency, the spatial distribution of sewage treatment plants, and their associated populations.
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Garside et al. (1976) confirmed the seasonal and spatial distribution of sewage-derived nitrogen and its contribution to much of the nitrogen in the Hudson Estuary, New York, and showed that primary production was not limited by nitrogen availability.
The molecular weight distribution of DOM in sewage not only reflected the characteristics of organic matter but also closely related to the degradation efficiency for wastewater (Chang et al. 2000).
Geographic differences of BPA in sludge were recently examined by Staples et al. (2010) who developed probabilistic exposure distributions of BPA in sewage sludge and proposed median (50th percentile) and 95th percentile values of 780 and 14 200 μg/kg for North America and 160 and 95 000 μg/kg for Europe.
The study concluded that the storage system of treated sewage would increase the distribution of antimicrobial resistance among bacterial population after the disposal or reuse of treated sewage for agricultural purposes.
The study revealed the role of the treated sewage in the distribution of pathogenic bacteria into the natural waster system.
In this paper, we propose and demonstrate an Event-driven Model Predictive Control (EMPC) methodology, which controls the flows of sewage streams containing the dosed chemical to ensure desirable distribution of the dosed chemical throughout the pipe sections of interests.
To adjust the distribution of dissolved oxygen (DO) in CWs and to improve the efficiency of sewage water purification, typical HSSF CWs were divided into different sections with enhanced functions.
Our approach can be extended to energy distribution networks, sewage systems, and even to networks that are not constant of size in time.
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