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Decomposition kinetics of primary sewage sludge (PSS) and synthetic faeces (SF), of various moisture contents, were investigated over different reaction times and temperatures using a hydrothermal batch reactor.
Chl a concentrations did not increase through time in the primary sewage plume but did increase up to 30% in the secondary sewage plume.
It is clear, from Table 7, that irrigation with primary sewage effluent decreased the CaCO3 content from 32.26 to 31.04 and 29.15% for primary sewage effluent treatments after 8, 16 and 24 months, respectively, of irrigation stage.
Pretreated food wastes, which were in pulp status, were injected to an anaerobic digester with primary sewage sludge.
Samples of wet primary sewage sludge (biosolids) were also collected on the same days and immediately stored on ice in polyethylene bottles.
Consequently, it followed by primary sewage effluent treatment (5.83, 8.71 and 2.90% less than tap water treatment for 8, 16 and 24 months stages, respectively).
Similar(49)
One discharges primary treated sewage and the other discharges secondary treated sewage but are otherwise similar.
Fifteen pilot-scale units were loaded with primary treated sewage in Langenreichenbach, Germany and monitored at the inlet, outlet and a several internal sample points between August 2010 and December 2011.
Mixtures of primary treated sewage and river water were placed in dialysis bags and incubated in situ under ambient conditions for seven days.
This iFBBR was operated with and without adding a new starch based flocculant (NSBF) to treat synthetic primary treated sewage effluent (PTSE).
To our knowledge, this paper presents for the first time the determination of ten primary amines in sewage sludge samples using PHWE.
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