2018
DOI: 10.1016/j.biortech.2018.06.080
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Improving anaerobic fermentation of waste activated sludge using iron activated persulfate treatment

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Cited by 109 publications
(20 citation statements)
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“…en, the production of SCFA gradually decreased until day 8, and the total SCFA content in all reaction systems increased slightly and reached the second peak on day 9. en, the production of SCFA continued to decrease in the remaining time. e two increasing trends of SCFA production during anaerobic fermentation are inconsistent with the results of previous studies [47,48]. Further data analysis showed that the concentration of DEHP in the reaction system did not significantly change the yield of SCFA.…”
Section: Effect Of Dehp On Scfa Production By Sludge Anaerobiccontrasting
confidence: 82%
“…en, the production of SCFA gradually decreased until day 8, and the total SCFA content in all reaction systems increased slightly and reached the second peak on day 9. en, the production of SCFA continued to decrease in the remaining time. e two increasing trends of SCFA production during anaerobic fermentation are inconsistent with the results of previous studies [47,48]. Further data analysis showed that the concentration of DEHP in the reaction system did not significantly change the yield of SCFA.…”
Section: Effect Of Dehp On Scfa Production By Sludge Anaerobiccontrasting
confidence: 82%
“…The fluorescence peak location and intensity in different reactors mean the variation of fluorescing substances. For example, the red‐shift of the fluorescence peak is connected with the increase of some functional groups such as hydroxyl, carboxyl and carbonyl, while a blue‐shift of the fluorescence peak means a decline in these groups …”
Section: Resultsmentioning
confidence: 99%
“…, there are three main typical fluorescent signals in all the samples. The fluorescent signals located at the excitation/emission wavelengths of 250–400/320–380 (Peak A), 220–255/330–380 (Peak B), and 250–400/380–500 (Peak C) are ascribed to microbial by‐products, tryptophan protein‐like substances and humic acid‐like substances, respectively . Among the earlier materials, microbial by‐products are thought to be biodegradable substances, while tryptophan protein‐like and humic acid‐like substances are considered as non‐biodegradable compounds .…”
Section: Resultsmentioning
confidence: 99%
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