Alkaline fermentation has been considered as one of the efficient methods for waste activated sludge (WAS) treatment, but usually limited by microbial fermentation activities under extreme pH condition. One newly isolated alkali-tolerant strain Corynebacterium pollutisoli SPH6 was used to assess its potential role and effect on WAS alkaline fermentation process. Results from response surface method showed that the optimal organic nitrogen degradation rate by SPH6 was obtained under temperature of 35 °C, initial pH of 10, shaking speed of 80 rpm, inoculation ratio of 6.5%. Batch-scale experiments demonstrated that, compared with the control group, the inoculation of SPH6 finally achieved higher productions with 13.4% of carbohydrates, 27.1% of protein and 25.4% of total volatile fatty acids (VFAs), and more predominant functional bacteria characterized by high-throughput sequencing, such as genera Acinetobacter in phylum Proteobacteria, Tissierella and Acetoanaerobium in phylum Firmicutes. The strain SPH6 might play a vital role in maintaining and facilitating the growth and diversity of functional bacteria in WAS alkaline fermentation process. It has implied promising practical application of the present strain in enhancing WAS reduction and utilization.
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http://dx.doi.org/10.1016/j.chemosphere.2019.125072 | DOI Listing |
J Environ Manage
December 2024
Faculty of Science and Technology, Norwegian University of Life Sciences, P.O. Box 5003, Aas, 1430, Norway.
Primary sludge can serve as an internal carbon source for denitrification in wastewater treatment plants (WWTPs). This study explores the use of alkaline treatment to produce a fermentation broth from primary sludge, which predominantly contains short-chain volatile fatty acids (VFAs), with acetic acid and propionic acid making up over 65% of the total VFAs. The performance of this fermentation broth as a sole carbon source for denitrification was compared with that of sodium acetate, acetic acid, methanol, and ethanol in both biofilm and activated sludge systems.
View Article and Find Full Text PDFJ Environ Manage
December 2024
School of Civil and Environmental Engineering, University of New South Wales, Sydney, 2052, NSW, Australia. Electronic address:
Transforming waste activated sludge (WAS) into medium-chain fatty acids (MCFAs) via chain elongation (CE) technology is sustainable, yet pH effects on this process are poorly understood. In this study, semi-continuous flow experiments demonstrated that WAS degradation was highest under alkaline pH (10) but unsuitable for CE. Continuous output of MCFAs indicated that CE could be successfully performed under acidic pH (5) and neutral pH (7).
View Article and Find Full Text PDFAnimals (Basel)
November 2024
Department of Animal Science, College of Animal Science and Technology, Foshan University, Foshan 528225, China.
This study aims to investigate the effects of fermented soybean hulls (FSHS) on reproductive performance, plasma biochemical profiles, immune parameters, and fecal microbiota in sows. A total of 325 sows were randomized into five groups, each fed a diet with varying FSHS proportions: 0% (control), 2% (FSHS2), 4% (FSHS4), 6% (FSHS6), and 8% (FSHS8). Diets were prepared by replacing conventional soybean hulls with FSHS in equal amounts.
View Article and Find Full Text PDFBioresour Technol
December 2024
School of Water Conservancy and Transportation, Zhengzhou University, Zhengzhou 450001, China. Electronic address:
In this study, the alkaline fermentation of combined lipid-rich waste (LRW) was explored to produce volatile fatty acids (VFAs). By introducing sulfate as an external electron acceptor, the long-chain fatty acid (LCFA) metabolic pathway was enhanced, achieving a VFA yield of 671.1 ± 21.
View Article and Find Full Text PDFSci Total Environ
December 2024
School of Ecology and Environment, Beijing Technology and Business University, Beijing 100048, China. Electronic address:
In this study, enhanced membrane coagulation (EMC) sludge was subjected to various alkaline (pH 7.2, 10, and 11), temperature (35 °C and 55 °C), and duration (0.5 h and 1 day) pretreatment conditions before being inoculated into biogas reactors operated for 176 days.
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