Effects of sucrose amendment on ammonia assimilation during sewage sludge composting

Composting is a biological decomposition process that occurs from microbial progression, which brings about the degradation and stabilization of various organic waste into compost. During composting, the emission of undesirable odor adversely affects compost quality and causes environmental deterioration. Also, odor emission from composting adversely affects human health and well-being. Ammonia (NH3), volatile organic compounds (VOCs), and hydrogen sulfide (H2S) are major components of odorous gases responsible for unpleasant odor. Physiological parameters such as pH, temperature, and aeration affect the pattern of odor emission during the composting process. The lack of techniques for the accurate identification and estimation of odor and control are some major challenges associated with composting. Therefore, the present review article concentrates on challenges and solutions to odor control. Biotrickling filter, optimization of process parameters, usage of additives, microbial inoculation, and pre-treatment techniques are practiced to lower odor emission during the process. The application of metagenomics may provide insight into the various biogeochemical pathways that can be explored in the future for odor control.

Challenges and Control Strategies of Odor Emission from Composting Operation

New insights into the interactions between carbon dioxide and ammonia emissions during sewage sludge composting.

Co-composting produces a valuable compost material that can be used as valuable soil amendment. The process of the co-composting and control of the composting factors are the current challenges for the researchers. There are different factors that govern the quality, stability and the maturity of the co-compost in terms of amount of plant nutrients and reduction of heavy metals. Among these, C:N ratio is a parameter that can affect the loss of plant nutrients. Different studies showed wide ranges of C:N ratios (14-40) for maturity of quality compost. Temperature, aeration and types of the bulking agents also regulate the process of co-composting. Most widely used co-composted materials are animal manures with agro-wastes (sawdust, wheat straw, rice straw, corn stalks etc.). This practice brought substantial loss of heavy metals and maximum retention of plant nutrients. Higher nutrients contents of the compost and favourable soil properties as a result of co-composting of the saw dust, cow dung and egg shells have been reported. The application of co-composted dairy manure with wheat straw and sawdust produced higher plant biomass. Co-compost of cattle manure with rice straw produced an organic matter, total N and C:N ratio contents suitable for soil amendment. Therefore, this review focuses on the characteristics and utilization of organic waste after a reasonable co-composting process.

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Characterization and Recycling of Organic Waste after Co-Composting - A Review

Sewage sludge composting is an important environmental measure. The reduction of nitrogen loss is a critical aim of compost maturation, and the addition of spent mushrooms (SMs) and herbal residues (HRs) may be helpful. To evaluate the nitrogen transformations during co-composting of sewage sludge, SMs, and HRs, windrows were constructed in a residual processing plant. Dewatered sewage sludge and sawdust were mixed with SMs and HRs at two proportions on a fresh weight basis, 3:1:1 (sewage sludge:sawdust:SMs or HRs) and 3:1:2 (sewage sludge:sawdust:SMs or HRs). The mixture was then composted for 40 d. Changes in the physicochemical characteristic of sewage sludge during composting were recorded and analyzed. Addition of SMs and HRs accelerated the temperature rise, mediating a quicker composting maturation time compared to control. The addition also resulted in lower nitrogen losses and higher nitrate nitrogen levels in the compost products. Among the windrows, SM and HR addition improved the nitrogen status. The total nitrogen (TN) and nitrogen losses for SM and HR treatments ranged from 22.45 to 24.99 g/kg and from 10.2% to 22.4% over the control values (18.66-21.57 g/kg and 40.5%-64.2%, respectively). The pile with the highest proportion of SMs (3:1:2 (sewage sludge:sawdust:SMs)) had the highest TN level and the lowest nitrogen loss. The germination index (GI) values for all samples at maturity were above 80%, demonstrating optimal maturity. The addition of SMs and HRs augments sewage composting.

Nitrogen transformations during co-composting of herbal residues, spent mushrooms, and sludge

Ammonia assimilating bacteria were isolated from composting processes and their abilities to assimilate ammonia were evaluated. In the prefermentation stage of the composting, 104.7 and 103.7 (CFU/ g) of ammonia assimilating bacteria were detected on the medium which contained ammonia as a sole nitrogen, at 37°C and 55°C, respectively. They were 104.6 and 103.2 in the end of the primary fermentation, and 105.1 and 103.2 in the end of the secondary fermentation, respectively. When isolates were purely cultivated in sterilized compost extract medium, many of them consumed ammonia not by nitrification but by assimilation. They still assimilated ammonia even in nonsterilized compost extract medium, i.e. mixed culture with the live microbial flora of the compost. However, isolates which showed high ammonia assimilating ability in the pure culture did not always show high abilities in nonsterilized compost extract media. Isolates which showed high ammonia assimilating ability in the nonsterilized medium were id...

Distribution of Ammonia Assimilating Bacteria In the Composting Process

We investigated microorganisms that assimilated ammonia in lagoon treatment processes. Ammonia-assimilating microorganisms were detected by nitrogen-limited medium that contained ammonia as the sole nitrogen source. Numbers of ammonia-assimilating aerobes (log CFU/g) were 3.4, 4.8, 5.0, 4.8 and 5.0 (log CFU/mL) on the culture plate incubated at 4°C, 10°C, 15°C, 20°C and 25°C, respectively. Many isolates used ammonia in high rates when they were purely cultivated in nitrogen-limited medium added to sterilized lagoon extract. Many of them used ammonia even when they were cultivated in media containing viable microbial flora of the lagoon. Among them, enterobacteriaceae and Pseudomonas sp. were identified by analysis of 16S ribosomal DNA.

Characterization of ammonia-assimilating bacteria in a lagoon for wastewater from a paddock of dairy cattle

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Distribution of Ammonia Assimilating Bacteria In the Composting Process

Characterization of ammonia-assimilating bacteria in a lagoon for wastewater from a paddock of dairy cattle