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Effects of composite lactic acid bacteria agent and anaerobic fermentation pretreatment on aerobic composting of cattle manure
Transactions of the Chinese Society of Agricultural Engineering 2026, 42(2): 279-286
Published: 30 January 2026
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Aerobic composting has been limited by the relatively high pH value of the cow manure compost products. The organic fertilizer quality can be required to reduce nutrient loss. The acid-producing bacteria can be expected to reduce the pH value and nitrogen loss in the cow manure compost. But, its addition can often be regulated during composting. This study aims to explore the effects of the composite lactic acid bacteria agent and anaerobic fermentation pretreatment on the aerobic composting of the cattle manure. The lactic acid bacteria were also isolated and then screened from the fresh cow manure. Four treatments were designed: T1, the material was added with a composite bacterial agent for 4 days before aerobic fermentation; T2, the composite bacterial agent was added, followed by aerobic fermentation with ventilation; T3, sulfuric acid was added, followed by aerobic fermentation with ventilation; T4, sulfuric acid and the composite bacterial agent were added and fully mixed before aerobic composting. The original aerobic composting was used as the control (CK). The results show that the 21 suspected strains of the lactic acid bacteria were isolated from the fresh cow manure. Two target strains were obtained after initial and secondary screenings, based on their rapid growth and strong acid production. These strains were identified as Lactobacillus amylovorus LB31 and Weissella paramesenteroides BY1. The optimal viable cell ratio of the composite bacterial agent was prepared from the two strains of 7:3. The pH value of the material also decreased from 7.67 to 7.38 after anaerobic fermentation pretreatment. The T1 treatment shared a 4.07% reduction in the pH value, compared with the CK. Furthermore, the T1 treatment also exhibited the least carbon and nitrogen loss at the end of the composting, which decreased by 27.53% and 37.50%, respectively. The mass fractions of the available phosphorus and available potassium increased by 14.68% and 10.95%, respectively, whereas the pH value decreased by 0.46. In conclusion, the optimal procedure was obtained to add a 3.0% mass fraction of composite lactic acid bacteria agent into cow manure compost, followed by 4 days of anaerobic fermentation and aerobic composting. The pH value of the compost material and product was significantly reduced due to low nutrient loss during composting. This finding can provide the bacterial strain resources for the application of the lactic acid bacteria in composting. While the theoretical and technical foundations can also offer to combine the anaerobic and aerobic processes for the low pH compost and nutrient loss.

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Farmland water purification in Yellow River irrigation area based on near-natural eco-circulation system
Transactions of the Chinese Society of Agricultural Engineering 2025, 41(18): 101-110
Published: 30 September 2025
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The Yellow River irrigation area in Ningxia is one of the important river sections affecting the water quality of the Yellow River. The main pollution source is the farmland backwater in the irrigation area, and the water quality is generally lightly polluted. In order to implement the comprehensive management of agricultural non-point source pollution, it is necessary to strictly control the discharge of farmland backwater into the Yellow River and strengthen the construction of ecological interception and purification facilities. This study investigated the effects of water quality biological purification technology and near-natural ecological circulation system technology on the water purification in the farmland. In 2022, in a pond at the end of the first drainage ditch of Zhongwei, the study comprehensively used the constructed wetland water quality biological purification technology and the near-natural ecological circulation system technology, selected suitable aquatic and terrestrial plants, and used eutrophication pollution factors as the core indicators. The near-natural eco-circulation system included sediment reuse, selection and growth control of aquatic organisms, fillers for purification zones, construction of bird shelters, and reuse systems for purified water irrigation. The system was constructed by the followed steps. First, after the Yellow River water was channeled through irrigation canals at all levels to farmlands, the return water flowed into constructed wetlands via drainage ditches at all levels. Through eco-biological purification processes involving aquatic plants, aquatic animals, and microorganisms, a small portion of the water meeting the standards was reused for irrigation, while most of it was discharged back into the Yellow River for recycling in the lower reaches. The sediment was comprehensively utilized as ecological products, such as improving sandy soil, increasing farmland fertility, and processing into organic fertilizers. Secondly, the constructed wetland itself, composed of aquatic and terrestrial systems, formed a wetland park and a large bird habitat system. It not only beautified the environment but also provided places for birds to inhabit, forage, breed as temporary shelters. It can also be used for human recreation and bird watching under low-disturbance conditions. In the food chain system, there was an aquatic food chain consisting of aquatic plants, herbivorous fish, shrimps, mollusks, crustaceans, and carnivorous fish. These, together with terrestrial plants, their fruits and seeds, and terrestrial insects, were involved in the food chain of birds (both herbivorous and carnivorous birds). A larger near-natural ecosystem was formed by wetlands, woodlands, farmlands, and animals and plants. The water quality pH value, chemical oxygen demand, total nitrogen, ammonia nitrogen and total phosphorus indicators were analyzed and evaluated before and in the two years after the implementation of the technology. Before the technique implement, the water standard from the farmland presented above Class V. After the water purification was applied, the average mass concentration reduction rates of chemical oxygen demand, total nitrogen, ammonia nitrogen and total phosphorus in the second year after the implementation were 41.97%, 33.27%, 56.96% and 72.22%, respectively, compared with those before the implementation. The comprehensive pollution index of water quality decreased from 0.72 to 0.45, and it was generally stable at Class IV water and above standards. A near-natural ecological circulation system suitable for the treatment of lightly polluted water in the Yellow River was constructed, which enriched biodiversity, and the agricultural water environment continued to improve, providing a low-interference and low-pollution living space for birds. This study provides a reference for the ecological purification treatment of farmland drainage.

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