Use of Bacillus subtilis D9 to purify coastal aquaculture wastewater and improve grass carp resistance to Vibrio infection

IF 2.2 2区 农林科学 Q2 FISHERIES Aquaculture Environment Interactions Pub Date : 2021-01-01 DOI:10.3354/aei00404
Y. Shao, H. Zhong, L. Wang, Mma Elbashier
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Abstract

In coastal areas of China, high-density aquaculture has caused environmental problems and fish health concerns. Bacillus subtilis D9 is a new strain isolated from coastal soils which could be used in aquaculture to improve the water environment. We investigated the effect of B. subtilis D9 on the purification of coastal aquaculture wastewater and the resistance of grass carp Ctenopharyngodon idellus to pathogenic Vibrio infection. Three inoculation levels of B. subtilis D9 were used (5.5 × 107, 5.5 × 108 and 5.5×109 cfu ml-1 as BD7, BD8 and BD9, respectively), together with sterilized saline water without B. subtilis D9 as the Control. B. subtilis D9 at the inoculation level of BD8 showed the best performance with 81, 87, 91, 52 and 86% removal of NH4+-N, NO3--N, total nitrogen (TN), NO2--N and turbidity, respectively, after 25 d of treatment. These values were significantly higher than at the BD7, BD9 and Control levels. Under aeration (AIR) conditions, B. subtilis D9 at the inoculation level of BD8 showed removal efficiency of 93, 91, 95, 76 and 89%, respectively. In contrast it was only 26, 29, 16, 10 and 57% in an inactivated bacteria liquid (IBL) treatment. After 22 d of infection by Vibrio parahaemolyticus, significant differences were found in weight gain, specific growth rate and relative percentage of survival among grass carp grown on AIR, BD8 or IBL wastewater. In summary, B. subtilis D9 with aeration has beneficial effects on the purification of coastal aquaculture wastewater and on the resistance of grass carp to disease caused by V. parahaemolyticus.
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利用枯草芽孢杆菌D9净化沿海养殖废水,提高草鱼对弧菌感染的抗性
在中国沿海地区,高密度的水产养殖造成了环境问题和鱼类健康问题。枯草芽孢杆菌(Bacillus subtilis D9)是一种从沿海土壤中分离到的新菌株,可用于水产养殖,改善水体环境。研究了枯草芽孢杆菌D9对滨海养殖废水净化及草鱼对致病性弧菌感染的抗性的影响。采用3个接种水平的枯草芽孢杆菌D9(分别为5.5× 107、5.5× 108和5.5×109 cfu ml-1)接种BD7、BD8和BD9,并以不含枯草芽孢杆菌D9的无菌盐水为对照。接种BD8水平的枯草芽孢杆菌D9在处理25 d后表现最佳,对NH4+-N、NO3——N、总氮(TN)、NO2——N和浊度的去除率分别为81%、87%、91%、52%和86%。这些数值显著高于BD7、BD9和对照水平。在曝气(AIR)条件下,接种BD8的枯草芽孢杆菌D9的去除率分别为93%、91%、95%、76%和89%。相比之下,灭活菌液(IBL)处理仅为26%、29%、16%、10%和57%。副溶血性弧菌感染草鱼22 d后,分别饲喂AIR、BD8和IBL废水的草鱼增重、特定生长率和相对存活率均有显著差异。综上所述,经曝气处理的枯草芽孢杆菌D9对滨海养殖废水的净化和草鱼对副溶血性弧菌病的抗性均有良好的效果。
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来源期刊
Aquaculture Environment Interactions
Aquaculture Environment Interactions FISHERIES-MARINE & FRESHWATER BIOLOGY
CiteScore
4.90
自引率
13.60%
发文量
15
审稿时长
>12 weeks
期刊介绍: AEI presents rigorously refereed and carefully selected Research Articles, Reviews and Notes, as well as Comments/Reply Comments (for details see MEPS 228:1), Theme Sections and Opinion Pieces. For details consult the Guidelines for Authors. Papers may be concerned with inter­actions between aquaculture and the environment from local to ecosystem scales, at all levels of organisation and investigation. Areas covered include: -Pollution and nutrient inputs; bio-accumulation and impacts of chemical compounds used in aquaculture. -Effects on benthic and pelagic assemblages or pro­cesses that are related to aquaculture activities. -Interactions of wild fauna (invertebrates, fishes, birds, mammals) with aquaculture activities; genetic impacts on wild populations. -Parasite and pathogen interactions between farmed and wild stocks. -Comparisons of the environmental effects of traditional and organic aquaculture. -Introductions of alien species; escape and intentional releases (seeding) of cultured organisms into the wild. -Effects of capture-based aquaculture (ranching). -Interactions of aquaculture installations with biofouling organisms and consequences of biofouling control measures. -Integrated multi-trophic aquaculture; comparisons of re-circulation and ‘open’ systems. -Effects of climate change and environmental variability on aquaculture activities. -Modelling of aquaculture–environment interactions; ­assessment of carrying capacity. -Interactions between aquaculture and other industries (e.g. tourism, fisheries, transport). -Policy and practice of aquaculture regulation directed towards environmental management; site selection, spatial planning, Integrated Coastal Zone Management, and eco-ethics.
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