Low-technology recirculating aquaculture system integrating milkfish Chanos chanos, sea cucumber Holothuria scabra and sea purslane Sesuvium portulacastrum

IF 2.2 2区 农林科学 Q2 FISHERIES Aquaculture Environment Interactions Pub Date : 2020-11-05 DOI:10.3354/aei00377
Paula Senff, P. Blanc, M. Slater, A. Kunzmann
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引用次数: 4

Abstract

Closed recirculation aquaculture systems (RAS) in combination with integrated multitrophic aquaculture (IMTA) are considered best management practices, but high material costs and difficult maintenance still hinder their implementation, especially in developing countries and the tropics. Few case studies of such systems with tropical species exist. For the first time, an extremely low-budget system was tested combining the halophyte sea purslane Sesuvium portulacastrum and a detritivore, sandfish Holothuria scabra, with finfish milkfish Chanos chanos over 8 wk on Zanzibar, Tanzania. In a 2 m3 RAS, milkfish and sea purslane showed good growth, producing an average (±SD) of 1147 ± 79 g fish and 1261 ± 95 g plant biomass, while sea cucumber growth was variable at 92 ± 68 g. The system operated without filter units and did not discharge any solid or dissolved waste. Water quality remained tolerable and ammonia levels were reliably decreased to <1 mg l−1. A NO2 peak occurred within the first 30 d, indicating good biofilter performance of the different system compartments. Changes in dissolved inorganic nitrogen (DIN) species support the notion that the sea cucumber tank was the main site of nitrification, while the hydroponic halophyte tank acted as a net sink of NO3. A nitrogen budget accounted for 63.7 ± 5.3% of the nitrogen added to the system as fish feed. Increasing the plant to fish biomass ratio to 5:1 would fully treat the DIN load. The experiment provides proof-of-concept of a simple pilotscale RAS, integrating tropical species at 3 trophic levels.
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目鱼、海参、马齿苋的低技术循环水养殖系统
封闭再循环水产养殖系统(RAS)与综合多营养水产养殖(IMTA)相结合被认为是最佳管理做法,但高昂的材料成本和难以维护仍然阻碍了其实施,尤其是在发展中国家和热带地区。很少有关于热带物种的此类系统的案例研究。在坦桑尼亚桑给巴尔,首次测试了一种极低预算的系统,该系统将盐生海洋马齿苋Sesuvium portulacastrum和碎屑食草动物沙鱼Holothuria scabra与鳍鱼乳鱼Chanos Chanos相结合,为期8周。在2 m3 RAS中,乳鱼和海马齿苋表现出良好的生长,产生1147±79 g鱼和1261±95 g植物生物量的平均值(±SD),而海参的生长在92±68 g时是可变的。该系统在没有过滤装置的情况下运行,不排放任何固体或溶解废物。水质仍然可以忍受,氨水平可靠地降低到<1 mg l−1。NO2峰值出现在最初的30天内,表明不同系统隔室的生物过滤器性能良好。溶解无机氮(DIN)物种的变化支持了这样一种观点,即海参池是硝化的主要场所,而水培盐生植物池是NO3的净汇。氮预算占作为鱼类饲料添加到系统中的氮的63.7±5.3%。将植物与鱼类的生物量比提高到5:1将完全处理DIN负荷。该实验提供了一个简单的中尺度RAS概念的证明,该概念整合了3个营养级的热带物种。
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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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