Effects of Salinity Regulation Methods on Establishment of Marine Biological Flocculation Culture System
WU Huifang1, LUO Guozhi1,2,3, TAN Hongxin1,2,3, MENG Haoyan1
1.Research and Development Center of Aquaculture Engineering of Shanghai, Shanghai 201306, China; 2.NationalDemonstration Center for Experimental Fisheries Science Education, Shanghai Ocean University, Shanghai 201306, China; 3.Shanghai Collaborative Innovation Center for Aquatic Animal Genetics and Breeding, Shanghai 201306, China
Abstract:Effects of three salinity addition methods on culture flocs and the start-up efficiency of bioflocculation system were investigated in nine cylindrical aquaculture buckets with a volume of 100 L and with eel feed as raw materials, in which salinity was adjusted to 30 at the beginning of the experiment in the first group, the salinity was increased by 5 degrees every day after the end of the depression, adding 1 degree every 3 hours in the second group, and the salt was added into cultured freshwater biological flocculation system according to the way of adding salt in the second group in the third group. After startup, the removal efficiency of 10 mg/L ammonia nitrogen in three treatment groups was monitored.The results showed that the contents of ammonia nitrogen and nitrite nitrogen in the second and third groups were decreased to low level before the salinity was adjusted to 30 in first group. During the culture period, there was better settleability of flocs in the second and third groups than that in the first group. The high-throughput sequencing revealed that Flavobacteria was the dominant class in the biological flocculation system with salinity of 30, and Sphingobacteria was the dominant class in the flocculation system with initial salinity of 30. Actinomycetes is the dominant class in the biological flocculation system of freshwater culture and redomestication into seawater. Leptobactrrium and norank_f_Segniliparacea were the dominant genus of marine biological flocculation system with salinity of 30.It was concluded that the second salt regulation method was the most beneficial to cultivate marine biological flocculation system combined with the continuous monitoring of the removal effect of ammonia nitrogen in the three treatment groups after start-up, without significant difference (P>0.05).
[1]贾建三. 新世纪水产养殖的现状、问题与展望[J].中国渔业经济研究,2000(4):34-41. [2]Schryver P D, Verstraete W. Nitrogen removal from aquaculture pond water by heterotrophic nitrogen assimilation in lab-scale sequencing batch reactors[J]. Bioresource Technology,2009,100(3):1162-1167. [3]Avnimelech Y. Bio-filters: the need for an new comprehensive approach[J]. Aquacultural Engineering,2006,34(3):172-178. [4]Tovar A, Moreno C, Manuel P M, et al. Environmental implications of intensive marine aquaculture in earthen ponds[J]. Marine Pollution Bulletin,2000,40(11):981-988. [5]王潮辉,高启,谭洪新,等. 生物絮凝系统构建过程对吉富罗非鱼免疫酶和生长的影响[J].中国水产科学,2015,22(4):707-715. [6]李文清. 不同盐度条件下生物絮凝——罗非鱼养殖效果的研究[D].上海:上海海洋大学,2015. [7]Hamoda M F, Al-Attar I M S. Effects of high sodium chloride concentrations on activated sludge treatment[J]. Water Science & Technology,1995,31(9):61-72. [8]Doudoroff M. Experiments on the adaptation of E. coli to sodium chloride[J]. Journal of General Physiology,1940,23(5):585-611. [9]Kincannon D F, Jr A F G. Response of biological waste treatment systems to changes in salt concentrations[J]. Biotechnology & Bioengineering,1968,10(4):483-496. [10]邓应能,赵培,孙运忠,等. 生物絮团在凡纳滨对虾封闭养殖试验中的形成条件及作用效果[J].渔业科学进展,2012,33(2):69-75. [11]Correia E S, Wilkenfeld J S, Morris T C, et al. Intensive nursery production of the Pacific white shrimp Litopenaeus vannamei using two commercial feeds with high and low protein content in a biofloc-dominated system[J]. Aquacultural Engineering,2014,59(4):48-54. [12]Luo G Z, Li W Q, Tan H X, et al. Comparing salinities of 0, 10 and 20 in biofloc genetically improved farmed tilapia (Oreochromis niloticus) production systems[J]. Aquaculture & Fisheries,2017,2(5):220-226. [13]Pronk M, Bassin J P, de Kreuk M K, et al. Evaluating the main and side effects of high salinity on aerobic granular sludge[J]. Applied Microbiology & Biotechnology,2014,98(3):1339-1348. [14]马涛,罗国芝,谭洪新,等.碱度对水产养殖絮体生物学特性及氨氮转化的影响[J].水产科学,2017,36(4):421-428. [15]国家环境保护局《水和废水监测分析方法》编委会.水和废水监测分析方法[M].4版.北京:中国环境科学出版社,2002. [16]王淑莹,崔有为,于德爽,等.无机盐对活性污泥沉降性的影响[J].环境工程,2003,21(5):7-9. [17]赵凯峰,王淑莹,叶柳,等. NaCl盐度对耐盐活性污泥沉降性能及脱氮的影响[J].环境工程学报,2010,4(3):570-574. [18]张兰河,田蕊,陈子成,等. NaCl盐度对A2/O工艺去除废水污染物和系统微生物的影响[J].农业工程学报,2018,34(10):231-237. [19]路海玲. 土壤盐对棉田土壤微生物活性和土壤肥力的影响[D].南京:南京农业大学,2011. [20]Pankhurst C E, Yu S, Hawke B G, et al. Capacity of fatty acid profiles and substrate utilization patterns to describe differences in soil microbial communities associated with increased salinity or alkalinity at three locations in South Australia[J]. Biology & Fertility of Soils,2001,33(3):204-217. [21]Mitra S, Matsuo Y, Haga T, et al. Leptobacterium flavescens gen. nov.,sp. nov.,a marine member of the family Flavobacteriaceae, isolated from marine sponge and seawater[J]. International Journal of Systematic & Evolutionary Microbiology,2009,59(Pt 2):207-212. [22]安治武. 微生物制剂对养殖水体的净化效果初步研究[D]. 青岛:青岛理工大学,2016. [23]Kincannon D F, Jr A F G. Response of biological waste treatment systems to changes in salt concentrations[J]. Biotechnology & Bioengineering,1968,10(4):483-496. [24]Wang Z, Gao M, She Z, et al. Effects of salinity on performance, extracellular polymeric substances and microbial community of an aerobic granular sequencing batch reactor[J]. Separation & Purification Technology,2015,144(39):223-231. [25]Reid E, Liu X, Judd S J. Effect of high salinity on activated sludge characteristics and membrane permeability in an immersed membrane bioreactor[J]. Journal of Membrane Science,2006,283(1):164-171.