文章摘要
太湖地区河蟹“养殖-净化”复合系统氮磷循环模拟模型研究
A Modeling Simulation for Nitrogen and Phosphorus Cycling in the Crab Cultivation-Purification System in the Taihu Lake District, China
投稿时间:2016-10-18  
DOI:10.13254/j.jare.2016.0252
中文关键词: 河蟹,集约化养殖,生态循环,氮磷养分,系统动力学模型
英文关键词: crab, intensive cultivation, ecological recycling, N,P nutrient, system dynamic model
基金项目:江苏省农业科技自主创新资金项目(CX(14)2015,CX(16)1003);江苏省高校哲学社会科学一般项目(2015SJD099)
作者单位E-mail
朱冰莹 南京农业大学人文与社会发展学院, 江苏 南京 210095  
董佳 南京农业大学人文与社会发展学院, 江苏 南京 210095  
陆长婴 江苏太湖地区农业科学研究所, 江苏 苏州 215155  
施林林 江苏太湖地区农业科学研究所, 江苏 苏州 215155  
沈明星 江苏太湖地区农业科学研究所, 江苏 苏州 215155 596005553@qq.com 
杨海水 南京农业大学农学院, 江苏 南京 210095 yanghaishui@njau.edu.cn 
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中文摘要:
      以“养殖-净化”复合系统为对象,探讨河蟹养殖尾水达标排放(地表Ⅲ类水)的工程与技术措施。通过构建系统动力学模型,模拟河蟹养殖尾水达标排放的最佳养殖塘与净化塘的面积比,及不同饵料替代比例、水质调控技术与净化效率对养殖塘和净化塘水体TN和TP浓度的影响。模拟结果显示,在常规养殖条件下,要使净化尾水达到地表Ⅲ类水标准,养殖塘与净化塘的最佳面积比为20.5∶1。商品饲料代替5%、10% 和15%时,养殖塘TN浓度分别降低3.1%、6.3% 和 10.0%,TP浓度分别降低4.2%、8.3% 和8.3%;净化塘TN浓度分别降低4.5%、10.1% 和14.6%。养殖塘水质调控技术对养殖塘和净化塘水体的TN和TP浓度无显著影响。与水葫芦收获1次相比,收获2次和3次的养殖塘TN浓度分别显著降低10.0%和10.0%,TP浓度降低11.1%和11.1%;净化塘TN浓度分别降低16.1%和17.2%。水葫芦收获2次与3次对养殖塘和净化塘水体TN、TP浓度变化无显著影响。以上结果表明,河蟹养殖工程可以按照养殖塘与净化塘的面积比为20.5∶1进行构建,二塘水体的TN、TP浓度随商品饲料替代比例增加而降低;净化塘水葫芦只需收获2次,净化水质即可达标地表Ⅲ类水。
英文摘要:
      This study aims to integrate the ‘Crab-Grass-Snail’ system and the ‘Cultivating-Purifying’ system into a more comprehensive recycling ecosystem, and theoretically investigate the engineering practice to meet the Ⅲ type surface water standard. Through constructing a system dynamic model, this study simulated the optimal area ratio between crab cultivation pond and purification pond, as well as testing the effects of feed substitution ratio, water quality regulation technology and purifying efficiency on TN and TP concentration. The simulation results showed that the optimal area ratio for cultivation pond and purification pond was 20.5 to meet the Ⅲ type surface water standard. It was reduced by 3.1%, 6.3% and 10.0% for TN concentration and by 4.2%, 8.3% and 8.3% for TP concentration in the cultivation pond with a substitution of commercial feeds for 5%, 10% and 15%, respectively. TN concentration was decreased by 4.5%, 10.1% and 14.6% in the purification pond with a substitution of commercial feeds for 5%, 10% and 15%, respectively. Water quality regulation technology did not affect TN and TP concentration in the cultivation and purification ponds. Compared with one time's harvest for water hyacinth, it was reduced 10.0% and 10.0% for TN concentration and 11.1% and 11.1% for TP concentration in the cultivation pond by harvest two times and three times, respectively. TN concentration was decreased by 16.1% and 17.2% in the purification pond. In summary, N and P input from commercial feeds were an important cause for the over-range of N and P concentration in the residue water. TN and TP concentration will decrease with increasing substitution rate for commercial feeds in the cultivation and purification ponds. It needs only to harvest two times for water hyacinth when the purifying water will meet the Ⅲ type surface water standard. These results will provide theoretical evidence for engineering design and the mating management practice for the crab ecological cultivation.
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