农业环境科学学报
農業環境科學學報
농업배경과학학보
Journal of Agro-Environment Science
2015年
4期
769-775
,共7页
松花江流域%营养盐%空间分布%土地利用
鬆花江流域%營養鹽%空間分佈%土地利用
송화강류역%영양염%공간분포%토지이용
the Songhua River Basin%nutrient%spatial distribution%land use
应用综合污染指数法,结合2013—2014年对松花江流域进行水生态野外全面调查的结果,将流域内历时2年所调查的122个采样点的营养盐分为5个等级进行评价,分析流域内营养盐的污染状况及空间分布。结果表明:松花江流域营养盐评价等级(极好、好、一般、差和极差)的比例分别为10.66%、15.57%、20.49%、28.69%和24.59%,支流的评价结果明显好于干流;各子流域的营养盐污染程度排序为松花江干流﹥第二松花江﹥牡丹江﹥嫩江。研究区内土地利用类型与营养盐评价结果关系密切,尤其是农业非点源污染对流域含氮营养盐的影响较为显著。
應用綜閤汙染指數法,結閤2013—2014年對鬆花江流域進行水生態野外全麵調查的結果,將流域內歷時2年所調查的122箇採樣點的營養鹽分為5箇等級進行評價,分析流域內營養鹽的汙染狀況及空間分佈。結果錶明:鬆花江流域營養鹽評價等級(極好、好、一般、差和極差)的比例分彆為10.66%、15.57%、20.49%、28.69%和24.59%,支流的評價結果明顯好于榦流;各子流域的營養鹽汙染程度排序為鬆花江榦流﹥第二鬆花江﹥牡丹江﹥嫩江。研究區內土地利用類型與營養鹽評價結果關繫密切,尤其是農業非點源汙染對流域含氮營養鹽的影響較為顯著。
응용종합오염지수법,결합2013—2014년대송화강류역진행수생태야외전면조사적결과,장류역내력시2년소조사적122개채양점적영양염분위5개등급진행평개,분석류역내영양염적오염상황급공간분포。결과표명:송화강류역영양염평개등급(겁호、호、일반、차화겁차)적비례분별위10.66%、15.57%、20.49%、28.69%화24.59%,지류적평개결과명현호우간류;각자류역적영양염오염정도배서위송화강간류﹥제이송화강﹥모단강﹥눈강。연구구내토지이용류형여영양염평개결과관계밀절,우기시농업비점원오염대류역함담영양염적영향교위현저。
In this research, 122 samples were obtained from the Songhua River Basin to investigate spatial distribution and pollution of nutri-ents in river water using the comprehensive pollution index method in combination with the results of the 2-year field survey of aquatic e-cosystems from 2013 to 2014. The results showed that the percentages of the excellent, good, moderate, poor and terrible grades of nutrient assessment were respectively 10.66%, 15.57%, 20.49%, 28.69%and 24.59%. The lowest scores of nutrient assessment were found in the Nenjiang River, the Mudan River, the Songnen Plain, the Sanjiang Plain and the Second Songhua River Basin. Nutrient pollution was less in the tributaries than in the main streams. The pollution of the nutrients in river water was in order of the main stream of the Songhua River﹥the Second Songhua River﹥the Mudan River﹥the Nen River. The three nutrient indicators(TN, TP and NH3-H)were significantly different. The assessment method based on grades divided by the same standards was feasible. Land use had profound impacts on nutrient pollution in river water, especially the non-point source pollution of agriculture that affected nitrogenous pollution more significantly.