农业工程学报
農業工程學報
농업공정학보
2013年
24期
124-131
,共8页
张微微%李红%孙丹峰%周连第
張微微%李紅%孫丹峰%週連第
장미미%리홍%손단봉%주련제
氮%磷%模型%农业污染%怀柔水库流域
氮%燐%模型%農業汙染%懷柔水庫流域
담%린%모형%농업오염%부유수고류역
nitrogen%phosphorus%models%agricultural pollution%Huairou reservoir watershed
流域尺度农业污染负荷估算及其时间上的变化分析可为流域农业结构调整以及水污染控制和治理提供科学依据。利用输出系数模型,对怀柔水库上游两怀流域2000年和2011年的农业污染负荷总氮和总磷进行了估算和变化分析,揭示了各类农业活动对两怀流域氮磷污染的影响。结果表明:从2000到2011年两怀流域农业氮和磷负荷总量有增加的趋势,分别从2000年的454.029和51.014 t上升到2011年的485.961和58.437 t,其中水产养殖氮、磷负荷量增加比重最大。流域内农业土地利用及产业结构变化是引起氮磷污染负荷发生变化的主要原因。建议针对不同污染源类型,采取相应减控措施减少各类污染物排放量;同时,大力发展流域循环经济模式,实现种植业、养殖业和农村生活废弃物的资源化和再生利用。
流域呎度農業汙染負荷估算及其時間上的變化分析可為流域農業結構調整以及水汙染控製和治理提供科學依據。利用輸齣繫數模型,對懷柔水庫上遊兩懷流域2000年和2011年的農業汙染負荷總氮和總燐進行瞭估算和變化分析,揭示瞭各類農業活動對兩懷流域氮燐汙染的影響。結果錶明:從2000到2011年兩懷流域農業氮和燐負荷總量有增加的趨勢,分彆從2000年的454.029和51.014 t上升到2011年的485.961和58.437 t,其中水產養殖氮、燐負荷量增加比重最大。流域內農業土地利用及產業結構變化是引起氮燐汙染負荷髮生變化的主要原因。建議針對不同汙染源類型,採取相應減控措施減少各類汙染物排放量;同時,大力髮展流域循環經濟模式,實現種植業、養殖業和農村生活廢棄物的資源化和再生利用。
류역척도농업오염부하고산급기시간상적변화분석가위류역농업결구조정이급수오염공제화치리제공과학의거。이용수출계수모형,대부유수고상유량부류역2000년화2011년적농업오염부하총담화총린진행료고산화변화분석,게시료각류농업활동대량부류역담린오염적영향。결과표명:종2000도2011년량부류역농업담화린부하총량유증가적추세,분별종2000년적454.029화51.014 t상승도2011년적485.961화58.437 t,기중수산양식담、린부하량증가비중최대。류역내농업토지이용급산업결구변화시인기담린오염부하발생변화적주요원인。건의침대불동오염원류형,채취상응감공조시감소각류오염물배방량;동시,대력발전류역순배경제모식,실현충식업、양식업화농촌생활폐기물적자원화화재생이용。
Increased nutrient (i.e., nitrogen and phosphorus) concentrations have been observed in the surface water bodies inmany counties. Agricultural non-point source (NPS) pollution has been identified as one of the most important factors in causing water quality deterioration. To control NPS pollution effectively, it is necessary to quantifying agricultural pollution loads and understanding contribution of the pollution sources. Furthermore, watershed-based analysis can provide scientific basis for agricultural practices and water pollution control. In this paper, the general export coefficient model was used to estimate the loads of total nitrogen (TN) and total phosphorus (TP) from the upper Lianghuai basin of Huairou Reservoir for year 2000 and 2011. The model results showed that the total nitrogen and total phosphorus loads in 2000 were mainly contributed from the farmland planting, livestock and poultry breeding., while aquatic agriculture mainly contributed the total nitrogen and total phosphorus loads in 2011. Agricultural nitrogen and phosphorus loads increased in the study area during two year period. The nitrogen load increased from 454.029 ton in 2000 to 485.961 ton in 2011, while phosphorus load increased from 51.014 ton in 2000 to 58.437 ton in 2011. The nitrogen and phosphorus loads from aquatic agriculture took account of the largest percentage among the agricultural pollution sources. The agricultural land use and industrial structure changes caused nitrogen and phosphorus loads changed from 2000 to 2011 in the study basin. In the future, the corresponding control measures are recommended according to different pollution sources in order to reducing their pollution discharges. Moreover, recycling economy pattern is encouraged to achieve the resource utilization and reuse of planting, breeding and rural life waste.