CAJ | 학술논문

为研究曹娥江流域农业非点源氮磷输出负荷量，将流域降雨及不同营养源产生的氮磷“合成”考虑，提出了产污系数以表征降雨产汇流过程氮磷输出强度，改进了输出系数模型，并探索发现流域年降雨强度与氮磷产污系数之间呈指数正相关，由此构建了基于年降雨强度的农业非点源氮磷输出负荷模型。利用此模型估算了农业污染源氮磷输出负荷量，显示2005－2010年流域总氮（total nitrogen，TN）年输出总量为5456.60～12268.38 t，总磷（total phosphorus，TP）为393.19～820.65 t，年度分布不均，降雨对TN输出总量的贡献率高达54.75%～69.67%。不同农业污染源对TN、TP输出总量的贡献率表明，该流域农业非点源氮磷输出负荷主要来源于人畜，应加强农村生活污水及垃圾、畜禽养殖粪便等治理，进一步控制农田过量施肥，减少耕地氮磷流失。
위연구조아강류역농업비점원담린수출부하량，장류역강우급불동영양원산생적담린“합성”고필，제출료산오계수이표정강우산회류과정담린수출강도，개진료수출계수모형，병탐색발현류역년강우강도여담린산오계수지간정지수정상관，유차구건료기우년강우강도적농업비점원담린수출부하모형。이용차모형고산료농업오염원담린수출부하량，현시2005－2010년류역총담（total nitrogen，TN）년수출총량위5456.60～12268.38 t，총린（total phosphorus，TP）위393.19～820.65 t，년도분포불균，강우대TN수출총량적공헌솔고체54.75%～69.67%。불동농업오염원대TN、TP수출총량적공헌솔표명，해류역농업비점원담린수출부하주요래원우인축，응가강농촌생활오수급랄급、축금양식분편등치리，진일보공제농전과량시비，감소경지담린류실。
In order to study the output loads of TN (total nitrogen) and TP (total phosphorus) from agricultural non-point sources in Cao'e River basin in Shaoxing, an improved export coefficient model for TN and TP was firstly established. According to the theory of black box, the TN and TP from rainfall and agricultural pollution sources were respectively integrated to the total amount of pollutant in this model, and the output intensity of TN and TP in the transportation process was taken into account for the pollutant producing coefficient for the basin, which reflected the effects on the output of TN and TP due to the various losses during the process of rainfall runoff and pollutant transport. After that, the total output loads of TN and TP from agricultural non-point sources during 2005-2010 were estimated using this improved export coefficient model, in which the basic data were obtained from Shaoxing Statistical Yearbook. When the values predicated by the model were compared with those measured by the experiments, the authors found that the total output loads of TN and TP from agricultural non-point sources during 2005-2010 were greatly influenced by rainfall. The total output loads of TN and TP had a positive exponential relationship with the annual rainfall intensity, and therefore a new improved export coefficient model for TN and TP based on rainfall intensity was also established. Finally, this new model was applied to estimate the output loads of TN and TP from various agricultural pollution sources in Cao'e River basin. The estimation results showed that the total output loads of TN were annually far greater than that of TP from agricultural non-point sources during 2005-2010, and the maximum was up to 20.67 times, but with the influence of annual rainfall intensity, they presented uneven temporal distribution during 2005-2010, and the annual total output loads of TN ranged from 5456.60 to 12268.38 t and those of TP ranged from 393.19 to 820.65 t. In those years, when the rainfall intensity was small, the total output loads of TN and TP were both relatively low, and the contributions of rainfall to output loads of TN were up to 54.75%-69.67%, indicating that rainfall had become a key pollution source for TN output in Cao'e River basin. In addition, the results also showed that the order for the contributions of various agricultural pollution sources to output loads of TN from high to low was as follows: rural residents, livestock and poultry, and agricultural land. As a result of shortage of environmental infrastructure in rural area, deficiency of life sewage collection pipe, discharging the polluted water into river directly, and letting off waste randomly, rural life became primary agricultural pollution source to the output of TN in Cao'e River basin. However, the contributions of various agricultural pollution sources to output loads of TP decreased in the order of livestock and poultry, rural residents and agricultural land, and the contributions to output loads of TP from livestock and poultry (44.75%-55.74%) were significantly greater than that from rural residents in Cao'e River basin, showing that the problem of fecal pollution should be paid enough attention with the rapid development of livestock and poultry breeding industry. In comparison, the contributions to output loads of TN and TP from agricultural land were smaller, but the output loads of TN and TP from cultivated land were annually greater than that from garden plot and forest land. Therefore, it was necessary to further control the excessive fertilization in agricultural land to reduce the loss of nitrogen and phosphorus. The improved export coefficient model for TN and TP in this paper had certain applicability in Zhejiang area, however, in order to further improve the accuracy of the model, it was still necessary to strengthen the monitoring of regional rainfall runoff and the study on the uncertainty of model parameters in the future.