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缺水地区人类活动净氮输入与河流响应特征——以海河流域为例
引用本文:陈岩,高伟,王东,刘永,吴悦颖,郭怀成.缺水地区人类活动净氮输入与河流响应特征——以海河流域为例[J].环境科学学报,2016,36(10):3600-3606.
作者姓名:陈岩  高伟  王东  刘永  吴悦颖  郭怀成
作者单位:1. 北京大学, 环境科学与工程学院, 北京 100871;2. 环境保护部环境规划院, 北京 100012,云南大学, 生态学与环境学院, 昆明 650091,环境保护部环境规划院, 北京 100012,北京大学, 环境科学与工程学院, 北京 100871,环境保护部环境规划院, 北京 100012,北京大学, 环境科学与工程学院, 北京 100871
基金项目:国家水体污染控制与治理科技重大项目(No.2013ZX07102-06);国家自然科学基金(No.41222002)
摘    要:人类活动净氮输入(NANI)是影响河流氮输出的重要因素,研究两者的响应关系对制定氮污染的削减策略具有重要意义.基于NANI核算模型,评估了海河流域人为氮输入强度,并采用实测数据估算了同期的河流氮输出,最终得到干旱缺水区河流氮输出对NANI的响应特征.结果表明,海河流域2008—2012年均NANI输入强度为13258 kg·km~(-2)·a~1,化肥施用、食品与饲料输入、大气沉降和农作物固氮分别占76%、17%、5%和2%;在空间分布上,黑龙港运东子流域的NANI负荷最高,达到24238 kg·km~(-2)·a~(-1),最小的是永定河子流域,为5320 kg·km~(-2)·a~(-1);海河流域主要河流的氮通量与子流域NANI输入呈现显著正相关关系(p0.05),NANI变化可解释67%的河流氮通量变化.然而,仅2%的NANI由河流输出,这一比例低于其他地区研究成果,表明缺水地区河流作为氮输出的功能被削弱,河流不是流域氮输出的主要途径.

关 键 词:人类活动净氮输入(NANI)  物料平衡  非点源  干旱区  海河流域
收稿时间:2016/1/13 0:00:00
修稿时间:3/7/2016 12:00:00 AM

Net anthropogenic nitrogen inputs (NANI) and riverine response in water shortage region:A case study of Haihe River watershed
CHEN Yan,GAO Wei,WANG Dong,LIU Yong,WU Yueying and GUO Huaicheng.Net anthropogenic nitrogen inputs (NANI) and riverine response in water shortage region:A case study of Haihe River watershed[J].Acta Scientiae Circumstantiae,2016,36(10):3600-3606.
Authors:CHEN Yan  GAO Wei  WANG Dong  LIU Yong  WU Yueying and GUO Huaicheng
Institution:1. College of Environmental Sciences and Engineering, Peking University, Beijing 100871;2. Chinese Academy For Environmental Planning, Beijing 100012,School of Ecology and Environmental Science, Yunnan University, Kunming 650091,Chinese Academy For Environmental Planning, Beijing 100012,College of Environmental Sciences and Engineering, Peking University, Beijing 100871,Chinese Academy For Environmental Planning, Beijing 100012 and College of Environmental Sciences and Engineering, Peking University, Beijing 100871
Abstract:Net anthropogenic nitrogen inputs (NANI) is considered a significant factor influencing riverine N export, and exploring their relationship is key to make countermeasures of mitigating N pollution. The relationship between NANI and riverine N export was established for the Haihe River Basin, where the former was calculated using NANI model and the latter was estimated based on monitoring data. Results indicate that i) the NANI in Haihe River watershed reaches 13258 kg·km-2·a-1 averaged from 2008 to 2012; ii) synthetic fertilizer, food/feed imports, atmospheric deposition, and agricultural fixation accounts for 76%, 17%, 5% and 2% of NANI, respectively; iii) Heilonggang River-Yundong Canal sub-watershed was ranked as the highest hotspot with NANI of 24238 kg·km-2·a-1, whereas Yongding River sub-watershed was the area with the lowest NANI of 5320 kg·km-2·a-1; iv) 67% variation of riverine N exports could be explained by the NANI (p<0.05). However, only 2% of NANI was exported by rivers according to the regression, which is much lower than the results from other case studies, indicating that river is not a significant output of watershed N in arid regions.
Keywords:net anthropogenic nitrogen inputs (NANI)  mass balance  non-point source  arid region  Haihe River watershed
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