非点源污染模型AnnAGNPS在三峡库区林农复合小流域模拟效果评定

应用连续农业非点源污染AnnAGNPS模型(Annualized AGricultural NonPoint Source Model)模拟三峡库区林农复合小流域的径流、泥沙和营养物输出,以2003年和2004年的小流域观测数据对模型分别进行校准和验证,并以统计参量决定系数(R2)、Nash-Sutcliffe效率系数(E)和相对误差(VE)对模拟结果进行评定.结果表明,径流量模型模拟结果误差在可接受范围之内,模型校准期模拟值VE值为5.0%(R2=0.93,p<0.05),验证期内模型VE值为6.7%(R2=0.90,p<0.05);与径流模拟比较,泥沙模拟结果精度较低,校准期内模型VE值为15.1%(R2=0.63,p<0.05),验证期内模型VE值为26.7%(R2=0.59,p<0.05);次降水较小,产生径流和泥沙较少时,模型模拟值则偏高,反之则偏低.氮输出模拟决定系数R2值0.68(p<0.05),略高于磷输出模拟决定系数(R2=0.65,p<0.05).模型对径流输出的模拟精度高于对泥沙和营养物的输出模拟.在三峡库区农林复合小流域应用AnnAGNPS模型模拟农业非点源污染输出满足流域管理要求.     

城市入河径流排放口总污染特征研究

流入城市雨源性河流的径流污染不容忽视,以我国南方典型城市深圳市的福田河流域为研究对象,经过18场典型降雨径流的测定,从污染过程线、径流初期效应识别和降雨事件平均浓度(EMC)等方面分析和讨论了城市河流入河径流排放口的总污染特征规律,有利于指导城市河流污染控制.结果表明,排放口地表径流浓度随时间变化历程中,COD、SS、TN、TP和BOD5普遍超出地表Ⅴ类水标准十多倍以上,某典型降雨场次的重金属(铬、镉、铜、砷和汞)污染较为严重,研究区排放口的浓度范围和平均值均高于重庆沙坪坝雨水口和加拿大Silerwood的雨水排放口,但低于武汉十里铺排放口.COD、SS、BOD5的初期效应尤为明显并且COD和SS冲刷强度较大,TN、TP初期效应不明显.COD、SS、TN、TP和BOD5的EMC浓度平均值分别为224.14、571.15、5.223、2.04、143.5 mg/L,在某种程度上,深圳市研究点的COD和SS的EMC值高于邻近的澳门、珠海,TN、TP值高于北京、广州、上海等城市,与国外的一些研究结果相比较,EMC值比韩国、美国及加拿大一些城市地表径流污染物浓度高得多,可见由排放口入河的径流总污染极其严重并需要治理.     

高速公路雨水径流重金属污染初期效应

通过对8场降雨高速公路路面雨水径流中溶解态和颗粒态Cd、Cu、Pb和Zn 4种重金属进行现场取样检测,在定性分析径流重金属污染初期效应存现的基础上,定量分析了重金属污染初期效应的显著程度,并探讨了降雨特征对径流重金属污染初期效应的影响.无因次累积负荷分数-累积体积分数曲线分析结果表明,大多数降雨事件中总重金属存在较显著的初期效应,除溶解态Pb不具有初期效应外,其余溶解态与颗粒态重金属均存在较显著的初期效应.少数降雨事件的径流在中后期存在二次冲刷效应.初期冲刷比值分析结果表明,拦截并处理径流初期25%流量(径流的体积分数,下同)可去除整个降雨事件中所排放的35%～39%(质量分数,下同)的重金属污染负荷.总重金属初期效应的显著程度顺序如下:Cd>Cu>Zn>Pb;溶解态重金属初期效应的显著程度顺序如下:Cd>Zn>Cu>Pb;颗粒态重金属初期效应的显著程度顺序为:Cu>Cd>Pb>Zn.重金属初期冲刷比值与降雨特征相关性分析表明,平均降雨强度对径流重金属污染负荷初期效应的影响显著,降雨历时、降雨量、前期晴天数和产流时间对径流重金属污染负荷初期效应的影响较小.     

高速公路路面径流沉降过程中重金属去除特性

在对南京机场高速公路令桥段2008年2月~2009年2月15场降雨事件初期路面径流进行自由沉降试验的基础上,考察了自由沉降过程中Cu、Zn、Cd、Pb 4种重金属的去除率随时间的变化特征.同时,重点分析了重金属去除与截留沉速和悬浮固体(SS)去除的关系,并探讨了降雨特征和径流pH值对重金属去除特性的影响.结果表明,沉降开始30min内Cu、Zn、Cd、Pb去除率增长迅速,30min去除率均占2h总去除率的60%以上.Pb的2h平均去除率最高,可达25.62％,Cu、Cd和Zn的2h平均去除率分别为21.20%、19.97%和19.10%.同一重金属的沉降去除率每提高10%,截留沉速范围及上限值减少5倍左右.截留沉速相同时,Pb的去除效果最好,Cd、Cu、Zn的去除效果相差不大.SS与Cu、Zn、Cd、Pb沉降去除率之间的相关性存在差异,Pb多数以颗粒态形式存在,因而SS与Pb沉降去除率相关系数最大,其相关系数为0.8126(p=0.0002）;SS与Cd、Cu、Zn沉降去除率的相关系数分别为0.6871、0.6804、0.7653.路面径流pH值对重金属去除特性的影响显著,与4种重金属沉降去除率均呈正相关,且与Zn、Cd、Pb的相关系数均大于0.5;Zn主要以溶解态形式存在,因而Zn沉降去除率受pH值影响最明显,两者在0.05水平上显著相关(p=0.029).     

Determining the robust optimal set of BMPs for urban runoff management in data-poor catchments

Mismanagement of urban runoff can result in inundation which causes serious problems in providing urban services. Best management practices (BMPs) are used for urban runoff management. In this study, a method is proposed to determine the robust optimal set of BMPs for runoff management in data-poor catchments in urban areas. This method includes five main steps: (1) Sensitivity analysis to determine effective parameters in rainfall-runoff simulation model, (2) Calibration of the rainfall-runoff model based on selected effective parameters, (3) Developing a multi-objective optimization model to obtain the optimal sets of BMPs, (4) Selecting the final solutions using the Nash approach for ranking, (5) Evaluation of the robustness of the selected solution using the Management Option Rank Equivalence method. The proposed method is examined in an urban basin located in the north of Tehran, Iran. The results show that the proposed approach provides reliable results for urban runoff management in data-poor areas.     

暴雨径流污染负荷计算的响应函数模型

暴雨径流污染具有影响面广,监测、控制和处理困难而复杂的特点,其负荷定量化是进行治理与控制的重要基础与中心环节。从我国的实际出发,建立了一个完整的流域暴雨径流污染负荷模型,包括降雨径流模型、流域产污模型与污染物迁移转化模型。野外实测资料检验表明,该模型具有计算简便、精度高、适应性强的特点。重点论述暴雨径流过程中的污染物迁移转化模型     

用人工湿地处理乳制品厂废水的研究

在进水ＣＯＤ浓度４００ｍｇ／Ｌ－８００ｍｇ／Ｌ,温度１５℃－２３℃时,人工湿地装置处理乳制品加工废水的ＣＯＤ去除率达９７％－９８％,面积负荷率达２３．３ｇ／（ｍ＾２．ｄ）－２８．２ｇ（ｍ＾２．ｄ）,ＢＯＤ５的去除率达９７％－９９％,ＢＯＤ５的面积负荷率为１２．６ｇ（ｍ＾２．ｄ）－１７．２ｇ（ｍ＾２．ｄ）,几乎７０％－９０％ＣＯＤ和ＢＯＤ５去除率发生在进水沟段。     

EVALUATION OF RUNOFF,EROSION, AND PHOSPHORUS MODELING SYSTEM—SIMPLE1

ABSTRACT: The purpose of this study was to evaluate the performance of Spatially Integrated Models for Phosphorus Loading and Erosion (SIMPLE) in predicting runoff volume, sediment loss, and phosphorus loading from two watersheds. The modeling system was applied to the 334 ha QOD subwatershed, part of the Owl Run watershed, located in Fauquier County, Virginia, and to the 2240 ha watershed, Battle Branch, located in Delaware County, Oklahoma. Simulation runs were conducted at cell and field scales, and simulation results were compared with observed data. Runoff volume and dissolved phosphorus loading were measured at the Battle Branch watershed. Runoff volume, sediment yield, and total phosphorus loading were measured at the QOD site. SIMPLE tended to underestimate runoff volumes during the dormant period, from November to March. The comparison between observed and predicted dissolved phosphorus showed better correlation than for observed and predicted total phosphorus loading. Cell level simulations provided similar estimates of runoff volume and phosphorus loading when compared to field level simulations for both watersheds. However, observed sediment yields better compared with the values predicted from the cell level simulation when compared to field level simulation. Finally, results of model evaluation indicated that SIMPLE's predictive ability is acceptable for screening applications but not for site-specific quantitative predictions.     

STAKEHOLDER INVOLVEMENT AND SOCIAL CAPITAL: KEYS TO WATERSHED MANAGEMENT SUCCESS IN ALABAMA1

ABSTRACT: Forces driving the initiation of watershed management activities in Alabama have ranged from top-down, agency-led initiatives to bottom-up, citizen-led initiatives. A number of watershed projects in Alabama were examined including three NPS projects funded by U.S. EPA grants and a more comprehensive locally-initiated watershed management authority. Watershed projects were categorized into four different models. Factors which produced significant differences in the development and utilization of social capital and local capacities for watershed management were investigated. The success of watershed management initiatives was examined qualitatively and appears to correlate with a number of social factors. These factors include the extent of stakeholder involvement, the availability of social capital in the watershed, and the presence of a real or perceived water resource concern or problem. Both short term project success and the longer term prognosis for continued watershed management activities seems to depend most upon the amount of social capital in the watershed. Two major changes in resource management programs and organizations could lead to increased focus on and support for local watershed management initiatives. These are reorganization of resource management agencies around watershed units, and assignment of at least one staff person in each watershed unit to watershed management.     

ROLE OF EROSION PROCESSES IN TRANSFER OF RADIONUCLIDES: RESULTS OF FIELD EXPERIMENTS1

ABSTRACT: An experimental one-year fieldwork has been conducted in the vicinity of the Chernobyl NPP, within an agricultural watershed, to study the transfer of radionuclides brought into the environment by the disaster of 1986. Presented are results of observation of the washout of ¹³⁷Cs from the runoff plot both in natural conditions and under artificial rainfalls. Beside traditional hydro-logical methods, new techniques were used allowing to consider microtopographical peculiarities of the runoff plot and their role in the redistribution of radionuclides. The estimate of the annual mass balance for the soil and the radionuclides within the runoff plot has shown that, regardless of significant areal variation of their concentration, the ¹³⁷Cs washout with the solid runoff resulted from artificial rainfalls amounts to some 1 percent of its reserves in the uppermost 5 cm of the topsoil. The same parameter for the natural runoff is lower by an order of magnitude. Both these factors of self-purification are about two times less than natural radioactive decay of ¹³⁷Cs.