THE DISCHARGE OF SEDIMENT IN CHANNELIZED ALLUVIAL STREAMS1

ABSTRACT: Approximately 400 million cubic feet of channel sediments have been delivered to the Mississippi River from the Obion-Forked Deer River system in the last 20 years. The discharge of sediment from these channelized networks in West Tennessee varies systematically with the stage of channel evolution. Variations in yields over time reflect the shifting dominance of fluvial and mass-wasting processes as the networks adjust to lower energy conditions. Maximum bed-material discharges occur during the initial phases of degradation (Stage III). In contrast, yields of suspended-sediment peak during the threshold stage (Stage 1V: large-scale mass wasting) as sediments are delivered from main-channel banks and tributary beds. Suspended-sediment yields then decrease as aggradation (Stage V) becomes the dominant trend in the main channels, but remains relatively high through restabiliza-tion (Stage VI) because of continued degradation and widening in the tributaries. Bed-material discharges decrease from the degradation stage (III) to Stage V, and increase again during restabiliza-tion (Stage VI) because secondary aggradation increases gradients and incipient meandering serves to rework bed sediments. This secondary maxima in bed-material discharge is analogous to those described previously as complex, or oscillatory, response. The trends of sediment production and transport described from these rejuvenated networks are in agreement with experimental and theoretical results of earlier investigations.     

Local Area Quotas for Industrial Emissions along Reaches of the Pearl River in Guangdong

There is an obvious departure from the regional equilibrium of developments between the upper and lower reaches of the Pearl River in Guangdong, which resulted in ＂the effects of contra-geography-grads development＂. It is mainly because the upriver mountainous areas have been deeply stuck in industrialization delay and marginalization plights, so that nearly 40 million local people have conceived a dream to get rid of ＂the vicious circle of poverty＂ by speeding up industrial development. But the problem is that such industrialization efforts on a large scale in mountainous areas are encountering the bottleneck of environmental capacity that strictly limits industrial emissions along the upper reaches of any water system. As a solution, an institutional arrangement called ＂the Local Area Quotas for Industrial Emissions along the Pearl River＂ is put forward supposed to give corresponding compensation to the rights of industrial development yielded by some areas with lower environmental capacity through the distribution and trading of IDQs.     

管式电除尘器“伞形罩”结构的应用

本文通过分析立式管式电除尘器结构及使用现状 ,总结其失效的主要原因在于阳极 (圆筒管 )的清灰不力。为解决清灰不力的问题 ,提出了“伞形罩”阳极结构 ,其具有的不积尘、自动排灰功能 ,经实践检验 ,效果显著     

乡镇工业电镀行业主要污染物排放量的估算方法

电镀分有氰电镀与无氰电镀两类。乡镇工业电镀行业的环境污染最主要是氰污染和铬污染。本文针对乡镇电镀行业的特点,调查了湖南省沅江市、四川省新都县、湖北省黄陂县、汉川县以及江苏省部分县市乡镇电镀厂,将收集资料及实际监测资料进行回归分析,得出乡镇电镀行业的污染物发生量大小与原材料的消耗有关,可以用多元回归方程估算乡镇电镀行业主要污染物发生量。这一估算方法简单易行,实用可靠,操作方便。     

应用指数平滑法建立城市工业三废排放量预测模型

指数平滑法是常用的一种时间序列预测方法，但用于环境预测的先例则较少。本文以南通市１９８１－１９９０年工业三废排放量时间序列为例，简要介绍了该法的原理以及平滑计算、建模、预测和精度分析的过程，并对其在环境预测中的应用效果进行了探讨，结果表明，该法与目前环境预测中常用的回归法相比，具有数据来源较易，不需要特殊分布，计算简单，精度较高等明显的优点，充分显示出该法在环境预测中应用的可行性。     

长江干支流输沙量减少趋势及其影响因素浅析

通过对长江干支流各主要水文控制站的多年径流量、输沙量、含沙量、中值粒径等水沙基本特征值的统计分析，表明在过去的近50年时间内，长江干支流的年径流量中心趋势不存在具有显著统计意义的变化，而输沙量、含沙量、中值粒径值均有明显的下降态势。以水库建设和水土保持为主的人类活动是长江干支流泥沙输移量减少趋势的重要影响因素，在20世纪90年代以前长江输沙量的减少主要是水库建设的影响，之后随着“长治”工程的展开则兼具了水库建设和水土保持的影响，未来水土保持工作对长江保水减沙的长期效益将更为显著。     

乌江干流中上游水电梯级开发水温累积效应

以乌江流域洪家渡库尾至乌江渡坝下的水电工程干扰典型段为研究区域，利用建坝前后的水温实测资料，采用建坝前天然水温和建坝后下泄水温比较法，对乌江干流梯级水库水温时空分布特征进行分析。研究结果表明：对天然水温改变最大的电站为洪家渡和乌江渡，前者是受水库水温结构自身影响，后者是梯级联合运行的结果；梯级联合运行使库区水温分层有所减弱，随着时间的推移或上游梯级电站的建成，电站下泄水温年变化过程趋于均化，与天然水温的延迟也越加明显；不同的水库水温结构对水温累积效应的影响也各不相同，稳定分层型水库对水温累积具有正效应，混合型水库具有负效应，过渡型水库处于两者之间，体现了梯级电站的水温累积影响，为研究减缓下泄低温水的对策措施提供依据和参考。     

基于地表水源热泵尾水排放的江河热环境容量研究

运用FLUENT软件对重庆市洪崖洞水源热泵系统尾水排入受纳水域的过程进行二维数值模拟,选取FLUENT中非耦合、隐式求解器对模型内的定常流动进行求解,得出受纳水域受水源热泵系统温排水影响后的温度梯度和温升面积。在温排水流量为4 500 m3/h、温差为6℃的条件下,得出受纳水域温升值超过1℃的水域面积约为1 600 m2,为模拟江河水域面积的2.0%。选取1℃温升值作为温升带边界控制值,在热泵系统最大负荷工况下,计算得出受纳水域的热环境容量为312.5(m.3℃)/s,剩余热环境容量为306.25(m.3℃)/s。根据地表水环境质量标准,该工程温排水量小于受纳水域的热承载力,不会对受纳水域生态环境造成热污染。     

太阳模拟器大功率短弧氙灯放电特性试验测试

目的增强太阳模拟器氙灯驱动运行的可靠性,给太阳模拟器研制提供技术保障,针对太阳模拟器大功率短弧氙灯放电特性进行试验研究。方法设计太阳模拟器的大功率短弧氙灯放电特性测试方法,然后通过理论计算和实际测试验证氙灯电源初始电流对短弧氙灯放电特性的影响,并采用增设优化电路的方法对其放电特性进行改善。结果在初始电流为70 A和120 A两种情况下,弧光放电电流到达谷值以后的电流稳定度分别为1.8616和0.9867,增设优化电路后,再次进行短弧氙灯放电特性测量,将初始电流降低到60 A,而稳定度可达到0.5409。结论改善后的电路基本可实现短弧氙灯放电理想状态,完成了对短弧氙灯进入电流击穿阶段后形成的稳定弧光放电电流特性的优化,大大提升了氙灯点灯成功率,为增强太阳模拟器可靠性提供了试验支持。     

AGRICULTURAL LEGISLATION'S POTENTIAL IN REDUCING DISCHARGE OF POLLUTANTS1

ABSTRACT: Agricultural lands (including most forest lands) make up almost four-fifths of the total land area of the United States and include, or are traversed by, perhaps an equal proportion of our ground and surface waters. Therefore, a very large part of our environment is directly “agriculture-related” in any consideration of the discharge of pollutants. Several important Federal and State laws relate to the control or abatement of agriculture-related pollution. Existing legislation generally mandates the control or abatement of pollution (from point or nonpoint sources) or authorizes the use use of public funds or other resources for such purposes. Some of these laws can be effective instruments in keeping pollutants from being discharged into surface or ground waters or into the air, but the degree to which some pollutants originating from agricultural lands and operations constitute a serious environmental hazard in waters remains controversial. Although most of the technology exists to reduce greatly the movement of these pollutants, investments are often required which benefit the nonfarm public without economic returns to the farmer. Whether a zero discharge is either an environmentally or economically feasible alternative to more limited or selective control, is explored. However, if the public is willing to bear its reasonable share of the cost for clean air and water, the needed basic legislation already largely exists. Under it, agricultural land holders may apply program standards and use their own and available program resources to bring about effective control or abatement of pollutants.