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Benzene in Groundwater: Chemical Behavior and Treatment 地下水中苯:化学行为及处理
Pub Date : 2019-12-29 DOI: 10.1002/9781119300762.wsts0209
J. Jacobs
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引用次数: 0
Geochemistry of Great Salt Lake 大盐湖的地球化学
Pub Date : 2019-12-29 DOI: 10.1002/9781119300762.wsts0072
W. Johnson, W. Wurtsbaugh, G. Belovsky, B. Baxter, F. Black, C. Angeroth, P. Jewell, Shu Yang
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引用次数: 8
Hofmeister Effects 他认为影响
Pub Date : 2019-12-29 DOI: 10.1002/9781119300762.wsts0198
D. Parsons, Mathias Boström, Werner Kunz, B. Ninham
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引用次数: 0
Acid Mine Drainage: Sources and Treatment in the United States 酸性矿井排水:美国的来源和处理
Pub Date : 2019-12-29 DOI: 10.1002/047147844X.GW3
J. Skousen, P. Ziemkiewicz, L. McDonald
Acid mine drainage (AMD) occurs when metal sulfides are exposed to oxidizing conditions. Leaching of reaction products into surface waters pollute over 20,000 km of streams in the United States alone. Mining companies must predict the potential of creating AMD by using overburden analyses. Where a potential exists, special handling of overburden materials and quick coverage of acid-producing materials in the backfill should be practiced. The addition of acid-neutralizing materials can reduce or eliminate AMD problems. Placing acid-producing materials under dry barriers can isolate these materials from air and water. Other AMD control technologies being researched include injection of alkaline materials (ashes and limestone) into abandoned underground mines and into buried acid material in mine backfills, remining of abandoned areas, and installation of alkaline recharge trenches. Chemicals used for treating AMD are Ca(OH)2, CaO, NaOH, Na2CO3, and NH3, with each having advantages under certain conditions. Under low-flow situations, all chemicals except Ca(OH)2 are cost effective, whereas at high flow, Ca(OH)2 and CaO are clearly the most cost effective. Floc, the metal hydroxide material collected after treatment, is disposed of in abandoned deep mines, refuse piles, or left in collection ponds. Wetlands remove metals from AMD through formation of oxyhydroxides and sulfides, exchange and organic complexation reactions, and direct plant uptake. Aerobic wetlands are used when water contains enough alkalinity to promote metal precipitation, and anaerobic wetlands are used when alkalinity must be generated by microbial sulfate reduction and limestone dissolution. Anoxic limestone drains are buried trenches of limestone that intercept AMD underground to generate alkalinity. Under anoxia, limestone should not be coated with Fe+3 hydroxides in the drain, which decreases the likelihood of clogging. Vertical flow wetlands pretreat oxygenated AMD with organic matter to remove oxygen and Fe+3, and then the water is introduced into limestone underneath the organic matter. Open limestone channels use limestone in aerobic environments to treat AMD. Coating of limestone occurs, and the reduced limestone dissolution is designed into the treatment system. Alkaline leach beds, containing either limestone or slag, add alkalinity to acid water. At present, most passive systems offer short-term treatment and are more practical for installation on abandoned sites or watershed restoration projects where effluent limits do not apply and where some removal of acid and metals will benefit a stream. Keywords: acid-base accounting; acid-producing material; acid-neutralizing material; alkalinity-producing systems; anoxic limestone drains; chemical treatment; open limestone channels; passive treatment; wetlands
酸性矿井排水(AMD)发生时,金属硫化物暴露在氧化条件。仅在美国,反应产物渗入地表水就污染了2万多公里的河流。矿业公司必须通过覆盖层分析来预测产生AMD的可能性。如果存在潜在风险,应对覆盖层材料进行特殊处理,并对充填体中的产酸材料进行快速覆盖。加入酸中和材料可以减少或消除AMD问题。将产酸物质置于干燥的屏障下可以使这些物质与空气和水隔绝。正在研究的其他AMD控制技术包括将碱性物质(灰烬和石灰石)注入废弃的地下矿山和矿山回填区的埋藏酸性物质,开采废弃区域,以及安装碱性补给壕。用于治疗AMD的化学物质有Ca(OH)2、CaO、NaOH、Na2CO3和NH3,每种化学物质在一定条件下都具有优势。在低流量情况下,除Ca(OH)2外的所有化学品都具有成本效益,而在高流量情况下,Ca(OH)2和CaO显然是最具成本效益的。絮凝体,即处理后收集的金属氢氧化物材料,被弃置在废弃的深矿、垃圾堆或留在收集池中。湿地通过形成氢氧化物和硫化物、交换和有机络合反应以及直接植物吸收来去除AMD中的金属。当水含有足够的碱度以促进金属沉淀时使用好氧湿地,当必须通过微生物硫酸盐还原和石灰石溶解产生碱度时使用厌氧湿地。缺氧石灰石排水沟是埋在地下的石灰石沟槽,它拦截AMD以产生碱度。在缺氧情况下,石灰石不应在排水管中涂上铁+3氢氧化物,这样可以减少堵塞的可能性。垂直流湿地用有机物对含氧AMD进行预处理,去除氧和铁+3,然后将水引入有机物下面的石灰岩中。开放的石灰石通道在有氧环境中使用石灰石来治疗AMD。发生石灰石涂层,并将石灰石还原溶解设计到处理系统中。含有石灰石或矿渣的碱性浸出床向酸性水中添加碱度。目前,大多数被动系统提供短期处理,更实用的是安装在废弃场地或流域恢复项目上,因为这些地方不适用排放限制,而且一些酸和金属的去除将有利于河流。关键词:酸碱核算;制造酸性物质材料;acid-neutralizing材料;alkalinity-producing系统;缺氧石灰石排水;化学处理;开阔的石灰岩河道;被动治疗;湿地
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引用次数: 0
Arctic Shipping and Polar Seaways 北极航运和极地航道
Pub Date : 2019-12-29 DOI: 10.1002/9781119300762.wsts0098
Julie Babin, F. Lasserre, P. Pic
Climate change in the Arctic triggered a series of discourses about the opening up of a previously unreachable region. The long-fantasized northern routes would be on the verge of becoming actual seaways as a consequence of the melting of sea ice. In reality, navigation remains difficult in the Arctic, transits are still very limited, as sea ice is still a major constraint. The passages have always intrigued though, provoking fascination as early as when the Vikings reached the western coast of Greenland, to the vivid reaction to the Russians planting a flag on the North Pole in 2007. With climate change, the Arctic is being scrutinized more than ever; hence, the numerous discourses about navigation in particular. In this article, we analyze the development of both the Northwest Passage (NWP) and the Northern Sea Route (NSR). We then investigate the recent trends in Arctic shipping in order to put those discourses into perspective and portray the current tendency.
北极的气候变化引发了一系列关于开放这个以前无法到达的地区的讨论。由于海冰融化,人们长期幻想的北方航线即将成为真正的海上航线。在现实中,北极地区的航行仍然困难,过境仍然非常有限,因为海冰仍然是一个主要制约因素。然而,这些段落一直很吸引人,早在维京人到达格陵兰岛西海岸时就激起了人们的兴趣,直到2007年俄罗斯人在北极插上国旗时的生动反应。随着气候变化,北极受到的关注比以往任何时候都多;因此,有许多关于导航的论述。本文对西北航道(NWP)和北海航道(NSR)的发展进行了分析。然后,我们调查了北极航运的最新趋势,以便将这些话语纳入视角并描绘当前的趋势。
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引用次数: 4
Applications of Stable Isotopes to Studies of Paleohydrology and Paleoclimatology 稳定同位素在古水文和古气候学研究中的应用
Pub Date : 2019-12-29 DOI: 10.1002/9781119300762.wsts0042
Zhengyu Xia, Zicheng Yu
The term isotope, derived from Greek, means occupying the same position in the periodic table. Isotopes are variant forms of a particular chemical element that have the same number of protons (atomic number) but differ in the number of neutrons in the atomic mass. Isotopes come in two basic types: radioactive (unstable) and stable. Radioactive isotopes are nuclides that are unstable and spontaneously decay into other new isotopes, whereas stable isotopes are nuclides that do not appear to decay radioactively. Hydrogen and oxygen have a number of isotopes, including radioactive and stable isotopes. The two stable isotopes of hydrogen, 1H and 2H (also called deuterium and denoted as D), have natural abundances of 99.9885% and 0.0115% in hydrosphere, respectively. The third isotope of hydrogen, 3H (tritium), is unstable with a half-life of 12.23 years. The stable isotopes of oxygen, including 16O, 17O, and 18O, have natural abundances of 99.762%, 0.0379%, and 0.200% in hydrosphere, respectively. Other isotopes of oxygen are radioactive and very short-lived. In isotope geochemistry, it is a convention to use the atomic abundance ratio of the rare isotope to the major isotope (e.g. 18O/16O, 2H/1H) relative to a standard of known isotopic composition to describe the isotopic composition of samples as: δ (in ‰) = ( Rx Rs − 1 ) × 1000
同位素这个词来源于希腊语,意思是在元素周期表中占据相同的位置。同位素是一种特定化学元素的变体,具有相同数量的质子(原子序数),但原子质量中的中子数不同。同位素有两种基本类型:放射性(不稳定)和稳定。放射性同位素是不稳定的核素,会自发衰变为其他新同位素,而稳定同位素是似乎不会发生放射性衰变的核素。氢和氧有许多同位素,包括放射性同位素和稳定同位素。氢的两种稳定同位素1H和2H(又称氘,用D表示)在水圈中的自然丰度分别为99.9885%和0.0115%。氢的第三种同位素3H(氚)是不稳定的,半衰期为12.23年。氧的稳定同位素16O、17O和18O在水圈中的天然丰度分别为99.762%、0.0379%和0.200%。氧的其他同位素是放射性的,寿命很短。在同位素地球化学中,通常使用稀有同位素与主要同位素(如18O/16O, 2H/1H)相对于已知同位素组成标准的原子丰度比来描述样品的同位素组成:δ(‰)= (Rx Rs−1)× 1000
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引用次数: 2
Arsenic in Groundwater: Chemical Behavior and Treatment 地下水中的砷:化学行为和处理
Pub Date : 2019-12-29 DOI: 10.1002/9781119300762.wsts0218
David B. Vance, J. Jacobs
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引用次数: 0
Groundwater Flow 地下水流动
Pub Date : 2019-12-29 DOI: 10.1002/9781119300762.wsts0075
O. Strack
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引用次数: 0
Environmental and Public Health Issues: Community Engagement in Environmental Justice Populations 环境和公共卫生问题:社区参与环境正义人口
Pub Date : 2019-12-29 DOI: 10.1002/9781119300762.wsts0183
M. Neet, Jamelle H. Ellis, Zachary H. Hart, Geoffrey I. Scott, D. Friedman, R. H. Kelsey, D. Porter
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引用次数: 0
Mercury in Water 水中汞
Pub Date : 2019-12-29 DOI: 10.1002/9781119300762.wsts0001
B. Gu, Xia Lu, A. Johs, E. Pierce
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引用次数: 2
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