测绘技术服务于生猪养殖业环保整治的探讨

近年来,生猪养殖业陆续开展了生猪禁养工作。通过划定生猪禁养区域,对禁养区内的"散、小、乱"养猪场进行清拆和整顿,再引进大型现代化生猪养殖场来发展企业化、规范化的生猪养殖是整治工作的常见思路,需要精准的数据、科学的理论作为支撑。本文以广州市增城区为例,从生猪禁养范围图制作和专题数据统计两方面探讨了测绘技术在生猪养殖业环保整治工作中的应用。通过数据提取、缓冲区分析、叠加分析、面的差异运算、地图编制等测绘技术的综合应用,证实了其服务于生猪养殖业环保整治工作的实用性、高效性和科学性,为各省市开展生猪养殖业环保整治工作提供了翔实的参考资料。     

Spatial variability of soils and stream sediments and the remediation effects in a Portuguese uranium mine area

The old Senhora das Fontes uranium mine, located in central Portugal, was closed down in 1971. The treatment of ores from this mine and other mines by heap-leach ended in 1982. Seven dumps partially covered by vegetation were left in the area. Soil and stream sediment samples were collected in December 2009. The remediation was carried out from May 2010 to January 2011. Stream sediment samples were collected again in October 2013. Before the remediation, soils from inside the mine influence area have higher Al, As, Co, Cr, Cu, Fe, Ni, Sr, Th, U and Zn concentrations than soils from outside this area, due to radionuclides, metals and metalloid released from the mine dumps. The principal component analysis (PCA) shows a distinction between soils from inside and outside the mine influence area. The U(VI), As(V) and metals from soils can be adsorbed to Fe-oxyhydroxides and the humic acid can increase the U uptake. Soils must not be used for public or private green and residential areas, because they are contaminated in U, As, Co, Cd and Ni. Before the remediation, downstream sediments have higher Al, As, Cu, Mn, Ni, Pb, U and Zn than upstream sediments, due to erosion and percolation of water through the mine dumps. The PCA shows a distinction between downstream and upstream sediments. The U(VI), Th and As(V) can be adsorbed to Fe-oxyhydroxides. The stream sediments are contaminated in As, Mn, Th and U. Downstream sediments are the most contaminated in U and As. After the remediation, upstream and downstream sediments have generally higher Al, Fe, As, Cr, Ni, Th, U and Zn concentrations than before the remediation, attributed to the relocation of dumps. Radionuclides, metals and metalloids were transported by surface water. Consequently downstream sediments have higher Al, As, Cu, Mn, Ni, Th, U and Zn concentrations than upstream sediments. The U(VI), Th and As(V) can be adsorbed to Fe-oxyhydroxides. Stream sediments became more contaminated in U, Th and As than before the remediation, but more intensively downstream.     

内蒙古包头某铁矿尾矿库生态修复的植物优选研究

【研究目的】植物修复技术因其具有绿色、经济、环保的特点,在矿山生态修复中应用广泛,而调查和筛选矿山周边适应本地生境的植物物种是进行植物生态修复的关键环节。【研究方法】通过野外调查取样和室内分析测试相结合的方法,对内蒙古包头某废弃铁矿尾矿库及周边11种优势植物的重金属含量、重金属迁移富集能力及其上覆土壤重金属特征进行分析研究,以期筛选优良修复植物,为矿区生态修复提供科学依据。【研究结果】该废弃铁矿尾矿库及周边土壤Fe、Mn、Cu、Pb、Zn、Cr、Cd、F含量均远超过河套平原土壤背景值,地累积指数显示污染等级为2～7级,污染程度从轻—中度污染到极强度污染。植物地下部分各元素含量总体上高于地上部分,除Cu外各植物重金属含量大多超出了正常值范围。【结论】沙蒿和独行菜具有富集型植物特征,玉米、狗尾草、虎尾草和拂子茅属于根部囤积型,碱蓬、灰条菜、苍耳、新疆杨和红柳符合规避型植物特征。可根据植物对重金属的吸收和富集特点,科学合理地选择适宜的植物进行矿区受污染土壤植物修复。创新点：研究了废弃铁尾矿库及周边11种优势植物的重金属特征;揭示了优势植物对重金属的吸收机制。     

MICP技术联合多孔硅吸附材料对锌铅复合污染土固化/稳定化修复的试验研究

近年来,工业和科技的快速发展使得重金属污染土固化/稳定化的修复研究成为热点。运用微生物诱导碳酸钙沉淀(MICP)技术联合吸附材料对锌铅复合重金属污染土进行固化/稳定化的修复,通过无侧限抗压强度试验、毒性浸出试验,评价处理前后污染土的固化效果与重金属的稳定化效果,结合扫描电镜(SEM)和X射线衍射(XRD)等检测手段,揭示MICP技术处理锌铅重金属污染土的修复机制。研究结果表明,采用MICP技术对锌铅重金属污染土进行固化/稳定化之后,可以有效降低污染土中有害重金属的浸出性。当矿化时间为10d时,试样无侧限抗压强度为942.5k Pa;铅的浸出浓度为4.20mg/L,比未处理时降低了44.81%;锌的浸出浓度为4.31mg/L,比未处理时降低了46.19%,效果显著。在此基础上,添加10%的多孔硅吸附材料后,试样无侧限抗压强度可达到1 021 kPa,强度提高了8.3%;铅的浸出浓度为2.45mg/L,与未经处理时相比,降幅达到了67.81%,与单纯MICP方法处理时相比,铅浸出浓度被二次降低了41.67%;锌的浸出浓度仅为2.93 mg/L,与未经处理时相比,降幅达到了63.4%,与单纯...     

凹凸棒石用于修复铜锌镉重金属污染土壤的研究

利用凹凸棒石黏土矿物优异的物化性能对采集的安徽铜陵地区重金属污染土壤进行盆栽修复试验,以降低种植蔬菜中重金属污染物的有效态含量。凹凸棒石与矿区土壤的质量配比设置5组(1∶10、1∶20、1∶40、1∶100以及原土),选择适宜在北京生长的四季小白菜和北京快菜进行种植,盆栽试验结果表明,使用凹凸棒石黏土矿物可以将土壤的pH值提高到5～8,改善了矿区的土壤环境条件,提高黏土矿物对重金属的吸附性能;通过适量添加凹凸棒石黏土矿物,对Cu元素的平均修复率达到31.50%,Zn元素的平均修复率达到26.15%,Cd元素的平均修复率达到34.92%,能够有效减少蔬菜对Cu、Zn、Cd三种重金属元素的吸收。凹凸棒石与土壤的质量比为1∶20时,对污染土壤的修复效果最佳。     

土壤污染修复技术探讨

在综述我国土壤污染现状的基础上,分析了土壤污染的主要来源、特点,介绍了污染土壤的修复技术,并对各种修复方法的应用特点作了比较。     

Landslide hazard of slopes of sewage treatment plant lagoons constructed in colluvium deposits

A landslide occurred in colluvial deposits at one of the lagoons of Wadi Es-Sir Sewage Treatment Plant Project (under construction) in Jordan. This paper summarizes the geotechnical investigations conducted at three lagoon sites in the project area including the failed lagoon. Results of stability analyses are presented along with recommendations to stabilize the slided lagoon and surrounding areas.     

Lead contamination of soil along road and its remediation

With a rapid development of road systems and an associated drastic increase in number of automobiles, the traffic has induced more and more obvious environmental pollution such as noise, dust, emission and heavy metal contamination. Lead, as one of the most harmful heavy metal contaminants, can execute a significant impact on soil quality and plant growth, depending on its form, as well as its transport and accumulation in soil. This paper describes the source and characteristics of Pb contaminant in soil along a road, and reviews the results of research on remediation of Pb-contaminated soils, aiming at identifying promising approaches to soil remediation along roads.     

Electrokinetic remediation of an electroplating site: design and scale-up for an in-situ application in the unsaturated zone

In-situ electrokinetic remediation of contaminated soils requires integrated approaches and adequately engineered setups to control relevant mass fluxes. Based on laboratory findings, this study presents the design of a pilot-scale remediation at an operating electroplating site. The fine-textured soil developed from Jurassic limestone exhibits a chromium, copper, nickel, and zinc contamination down to depths of more than 4 m. The feasibility of an electrokinetic remediation in the unsaturated zone was tested in a lab-scale experiment with subsoil material sampled at the site. The electrodes were placed in water-impermeable, ion-selective membrane wells. This construction allows the necessary watering of the electrodes, maintains unsaturated conditions in the soil compartment, and enables the transfer of contaminant ions into the wells. In addition, the soil is protected from pH changes caused by water electrolysis at the electrodes. The setup includes a watering and drainage system to compensate the electroosmotic water flux and impede desiccation of the anodic region. With a direct current of 70 V and an electric field strength of 2.2 V cm⁻¹, contaminant removal rates amounted up to 27% and 66% (w/w) of the initial zinc/copper and chromium/nickel concentrations. Copper, nickel, and zinc accumulated in the cathode well, while chromate species were enriched in the anode well. Given the successful lab-scale remediation, the pilot plant was designed for the in-situ treatment of a soil volume of 12 m³ below a production hall. A power of 500 V DC at a maximum current of 30 A is supplied by a transformer rectifier. This yields an electric field strength comparable to the lab-scale experiment and thereby similar contaminant transport velocities. A vacuum distillation unit is employed for process water reuse and to control electrolyte conductivity. To cope with chlorine gas generation at the anodes a gas absorber unit is employed. According to the lab-scale results, about 2, 9, 9, and 15 kg zinc, chromium, copper, and nickel, respectively, are expected to be removed from the field plot during an operation time of 10 months.     

Mercury concentrations in a contaminated river system in Kazakhstan and biomonitoring of the local population

The River Nura in central Kazakhstan has been heavily contaminated by mercury （Hg） from an acetaldehyde plant located in the industrial city of Temirtau. The plant released Hg-containing wastewater into the river from the 1950s until the mid 1990s and strongly contaminated the bed sediments up to 25 km downstream. In addition, a local power station released an estimated 6 million tonnes of fly-ash into the water which has adsorbed much of the Hg and has become mixed with the natural sediments. River water,fish and agricultural land in the floodplain are also contaminated by Hg. Humans are exposed to Hg primarily via the consumption of contaminated fish from the river. A survey was undertaken in June/July 2005 to investigate Hg concentrations in river water, drinking water, sediments and fish. To estimate the risk posed to the local population, approximately 300 hair samples were collected from people living in villages near the most contaminated section of the river, at a distance of between 5 and 30 km downstream of the acetaldehyde plant, and their dietary habits were recorded. Mercury concentrations in river water ranged from 2-3 ng/L upstream of the source of the pollution to 348 ng/L downstream of the factory outfall pipe. Some drinking water wells close to the river were contaminated, but deeper wells had Hg concentrations below the detection limit.