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261.
Assessment of fates of estrogens in wastewater and sludge from various types of wastewater treatment plants 总被引:1,自引:0,他引:1
We measured five estrogens in the wastewater samples from the municipal wastewater treatment plants (M-WWTPs), livestock wastewater treatment plants (L-WWTPs), hospital WWTPs (H-WWTPs) and pharmaceutical manufacture WWTPs (P-WWTPs) in Korea. The L-WWTPs showed the highest total concentration (0.195-10.4 μg L−1) of estrogens in the influents, followed by the M-WWTPs (0.028-1.15 μg L−1), H-WWTPs (0.068-0.130 μg L−1) and P-WWTPs (0.015-0.070 μg L−1). Like the influents, the L-WWTPs (0.003-0.729 μg L−1) and the M-WWTPs (0.001-0.299 μg L−1) also showed higher total concentration of estrogens in the effluents than the H-WWTPs (0.002-0.021 μg L−1) and P-WWTPs (0.011 μg L−1 in one sample). The L-WWTPs (37.5-543 μg kg−1, dry weight) showed higher total concentrations in sludge than the M-WWTPs (3.16-444 μg kg−1, dry weight) like the wastewater. The distribution of estrogens in the WWTPs may be affected by their metabolism in the human body, their transition through biological treatment processes, and their usage for livestock growth. Unlike the concentration results, the daily loads of estrogens from the M-WWTPs were the highest, which is related to the high capacities of WWTPs. 相似文献
262.
Lee TG Eom Y Lee CH Song KS 《Journal of the Air & Waste Management Association (1995)》2011,61(10):1057-1062
A simple and highly effective stabilization/solidification (S/S) technology of elemental mercury using only sulfur with paraffin is introduced. First, elemental mercury is mixed with an excess of sulfur powder and heated to 60 degrees C for 30 min until elemental mercury is converted into mercuric sulfide (HgS black, metacinnabar) (Step 1). Then, metacinnabar with additional sulfur is poured into liquid paraffin (Step 2). Finally, the mixture is melted at 140 degrees C and settles to the bottom of the vessel where it cools and solidifies under the layer of liquid paraffin (Step 3). The proposed S/S method with sodium sulfide nonahydrate (Na2S x 9H2O) as an additive is also tested for comparison. The average toxicity characteristic leaching procedure test values are 6.72 microg/L (no additive) and 3.18 microg/L (with additive). Theses concentrations are well below the Universal Treatment Standard (25 microg/L). Effective diffusion coefficient evaluated from accelerated leach test and average headspace concentration of Hg vapor after 18 hr are 3.62 x 10(-15) cm2/sec, 0.55 mg/m3 (no additive) and 5.86 x 10(-13) cm2/sec, 0.25 mg/m3 (with additive). 相似文献
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采用溶胶凝胶法制备LixNi1-xO和ZnO粉体,利用球磨法制备ZnO/LixNi1-xO复合粉体,以紫外光为光源,通过降解甲基橙,研究了锂掺杂及n-p复合对氧化镍的光催化性能影响。结果表明:当投放量为0.1 g/L,x≤0.075(摩尔分数)的锂掺杂氧化镍均比未掺杂氧化镍的光催化活性高。当锂掺杂摩尔分数为0.025,投放量为0.4 g/L时锂掺杂氧化镍的光催化活性最佳,甲基橙最高降解率达到93.1%。当ZnO/Li0.025Ni0.975O在质量比为1∶1,投放量为0.2 g/L时光催化活性最佳,甲基橙最高降解率达到98.1%。 相似文献
266.
The moisture from skin sweat and atmospheric water affects the thermal protective performance provided by multilayer protective clothing. Four levels of moisture content were selected to evaluate the impact of moisture on thermal protection under dry (thermal radiation) and wet (thermal radiation and low-pressure steam) heat exposure. Also, the role of moisture and its relationship with exposure time were analyzed based on skin heat flux and Henriques integral value. The addition of moisture to a fabric system was found to result in differences in second-degree and third-degree skin burn times. When moisture is added to a fabric system, it both acts as a thermal conductor to present a negative effect and provides a positive effect owing to thermal storage of water and evaporative heat loss. The positive or negative effects of moisture are mainly dependent on the thermal exposure time, the moisture content and the presence of hot steam. 相似文献
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荷兰浅水湖的生态恢复实践 总被引:3,自引:0,他引:3
湖泊的富营养化导致了湖泊生态系统的失衡。要使湖泊获得生态恢复,只通过控制入湖的营养负荷是不够的。荷兰的实践证明,外部营养负荷的大量减少并没有带来预期的恢复效果,而通过湖泊的换水和生物控制,湖泊的透明度、水生植物等得到了迅速改善。根据荷兰方面提供的资料,介绍了荷兰通过换水和生物控制进行浅水湖的生态恢复实践和取得的经验。 相似文献
269.
中国红十字会是中国整体灾害应急体系的重要组成部分,建立健全红十字会应急体系建设对备灾、应急工作至关重要。中国红十字会应急体系建设主要包括红十字会应急预案、应急物资储备系统、应急救援队伍、应急宣传培训与演练、信息传递系统等。红十字会应急体系建设也存在应急预案的不健全和缺乏针对性、物资储备系统有待健全、应急队伍建设有待加强、应急救护体系不协调等不足。本文从改革和健全红十字会应急预案、大力发展红十字应急组织、深入推进红十字会物资储备库建设、普及全民应急救护、健全红十字应急网络、学习西方国家经验等方面提出加强红十字会灾害应急工作的对策建议。 相似文献
270.