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111.
纳米塑料作为一种新兴污染物在水中可长久稳定存在,其表面吸附的重金属对水环境产生了潜在危害.本文研究了纳米塑料聚苯乙烯微球在吸附时间、溶液pH、氯化钠溶液、锰离子、温度等不同实验条件下对铅离子的吸附行为.结果表明,粒径为400 nm的单分散聚苯乙烯微球可快速吸附铅离子,吸附平衡时间约为30 min,吸附率达到53.30%.聚苯乙烯微球对铅离子的吸附动力学符合伪一级动力学,吸附等温线遵循Freundlich模型,吸附过程主要为非线性吸附.随着溶液pH的增加,铅离子平衡吸附量增加,静电作用是影响铅离子在聚苯乙烯微球上吸附的关键因素.增加溶液盐浓度,微塑料发生聚集,比表面积减小,吸附位点减少,铅离子的吸附量显著降低,在3.5%氯化钠溶液中,纳米塑料对铅离子的吸附率仅为7.5%.与重金属锰离子共存,可促进聚苯乙烯微球对铅离子的吸附.升高温度,纳米塑料对铅离子的平衡吸附量增加. 相似文献
112.
The purpose of this study is to present a library of analytical solutions for the three-dimensional contaminant transport in uniform flow field in porous media with the first-order decay, linear sorption, and zero-order production. The library is constructed using Green’s function method (GFM) in combination with available solutions. The library covers a wide range of solutions for various conditions. The aquifer can be vertically finite, semi-infinitive or infinitive, and laterally semi-infinitive or infinitive. The geometry of the sources can be of point, line, plane or volumetric body; and the source release can be continuous, instantaneous, or by following a given function over time. Dimensionless forms of the solutions are also proposed. A computer code FlowCAS is developed to calculate the solutions. Calculated results demonstrate the correctness of the presented solutions. The library is widely applicable to solve contaminant transport problems of one- or multiple- dimensions in uniform flow fields. 相似文献
113.
114.
以互花米草为原料,采用中温(35±1)℃批式发酵的方式,考察了NaOH高温碱间歇式处理对互花米草厌氧消化过程的影响.结果表明,互花米草一次发酵至产气停止,单位TS产气量为263mL/g,发酵过程中出现酸化现象, pH值最低为5.17.二次发酵原料为一次发酵后的固体残余物,主要组分为可分解有机物以及一些难分解有机物,过程中未出现酸化现象, pH值经短暂下降后很快稳定在7.5左右,累积产气量在一次发酵的基础上提高了46%.互花米草单位TS产气量为383mL/g.消化液中有机酸乙酸含量最大,丙酸和丁酸含量相当. 相似文献
115.
采用共沉淀法合成了不同Ce与Ti摩尔比的CePO4-TiO2复合材料,利用XRD、TEM、NH3-TPD和H2-TPR技术对其物理化学性质进行了表征,并对其NH3-SCR活性进行了评价。实验结果表明:随着CePO4含量的增加,催化剂的活性提高;当Ce与Ti的摩尔比为8:2时催化剂的活性最高,230 ℃的NO转化率达到100%,且具有更广的温度窗口,优于纯CePO4。表征结果显示,CePO4与TiO2形成固溶体后,颗粒尺寸较为均匀,强酸位的数量增多,氧化还原性能提升,从而提高了催化剂的SCR反应活性,同时改善了其抗水抗硫性能。 相似文献
116.
城市化进程中失地农民的贫困问题及其治理 总被引:1,自引:0,他引:1
运用文献研究法和定性分析方法,借鉴社会学与人类学相关理论,探讨失地农民的贫困问题,总结失地农民贫困的类型,分析失地农民的贫困原因,并提出治理对策。结果发现:部分失地农民在城市中面临着贫困问题,经济贫困、文化贫困、能力贫困和权利贫困是主要贫困类型。导致失地农民贫困的因素主要有体制与制度设置不合理、城市社会的剥夺与排斥、城乡文化的冲突与非物质文化变迁滞后以及失地农民个人能力缺失等。治理失地农民贫困问题必须从宏观层面强化制度与政策的保障作用,从微观层面加强失地农民的自身能力建设。 相似文献
117.
在常温条件下,采用生物滴滤塔处理模拟甲硫醚废气,考察了气体空床停留时间(EBRT)、容积负荷、喷淋密度及营养液pH对生物滴滤塔性能的影响。实验结果表明:当EBRT为90 s、进气甲硫醚质量浓度为150 mg/m~3、喷淋密度为0.65 m~3/(m~2·h),营养液pH为6.8时,甲硫醚去除率为90%;容积负荷高于15 g/(m~3·h)时,对生物滴滤塔的性能产生抑制作用;EBRT为90 s及60 s时,最佳喷淋密度分别为0.56~0.65 m~3/(m~2·h)及0.65~0.75 m~3/(m~2·h);降解甲硫醚的微生物对pH的变化较敏感,最适营养液pH为6~7。 相似文献
118.
Jörg Luster Manoj Menon Sandra Hermle Rainer Schulin Madeleine S. Günthardt-Goerg Bernd Nowack 《Water, Air, & Soil Pollution: Focus》2008,8(2):163-176
Soil translocation for recultivation of soil removed from construction sites and for the preparation of refilled lysimeters
inevitably involves disturbance of soil structure, and, if intermediate storage is included, also drying and rewetting of
the soil. We report on an experiment with model forest ecosystems, where uncontaminated forest subsoils were covered with
non-contaminated or freshly heavy metal (mainly Zn and Cu) contaminated topsoil in large lysimeters. Monitoring of the chemical
composition of the drainage water revealed two distinct soil conditioning phases. During an initial phase of about a year
strongly elevated nitrate and sulfate concentrations occurred that were attributed to a mineralisation flush caused by the
increased accessability of mineralisable nitrogen and sulfur in destroyed aggregates. These effects were significantly larger
in lysimeters with calcareous subsoil than in those with acidic subsoil. The second phase was characterised by a gradual decrease
in dissolved organic carbon and sulfate concentrations, in particular in the acidic subsoil. This decrease may be attributed
to the depletion of pools made accessible during aggregate destruction or the formation of new aggregates. These chemical
changes had only little effects on the concentrations of copper and zinc in the drainage water. Based on our results, it can
be concluded that large refilled lysimeters can be used for many purposes without risk of compromised results, if a conditioning
phase of about 1 year with sufficiently moist soil conditions is respected. Nevertheless, gradual changes in soil chemical
characteristics still occur after this initial phase. Implications for the recultivation of sites using relocated soils are
discussed. 相似文献
119.
P.-A. Dastous J. Nikiema G. Soreanu L. Bibeau M. Heitz 《Water, Air, & Soil Pollution: Focus》2008,8(3-4):275-285
This study presents the experimental results obtained during long-term operation of two biofilters treating two alcohols:
methanol and ethanol. The biofilters used for this purpose were previously packed with a compost material made from tobacco
processing residues. The alcohols concentrations tested lay between 0.40 and 3.20 g/m3 for methanol, and 0.55 and 5.05 g/m3 for ethanol. The empty bed residence time in each biofilter was 60 s. Biofilter inlet loads of less than 190 and 300 g/m3/h for the methanol and ethanol additions respectively, were thereafter evaluated. In addition, the concentrations of nutrient
nitrogen were also varied, from 0.1 to 2.0 g-N/l and from 0.3 to 11.3 g-N/l for the ethanol and the methanol, respectively.
The results thus obtained have made it possible to select the optimal nitrogen concentrations which, for the cases examined,
turn out to be 0.3 g-N/l and between 2 and 3.8 g-N/l for the ethanol and methanol substrates, respectively. The maximum elimination
capacities obtained in this study were 82 and 150 g/m3/h, respectively for the methanol and ethanol cases. It was therefore concluded that, for a readily biodegradable compound
such as ethanol, the nitrogen requirement is substantially lower than that needed for the methanol degradation, the latter
appearing to be more difficult to degrade biologically under similar operating conditions. The production rate of the co-product
carbon dioxide during methanol and ethanol biofiltration was also investigated. Also, a good correlation was found to exist
between the temperature and the conversion achieved in the biofilter. 相似文献
120.
Mary Beth Adams James N. Kochenderfer Pamela J. Edwards 《Water, Air, & Soil Pollution: Focus》2007,7(1-3):267-273
In 1989, a watershed acidification experiment was begun on the Fernow Experimental Forest in West Virginia, USA. Ammonium
sulfate fertilizer (35.5 kg N ha−1 yr−1and 40.5 kg S ha−1 yr−1) was applied to a forested watershed (WS3) that supported a 20-year-old stand of eastern deciduous hardwoods. Additions of
N and S are approximately twice the ambient deposition of nitrogen and sulfur in the adjacent mature forested watershed (WS4),
that serves as the reference watershed for this study. Acidification of stream water and soil solution was documented, although
the response was delayed, and acidification processes appeared to be driven by nitrate rather than sulfate. As a result of
the acidification treatment, nitrate solution concentrations increased below all soil layers, whereas sulfate was retained
by all soil layers after only a few years of the fertilization treatments, perhaps due to adsorption induced from decreasing
sulfate deposition. Based on soil solution monitoring, depletion of calcium and magnesium was observed, first from the upper
soil horizons and later from the lower soil horizons. Increased base cation concentrations in stream water also were documented
and linked closely with high solution levels of nitrate. Significant changes in soil chemical properties were not detected
after 12 years of treatment, however. 相似文献