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101.
Kinetic and equilibrium isotherm studies for the adsorptive removal of Brilliant Green dye from aqueous solution by rice husk ash 总被引:3,自引:0,他引:3
The present study deals with the adsorption of Brilliant Green (BG) on rice husk ash (RHA). RHA is a solid waste obtained from the particulate collection equipment attached to the flue gas lines of rice husk fired boilers. Batch studies were performed to evaluate the influences of various experimental parameters like initial pH (pH0), contact time, adsorbent dose and initial concentration (C0) on the removal of BG. Optimum conditions for BG removal were found to be pH0 approximately 3.0, adsorbent dose approximately 6 g L(-1) of solution and equilibrium time approximately 5 h for the C0 range of 50-300 mg L(-1). Adsorption of BG followed pseudo-second-order kinetics. Intra-particle diffusion does not seem to control the BG removal process. Equilibrium isotherms for the adsorption of BG on RHA were analyzed by Freundlich, Langmuir, Redlich-Peterson (R-P), Dubnin-Radushkevich (D-R), and Temkin isotherm models using a non-linear regression technique. Langmuir and R-P isotherms were found to best represent the data for BG adsorption onto RHA. Adsorption of BG on RHA is favourably influenced by an increase in the temperature of the operation. Values of the change in entropy (DeltaS0) and heat of adsorption (DeltaH0) for BG adsorption on RHA were positive. The high negative value of change in Gibbs free energy (DeltaG0) indicates the feasible and spontaneous adsorption of BG on RHA. 相似文献
102.
以间歇-分阶段进水方式进行了模拟酸雨柱式动态淋溶实验.结果表明,间歇-阶段性酸雨入侵会影响填埋飞灰中Pb、Zn、Cu、Cr和Ni的浸出行为;尤其间歇停滞期后的初期酸雨入侵会增加多数重金属的再浸出水平,且该部分重金属的释放主要源于前阶段酸雨侵蚀过程中所形成的非稳定性(弱酸态)重金属.各酸雨侵蚀阶段,部分重金属(如Pb-Zn)的浸出行为具有相关性,这与各重金属在飞灰基质内的赋存形态、矿物相稳定性及酸性侵蚀程度等有关.各阶段酸雨入侵会相继溶出飞灰中的可溶性(NaCl、KCl等)、难溶性氯盐(CaClOH)以及微溶性钙盐(CaSO4),并增加CaCO3和Ca-Al-Si-O等矿物的峰强.各阶段酸雨入侵会使初始飞灰表面的团簇状结构逐渐被酸性(H+)侵蚀作用破坏,并暴露出大量棒状或条形状CaCO3晶体,且随着酸雨入侵次数的增加,CaCO3也将逐渐被侵蚀破坏.本研究为非连续酸性降雨条件下填埋稳定化飞灰的重金属浸出行为评价及风险管控提供了科学依据. 相似文献
103.
采用Mg-Fe型类水滑石(LDH)吸附剂提纯污泥焚烧飞灰(ISSA)浸出液中的磷,探究了吸附剂煅烧对磷吸附效果的影响及磷吸附和脱附机理.研究发现,在高浓度磷溶液(>1000mg/L)中,未煅烧的类水滑石(LDHu)磷吸附容量高于煅烧后的类水滑石(LDHc).LDHu具有典型的层状结构,磷的吸附与脱附主要通过磷和金属离子沉淀-溶解、静电吸附-排斥、配位作用和离子交换实现.而LDHc层状结构消失,形成双金属氧化物,不存在明显的阴离子交换作用.经LDHu或LDHc吸附和NaOH溶液脱附后,ISSA浸出液均具有良好的磷纯化效果,磷相对纯度从36%分别上升至77%和69%,磷回收率分别为84%和57%.纯化后的溶液适合制备高值含磷产物. 相似文献
104.
105.
Kangjoo Kim Sung-Min Park Jinsam Kim Seok-Hwi Kim Yeongkyoo Kim Jeong-Tae Moon Gab-Soo Hwang Wang-Seog Cha 《Chemosphere》2009,77(2):222-227
The geochemical behavior of As in porewaters of an alkaline coal ash disposal site was investigated using multilevel samplers. The disposal site was in operation from 1983 until 1994 and was covered with 0.3–0.5 m thick soils in 2001 when this study was initiated. Sequential extraction analyses and batch leaching experiments were also performed using the coal ash samples collected from the disposal site. The results suggest the important roles of siderite (FeCO3) precipitation/dissolution and soil cover, which have been ignored previously. Arsenic levels in the porewater were very low (average of 10 μg L−1) when the site was covered with soil due to coprecipitation with siderite. The soil cover enabled the creation of anoxic conditions, which raised the Fe concentration by the reductive dissolution of Fe-(hydr)oxides. Because of the high alkalinity generated from the alkaline coal ash, even a small increase in the Fe concentration (0.66 mg L−1 on average) could cause siderite precipitation. When the soil cover was removed, however, an oxidizing condition was created and triggered the precipitation of dissolved Fe as (hydr)oxides. As a result, the dissolution of previously precipitated As-rich siderite caused higher As concentration in the porewater (average of 345 μg L−1). 相似文献
106.
Summary. Host plant odours are known to be important in long-range host location by the cabbage root fly, whereas at short distances
orientation is mainly visual. We show that olfaction also plays a significant role after a fly lands on a plant and before
it moves down onto the soil to oviposit. Host plant acceptance by the cabbage root fly seems to result from a synergistic
response to simultaneously perceived olfactory and contact chemostimulation.
Received 12 May 1999; accepted 24 July 1999 相似文献
107.
Hyokeun Park 《Environmental pollution (Barking, Essex : 1987)》2010,158(5):1420-56
Polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs), and polychlorinated biphenyls (PCBs) in human have been studied extensively; however, polychlorinated naphthalenes (PCNs) have been studied less widely. The mean concentrations of PCNs, PCDDs, PCDFs, and PCBs in 61 healthy human volunteers were 2170 pg/g lipid, 452 pg/g lipid, 116 pg/g lipid, and 120 ng/g lipid respectively, and the mean toxic equivalents (TEQs) contributed by PCNs, PCDDs, PCDFs, and PCBs were 5.88, 5.22, 5.48, and 5.33 pg/g lipid, respectively. PCNs contributed to 26.8% of the total TEQs. 1,2,3,7,8-PeCDD, 2,3,4,7,8-PeCDF, PCB126, and hepta-CN-73 accounted for >62% of the total TEQs in the human serum samples. The overall serum PCN homologue profiles of all subjects were dominated by tetra- and penta-CN homologues, and the most predominant individual congener was hepta-CN-73, which contributed 17.5% of the total serum PCN concentration. Enrichment of hepta-CN-73 in the human serum samples might be due to contributors from combustion sources. 相似文献
108.
109.
110.
Reclamation and revegetation of fly ash disposal sites - Challenges and research needs 总被引:1,自引:1,他引:0
Haynes RJ 《Journal of environmental management》2009,90(1):43-53
Coal-fired power generation is a principal energy source throughout the world. Approximately, 70-75% of coal combustion residues are fly ash and its utilization worldwide is only slightly above 30%. The remainder is disposed of in landfills and fly ash basins. It is desirable to revegetate these sites for aesthetic purposes, to stabilize the surface ash against wind and water erosion and to reduce the quantity of water leaching through the deposit. Limitations to plant establishment and growth in fly ash can include a high pH (and consequent deficiencies of Fe, Mn, Cu, Zn and P), high soluble salts, toxic levels of elements such as B, pozzalanic properties of ash resulting in cemented/compacted layers and lack of microbial activity. An integrated organic/biotechnological approach to revegetation seems appropriate and should be investigated further. This would include incorporation of organic matter into the surface layer of ash, mycorrhizal inoculation of establishing vegetation and use of inoculated legumes to add N. Leaching losses from ash disposal sites are likely to be site-specific but a sparse number of studies have revealed enriched concentrations of elements such as Ca, Fe, Cd, Pb, and Sb in surrounding groundwater. This aspect deserves further study particularly in the longer-term. In addition, during weathering of the ash and deposition of organic matter during plant growth, a soil will form with properties vastly different to that of the parent ash. In turn, this will influence the effect that the disposal site has on the surrounding environment. Nevertheless, the effects of ash weathering and organic matter accumulation over time on the chemical, physical and biological properties of the developing ash-derived soil are not well understood and require further study. 相似文献