助剂作用下超声浸取电解锰渣

用8-羟基喹啉、黄原酸钾、十六烷基三甲基溴化铵、磷酸三丁酯、柠檬酸5种物质作浸取助剂,考察了助剂作用下超声辅助浸取法从电解锰渣中提取锰的工艺条件。实验结果表明：用1%（质量分数）柠檬酸作浸取助剂,在固液比（g/mL）为1∶4、酸矿比（mL/g）为0.3∶1、浸取温度为70℃的条件下,超声浸取15min,锰浸出率平均可达57.28%,是加热酸浸法锰浸出率的2.72倍,是无助剂超声辅助浸取法锰浸出率的1.52倍。     

白泥复合衬层防渗稳定性的研究

为考察白泥复合防渗衬层的防渗稳定性和对污染物的阻滞去除能力,利用自制击实渗透仪对白泥和亚粘土防渗衬层进行了对比研究. 结果表明:白泥/亚粘土“夹层结构"复合衬层能保持低于国家防渗规范(10－7 cm/s)的防渗性,并对渗滤液中的重金属,COD_Cr和NH₄＋-N具有较强的阻滞去除能力,可以与常用的亚粘土防渗衬层相媲美,不过其淋滤出水ρ(Cl－)高,因此其长期防渗稳定性需进一步研究;60%白泥+40%亚粘土“混合式"复合衬层和白泥防渗衬层在渗滤液渗透作用下,其防渗性能不好,渗透系数超过国家防渗规范要求,因此不宜用于填埋场防渗.      

米糠生物质解毒含铬(Ⅵ)水溶液的研究

农林生物质是一种成本低、环境友好的重金属废水处理材料,也是受重金属污染环境的修复材料之一.实验讨论了初始pH值、米糠用量、吸附时间对含铬(Ⅵ)水溶液解毒的影响.结果表明,米糠对Cr(Ⅵ)存在吸附作用,同时也有解毒还原能力.100 mL浓度为100 mg/L的含铬溶液,在初始pH为2、米糠用量为3 g、吸附-反应平衡时间7 h的条件下,生物质吸附去除溶液中的铬为14.4%,而原溶液中Cr(Ⅵ)解毒了57.2%,米糠生物质吸附总铬的能力为0.48 mg Cr/g(生物质).米糠生物质有潜在的吸附铬和修复受铬污染环境的利用价值.     

臭氧法对酸性嫩黄G溶液的脱色效率和残留物的分析

实验考察了臭氧对酸性嫩黄G色度脱除和其溶液pH值的变化情况,并对降解溶液中的残留物进行定量分析。结果发现,20min时,脱色率达到97.5%;有酸性物质生成并使得溶液的pH值随反应时间的推移下降,pH与脱色率总体变化趋势一致。经反应,分子中的—SO3Na基团大部分生成了SO42-;N并没有氧化成NO2-、NO3-,而是生成其它含N化合物。     

POPs污染物莠去津在长期定位施肥土壤中的残留动态

在建立土壤中莠去津残留分析方法的基础上,采用室内培养法研究了该药在长期定位施肥处理土壤中的降解动态.土壤中的莠去津残留物用丙酮提取,经液-液分配和柱层析净化后,气相色谱检测.莠去津的最低检出量为6.4×10^-12　g,在土壤中的最低检出浓度为6.4×10^-9　g·kg^-1,土壤中0.11、1.1、11.0 mg·kg^-1这3个浓度的添加回收率分别为91.41%±4.36％、93.58%±4.54％、 90.35%±3.59％,符合农药残留分析要求.运用该残留分析方法研究了莠去津在长期定位施肥处理土壤中的残留动态.结果表明,莠去津在土壤中的降解遵循一级动力学方程,其在CK、NPK、NPK+M、NPK+S施肥处理土壤中的降解半衰期分别为20.6、 23.0、 28.5、 33.2 d,由LSR分析可知,NPK肥和有机肥的施入明显加快了莠去津在土壤中的降解.单独回归及逐步回归分析均证实莠去津在土壤中的降解半衰期与土壤中的碱解氮、有机质和全氮含量之间存在良好的正相关,其相关系数分别为0.998?3、0.982?6和0.952?1,原因可能是这些土壤养分为土壤微生物的活动提供了足够的碳素和氮素,微生物活性较高,从而致使莠去津在土壤中降解加快.     

利用废渣盐石膏制作轻型墙体材料

研究利用海盐化工产生的废渣盐石膏经过一定工艺处理,生产轻型墙体材料盐石膏空心条板,该产品与天然石膏空心条板相比,原料采用及生产工艺都有较大改进,生产成本却大幅度下降。经测试,该产品完全可替代天然石膏空心条板,技术性能指标达到了国家规定的相关标准。     

钢渣预处理含铬废水及其废渣与铬渣的固化

用钢渣对含铬废水进行预处理,探讨了钢渣粒度、用量、废水pH值和添加硫酸亚铁还原剂的影响.结果表明,经硫酸亚铁还原处理后再用钢渣处理比单纯用钢渣处理的效果明显提高,采用钢渣/总铬质量比为40的100目钢渣处理经硫酸亚铁还原后的含铬废水,总铬和Cr6 去除率分别达79%和84%,采用钢渣柱进行的两级淋滤实验进一步表明该方法可作为工业上含铬废水处理的预处理段.处理后的废钢渣同工业铬渣一起进行水泥固化,标准养护20 d后固化体表面Cr6 浸出率、破碎至5 mm粒径以下和酸雨淋溶下的浸出液Cr6 浓度均符合安全标准,可作为普通建材或进行填埋处置.     

Pyrolysis of rice husk and sawdust for liquid fuel

The paper is focused on studying how to convert rice husk and sawdust into liquid fuel. Rice husk, sawdust and their mixture were pyrolyzed at the temperature between 420℃ and 540℃, and the main product of liquid fuel was obtained. The experimental result showed that the yield of liquid fuel heavily depended on the kind of feedstock and pyrolysis temperature. In the experiments, the maximum liquid yields for rice husk, sawdust and their mixture were 56% at 465 ℃, 61% at 490℃ and 60% at 475℃ respectively. Analysis with GC-MS and other apparatus indicated that the liquid fuel is a complicated organic compound with low caloric value and can be directly used as fuel oil without any up-grading. As a crude oil, the liquid fuel can be refined to be vehicle oil.     

Ecological effects of crude oil residues on the functional diversity of soil microorganisms in three weed rhizospheres

Ecological effects of crude oil residues on weed rhizospheres are still vague. The quantitative and diversity changes and metabolic responses of soil-bacterial communities in common dandelion （Taraxacum officinale）, jerusalem artichoke （Silphiurn perfoliatum L.） and evening primrose （A colypha australis L.） rhizospheric soils were thus examined using the method of carbon source utilization. The results indicated that there were various toxic effects of crude oil residues on the growth and reproduction of soil bacteria, but the weed rhizospheres could mitigate the toxic effects. Total heterotrophic counting colony-forming units （CFUs） in the rhizospheric soils were significantly higher than those in the non-rhizospheric soils. The culturable soil-bacterial CFUs in the jerusalem artichoke （S. perfoliatum） rhizosphere polluted with 0.50 kg/pot of crude oil residues were almost twice as much as those with 0.25 kg/pot and without the addition of crude oil residues. The addition of crude oil residues increased the difference in substrate evenness, substrate richness, and substrate diversity between non-rhizospheric and rhizospheric soils of T. officinale and A. australis, but there was no significant （p〉0.05） difference in the Shannon＇s diversity index between non-rhizospheric and rhizospheric soils of S. perfoliatum. The rhizospheric response of weed species to crude oil residues suggested that S. perfoliatum may be a potential weed species for the effective plant-microorganism bioremediation of contaminated soils by crude oil residues.     

Process of rice straw degradation and dynamic trend of pH by the microbial community MC1

The process of the rice straw degradation in the fermentor with aeration at 290 ml/h was studied. The results of dissolved oxygen （DO） indicated that the optimum DO during cellulose degradation by microbial community MC1 ranged from 0.01 to 0.12 mg/L. The change model ofpH values was as follows： irrespective of the initial pH of the medium, pH values decreased rapidly to approximate 6.0 after being inoculated within 48 h when cellulose was strongly degraded, and then increased slowly to 8.0--9.0 until cellulose was degraded completely. During the degradation process, 15 kinds of organic compounds were checked out by GC-MS. Most of them were organic acids. Quantity analysis was carried out, and the maximum content compound was ethyl acetate which reached 13.56 g/L on the day 4. The cellulose degradation quantity and ratio analyses showed that less quantity （under batch fermentation conditions） and longer interval （under semi-fermentation conditions） of rice straw added to fermentation system were contributed to matching the change model of pH, and increasing the quantity and ratio of rice straw degradation during cellulose degrading process. The highest degradation ratio was observed under the condition office straw added one time every five days （under semi-fermentation conditions）.