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51.
铝盐絮凝剂及其环境效应 总被引:20,自引:1,他引:20
概述了铝盐絮凝剂的结构、形态分布及铝盐絮凝剂对环境所产生的一些不良影响,描述了铝盐絮凝剂对人体及各种生物体的毒性作用,同时,介绍了对污水后续处理的影响,并作了简要的评述。 相似文献
52.
Improvement of rape (Brassica napus) plant growth and cadmium uptake by cadmium-resistant bacteria 总被引:7,自引:0,他引:7
This study focuses on the screening of cadmium-resistance bacterial strains from heavy metal-polluted soils to examine their plant growth promotion and cadmium uptake in rape (Brassica napus). A large number of bacteria were isolated from heavy metal-polluted soil in Nanjing, China. Thirty isolates showing cadmium-resistance on Cd-amended medium were selected and evaluated for their potential to solubilize cadmium carbonate in solution culture. Atomic absorption spectrometer analysis showed variable amounts of water-soluble Cd (ranging from 24 to 117 mg l(-1)) released by the cadmium-resistant bacterial strains from cadmium carbonate. Qualitative analysis confirmed the presence of indole acetic acid as the auxin in the culture of these cadmium-resistant bacterial strains. Root elongation assay conducted on rape under gnotobiotic conditions demonstrated increases (up to 31%) in root elongation of inoculated rape seedlings compared to the control plants. Based upon cadmium-resistance, bio-activation of CdCO3 and growth-promoting activity, three isolates were selected for promoting plant growth and uptake of cadmium from cadmium-amended soil in pot experiments. Inoculation with the isolates was found to increase root dry weight (ranging from 8% to 20%) and shoot dry weight (ranging from 6% to 25%) of rape. An increase in cadmium content varying from 16 to 74%, compared to the non-inoculated control, was observed in rape plants cultivated in soil treated with 100 mgCd kg(-1) (as CdCl2) and inoculated with the isolates. The bacterial isolates were also able to colonize and develop in the rhizosphere soil of rape after root inoculation. 相似文献
53.
采用上流式分段污泥床(upflow staged sludge bed)反应器对聚酯废水进行了预处理试验研究.反应器内厌氧污泥经过近70 d的培养驯化后,用于处理聚酯废水.当进水COD值为800~2000 mg/L,HRT约为16~20 h时,其COD去除率基本能稳定在50%~55%之间;聚酯废水经预处理后,其BOD5/COD值由原来的0.3左右提高到约为0.6,取得了较好的预处理效果.但系统的总产气量由培养期的约13 L/d降至0.8 L/d左右,其中甲烷气体的含量也由50%下降至约6%. 相似文献
54.
55.
Electrochemical degradation of chlorophenoxy and chlorobenzoic herbicides in acidic aqueous medium by the peroxi-coagulation method 总被引:6,自引:0,他引:6
The degradation of 4-chlorophenoxyacetic acid (4-CPA), 4-chloro-2-methylphenoxyacetic acid (MCPA), 2,4-dichlorophenoxyacetic acid (2,4-D) and 2,4,5-trichlorophenoxyacetic acid (2,4,5-T) as chlorophenoxy herbicides, as well as of 3,6-dichloro-2-methoxybenzoic acid (dicamba) as chlorobenzoic herbicide, has been studied by peroxi-coagulation. This electrochemical method yields a very effective depollution of all compounds in acidic aqueous medium of pH 3.0 working under pH regulation, since they are oxidized with hydroxyl radicals produced from Fenton's reaction between Fe(2+) and H(2)O(2) generated by the corresponding Fe anode and O(2)-diffusion cathode. Their products can then be removed by mineralization or coagulation with the Fe(OH)(3) precipitate formed. Both degradative paths compete at low currents, but coagulation predominates at high currents. The peroxi-coagulation process of dicamba at I>or=300 mA leads to more than 90% of coagulation, being much more efficient than its comparative electro-Fenton treatment with a Pt anode and 1 mM Fe(2+), where only mineralization takes place. For the chlorophenoxy compounds, electro-Fenton gives a slightly lower depollution than peroxi-coagulation, because more easily oxidable products are produced. Oxidation of chlorinated products during peroxi-coagulation is accompanied by the release of chloride ion to the solution. The efficiency of this method decreases with increasing electrolysis time and current. The decay of all herbicides follows a pseudo-first-order reaction, with a similar constant rate for 4-CPA, MCPA, 2,4-D and 2,4,5-T, and a higher value for dicamba. 相似文献
56.
生物活性炭法深度处理纺织废水二级出水中生物活性的研究 总被引:6,自引:0,他引:6
采用上流式曝气生物活性炭法处理碱减量印染废水二级生物处理出水,利用TTC-脱氢酶活性(DHA)法监测反应器内DHA生物活性分布。研究发现反应器内生物炭表面附着生物膜活性较高,特别是反应器上部生物碳粒同样具有较高的DHA活性,这与反应器运行一年多能够保持对COD、色度和UV等较高去除率有一定关系。还研究了活性炭吸附、反应器反冲洗对DHA活性的影响。本研究为曝气生物活性炭法有效去除印染碱减量废水中难降解有机物提供了一定的理论依据。 相似文献
57.
微絮凝-超滤工艺处理微污染水源水的中试研究 总被引:2,自引:0,他引:2
进行了微絮凝.超滤工艺处理微污染水源水的中试研究。试验结果表明:在微絮凝-超滤工艺中,相同混凝剂投加量(相同金属摩尔浓度)下铁盐比铝盐的混凝效果好;微絮凝-超滤工艺的最佳絮凝时间为120s左右;最佳混凝剂投加量为2.2mg/L(以Fe计)。微絮凝-超滤工艺在改善出水水质和缓解膜污染方面均优于直接超滤工艺。微絮凝-超滤工艺的出水水质均符合建设部《城市供水水质标准》(CJ/T206-2005)要求。 相似文献
58.
59.
Ting Gui Gui F. Jia Jin Xu Shi J. Ge Xiao F. Long 《Journal of environmental science and health. Part. B》2019,54(4):326-335
A modified quick, easy, cheap, effective, rugged and safe (QuEChERS) method was developed for the determination of thiamethoxam and its metabolite clothianidin in citrus (including the whole citrus, peel and pulp) and soil samples by liquid chromatography-tandem mass spectrometry. The sample was extracted with acetonitrile and purified with octadecylsilane. The detection limits of both compounds were 0.0001–0.0002?mg kg–1, while the limit of quantification of thiamethoxam was 0.002?mg kg–1 and the limit of quantitation of metabolites was 0.001?mg kg–1. The recovery was 70.37%–109.76%, with inter-day relative standard deviations (RSD) (n?=?15) values ≤9.46% for the two compounds in the four matrices. The degradation curve of thiamethoxam in whole citrus and soil was plotted using the first-order kinetic model. The half-life of the whole citrus was 1.9–6.2?days, and the half-life of the soil was 3.9–4.2?days. The terminal residue of thiamethoxam (the sum of thiamethoxam and clothianidin, expressed as thiamethoxam) was found to be concentrated on the peel. The final residual amount of thiamethoxam in the edible portion (pulp) was less than 0.061?mg kg–1. The risk quotient values were all below 1, indicating that thiamethoxam as a citrus insecticide does not pose a health risk to humans at the recommended dosage. 相似文献
60.
通过HNO3-KOH对活性炭进行改性,采用扫面电镜(SEM)、比表面积分析(BET)、红外光谱分析(FT-IR)和Boehm滴定法对改性前后的活性炭进行表征,研究了改性前后的活性炭在不同条件下对微污染水源水中Ni2+的吸附能力和动力学。结果表明:改性活性炭表面含氧酸性官能团数量增加,比表面积和总孔容均略有降低,孔径变化不明显。在Ni2+浓度为0.4 mg·L-1,改性活性炭投加量5.0 g·L-1,温度30 ℃时,反应1 h去除率可达95.55%,剩余Ni2+浓度为0.017 8 mg·L-1,达到《生活饮用水卫生标准》(GB5749-2006)中的要求。相同条件下,改性前活性炭对Ni2+的去除率仅为74.45%,剩余Ni2+浓度达不到标准要求。活性炭对Ni2+的等温吸附更符合Langmuir方程,吸附动力学数据符合准二级动力学方程。 相似文献