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研究采用海藻酸钠(SA)为固定化载体包埋固定活体耐辐射奇球菌(Deinococcus radiodurans ),旨在探讨固定化活体耐辐射奇球菌颗粒对铀的吸附性能、减量化效果及减量后灰分中铀的赋存形态.结果表明,25℃、pH 值=3.5、投加量25 g/L、初始铀浓度为50 mg/L时,1 h左右可达吸附平衡,吸附率达95%以上,吸附过程符合准二级动力学方程.当初始铀浓度为100 mg/L时,最大吸附量达103.82 mg/g(DW).通过 HCl 解吸复吸3次仍可保持与原有的吸附量相当的水平;固定化颗粒经灰化处理后有较好的减量化效果,湿重和干重减重比分别为17.56和254.37.灰化前后经SEM-EDS、XRD分析,表明铀主要与固定化耐辐射奇球菌细胞中的磷结合成团簇的絮状物质,灰化后结晶成铀的磷酸盐,灰分主要成分为 CaCO3、Ca(UO2)(PO4).3 H2 O 和(Ca,U)(PO4).2 H2 O.

Sodium alginate(SA)immobilized live Deinococcus radiodurans beads were used to investigate the ad-sorption and elution for uranium as well as the volume reduction by ashing and the chemical speciation of urani-um in ashing.Results showed that the rate of adsorption would reach above 9 5% when the addition of SA im-mobilized D.radiodurans was 25 g/L,temperature was 25 ℃,pH was 3.5,and the initial uranium concentra-tion of 50 mg/L.The maximum adsorption capacity of 103.82 mg/g (dry weight)when the initial uranium con-centration of 100 mg/L.It could also be repeatedly used in multiple adsorption-desorption cycles that treatment by HCl adsorption capacity maintained after three cycles.The volume reduction results showed the SA immobi-lized D.radiodurans beads had a great weight reduction ratio by ashing process,which could reach about 254.4 times.The ashes were testing by SEM,EDS and XRD,It’s crystalline material,including CaCO3 ,Ca(UO2 ) (PO4 ).3 H2 O and (Ca,U)(PO4).2 H2 O.Showed that uranium mainly combined with the phosphorus which in immobilized D.radiodurans cells and form clusters flocculent substance,after ashing it formation of crystal-line phosphate of uranium.

参考文献

[1] 唐志坚;张平;左社强.低浓度含铀废水处理技术的研究进展[J].工业用水与废水,2003(4):9-12.
[2] 林莹;高柏;李元锋.核工业低浓度含铀废水处理技术进展[J].山东化工,2009(3):35-38.
[3] 魏广芝;徐乐昌.低浓度含铀废水的处理技术及其研究进展[J].铀矿冶,2007(2):90-95.
[4] 何颖;沈先荣;刘琼;蒋定文;王庆蓉;侯登勇;陈伟;刘玉明;李珂娴.微生物与铀的相互作用及其应用前景[J].环境科学与技术,2014(10):62-68.
[5] Hu MZC;Norman JM;Faison BD;Reeves ME.BIOSORPTION OF URANIUM BY PSEUDOMONAS AERUGINOSA STRAIN CSU - CHARACTERIZATION AND COMPARISON STUDIES[J].Biotechnology and Bioengineering,19962(2):237-247.
[6] 徐雪芹;李小明;杨麒;曾光明;金科.固定化微生物技术及其在重金属废水处理中的应用[J].环境污染治理技术与设备,2006(07):99-105.
[7] 辛蕴甜;赵晓祥.芽孢杆菌H-1菌株的固定化及降解动力学研究[J].环境科学与技术,2013(11):67-73.
[8] 秦胜东;郭嘉昒;刘玉存;马慧;尹政;吕利刚.固定化微生物技术研究进展及其在水处理中的应用[J].水处理技术,2014(10):6-11.
[9] S. F. D'Souza;Pinaki Sar;Sufia K. Kazy;B. S. Kubal.Uranium Sorption by Pseudomonas Biomass Immobilized in Radiation Polymerized Polyacrylamide Bio-Beads[J].Journal of environmental science and health, Part A. Toxic/hazardous substances & environmental engineering,20063(3):487-500.
[10] 刘明学;董发勤;李姝;亢武;孙宇;杜旭光;苟清碧.固定化耐辐射奇球菌对锶柱吸附与减量化研究[J].环境科学与技术,2014(6):32-37.
[11] 邓钦文;丁德馨;刘冬;王永东.耐辐射奇球菌对水中铀(Ⅵ)的吸附试验[J].金属矿山,2014(1):150-153.
[12] 李建平;林庆宇;闫研.超积累植物李氏禾叶细胞干粉对Cr(Ⅵ)的吸附特性研究[J].化学学报,2008(23):2646-2652.
[13] 李克斌;王勤勤;党艳;魏红;罗倩;赵锋.荞麦皮生物吸附去除水中Cr(VI)的吸附特性和机理[J].化学学报,2012(7):929-937.
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