离子交换与吸附
離子交換與吸附
리자교환여흡부
ION EXCHANGE AND ADSORPTION
2009年
6期
519-526
,共8页
赵玉清%陈吉群%张凤杰%王芳
趙玉清%陳吉群%張鳳傑%王芳
조옥청%진길군%장봉걸%왕방
嗜铅菌%水体铅%吸附条件%机理
嗜鉛菌%水體鉛%吸附條件%機理
기연균%수체연%흡부조건%궤리
Lead-resistant strain%Water body lead%Adsorption conditions%Mechanism
研究了实验室提供的嗜铅菌对水中铅离子吸附的条件和机理.讨论了吸附时间、pH、铅离子的质量浓度和菌的质量浓度对吸附的影响.结果表明,在pH=7.0、铅离子初始质量浓度为25mg/L、离心湿菌的质量浓度为1.06g/L、吸附时间为60min时,铅离子的吸附率达96.88%;实验条件下超标25倍的含Pb~(2+)废水,可迭排放标准;Pb~(2+)的最大吸附量为150mg/g.数学模型Langmuir和Freundlich方程均能很好地描述嗜铅菌对Pb~(2+)的吸附过程.对Pb~(2+)吸附前后的红外光谱表征表明,嗜铅菌表面多糖、蛋白质的羟基峰和羰基峰均有不同程度的紫移,羟基峰、糖苷峰等峰宽略增,说明菌体吸附,主要是表面基团的作用所致.用原子力显微镜对吸附前后的嗜铅菌检测可见,吸附后菌体的弹性变小、粘性变大、部分茵体有一定的收缩,说明以表面吸附为主的吸附过程,对菌细胞的聚合度有影响,菌体内部对铅也有一定的生物积累.
研究瞭實驗室提供的嗜鉛菌對水中鉛離子吸附的條件和機理.討論瞭吸附時間、pH、鉛離子的質量濃度和菌的質量濃度對吸附的影響.結果錶明,在pH=7.0、鉛離子初始質量濃度為25mg/L、離心濕菌的質量濃度為1.06g/L、吸附時間為60min時,鉛離子的吸附率達96.88%;實驗條件下超標25倍的含Pb~(2+)廢水,可迭排放標準;Pb~(2+)的最大吸附量為150mg/g.數學模型Langmuir和Freundlich方程均能很好地描述嗜鉛菌對Pb~(2+)的吸附過程.對Pb~(2+)吸附前後的紅外光譜錶徵錶明,嗜鉛菌錶麵多糖、蛋白質的羥基峰和羰基峰均有不同程度的紫移,羥基峰、糖苷峰等峰寬略增,說明菌體吸附,主要是錶麵基糰的作用所緻.用原子力顯微鏡對吸附前後的嗜鉛菌檢測可見,吸附後菌體的彈性變小、粘性變大、部分茵體有一定的收縮,說明以錶麵吸附為主的吸附過程,對菌細胞的聚閤度有影響,菌體內部對鉛也有一定的生物積纍.
연구료실험실제공적기연균대수중연리자흡부적조건화궤리.토론료흡부시간、pH、연리자적질량농도화균적질량농도대흡부적영향.결과표명,재pH=7.0、연리자초시질량농도위25mg/L、리심습균적질량농도위1.06g/L、흡부시간위60min시,연리자적흡부솔체96.88%;실험조건하초표25배적함Pb~(2+)폐수,가질배방표준;Pb~(2+)적최대흡부량위150mg/g.수학모형Langmuir화Freundlich방정균능흔호지묘술기연균대Pb~(2+)적흡부과정.대Pb~(2+)흡부전후적홍외광보표정표명,기연균표면다당、단백질적간기봉화탄기봉균유불동정도적자이,간기봉、당감봉등봉관략증,설명균체흡부,주요시표면기단적작용소치.용원자력현미경대흡부전후적기연균검측가견,흡부후균체적탄성변소、점성변대、부분인체유일정적수축,설명이표면흡부위주적흡부과정,대균세포적취합도유영향,균체내부대연야유일정적생물적루.
The adsorptive conditions and mechanism of lead ion by lead-resistant strain provided by laboratories in aqueous media were conducted. The adsorptive effects of adsorption time, pH,mass concentration of lead ion, mass concentration of strain to adsorption are discussed. The results indicate that lead ion removal rate can reach up to 96.88% in the following conditions: pH=7.0, initial mass concentration of lead ion was 25mg/L, the mass concentration of bacteria was 1.06g/L, adsorption time is 60min. Under experimental conditions, the wasting water whose lead ion concentration exceeds 25 folds can reach the discharge standard. The highest adsorptive capacity of Pb~(2+) may reach up to 150mg/g under the experimental conditions. Mathematic model Langmuir and Freundlich equations both can simulate the adsorption of lead ion by lead-resistant strain very well. Before and after the adsorption to lead ions by lead-resistant strain, the IR spectra show that the hydroxyl and carbonyl groups of polysaccharide and protein exhibit blue shifts in various degrees, the peak width of hydroxyl groups and C-O-C widened a little bit, which shows that the adsorption is mainly resulted from the function of the surface groups. The AFM detections indicate that the elasticity of bacteria decreases, the adhesiveness increases and part of the mycelium shrinks a little after adsorption, which shows that the adsorption mainly to the surface adsorption process has effect on the aggregation degree of strain cells, lead was also biologically accumulated in the mycelium meanwhile.