生物氧化磁黄铁矿产生铁离子

从广东云浮矿山酸性废水中富集获得氧化亚铁硫杆菌(Thiobacillus ferrooxidans),利用该氧化亚铁硫杆菌研究了反应时间、pH、温度、矿浆浓度和矿物粒度对磁黄铁矿生物氧化获得铁离子的影响。结果表明,在29℃,摇床转速200 r/min,10%接种量条件下,氧化亚铁硫杆菌可以明显促进磁黄铁矿的氧化,但反应后期有黄钾铁矾沉淀生成,不利于获得铁离子;控制溶液pH值为2.00,温度在29～36℃范围,可促进生物氧化磁黄铁矿获得铁离子;铁离子量随着矿浆浓度的增大和矿物粒度的减小而增加,优化的矿浆浓度和矿物粒径分别为6%和58μm左右。     

Kinetics of the biodegradation pathway of endosulfan in the aerobic and anaerobic environments

The enriched mixed culture aerobic and anaerobic bacteria from agricultural soils were used to study the degradation of endosulfan (ES) in aqueous and soil slurry environments. The extent of biodegradation was ∼95% in aqueous and ∼65% in soil slurry during 15 d in aerobic studies and, ∼80% in aqueous and ∼60% in soil slurry during 60 d in anaerobic studies. The pathways of aerobic and anaerobic degradation of ES were modeled using combination of Monod no growth model and first order kinetics. The rate of biodegradation of β-isomer was faster compared to α-isomer. Conversion of ES to endosulfan sulfate (ESS) and endosulfan diol (ESD) were the rate limiting steps in aerobic medium and, the hydrolysis of ES to ESD was the rate limiting step in anaerobic medium. The mass balance indicated further degradation of endosulfan ether (ESE) and endosulfan lactone (ESL), but no end-products were identified. In the soil slurries, the rates of degradation of sorbed contaminants were slower. As a result, net rate of degradation reduced, increasing the persistence of the compounds. The soil phase degradation rate of β-isomer was slowed down more compared with α-isomer, which was attributed to its higher partition coefficient on the soil.     

用电石渣浆制备烟气脱硫剂

采用电石渣浆经处理后配制成的电石渣试样作为脱硫剂,对除尘后锅炉烟气进行脱硫实验,在烟气巾s与c质量比约为1：30、吸收体系pH为7～8、温度为15℃的条件下,平均脱硫率达96．35％。采用电石渣浆上层清液作脱硫剂对锅炉烟气进行脱硫的工业试验,在烟气流速为2．8～4．2m／s、脱硫塔内nCa：n5=1．2：1、体系pH为7～8的条件下,平均脱硫率达90．66％,且脱硫塔出气口处SO2质量浓度明显低于GB13271-2001《锅炉大气污染物排放标准》。     

论双回路吸收塔及其循环浆液计算

双回路吸收塔运用于火电厂、烧结厂等的烟气脱硫系统。它具有传质效果好、脱硫率高、产生的石膏纯度高等特点,对于减少对自然界石膏资源的开发和保护资源上,具有很大的优势。通过对双回路塔的工作原理及其结构、性能特点论述,层层剖析,并进一步论证其循环浆液的计算方法。     

典型沼肥灌施农田重金属的时间多尺度特征分析

长期对农田进行沼肥灌施对土壤养分及重金属累积、迁移产生何种影响,尚缺乏系统的调查和研究。选取7—10年灌施沼肥的农田为研究对象,分析耕层土壤中Cu、Zn、Cr、Cd、Pb、Ni、Hg和As的全量及Cu、Zn各形态含量,并对污染水平及生态风险进行评价和预测。结果表明:持续灌施沼肥改变土壤的EC、pH等理化性质,造成P、K等营养元素和重金属Cu、Zn的显著累积。Cu、Zn平均积累速率分别为5.70~6.15、12.13~18.7 mg/(kg·年)。Cu和Zn含量之间具有显著相关性,表明它们同源。外源输入的稀释作用及形态转化使原土壤Cu、Zn赋存形态发生改变。综合污染指数法研究结果表明,养殖场土壤重金属均处于警戒水平。潜在生态风险指数法研究结果表明,养殖场土壤重金属危害程度整体表现为轻微生态危害。Cu、Zn年积累通量分别为10.26~11.07、21.83~33.66 kg/(hm²·年)。预测土壤中Cu、Zn浓度超出风险筛选值时间分别为10.19~11.01、9.16~14.14年。连续多年灌施沼肥将对土壤生态环境造成潜在风险。