稀土节能荧光灯生产过程中含汞废气处理的实践

用催化吸附 KMnO4溶液吸收化合净化法处理稀土荧光灯生产过程中含汞废气 ,经该工艺处理 ,排放的净化气低于GB162 97 1996《大气污染物综合排放标准》中汞污染物排放标准     

海绵铁预处理DSD酸废水的研究

用铁泥废渣制备水处理材料海绵铁,研究含碳球团直接还原的金属化率与还原时间,温度和铁泥粒度之间的关系,得到含碳球团制备海绵铁的反应参数。并对海绵铁预处理DSD酸废水的各种影响因素进行了试验研究,确定最佳试验条件;通过试验对海绵铁处理DSD酸废水的机理进行了探讨,确定它是电化学作用、电场作用、絮凝沉淀以及物理吸附等共同作用的结果。试验表明,海绵铁可作为高浓度DSD废水的预处理材料。     

Protozoan colonization on artificial substrates in relation to water quality in a tropical Indian harbour

ＩｎｔｒｏｄｕｃｔｉｏｎＩｎａｑｕａｔｉｃｅｃｏｓｙｓｔｅｍｓｂｉｏｌｏｇｉｃａｌｃｏｍｍｕｎｉｔｉｅｓａｒｅｒｅｍａｒｋａｂｌｙｃｏｍｐｌｅｘｉｎｂｏｔｈｔｈｅｉｒｏｐｅｒａｔｉｏｎａｎｄｒｅｓｐｏｎｓｅｔｏａｎｔｈｒｏｐｏｇｅｎｉｃａｃｔｉｖｉｔｉｅｓ.Ｔｈｉｓｈａｓｌｅｄｍａｎｙｉｎｖｅｓｔｉｇａｔｏｒｓｔｏｃｏｎｄｕｃｔｌａｂｏｒａｔｏｒｙａｎｄｆｉｅｌｄｓｔｕｄｉｅｓｆｏｒｅｖａｌｕａｔｉｎｇｔｈｅｅｃｏｌｏｇｉｃａｌｒｉｓｋｐｏｓｅｄｂｙｈｕｍａｎｓｔｏｅｃｏｓｙｓｔｅｍ(Ｃａｉｒｎｓ…     

微型生物与金属腐蚀的研究

主要研究了海洋微生物与金属腐蚀的相关性。通过调查、分析海洋微生物的性质,尤其是硫酸盐还原菌（ＳＲＢ）,用移植埋片法对海底沉积物中ＳＲＢ含量的分析,建立了ＳＲＢ含量与腐蚀率之间的表象关系,为海洋工程设计提供了重要数据。     

兰州市城市生活垃圾处理研究

城市生活垃圾是指在城市日常生活中或者为城市日常生活提供服务的活动中产生的固体废物以及法律、行政规定视为城市生活垃圾的固体废弃物.随着中国城市化进程的加快和人民生活水平的提高,城市生活垃圾也在以每年8%～10%的速度增长,若垃圾问题得不到妥善解决,就会制约兰州市的发展.在对兰州市城市生活垃圾处理现状及存在问题分析的基础上,根据兰州市生活垃圾的特性,提出兰州市城市生活垃圾的处理办法:兰州市城市生活垃圾应当推行分类收集制度,由目前单一的卫生填埋处理走向资源化综合处理.     

Efficient degradation of organic pollutants by S-NaTaO3/biochar under visible light and the photocatalytic performance of a permonosulfate-based dual-effect catalytic system

Removing large concentrations of organic pollutants from water efficiently and quickly under visible light is essential to developing photocatalytic technology and improving solar energy efficiency. This study used a simple hydrothermal method to prepare a non-metallic, S-doped NaTaO₃ (S-NTO) photocatalyst, which was then loaded onto biochar (BC) to form a S-NTO/BC composite photocatalyst. After uniform loading onto BC, the S-NTO particles transformed from cubic to spherical. The photogenerated electron-hole pair recombination probability of the composite photocatalyst was significantly lower than those of the NTO particles. The light absorption range of the catalyst was effectively widened from 310 nm UV region to visible region. In addition, a dual-effect catalytic system was constructed by introducing peroxymonosulfate (PMS) into the environment of the pollution to be degraded. The Rhodamine B, Methyl Orange, Acid Orange 7, tetracycline, and ciprofloxacin degradation efficiency at 40 mg/L reached 99.6%, 99.2%, 84.5%, 67.1%, and 70.7%, respectively, after irradiation by a 40 W lamps for 90 min. The high-efficiency visible-light catalytic activity of the dual-effect catalytic system was attributed to doping with non-metallic sulfur and loading of catalysts onto BC. The development of this dual-effect catalytic system provides new ideas for quickly and efficiently solving the problem of high-concentration organic pollution in aqueous environments, rationally and fully utilizing solar energy, and expanding the application of photocatalytic technology to practice.     

模拟垃圾填埋场稳定化过程研究

采用垃圾填埋堆体模拟装置，对杭州市城市生活垃圾在１９９８年２月至１９９８年１０月期间稳定化过程中的垃圾渗滤液水质指标变化、堆体内部温度变化、垃圾减量化、沉降高度和产气量进行了研究，装入模拟装置的２２１ｋｇ生活垃圾经８个月的降解后，垃圾减量化显著，总量降至１２７ｋｇ，其中有机组分由９４．８ｋｇ（４２．９％）降至２０．９３ｋｇ（１６．５％），无机组分由７２．７１ｋｇ（３２．９％）降至５３．６５ｋｇ（４     

城市生活垃圾综合处理系统的选择

以上海城市生活垃圾处置为对象，利用层次分析方法，选择了分选回收＋堆肥＋卫生填埋的综合处置系统，并且确定了堆肥方式应首先考虑仓式静态好氧堆肥。经过运行费比较，所选择的综合处置系统比现行的处置系统具有明显的优势。     

锌镉还原法的海水硝酸盐浓度

按照《海洋调查规范》(1991)中锌镉还原法 ,用三对基体来配制NO3 -标准溶液 :NaCl水 (31gNaCl加纯水至 1L)与无氮东海海水ECS、《海洋调查规范》(1991)人工海水SAS(NaCl水加MgSO4)与ECS和Strick land Parsons(1972 )人工海水SP72 (SAS加NaHCO3 )与ECS。经测定 ,且忽略标准曲线方程的截距 ,纯水与ECS的NO3 -还原率比为 0 .2 6 6 ,NaCl水与ECS的比为 0 .70 6 ,SAS与ECS的比为 0 .90 1,而SP72与ECS的比则为1.0 0 9。显然 ,用ECS和等价的SP72定出的值最接近天然海水中NO3 -的浓度。由《海洋调查规范》(1991)SAS定出的浓度须乘上 0 .90 1～ 0 .95 6后才接近海水中NO3 -浓度。     

Direct hydride derivatization of methyl- and ethylmercury chlorides in aqueous solution with KBH4

A convenient hydride derivatization procedure of methyl-and ethylmercury chlorides to volatile hydrides was reported. In sealed vials methylmercury and ethylmercury compounds in acidic aqueous solutions were converted into their volatile forms by the reaction with potassium tetrahydroborate(KBH4) and elvolved to the headspace of the vials. The gaseous analytes in the headspace were extracted and concentrated by solid phase microextraction(SPME) and injected into gas chromatography (GC) for separation and identified by mass selective detector(MS).