基于改进偏最小二乘法的近红外快速分析强化生物除磷污泥胞内PHA

聚β羟基烷酸酯(PHA)是强化生物除磷系统中颗粒污泥胞内重要碳源和能源,其快速测定对强化生物除磷机理研究有重要意义. 采用Savitzky-Golay平滑法(SG)-多元散射校正法(MSC)对污泥的近红外光谱进行预处理,通过改进的偏最小二乘法(iPLS、siPLS、biPLS)建立污泥样品近红外光谱与PHA含量的定量分析模型.结果表明,SG-MSC预处理减弱噪声和背景等表面因素对光谱的影响,采用联合区间偏最小二乘法(siPLS)将全光谱等分为30个子区间, 联合子区间[13 21 24 29]建立的模型预测效果最优,其交互验证均方根误差(RMSECV)和预测均方根误差(RMSEP)分别为0.2018和0.3120,校正集和预测集相关系数分别达到0.9925和0.9391,该光谱区段与PHA分子结构中C-H的伸缩变形、弯曲振动和C=O的伸缩振动密切相关. 改进偏最小二乘有效地优化光谱建模区域,提高模型预测能力,实现污泥胞内PHA含量的快速定量分析.     

Choice of chelating antidotes for acute cadmium intoxication∗

During acute oral intoxication by cadmium compounds, gastrointestinal epithelial damage contributes to immediate toxicity. However, secondary systemic toxicity may develop due to intestinal uptake of cadmium. This review presents an evaluation of the effects of chelators on the acute toxicity of cadmium after parenteral or oral exposure and on the intestinal uptake of cadmium. This review shows:

1. Chelating agents may affect the acute toxicity of cadmium in a variety of ways depending on the exposure route for cadmium and administration route for the chelator.

2. With regard to survival, systemic toxicity of absorbed cadmium is of major importance, as intraperitoneal administration of chelators could eliminate or reduce mortality due to orally administered cadmium chloride.

3. Lipophilicity of chelators and their cadmium complexes may result in extensively augmented intestinal uptake. However, hydrophilic chelators may efficiently reduce the intestinal cadmium uptake.

4. For hydrophilic chelators, the stability of the cadmium complex is an important determining factor of efficacy.

5. The optimal oral antidote towards orally administered cadmium are the BAL analogs, especially DMSA, while the optimal intraperitoneal antidotes towards orally or intraperitoneally administered cadmium are the higher members of the polyaminopolycarboxylate family, especially TTHA.

6. When administered simultaneously (DMSA orally and TTHA intraperitoneally), these chelators synergistically reduce the whole‐body retention of cadmium.

In conclusion, chelation treatment in acute oral cadmium intoxication should first prevent/reduce intestinal damage and uptake by rapid oral administration of a chelating antidote and then alleviate systemic toxicity due to absorbed cadmium and enhance renal/biliary cadmium excretion by parenteral administration of a chelating antidote.     

Photolysis of 3‐(3,4‐dichlorophenyl)‐1, 1 ‐Dimethylurea (Diuron) in dilute aqueous solution

Diuron samples at 40mg/L concentration were photolyzed with ultraviolet lamps and with natural sunlight to determine if data from ultraviolet lamp photolysis could be used to predict results from sunlight photolysis. Seven photoproducts were identified from the photolysis experiments. The identified photoproducts and the photoproduct yields were essentially the same for the two light sources.     

Electrochemical hydride generation of tin(II) and its determination by electrothermal atomic absorption spectrometry with in situ trapping in the graphite tube atomizer

An electrolytic hydride generation system for the determination of tin(II) by means of batch electrochemical hydride generation-electrothermal atomic absorption spectrometry (EcHG-ETAAS) with in situ trapping in a graphite tube atomizer is described. The effects of four permanent chemical modifiers – palladium, tungsten, iridium, and platinum – for graphite tube treatment on analyte absorbance and the effects of four cathode materials, i.e., Pb, Sn, Pb–Sn alloy, and glassy carbon, are checked. Three electrolytes, i.e., nitric acid, sulfuric acid, and hydrochloric acid, are examined as catholyte solutions. The influence of several parameters on EcHG is investigated using multivariate and univariate methods. Interferences of some concomitant ions are evaluated. The calibration curve is linear from 1 to 200?µg?L^?1, with a detection limit of 0.8?µg?L^?1 and a relative standard deviation of 6.2% (n?=?3) for 100?µg?L^?1 Sn(II). The proposed method was successfully applied in the analysis of real environmental water samples and reference materials, and good spiked recoveries over the range of 93.1–115% were obtained. The proposed technique provides a means for developing hydride generation of other elements.     

Dispersive liquid–liquid microextraction of cadmium(II) for preconcentration prior to flame atomic absorption spectrometric detection in water

A dispersive liquid–liquid microextraction procedure for cadmium(II) as its 2-(5-bromo-2-pyridylazo)-5-diethylamino-phenol chelate is presented. Carbon tetrachloride and methanol were used as extraction and dispersive solvents, respectively. After phase separation, the preconcentrated-separated cadmium(II) is determined by flame atomic absorption spectrometry with a microinjection technique. The factors which affected the extraction efficiency, i.e. the pH of the sample solution and the volumes of reagent and sample were investigated. The effects of some alkali, alkali earth, and transition metal ions, and of some anions on the recovery of cadmium were also studied. A preconcentration factor of 250 was obtained for a sample volume of 50?mL under optimum conditions. The method was validated by analysis of certified reference materials and applied to some water samples from Turkey.     

Comparison of sample digestion procedures for the determination of trace elements in antarctic krill by GF‐AAS

Two independent digestion procedures for Antarctic krill samples were compared. Dry ashing (DA) and microwave (MW) acid‐assisted digestion were tested for decomposing the samples to determine essential (Cu, Fe, Cr) and toxic elements (Cd, Pb) by graphite furnace‐atomic absorption spectrometry (GF‐AAS). A mixture of HNO₃ and H₂O₂ as digesting agent was used in the microwave procedure. For the dry ashing digestion, the organic matter was oxidated at 480°C in an open system. Both digestion methods were compared in terms of accuracy and applied to the analysis of a certified reference material: MURST‐ISS‐A2 (Antarctic krill).

The detection limits for the five elements analysed ranged from 3 to 150 ng g^‐1. Both digestion procedures are suitable for the decomposition of krill samples. However, dry ashing is not recommended to determine Pb and Cd because losses can occur.     

水汽对光腔衰荡光谱系统（CRDS）法测定CH_4的影响

分析了CRDS法测定CH4浓度与水汽含量间的关系,并建立了水汽含量在0.50%—2.45%（体积比,以V/V表示,下同）范围内的有效校正方法.采用CRDS法对水汽含量为0.93%的CH4标气进行多次测量,测量值经校正后与理论值的偏差均小于2.0×10-9（体积比,以V/V表示,下同）,最大偏差1.8×10-9,优于大气本底CH4观测质控标准.校正瓦里关站CRDS系统试运行期间的CH4实测数据（水汽含量为0.50%—2.45%）,与该站气相色谱-氢火焰离子化检测器系统（GC-FID系统,下同）同期测量结果相比,38.48%的数据偏差小于2.0×10-9,说明在系统未配备超低温冷阱除水单元之前,本文研究的校正方法适用于观测数据的校正.     

不同强度冷刺激对大鼠心脏、大脑、睾丸和肺脏中CIRP表达的影响

采用Western blot和实时荧光定量RT-PCR方法,研究不同强度不同时间冷刺激后大鼠心脏、大脑、睾丸和肺脏中冷诱导RNA结合蛋白(CIRP)的表达情况.结果表明:常温(20℃±1℃)下大鼠4种组织中均存在一定的CIRP的表达;急性冷刺激组(-10℃±1℃、-4℃±1℃、0℃±1℃、4℃±1℃)心脏、大脑和睾丸中CIRP mRNA表达在冷刺激0～6 h呈上升趋势,6 h时达到最高值,随后呈下降趋势,肺脏中CIRP mRNA表达在0～6 h呈下降趋势,在6 h时达到最低值,随后呈上升趋势;慢性冷应激组(10℃±1℃)大鼠心脏、大脑和睾丸3种组织中CIRP mRNA在不同时间点(1周、2周、3 W周)的表达均高于正常对照组(P>0.05),肺脏CIRP mRNA表达均低于对照组(P>0.05),并且同一组织不同时间点之间差异不显著(P>0.05).可见冷刺激后CIRP的表达存在一定规律并且表现出组织特异性,可能与组织保护特异性有关.     

硫精砂制酸尾气达标排放及资源化回收利用

硫精砂制酸排出的尾气中SO2含量一般为0.2%~0.5%(体积分数,下同),目前国内普遍采用一转一吸或两转两吸流程来吸收硫酸尾气,使SO2质量浓度达到低于860 mg/m3的国家二级排放标准。但随着国家颁布新的《硫酸工业污染物排放标准》,要求现有硫酸企业SO2排放质量浓度必须于2013年10月1日前全部低于400mg/m3,因此必须对尾气进行进一步的处理。本文结合湖北新洋丰肥业股份有限公司和武汉中东化工有限公司硫酸生产的实际情况,总结了采取三段氨吸法处理硫酸尾气的技术改造和资源化回收利用。     

纳米X型沸石制备及其对含铜废水处理

采用水热合成法以煅烧高岭土为原料合成了纳米级X型沸石分子筛,并采用透射电镜(TEM)和X射线衍射(XRD)进行了表征.研究了影响纳米X型沸石分子筛对Cu(Ⅱ)吸附的因素,包括纳米X型沸石分子筛用量、pH值、接触时间和温度.结果表明:投加0.4 g纳米X沸石分子筛,在pH为5.0、温度为25 C、吸附时间为10 min情况下,去除率达到99.65%,最大吸附量可达101.4 mg/g.采用0.5 mol/L的Na2EDTA能较完全洗脱纳米级X型沸石分子筛所吸附的Cu(Ⅱ),表明纳米级X型沸石分子筛能循环使用,可应用于含铜废水的处理.