不同反胶束体系萃取纤维素酶的条件优化对比研究

采用3种不同的表面活性剂双(2-乙基己基)磺基琥珀酸钠AOT、十六烷基三甲基溴化铵CTAB及鼠李糖脂RL)溶于正己醇/异辛烷相构建不同的反胶束体系,并对比研究了不同反胶束体系萃取纤维素酶的优化条件.分别探讨了水相pH值、表面活性剂浓度、离子强度和离子种类对纤维素酶萃取效率的影响.实验结果如下:在实验条件下,AOT、CTAB和RL 3种反胶束体系水相最佳pH值分别为3.0、8.0和3.0;表面活性剂最佳浓度依次为:AOT 23.7mmol/L、CTAB 15mmol/L和RL 2.75mmol/L;水相中NaCl浓度会影响纤维素酶的萃取率,3种表面活性剂构建的反胶束体系萃取纤维素酶的萃取率均随着盐离子浓度的增大而降低;水相中离子种类也会影响纤维素酶的萃取率.比较不同反胶束体系在最佳条件下萃取纤维素酶的最佳萃取率:CTAB>AOT>RL.     

SPE-RRLC-MS/MS法测定制药废水中青霉素G

建立了利用固相萃取-高分离度快速液相色谱-串联质谱(SPE-RRLC-MS/MS)测定制药废水中青霉素G残留的方法。水样以30%硫酸锌+20%亚铁氰化钾作为沉淀剂沉淀蛋白质后,上清液采用Oasis HLB固相萃取柱富集和净化,以0.01 mol/L乙酸铵溶液(加0.1%甲酸)+乙腈作为流动相进行等度洗脱,经Agilent Plus C18柱分离后,在串联质谱ESI(+)源下进行MRM检测。该方法的青霉素G检出限(S/N=3)为0.02μg/L,目标物在0.0020～1.0 mg/L范围内线性关系良好,线性相关系数为0.9997。在0.20,1.0,2.0μg/L添加水平平均回收率为74.6%～101.4%,相对标准偏差为4.49%～8.17%。该方法灵敏度高、重现性好、定性定量准确,可满足制药废水中青霉素G残留检测的要求。     

Chemical speciation and potential ecological risk assessment of heavy metals in volcanic rocks of Southern Qinghai,China

ABSTRACT

Seven volcanic rocks samples were collected from Southern Qinghai to analyze chemical speciation and migration behavior of heavy metals by sequential chemical extraction procedure and column leaching test. The geo-accumulation index, ecological risk index and the risk assessment code were applied to assess the heavy metal pollution and potential environmental effects in this area. Results revealed that the total concentrations of heavy metals did not exceed the background values in soil of this area. Most of the samples produced acid rock drainage. The order of heavy metal migration and transformation sequence in the volcanic rocks of Zhiduo region was Cd?>?Pb?>?As?=?Cu?=?Zn?=?Mn based on the geo-accumulation index and Cd caused heavy pollution, which was also confirmed by the leaching test. Moderate potential ecological risk posed by heavy metals occurred in the study area based on the potential ecological risk index. Cd contributed to most of ecological risk while the remaining heavy metals (except As) exerted medium to high risks to the environment according to the risk assessment code evaluation results. In summary, volcanic rocks possessed potential risks to the surroundings due to potential release of heavy metals. Cd that caused the pollution should be paid special attention.     

Remobilization of selected metal ions from Nile sediment (Egypt) according to sequential extraction and metal–EDTA complex

River sediments are basic components of our environment, providing nutrients for living organisms and serving as sinks for deleterious chemical species. The metal contents may be remobilized and released back into waters with changes in environmental conditions, thus affecting living organisms and human activities. This paper aims to determine the effect of a synthetic anthropogenic chelating agent (EDTA) as industrial discharges on the remobilization of several metals (Cu, Zn, Cd, and Pb) in River Nile sediments (at Aswan and Mansoura cities) under different concentrations and pH values, and to investigate the influence of metal–EDTA complexes on this remobilization. For these purposes, sequential extraction and experiments on the effect of pH and metal EDTA complex were carried out on the two representative sediment samples south and north of the River Nile in Egypt. The results of sequential extraction show that most of metal contents present in the residual form (Cu, 11.36–72.34%; Pb, 29.64–66.67%; and Zn, 43.76–50.09% at Aswan and Mansoura, respectively). Non-residual fractions which may be available for the remobilization by EDTA represented anthropogenic (industrial, agriculture, and domestic discharges) and lithiopogenic (metals bound to Fe and Mn oxides) sources. A clear increase was detected for Cu and Zn remobilization from the increase in EDTA concentrations, in contrast, Cd independent of the EDTA concentration and slight influence on Pb content. The remobilization of metals as a function of pH exhibited. The metals were greatly remobilized under the complexing action of EDTA, showing that some of these elements were adsorbed on the sediments. The remobilization rate of metals was dependent upon the added metal–EDTA complex (with the exchange rate being in the order Ca–EDTA>Zn–EDTA>Cd–EDTA>Cu–EDTA>Pb–EDTA), due to the stability constant of the metal–EDTA complex. The results of these experiments showed that heavy metals are greatly remobilized under the complexing action of EDTA when it is present in excess, so all precautions should be taken to prevent any wastewater containing EDTA or any chelating agents discharging directly or indirectly via the River Nile stream because most EDTA remains in the aquatic phase. The ability of this portion to remobilize metals from sediments should be taken into account.     

Spatial distribution of perfluorooctane sulfonate (PFOS) in major rivers in southwest Nigeria

Concentrations of perfluorooctane sulfonate (PFOS) were measured for the first time in major rivers within southwest, Nigeria. PFOS was concentrated from water and sediment using solid-phase extraction, identified and quantified with high-performance liquid chromatography coupled with tandem mass spectrometry. Concentrations of PFOS ranged from 1.71 to 16.19 ng L^?1 in water, and from 1.64 to 10.29 ng g^?1 in sediments across all locations. Comparatively, the concentrations of PFOS observed in this study were within the range ever measured in the environment. Field-based sediment water distribution coefficients (log K_d, L kg^?1) ranged from 2.08 to 3.56. While no correlation was observed between K_d and organic carbon contents, there was significant positive correlation between K_d and salinity (r² = 0.7867), which suggested that activities capable of increasing salinity can enhance PFOS removal from the environment.     

Determination of pentachlorophenol in human urine using solid phase extraction and GC‐MS analysis with stable isotope dilution

A method for the determination of pentachlorophenol (PCP) in human urine was developed. Urine samples were fortified with ¹³C₆‐IabeIed PCP and hydrolyzed with sulfuric acid prior to extraction. The urine samples were then passed through preconditioned solid phase extraction cartridges containing octadecylsilane adsorbent. The PCP was subsequently eluted from the cartridge with ethyl acetate and converted to pentachloroanisole prior to GC‐MS analysis. GC‐MS quantitation was performed using the technique of stable isotope dilution. Percent recoveries averaging 100, 97, and 111% were obtained for replicate urine samples fortified with approximately 2, 20, and 200 ng/mL of PCP, respectively. The method detection limit was estimated to be 0.2 ng/mL.     

Online solid phase preconcentration using EGDMA–MAA copolymer for lead determination by FAAS

A Ethylene glycol dimethacrylate (EGDMA) methacrylic acid (MAA) resin was used for preconcentration of lead at trace levels in water samples. For this purpose, a flow-injection, solid phase extraction method was developed for the determination of lead by flame atomic absorption spectrometry. Lead ions were sorbed on a EGDMA–MAA column at pH 4, followed by an elution step using 288 µL of 4.0 M nitric acid solution and determination by flame atomic absorption spectrometry. Optimum conditions for quantitative sorption involving the pH, sample volume, loading and elution flow rates, eluent type, and volume were investigated. A 868-fold enrichment factor could be reached. The detection limit for the water samples, estimated from the noise on the signal obtained for 250 mL of 10 µg L^?1 loaded at 4.9 mL min^?1 was 1.04 µg L^?1. The method was applied for lead determination in river water samples collected in Edirne, Turkey. Recoveries of spiked solutions (10 µg L^?1) to river water samples were quantitative. Finally, the method was validated by the analysis of certified reference material SRM 2704 (Buffalo River Sediment).     

A new procedure combining GC-MS with accelerated solvent extraction for the analysis of phthalic acid esters in contaminated soils

An optimized procedure based on gas chromatography-mass spectrometry (GC-MS) combined with accelerated solvent extraction (ASE) is developed for the analysis of six phthalic acid esters (PAEs), which are priority soil pollutants nominated by United States Environmental Protection Agency (USEPA). Quantification of PAEs in soil employs ultrasonic extraction (UE) (USEPA 3550) and ASE (USEPA 3545), followed by clean up procedures involving three different chromatography columns and two combined elution methods. GC-MS conditions under selected ion monitoring (SIM) mode are described and quality assurance and quality control (QA/QC) criteria with high accuracy and sensitivity for target analytes were achieved. Method reliability is assured with the use of an isotopically labeled PAE, di-n-butyl phthalate-d4 (DnBP-D4), as a surrogate, and benzyl benzoate (BB) as an internal standard, and with the analysis of certified reference materials (CRM). QA/QC for the developed procedure was tested in four PAE-spiked soils and one PAE-contaminated soil. The four spiked soils were originated from typical Chinese agricultural fields and the contaminated soil was obtained from an electronic waste dismantling area. Instrument detection limits (IDLs) for the six PAEs ranged 0.10–0.31 μg·L^-1 and method detection limits (MDLs) of the four spiked soils varied from a range of 20–70 μg·kg^-1 to a range of 90– 290 μg·kg^-1. Linearity of response between 20 μg·L^-1 and 2 mg·L^-1 was also established and the correlation coefficients (R) were all>0.998. Spiked soil matrix showed relative recovery rates between 75 and 120% for the six target compounds and about 93% for the surrogate substance. The developed procedure is anticipated to be highly applicable for field surveys of soil PAE pollution in China.     

土壤宏蛋白质组学蛋白质提取方法及其应用

土壤宏蛋白质组学在揭示土壤微生物功能、代谢与环境相互作用方面具有广阔的应用前景,但由于土壤样品的特殊性,土壤蛋白质提取步骤是限制土壤宏蛋白质组学大规模应用的瓶颈之一.本文从样品制备、提取方法、影响因素等方面综述了土壤蛋白提取方面的研究进展.一般来说,根据实验目的、蛋白种类及后续研究方法设计相应的分组成收集策略才能取得较好的提取效果.土壤总蛋白、胞内蛋白与胞外蛋白分别有不同的提取方法.总蛋白提取一般采用直接提取法;胞外蛋白不需要裂解;胞内蛋白提取方法有直接提取法和间接提取法等.裂解、浓缩、去除腐殖质的方法以及提取液、pH值的选择等也会影响提取效果.此外,简单介绍了土壤宏蛋白质组学的应用,并对今后的研究工作提出展望.表1参36     

水中痕量阿特拉津的测定方法研究

采用固相萃取与高效液相色谱结合的方法测定了水样中痕量阿特拉津的含量,研究了最佳固相萃取条件:选择洗脱液为乙腈,过样流速为5.0 mL/min。最佳的色谱条件:流动相为乙腈和水,温度为25℃,流速为1.0 mL/min,检测波长为222 nm。阿特拉津质量浓度在0.05～5 mg/L范围内线性关系良好,回归方程y=219.71x+2.2343,回收率平均值为98.46%,将该方法应用于实际环境水样的分析测定,操作简单,结果准确。