STAC有机膨润土的表征及其处理垃圾渗滤液的研究

文章以钙基蒙脱石为原料,经钠化后与十八烷基三甲基氯化铵(又称1831,简称STAC)进行离子交换反应,合成有机膨润土,通过XRD、IR 、SEM等测试仪,对有机膨润土的结构进行了分析,同时利用改性后的STAC有机膨润土对某垃圾填埋场中的渗滤液进行处理,用GC/MS对处理前后垃圾渗滤液中主要有机组分进行了分析,结果表明,...     

戊唑醇残留分析方法实验室内质量控制研究

文章确立了小麦、香蕉中戊唑醇残留检测方法,小麦样品加水10 mL用丙酮为萃取溶剂,石油醚液液分配,中性氧化铝柱层析净化,用气相色谱(GC-NPD)检测。香蕉样品加水5 mL用丙酮为萃取溶剂,石油醚液液分配,浓缩后用气相色谱(GC-NPD)检测。分别设置不同时间批次,同一批次间的平行样及实验室内人员分析,分别从方法灵敏度、方法准确度、方法精密度及其质量控制图、标准工作液的稳定性来探讨该方法的可靠性,结果表明该方法可以作为香蕉和小麦种戊唑醇残留检测的标准分析方法。     

用GC/MS分析火灾后苯板产生固体废物中的有机物

采用GC/MS方法对某苯板厂火灾后产生的固体废弃物进行检测分析.结果表明,在苯板火灾后产生的固体废弃物中检测出61种化合物,其中被美国EPA列入优先污染物的苯系物、萘和蒽等占总有机物12.2％.     

GC/MS法测定生物样品中多溴联苯醚类化合物

本研究建立了多溴联苯醚（PBDEs）生物样品分析方法,获得了优化的前处理条件、气相色谱和质谱检测条件.对定性定量方法及实验条件必须满足的要求进行了评价.通过质量控制（quality control, QC）对整个方法进行了验证.结果证明,本研究所建立的分析方法满足生物样品PBDEs测定的要求,回收率在50.5%～112.3%之间,回收率相对标准偏差在5.3%～9.9%之间,方法检测限在7.1～161.8 pg/g之间.在建立的方法基础上,测定了部分养殖和野生鱼类样品,测得的野生鳜鱼和鲫鱼以及2个养殖鲈鱼样品的结果分别为1.53、1.11、5.31和6.15 ng/g(干重),其中主要的同族体为BDE47.     

有机磷农药对缢蛏[Sinonovacula constricta (Lamarck)]显微结构的影响

在实验室模拟缢蛏的生长环境,研究乐果和三唑磷对缢蛏的毒性效应.以气相色谱法测定缢蛏体内有机磷农药的含量,并通过光镜观察有机磷农药对缢蛏鳃和消化腺显微结构的影响.结果表明:缢蛏体内乐果和三唑磷的含量随着水体中有机磷农药的增加而增加,有很好的剂量-效应关系,但是无线性相关性.乐果和三唑磷对缢蛏鳃显微结构的影响是:鳃丝变短,鳃丝间隔和基底膜结缔组织增生,鳃孔、血管腔堵塞;不同的是:在乐果胁迫下,上皮细胞纤毛脱落严重,而三唑磷胁迫下,上皮细胞纤毛增生.乐果和三唑磷对缢蛏消化腺显微结构的影响主要表现为腺细胞界限模糊,腺泡水肿变形、部分坏死;结缔组织增生,细胞间质疏松,出现许多空泡;有机磷农药的浓度高时消化腺细胞变性、坏死,细胞质囊泡化.     

Tracing the sources of refractory dissolved organic matter in a large artificial lake using multiple analytical tools

Structural and chemical characteristics of refractory dissolved organic matter (RDOM) from seven different sources (algae, leaf litter, reed, compost, field soil, paddy water, treated sewage) were examined using multiple analytical tools, and they were compared with those of RDOM in a large artificial lake (Lake Paldang, Korea). Treated sewage, paddy water, and field soil were distinguished from the other sources investigated by their relatively low specific UV absorbance (SUVA) values and more pronounced fulvic-like versus humic-like fluorescence of the RDOM samples. Microbial derived RDOM from algae and treated sewage showed relatively low apparent molecular weight and a higher fraction of hydrophilic bases relative to the total hydrophilic fraction. For the biopolymer types, the presence of polyhydroxy aromatics with the high abundance of proteins was observed only for vascular plant-based RDOM (i.e., leaf litter and reed). Molecular weight values exhibited positive correlations with the SUVA and the hydrophobic content among the different RDOM, suggesting that hydrophobic and condensed aromatic structures may be the main components of high molecular weight RDOM. Principal component analysis revealed that approximately 77% of the variance in the RDOM characteristics might be explained by the source difference (i.e., terrestrial and microbial derived) and a tendency of further microbial transformation. Combined results demonstrated that the properties of the lake RDOM were largely affected by the upstream sources of field soil, paddy water, and treated sewage, which are characterized by low molecular weight UV-absorbing and non-aromatic structures with relatively high resistance to further degradation.     

GC/MS法测定润滑油基础油中多环芳烃

对润滑油基础油中多环芳烃的气相色谱/质谱(GC/MS)测定方法进行了研究,探讨了样品的提取,固相萃取柱净化等前处理方法,同时也对仪器测定条件进行了优化.结果表明,在检测润滑油基础油中多环芳烃时,经优化的GC/MS法的加标回收率和精密度均达到较满意的水平.     

A new direct thermal desorption-GC/MS method: Organic speciation of ambient particulate matter collected in Golden, BC

Particulate matter having an aerodynamic diameter less than 2.5 μm (PM2.5) is thought to be implicated in a number of medical conditions, including cancer, rheumatoid arthritis, heart attack, and aging. However, very little chemical speciation data is available for the organic fraction of ambient aerosols. A new direct thermal desorption-gas chromatography/mass spectrometry (TD-GC/MS) method was developed for the analysis of the organic fraction of PM2.5. Samples were collected in Golden, British Columbia, over a 15-month period. n-Alkanes constituted 33–98% by mass of the organic compounds identified. PAHs accounted for 1–65% and biomarkers (hopanes and steranes) 1–8% of the organic mass. Annual mean concentrations were: n-alkanes (0.07–1.55 ng m⁻³), 16 PAHs (0.02–1.83 ng m⁻³), and biomarkers (0.02–0.18 ng m⁻³). Daily levels of these organics were 4.89–74.38 ng m⁻³, 0.27–100.24 ng m⁻³, 0.14–4.39 ng m⁻³, respectively. Ratios of organic carbon to elemental carbon (OC/EC) and trends over time were similar to those observed for PM2.5. There was no clear seasonal variation in the distribution of petroleum biomarkers, but elevated levels of other organic species were observed during the winter. Strong correlations between PAHs and EC, and between petroleum biomarkers and EC, suggest a common emission source – most likely motor vehicles and space heating.     

Pesticide dissipation curves in peach,pear and tomato crops in Uruguay*

Dissipation curves of azoxystrobin and of the neonicotinoids acetamiprid and thiacloprid in peach; azinphos-methyl and carbaryl in pear and azoxystrobin, chlorfenapyr and chlorpyrifos in high-tunnel tomato crops were studied in the Southern region of Uruguay. An analytical methodology based on solid phase extraction (SPE) and detection by High Performance Liquid Chromatography with Diode Array Detector (HPLC/DAD) was used for acetamiprid and thiacloprid. Coupled SPE and detection by Gas Chromatography with Mass Selective Detector (GC/MSD) was used for the detection of azinphos-methyl, azoxystrobin, carbaryl, chlorfenapyr and chlorpyrifos residues. Curves were modeled mathematically with Solver program of Microsoft Excel®. The best fit for acetamiprid and thiacloprid in peach was achieved with the exponential model (r²=0.961 and 0.944, respectively). In the case of peach fruits there is not a Maximum Residue Limit (MRL) for acetamiprid in the Codex Alimentarius, while 0.5 mg/kg is the value rated for thiacloprid. The MRLs accepted by the European Union (EU) are 0.1 mg/kg for acetamiprid and 0.3 mg/kg for thiacloprid. According to the curves determined in these experiments, thiacloprid residues 10 to 12 days after application (daa) were below the MRLs established by both sources. In the case of acetamiprid, 25 daa would be required, according to the exponential mathematical model, to get residues levels below the MRL values established by the EU. For azinphos methyl in pear, the residues detected were mathematically fitted to an exponential model (r²=0.999). According to it, residue levels under the MRL established by the EU (0.05 mg/kg) are gotten in our conditions in 20 daa. In plastic tunnel tomato chlorfenapyr residues were not detected from 16 daa, having the dissipation curve an exponential trend. In the same condition, there was not a decay of the azoxystrobin concentration during a 24-day trial, being it around 0.40 ± 0.05 mg/kg.     

Multiresidue determination of carbamate,organochlorine, organophosphorus,and dicarboximide pesticides in lettuce by GC/MS

An extraction method based on matrix solid-phase dispersion was developed to determine pirimicarb, methyl parathion, malathion, procymidone, α -endosulfan and β -endosulfan in lettuce using gas chromatography-mass spectrometry. The best results were obtained using 4.0 g of lettuce, 2.0 g of silica as dispersant sorbent, 0.1 g of activated carbon as clean up sorbent and acetonitrile as eluting solvent. The method was validated using lettuce samples fortified with pesticides at six different concentration levels (0.1 to 2.0 mg/kg). Average recoveries (7 replicates) ranged from 50 to 120 %, with relative standard deviations between 0.6 and 8.0 %. Detection and quantification limits for lettuce ranged from 0.01 to 0.02 mg/kg and 0.04 to 0.10 mg/kg, respectively.