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1.
建立了一种吹扫捕集-气相色谱/质谱法同时测定水中的乙醛、丙烯醛、丙烯腈、吡啶、松节油和丁基黄原酸的分析方法。结果表明,吹扫时间、脱附时间、脱附温度和盐酸用量是影响目标化合物测定的关键因素,对吹扫捕集条件优化后,各目标化合物线性良好,相关系数均0.998,检出限为0.13~2.22μg/L,加标回收率为80.5%~111%,相对标准偏差为1.1%~10.9%,能够满足地表水环境质量标准的要求。  相似文献   

2.
水中的乙醛、丙烯醛、丙烯腈和吡啶经吹扫捕集、解吸后,用HP-VOC毛细管色谱柱进行GC分离,用GC-MS法选择离子模式(SIM)下进行检测,外标法定量。结果表明,选择取样量25 m L,吹扫流量为40 m L/min,吹扫温度为40℃,吹扫时间为15 min,解吸时间为2 min,解吸温度为200℃,烘焙时间20 min,乙醛和吡啶质量浓度在0.025~0.60 mg/L之间,丙烯醛和丙烯腈质量浓度在0.002 5~0.10 mg/L之间时,校准曲线呈线性关系,相关系数r0.995,乙醛、丙烯醛、丙烯腈和吡啶的方法检出限分别为0.001 6,0.001 3,0.000 5和0.002 1 mg/L。对3个不同浓度样品进行空白加标实验,测量的回收率为87.8%~114.3%,相对标准偏差(n=6)为2.51%~10.4%。对3批实际水样进行分析,其中一个废水水样加标回收率为79.2%~103.8%,相对标准偏差(n=6)为3.04%~6.39%。  相似文献   

3.
采用吹扫捕集-气相色谱/质谱联用法测定水中的丙烯醛和丙烯腈,方法在5.00μg/L~200μg/L范围内线性良好,方法检出限分别为4.9μg/L和0.3μg/L。用该方法测定3个质量浓度水平的空白加标样,7次测定结果的RSD为2.8%~6.7%,加标回收率为90.4%~98.3%。用该方法测定某水库和某河流的地表水,丙烯醛和丙烯腈均未检出。  相似文献   

4.
水中乙醛、丙烯醛和丙烯腈3种测定方法的对比   总被引:1,自引:0,他引:1  
对比研究了大体积直接进样填充柱气相色谱法、顶空-气相色谱法和吹扫捕集-气相色谱法等3种测定水中乙醛、丙烯醛和丙烯腈的方法.结果表明,大体积直接进样法设备简单,但手动进样耗力费时,且灵敏度低,精密度差,直接水样分析易影响色谱柱和检测器的使用寿命;顶空法稳定性好,线性范围宽,相关性和精密度好,适合较高浓度水样的分析;吹扫捕集法操作简便,峰形好,检出限低,回收率高,适合低浓度水样的分析.顶空法和吹扫捕集法自动化程度高,均适用于大批量样品分析.  相似文献   

5.
建立了同时测定水中54种挥发性有机物(VOCs)的吹扫捕集-气相色谱-质谱联用法,并对吹扫捕集条件进行了优化。优化后的方法,54种VOCs在0.50~40.00μg/L质量浓度范围内线性良好,相关系数R2均0.995 6,检出限为0.021~0.105μg/L,加标回收率为76.4%~110.8%,相对标准偏差为2.33%~15.8%。该法操作简单,消耗费用低,分析速度快,具有良好的灵敏度、回收率和重现性,能够满足生活饮用水中54种VOCs的同时测定。  相似文献   

6.
利用顶空—气相色谱对水中乙醛、丙烯醛、丙烯腈和吡啶进行检测分析,优化了实验参数。该方法在0.1~5.0 mg/L范围线性关系良好,相关系数大于0.999 6,当取样量为10 ml时,方法检出限分别为0.03、0.02、0.01、0.02 mg/L。该方法用于空白加标和实际水样分析,加标回收率为75.5%~113%,相对标准偏差在2.7%~7.1%。本方法操作简单,选择性好,灵敏度、准确度高,可用于地表水、生活污水和工业污水中乙醛、丙烯醛、丙烯腈和吡啶的测定,效果满意。  相似文献   

7.
建立了吹扫捕集-气相色谱/质谱法(GC-MS)测定饮用水源地水中乙醛的方法。方法的检出限为0.5μg/L,相对标准偏差为3.9%~4.6%,加标回收率为92.5%~97.8%。该方法操作简单,灵敏度高,适用于水源水中乙醛的测定。  相似文献   

8.
顶空气质联用法测定水中四乙基铅、松节油和丙烯腈   总被引:2,自引:1,他引:1  
利用顶空气相色谱-质谱(HS/GC-MS)联用法对水中的四乙基铅、松节油和丙烯腈进行了检测分析,优化了实验参数。该方法线性关系良好,相关系数为0.997 0~0.999 9, 检出限为0.1~1.2 μg/L;方法用于饮用水、生活污水和工业废水中四乙基铅、松节油和丙烯腈的测定,并进行加标回收率实验,加标回收率为94.5%~104.4%;相对标准偏差为4.4%~9.5%。结果表明,方法能用于饮用水和废水中四乙基铅、松节油和丙烯腈的测定,效果满意。  相似文献   

9.
通过探讨影响四乙基铅富集效率的捕集管类型、吹扫温度和吹扫时间等因素,建立了吹扫捕集-气相色谱法测定水质中四乙基铅的分析方法。实验结果表明,使用Tenax捕集管,在吹扫温度为50℃、吹扫15 min的条件下测定水质中的四乙基铅,捕集效率为97.6%~98.2%,在0~100μg/L范围内线性良好,检出限为0.03μg/L,加标回收率为93.2%~100.5%,相对标准偏差为1.6%~3.2%。方法操作简便快捷、准确、实用且绿色环保不消耗有机溶剂,适于水质中四乙基铅的测定。  相似文献   

10.
吹扫捕集-气相色谱质谱法测定土壤中四乙基铅   总被引:1,自引:1,他引:0  
文章系统研究了土壤中四乙基铅的吹扫捕集-气相色谱质谱测定方法,优化了吹扫捕集前处理条件参数。结果表明,吹扫时间13 min、吹扫温度60℃,脱附温度190℃,脱附时间1 min为最佳的吹扫捕集方法参数。校正曲线的线性关系良好,相关系数大于0.999,方法检出限为0.3 μg/kg。采用该方法测定农田、公路两侧、加油站附近等3种不同类型的土壤样品并进行了加标回收实验,回收率范围为81.5%~108%。  相似文献   

11.
12.
We monitored nest boxes during 1997–1999 at Acadia National Park, Mt. Desert Island, ME and at an old-field site in Orono, ME to determine mercury (Hg) uptake in tree swallow (Tachycineta bicolor) eggs, tissues, and food boluses. Also, in 1998–1999 we monitored nest boxes at Grove Pond and Plow Shop Pond at a U.S. Environmental Protection Agency Superfund site in Ayer, MA. We recorded breeding success at all locations. On average among locations, total mercury (THg) biomagnified 2 to 4-fold from food to eggs and 9 to 18-fold from food to feathers. These are minimum values because the proportion of transferable methyl mercury (MeHg) of the THg in insects varies (i.e., 35%–95% of THg) in food boluses. THg was highest in food boluses at Aunt Betty Pond at Acadia, whereas THg in eggs was highest at the Superfund site. A few eggs from nests at each of these locations exceeded the threshold (i.e., 800–1,000 ng/g, wet wt.) of embryotoxicity established for Hg. Hatching success was 88.9% to 100% among locations, but five eggs failed to hatch from 4 of the 11 clutches in which an egg exceeded this threshold. MeHg in feathers was highest in tree swallows at Aunt Betty Pond and the concentration of THg in bodies was related to the concentration in feathers. Transfer of an average of 80%–92% of the Hg in bodies to feathers may have enhanced nestling survival. Residues of Hg in tissues of tree swallows in the Northeast seem higher than those of the Midwest.  相似文献   

13.
Vernal pools are sensitive environments that provide critical habitat for many species, including amphibians. These small water bodies are not always protected by pesticide label requirements for no-spray buffer zones, and the occurrence of pesticides in them is poorly documented. In this study, we investigated the occurrence of glyphosate, its primary degradation product aminomethylphosphonic acid, and additional pesticides in vernal pools and adjacent flowing waters. Most sampling sites were chosen to be in areas where glyphosate was being used either in production agriculture or for nonindigenous plant control. The four site locations were in otherwise protected areas (e.g., in a National Park). When possible, water samples were collected both before and after glyphosate application in 2005 and 2006. Twenty-eight pesticides or pesticide degradation products were detected in the study, and as many as 11 were identified in individual samples. Atrazine was detected most frequently and concentrations exceeded the freshwater aquatic life standard of 1.8 micrograms per liter (microg/l) in samples from Rands Ditch and Browns Ditch in DeSoto National Wildlife Refuge. Glyphosate was measured at the highest concentration (328 microg/l) in a sample from Riley Spring Pond in Rock Creek National Park. This concentration exceeded the freshwater aquatic life standard for glyphosate of 65 microg/l. Aminomethylphosphonic acid, triclopyr, and nicosulfuron also were detected at concentrations greater than 3.0 microg/l.  相似文献   

14.
The purpose of this article is to report on the testing of responses of multimetric macroinvertebrate and habitat indices to common disturbances to streams: stream habitat alteration, excessive sediment, and elevated metals concentrations. Seven macroinvertebrate community metrics were combined into a macroinvertebrate biotic index (MBI), and 11 channel morphology, riparian, and substrate features were combined into a habitat index. Indices were evaluated by comparing the habitat results to fish population surveys and comparing the macroinvertebrate results to habitat ratings, percent fine sediments measured by Wolman pebble counts, and copper concentrations. Macroinvertebrate scores decreased with increasing percentages of fine sediments measured either across the bankfull or instream channel widths. Macroinvertebrate scores decreased with increasing copper. One metric, richness of Ephemeroptera, Plecoptera, and Trichoptera (EPT) taxa, was more responsive to both copper and sediment than was the multimetric MBI. Habitat scores corresponded well with the age class structure of salmonids, but not with that of benthic sculpins. Both salmonid and sculpin age classes declined with increasing percentages of fine sediments. The decline was graded with the sculpin age classes, whether fine sediments were measured across the instream or bankfull channel, whereas salmonids consistently responded only to the instream fine sediments.  相似文献   

15.
Earthworms and soils were collected from 20 diverse sites in Maryland, Pennsylvania, and Virginia, and were analyzed for Pb, Cu, Zn, Cd, Cr, As, and Se. Correlation coefficients relating concentrations of the elements in earthworms to concentrations in soil were low (–0.20<r<+0.57). Species differences and ecological variables contributed to the variability in concentrations of these elements in earthworms. The maximum concentrations of Pb (2100 ppm), Zn (1600 ppm), Cd (23 ppm) and Se (7.6 ppm) detected in earthworms were in the range reported to be toxic to animals fed diets containing these elements; however, even in the absence of any environmental contamination, some species of earthworms may contain high concentrations of Pb, Zn, and Se. Earthworms of the genus Eisenoides, for example, were exceptional in their ability to concentrate Pb. When earthworms are used as indicators of environmental contamination, it is important to identify the species, to report the soil characteristics, and to collect similar earthworms from very similar but uncontaminated soil.  相似文献   

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17.
In this study, the relationships among environmental pollution, terrorism, foreign direct investments (FDI), energy consumption and economic growth is investigated for Afghanistan, Iraq, Nigeria, Pakistan, Philippines, Syria, Somalia, Thailand and Yemen covering the 1975–2017 period utilizing Panel cointegration tests, ANOVA tests, long-run estimators and panel trivariate Causality tests. ANOVA results are in favor of evidence of homogeneity between the selected countries. Long-run estimators reveal that terrorism, FDI, energy consumption and economic growth have statistically significant effects on environmental pollution. Panel trivariate Causality test determines the causal relationship between the variables. Accordingly, one-way causal nexus from terrorism to Carbon dioxide (CO2) emissions and from FDI inflows to CO2 emissions are found in the short-run. In the long-run, with strong causality results, the evidence of bi-directional causality between CO2 emissions and other variables, namely, terrorism, FDI inflow energy consumption and economic growth are detected.  相似文献   

18.
We evaluated exposure of aquatic biota to lead (Pb), zinc (Zn), and cadmium (Cd) in streams draining a Pb-mining district in southeast Missouri. Samples of plant biomass (detritus, periphyton, and filamentous algae), invertebrates (snails, crayfish, and riffle benthos), and two taxa of fish were collected from seven sites closest to mining areas (mining sites), four sites further downstream from mining (downstream sites), and eight reference sites in fall 2001. Samples of plant biomass from mining sites had highest metal concentrations, with means 10- to 60-times greater than those for reference sites. Mean metal concentrations in over 90% of samples of plant biomass from mining sites were significantly greater than those from reference sites. Mean concentrations of Pb, Zn, and Cd in most invertebrate samples from mining sites, and mean Pb concentrations in most fish samples from mining sites, were also significantly greater than those from reference sites. Concentrations of all three metals were lower in samples from downstream sites, but several samples of plant biomass from downstream sites had metal concentrations significantly greater than those from reference sites. Analysis of supplemental samples collected in the fall of 2002, a year of above-average stream discharge, had lower Pb concentrations and higher Cd concentrations than samples collected in 2001, near the end of a multi-year drought. Concentrations of Pb measured in fish and invertebrates collected from mining sites during 2001 and 2002 were similar to those measured at nearby sites in the 1970s, during the early years of mining in the Viburnum Trend. Results of this study demonstrate that long-term Pb mining activity in southeast Missouri has resulted in significantly elevated concentrations of Pb, Cd, and Zn in biota of receiving streams, compared to biota of similar streams without direct influence of mining. Our results also demonstrate that metal exposure in the study area differed significantly among sample types, habitats, and years, and that these factors should be carefully considered in the design of biomonitoring studies.  相似文献   

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This study was conducted to investigate the pollution load index, fraction distributions, and mobility of Pb, Cd, Cu, and Zn in garden and paddy soils collected from a Pb/Zn mine in Chenzhou City, China. The samples were analyzed using Leleyter and Probst’s sequential extraction procedures. Total metal concentrations including Pb, Cd, Cu, and Zn exceeded the maximum permissible limits for soils set by the Ministry of Environmental Protection of China, and the order of the pollution index was Cd > Zn > Pb > Cu, indicating that the soils from both sites seriously suffered from heavy metal pollution, especially Cd. The sums of metal fractions were in agreement with the total contents of heavy metals. However, there were significant differences in fraction distributions of heavy metals in garden and paddy soils. The residual fractions of heavy metals were the predominant form with 43.0% for Pb, 32.3% for Cd, 33.5% for Cu, and 44.2% for Zn in garden soil, while 51.6% for Pb, 40.4% for Cd, 40.3% for Cu, and 40.9% for Zn in paddy soil. Furthermore, the proportions of water-soluble and exchangeable fractions extracted by the selected analytical methods were the lowest among all fractions. On the basis of the speciation of heavy metals, the mobility factor values of heavy metals have the following order: Cd (25.2–19.8%) > Cu (22.6–6.3%) > Zn (9.6–6.0%) > Pb (6.7–2.5%) in both contaminated soils.  相似文献   

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