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1.
东北地区饮水型地氟病与地质环境   总被引:3,自引:1,他引:2  
东北地区饮水型氟中毒病具有病区分布广、病人多、病情重、危害大的特点,控制东北地区饮水型氟中毒病区分布的主要因素有气候、水文、地形地貌、地质构造、水文地质环境、地球化学环境.分析了地氟病与地质环境的关系,提出了饮水型氟中毒病区防病改水的途径和对策.  相似文献   

2.
关于全氟化合物(PFCs)在我国农村环境中的分布还未见相关的报道。本文利用固相萃取分离富集结合高效液相色谱-电喷雾负电离源串联质谱法分析我国东部8个农村地区土壤、地表水、地下水样品中17种PFCs的污染水平和组成特征, 并利用比值法初步判定了水环境中PFCs的污染来源。结果显示, 土壤中全氟羧酸类以PFOA为主(0.34~14.5 ng/g), 全氟烷基磺酸类以PFOS为主(0.02~0.08 ng/g);地表水中PFCs以PFOA、PFHxA、PFOS和PFBA为主(4.8~29.6、0.73~31.8、nd~7.1和nd~6.1 ng/L);地下水中PFCs主要为PFOA、PFHxA、PFBA(nd~176、nd~50.1和0.08~16.1 ng/L)。土壤及水环境中PFCs总体上呈现从南到北递减的趋势;地表水中PFCs污染源大致分为生活污水和大气沉降两大类, 其中大气沉降的贡献较大。  相似文献   

3.
关于全氟化合物(PFCs)在中国农村环境中的分布还未见相关的报道。本文利用固相萃取分离富集结合高效液相色谱-电喷雾负电离源串联质谱法分析中国东部8个农村地区土壤、地表水、地下水样品中17种PFCs的污染水平和组成特征,并利用比值法初步判定了水环境中PFCs的污染来源。结果显示,土壤中全氟羧酸类以PFOA为主(0.34~14.5 ng/g),全氟烷基磺酸类以PFOS为主(0.02~0.08 ng/g);地表水中PFCs以PFOA、PFHx A、PFOS和PFBA为主(4.8~29.6、0.73~31.8、nd~7.1和nd~6.1 ng/L);地下水中PFCs主要为PFOA、PFHx A、PFBA(nd~176、nd~50.1和0.08~16.1 ng/L)。土壤及水环境中PFCs总体上呈现从南到北递减的趋势;地表水中PFCs污染源大致分为生活污水和大气沉降两大类,其中大气沉降的贡献较大。  相似文献   

4.
为了解广州地区蔬菜基地有机污染物的分布情况,选取了6个代表性基地进行调查采样,测试分析了表层土壤、蔬菜及灌溉水中15种邻苯二甲酸酯(PAEs)化合物、16种多环芳烃(PAHs)化合物和19种有机氯农药(OCPs)化合物的质量分数及质量浓度.结果表明:在15种PAEs化合物的总质量分数(w(ΣPAEs))中,土壤样品为158.0~4 321.0 ng/g,蔬菜样品为1 134.0~48 576.0 ng/g;水样中15种PAEs化合物的总质量浓度(ρ(ΣPAEs))为632.0~14 271.0 ng/L;就单个化合物而言,以DiBP、DBP、DEHP三种污染物为主,其三项之和占所有PAEs质量分数的97.5%~99.1%;在16种PAHs化合物的总质量分数(w(ΣPAHs))中,土壤样品为28.48~1 121.96 ng/g,蔬菜样品为238.09~1 000.61 ng/g;水样中16种PAHs化合物的总质量浓度(ρ(ΣPAHs))为338.21~1 239.78 ng/L;在19种OCPs化合物的总质量分数(w(ΣOCPs))中,土壤为0.04~71.28 ng/g,蔬菜为1.08~9.18 ng/g.总体上看,各基地土壤中DBP质量分数均超标,多环芳烃类在灵山、花东、黄埔菜地土壤中存在轻微污染,有机氯农药均未出现污染.  相似文献   

5.
稀土的开发和广泛应用使得人们倍加关注其在环境中的分布及其环境地球化学行为。赣江作为鄱阳湖流域五大入湖河之一,发源于稀土资源富集的赣南地区,而其下游水体及周边地下水中稀土元素的含量和分异特征目前尚不完全清楚。以赣江北支水体及沉积物为研究对象,开展了稀土元素地球化学研究。结果表明,赣江北支水体中稀土元素总量在地表水中为230~1 146 ng/L(均值458.85 ng/L),地下水中为284~1 498 ng/L(均值634.94 ng/L),沉积物中稀土元素总量为177.9~270.7 mg/kg(均值226.99 mg/kg)。PHREEQC模拟计算表明,水体中的稀土元素主要以碳酸根络合物(REEC03+)的形式存在。地表水和地下水总体上均表现为重稀土元素相较于轻、中稀土元素富集,沉积物未表现出明显的富集特性;水体具有Ce、Eu负异常特点,而沉积物表现为Ce正异常和Eu负异常,指示氧化还原环境和水岩相互作用对稀土元素在水-沉积物系统中迁移转化的影响。地下水中稀土元素的含量沿流向具有上升趋势,而水体中重稀土元素的富集程度不断减弱,同时碳酸根络合物(REEC03+)的占比不断降低,反映水体中稀土元素的含量受到pH、胶体吸附、络合作用以及地下水-地表水相互作用的影响。水体中重稀土元素的富集受到碳酸根络合反应的影响,Ce、Eu负异常与Ce氧化沉淀和母岩特性相关。Gd异常值表明,研究区中下游水体中的Gd元素受到人为输入的影响。  相似文献   

6.
松嫩平原氟中毒区地下水氟分布规律和成因研究   总被引:6,自引:0,他引:6       下载免费PDF全文
自中新生代以来,在松嫩平原巨大的断陷盆地内沉积了巨厚的古近-新近系和第四系沉积物,形成了由潜水和承压水组成的大型蓄水构造。该区潜水和第四系承压水氟含量较高,在194个样品中,氟的均值为3.45mg/L,范围值为0.25~14mg/L。饮用高氟地下水导致氟中毒大规范流行。研究表明高氟地下水主要分布在山前补给区-蒸发排泄区的过渡带和盆地中部地下水强烈蒸发带,地下水化学类型为HCO3-Na·Mg和HCO3-Cl·Na型,总溶解性固体含量为689.84~2005.6mg/L。高氟水的形成与气候、水文、地质构造、岩石与土壤、水文地质和水化学条件等自然因素有关,同时受不合理开采地下水等人为因素的影响。开展氟病区地下水环境特征和高氟水成因研究对于有效实施安全供水有重要意义。  相似文献   

7.
为了识别石家庄市南部污灌区地下水硝酸盐污染来源, 采集5种潜在污染源和19组地下水样用于化学和氮同位素分析.灌溉污水NH4+的δ15N值较低(4.0‰), 施化肥土壤和粪堆下土壤NO3-的δ15N值分别为1.4‰和12.4‰; 仅施厩肥的蔬菜种植区下伏近30 m厚包气带沉积物NO3-的δ15N分布显示, 来自动物粪便的NO3-已运移到11.5 m以下包气带, 均值10.9‰; 污水灌溉农田下伏厚层包气带沉积物样品分析结果指示, 土壤层下伏包气带沉积物δ15N值变幅较小, 均值5.7‰.污灌区内除一深井外, 其他水井地下水硝酸盐浓度变化在52.6~124.5 mg/L之间, 均值79.72 mg/L, δ15N值变化在5.3‰~8.3‰之间, 均值7.0‰.污灌区地下水的δ15N值较污灌区土壤层下伏包气带沉积物的δ15N值高, 表明地下水NO3-除了来自灌溉的污水外, 还有δ15N值更高的其他来源, 这些来源主要是人和动物粪便.利用线性混合模型计算, 污灌区地下水NO3-来自灌溉的污水, 约占76%, 而来自人和动物粪便的NO3-约占24%.为控制污灌区地下水NO3-浓度进一步增长, 不仅要加强污水灌溉管理, 还要加强人和动物粪便的管理.   相似文献   

8.
陆生植物氮同位素组成与气候环境变化研究进展   总被引:3,自引:0,他引:3  
近年来,由于植物氮同位素组成(δ15N)记载了气候环境变化的信息,因而被广泛应用于全球变化研究中,成为古气候环境再造和了解现代气候环境变化信息的有力工具。然而,人们对气候环境引起的δ15N变化及其指示的气候环境意义并不完全清楚,这就有可能限制植物δ15N在古气候环境变化等领域研究中的应用。在概述植物氮同位素分馏和植物不同氮源的氮同位素分布的基础上,分析了温度、降水、大气CO2浓度和海拔高度等气候环境因子对陆生植物δ15N的影响以及它们的关系。指出了目前研究中存在的问题及其研究前景,认为在全球变化研究中利用植物氮同位素技术不仅可以重建古气候环境(如重建大气CO2浓度变化),揭示历史时期温度、降水的变化,而且还可以在一定的时间和空间上综合反映生态系统氮循环的特征。  相似文献   

9.
根据2010年5月至2010年10月每月对青木关地下河河水的监测数据,利用15N同位素技术并结合水化学指标,分析地下河的水化学特征以及硝态氮来源的时空变化特征。结果表明,地下河出口丁家龙洞硝态氮浓度(5.077mg/L)比入口天池硝态氮浓度(0.842mg/L)高6倍多。入口天池处地下河河水硝态氮浓度比较低,δ15N浓度变化范围为-7.0475‰~+7.059‰,变化幅度不大,说明该点的氮污染较低,地下水受外界影响较小,污水和粪便不是主要的δ15N来源。出口丁家龙洞处的δ15N浓度变化范围在-21.453‰~+37.825‰,总体浓度高且变化幅度大,受上游养猪场粪便直接排入及降水影响较大。   相似文献   

10.
吉林省饮水型砷中毒区是继中国内蒙古和山西病区后发现的新病区。该病区主要分布在吉林省西部的通榆县和洮南市,其水文地质单元属于松嫩平原大型蓄水盆地的西部,是由第四系潜水、承压水和新近系承压水组成的多层结构的含水系统。采用瞬时采样法采集了区内潜水和承压水样品,共194份;通过GIS的空间叠加技术、化验与测试技术,进行了区域水化学环境特征与饮水型砷中毒的关系研究。结果表明:受区域地质构造控制,在低洼地带堆积了巨厚的粉砂淤泥质冲积物和富含有机质的湖积物,为地下水砷的赋存提供了空间。区域地下水砷含量的范围值为0.001~0.339 mg·L-1,水砷价态以As(V)为主,高砷水主要分布在由若干隆起形成的中间低洼地带中地下水埋深大于10 m的潜水、第四系和新近系承压水含水层中。高砷地下水的形成与特定的水文地质条件和水化学环境有关,氯化物重碳酸钠型水中的砷含量最高。臭葱石(FeAsO4·2H2O)等含铁、含锰矿物在进入地下水的溶解过程中,形成铁、锰的氧化物和砷的化合物,如砷酸盐和亚砷酸盐。伴随着水环境中Eh的降低,氧化物被还原形成更为活泼的离子组分,吸附在氧化物表面的含砷化合物进而解吸,使砷从含水层的沉积物中向水中溶解和迁移。  相似文献   

11.
This study assessed the state of waters in Belgrade regarding pollution with musk compounds as the target contaminants. Eleven of these compounds were alicyclic, two were macrocyclic, and one was polycyclic. Solid-phase microextraction was used for the isolation of these compounds from waste, surface and underground waters and from processed water prepared for drinking, while comprehensive orthogonal two-dimensional gas chromatography with mass spectrometry was used as the final analytical method. In wastewater samples, galaxolide was detected in concentrations of 1.13 and 0.40 μg/L, while in the Sava River and underground water its concentrations were 0.09 and 0.038 μg/L. The lowest concentrations of the investigated musk compounds were detected in underground water samples, indicating that this is the cleanest water of all the analyzed sources with respect to musk compounds. Comparing the results of musk compound concentrations determined in surface river water samples and clean river water samples utilized for drinking, a lower concentration of these compounds was detected in the clean river water samples. The majority of musk compounds were found in waters utilized for drinking. Based on the concentration values, we conclude that the analyzed waters are moderately polluted with these compounds.  相似文献   

12.
Gadolinium chelates have been used since 1988 as contrast agents in magnetic resonance imaging (MRI), and produce positive anthropogenic Gd anomalies in rare earth element (REE) patterns of river and lake waters. These Gd compounds are not removed in wastewater treatment plants (WWTP) due to their high stabilities, and are transferred to surface waters with the clearwater discharge from WWTP. Through natural and induced bank filtration, the anthropogenic Gd is also transported into groundwater. To date, there are no related acute health risks known, but the potential long-term effects of exposure to low doses have not been studied.Here REE data is presented for tap water from the City of Berlin, Germany, a metropolitan area that is known for its anthropogenic Gd-rich rivers and groundwater. Natural and induced bank filtration play important roles in Berlin’s freshwater resource management. Therefore, the extent to which municipal tap water that is used as drinking water is affected by anthropogenic Gd was investigated. Large positive Gd anomalies were found in tap water samples from the western districts of Berlin, indicating the presence of up to 18 ng/L of anthropogenic Gd on top of a geogenic background of 0.54 ng/L. In marked contrast, the amount of anthropogenic Gd in tap water from the eastern districts of Berlin is negligible to minor (maximum of 0.18 ng/L on top of a geogenic background of 0.26 ng/L). This strong regional difference likely results from the specific historical situation of Berlin, where before the re-unification of Germany in 1990, natural and induced bank filtration were necessities in isolated West Berlin, but unimportant in East Berlin, a situation that has seen little change during the past 20 years. Thus, drinking water resources in the western part of Berlin are more strongly affected by anthropogenic Gd than those in the eastern part. The high anthropogenic Gd concentrations found in some tap waters in Berlin clearly show that the Gd initially used as contrast agent is removed neither during natural nor artificial water treatment. This is further evidence for the high stability and long environmental half-lives of these compounds. Considering that the amount of anthropogenic Gd in the Havel River in Berlin has increased more than 4-fold over the past 15 years and that water migration from the Havel River to the groundwater wells take years to decades, the amounts of anthropogenic Gd in West Berlin tap water will increase further over the next few years. Due to its presence in tap water that is consumed as drinking water, millions of people are exposed to low doses of these anthropogenic Gd chelates. Additional data for the City of London, UK, for example, indicate that this is not a local phenomenon confined to the City of Berlin, but rather a common feature of tap water in metropolitan areas and megacities in countries with highly developed health care systems. Hence, the REE distribution in tap waters used for human consumption should be monitored, especially since the anthropogenic Gd chelates can also be used as tracers for emerging microcontaminants such as steroids, pharmaceuticals and personal care products.  相似文献   

13.
郑松 《贵州地质》2003,20(3):187-191
地下水的开发是解决贵州饮水问题的主要途径之一,通过对泉水开发过程中存在的主要问题的分析,提出了解决问题的有效措施——制定地方标准,以确保饮用泉水质量安全,为饮用天然泉水的生产经营及质量技术监督执法提供可靠的技术法规保障。  相似文献   

14.
Mercury as a toxic element poses environmental concerns, especially in historically Hg-mined districts. The Wanshan Hg mine located in the eastern part of Guizhou Province, southwestern China, ranks the largest Hg-producing district in China. Mining at Wanshan was initiated in 221 B.C., but ceased in 2001. Approximately 22000 tons of Hg, 6000 tons of cinnabar and large quantities of mine-wastes had been produced at Wanshan. Significant quantities of calcines, which were piled irregularly near the old mine processing sites and retorts, continue to impact the local environments in the Wanshan area. In this study, a regional contamination of mercury in surface waters collected from the Meizixi, Dashuixi, Huandao and Gaolouping rivers, whose upstreams or branches originate from the hilly karstic area and receive drainage arising from the calcines, was investigated by determining all Hg species in a base-flow and a flood-flow season. Reactive, dissolved, particulate, and total Hg concentrations in surface water varied from 0.60 to 400 ng/L, 11 to 430 ng/L, 1.4 to 9210 ng/L, and 15 to 9260 ng/L, respectively. Total methylmercury in water samples ranges from 0.31 to 25 ng/L. The concentrations of total Hg and particulate Hg in water samples collected during the flood season are higher than those in the base-flow season, whereas, the concentrations of dissolved and reactive Hg are lower with the peak values observed in water samples collected in the base-flow season. A strong positive correlation between total Hg and particulate Hg is noticed in the water samples collected from Hg-mined areas with the proportion higher than 80%.  相似文献   

15.
以近年来备受关注的持久性有机污染物———全氟化合物为研究目标物,黄河河口段为目标研究区域,应用高效液相色谱-串联质谱法测定黄河河口段河水、自来水和浅层地下水中的19种全氟化合物含量,描述研究该区域水体中全氟化合物的污染水平和分布规律,并探讨水体中全氟化合物的来源。结果表明,全氟丁酸和全氟辛酸是黄河河口段水体中最主要的全氟化合物,黄河水中的全氟丁酸和全氟辛酸浓度分别为1.61~4.20ng/L和2.04~3.36 ng/L。浅层地下水中各待测物检出率都很低;自来水中全氟丁酸和全氟辛酸的浓度分别为1.62~3.24 ng/L和4.66~9.34 ng/L;自来水与黄河水中全氟化合物的组成特征明显不同。东营地区黄河水中全氟辛烷磺酸的浓度与国内其他北方城市相比浓度相当,明显低于长江水和珠三角地表水;全氟辛酸的浓度与呼和浩特市周边河水以及北京官厅水库中浓度相当,相比国内其他地区处于较低水平。  相似文献   

16.
Arsenic in drinking water has been shown to increase the risk of urothelial carcinoma and lung cancer. However, the lifetime risk of developing urothelial carcinoma and lung cancer caused by exposure to arsenic in drinking water has not been reported. This study aimed to assess the lifetime risk of urothelial carcinoma and lung cancer caused by arsenic exposure from drinking water and cigarette smoking habit for residents living in the arseniasis-endemic area in Northeastern Taiwan. We recruited 8086 residents in 1991–1994 and monitored them for their newly developed types of cancers, identified by computerized linkage with the national cancer registry profile. There were 37 newly diagnosed urothelial carcinoma cases and 223 new lung cancer cases during the follow-up period (until 2007). The lifetime (35–85 years old) cumulative risk of developing urothelial carcinoma from an arsenic concentration in the drinking water of <10, 10–99, and 100+ μg/L was 0.29%, 1.07% and 3.43%, respectively. The corresponding probabilities were 7.42%, 8.99% and 17.09% for the lifetime risk of developing lung cancer. Cigarette smoking was associated with an increased risk of urothelial carcinoma and lung cancer, showing the hazard ratio (95% confidence interval) of 2.48 (1.27–4.82) and 3.44 (2.00–5.90) after adjusting for the arsenic concentration in drinking water. After adjusting for cigarette smoking, the hazard ratio (95% confidence interval) of developing urothelial carcinoma caused by the arsenic concentration in drinking water of <10, 10–99 and 100+ μg/L was 1.0 (the reference group), 2.18 (0.59–8.01), and 8.71 (2.49–30.48), respectively. The corresponding figures were 1.0 (the reference group), 1.14 (0.80–1.61), 1.84 (1.28–2.65) for lung cancer. Synergistic effects on the development of urothelial carcinoma and lung cancer existed between the arsenic exposure level and cigarette smoking. It is suggested that people who have had a high exposure to arsenic in drinking water should stop smoking cigarettes to lower their lifetime risk of urothelial carcinoma and lung cancer.  相似文献   

17.
福建兴化湾水体有机氯农药污染状况   总被引:11,自引:2,他引:11  
利用气相色谱-电子检测器对福建兴化湾河水和海水中的19种有机氯农药(HCHs、DDTs等)进行的分析结果表明,几种有机氯农药尽管已停止生产多年,但在河水及海水中仍有残留.二者的有机氯农药的质量浓度分别为10.96~56.31,5.78~161.64 ng/L ,同国内外其他港口海区及河流相比,其污染程度相对较低.丰水期河水中DDT的降解产物主要为DDE,而海水中DDT的降解产物主要为DDD.同时,对有机氯农药现状的分析表明,近年来仍有有机氯农药污染的输入,其农药的使用主要集中在六六六和滴滴涕上.  相似文献   

18.
In the past researches conducted on the territory of Serbia, 5 regional geotectonic units have been distinguished with registered occurrences of 230 mineral springs. Recent analyses of the bottled mineral waters quality have not included systematic examinations of micro-components present in these waters. Based on the analyses of the bottled mineral waters (EuroGeoSurveys Geochemistry Expert Group), it has been observed that the water quality is greatly influenced by the chemical composition of igneous intrusions, regardless of the fact that the analyzed waters have been taken from different aquifers (Neogene sediments, limestone, flysch, schist).  相似文献   

19.
重庆典型岩溶区地下河水体有机氯农药污染初步研究   总被引:7,自引:4,他引:3  
利用GC-ECD对重庆典型岩溶区地下河水体中有机氯农药(OCPs)进行检测,结果表明,地下河水中OCPs浓度为3.41~51.34ng/L,均值为13.23ng/L;滴滴涕(DDTs)浓度为0.07~2.37ng/L,均值为0.72ng/L;六六六(HCHs)浓度为1.16~39.82ng/L,均值为7.89ng/L。南川湾滩地下河水体有机氯农药污染最为严重,其上游纸厂排放废水是影响该地下河有机氯农药污染的主要原因。与国内外其它河流相比较,研究区地下河水体有机氯农药含量处于中低水平。由于岩溶区特殊的二元结构,地表水体一旦受到污染,将直接影响到地下水体。因此,对岩溶地下河进行有机污染物的调查研究具有重要的现实意义   相似文献   

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