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1.
为研究重庆老龙洞地下河不同部位水体、表层沉积物有机氯农药分布特征,用气相色谱-微池电子捕获检测器(GC-μECD)分析了样品中OCPs含量。结果表明:研究区水样、表层沉积物中OCPs检出率均为100 %,其浓度在时间上存在季节差异,水体中OCPs、DDTs、HCHs含量丰水期小于枯水期,而在表层沉积物中则表现为OCPs、HCHs丰水期大于枯水期,DDTs丰水期小于枯水期;在空间上则表现为水体中有机氯农药总体下游大于上游,而沉积物中则与之相反。通过对比可知,岩溶洞穴环境由于缺乏光照,空气流动缓慢,生物活动不频繁,使水体中的HCHs不易降解,沉积物中的HCHs不易重新释放而浓度高于洞外。枯水期由于洞内流速较小且变幅不大,水体中的DDTs大量沉积因而其浓度低于洞口,而丰水期洞口因受大量雨水的稀释作用DDTs反而低于洞内的含量;洞内沉积物中的DDTs则因洞内环境恒定不易重新释放和枯水期水体中的大量沉积而一直高于洞外。洞穴环境、不同污水汇入对水体中DDTs和表层沉积物中DDTs、HCHs的组成结构均有不同程度的影响,而对水体中HCHs的组成结构影响不大。此外,地下河不同部位污染源的输入对有机氯污染物的组成结构也有影响。与国内外水体及表层沉积物中HCHs、DDTs相比较,研究区水体、表层沉积物中HCHs、DDTs浓度分别处于中等和偏高水平。   相似文献   

2.
大石围天坑群土壤中有机氯农药的分布与富集特征   总被引:1,自引:0,他引:1  
选择典型的岩溶地区广西乐业大石围天坑群为研究区,采集不同岩溶地形的土壤,利用 GC-ECD 气相色谱仪测定六六六(HCHs)和滴滴涕(DDTs)两种有机氯农药的浓度.结果表明,大石围天坑群地表土壤、天坑绝壁土壤、天坑底部土壤以及地下河(洞穴)土壤中的 HCHs 和 DDTs 平均浓度分别为0.06 ng/g 和0.02 ng/g、0.31 ng/g 和0.27 ng/g、0.96 ng/g 和0.28 ng/g 以及0.14 ng/g 和0.10 ng/g.研究区土壤中有机氯农药总检出率为:天坑地表<天坑绝壁<天坑底部<地下河(洞穴),随高程降低而增高;有机氯农药(OCPs = HCHs + DDTs)浓度的空间分布特征为:天坑底部>天坑绝壁>地下河(洞穴)>天坑地表,天坑底部 OCPs 浓度明显高于顶部;因此,大石围天坑呈现明显的有机污染物“冷陷阱效应”  相似文献   

3.
在2010年5月调查了沈阳市细河沿岸表层土壤中有机氯农药(OCPs)和多氯联苯(PCBs)的污染现状,评价土壤中OCPs残留的生态风险。沈阳细河沿岸表层土壤中HCHs浓度范围分别为2.32~15.90 ng/g,平均浓度为8.99ng/g。DDTs浓度范围分别为9.06~111.6 ng/g,平均浓度为37.08 ng/g。7种PCBs异构体总平均浓度为1.01ng/g,大部分采样点OCPs和PCBs未超过国家土壤环境质量标准,推断近期可能有林丹的使用但没有新的DDTs污染源输入,但个别地点土壤中的DDTs残留浓度对生态系统健康构成了潜在的威胁。大气蒸汽态HCHs浓度为18.97 ng/m3;DDTs浓度为42.27 ng/m3;PCBs浓度为20.59 ng/m3。研究表明大气长距离传输对该区域的OCPs污染也有较为明显的影响。初步运用逸度概念模型进行分析,发现HCHs和DDTs的逸出方向为从土壤向大气挥发。  相似文献   

4.
沈阳郊区表层土壤有机氯农药残留特征及风险评价   总被引:2,自引:0,他引:2       下载免费PDF全文
利用GC-ECD定量测定了沈阳郊区21个表层土壤样品中有机氯农药(OCPs)的含量,并对其残留特征、可能来源及生态风险进行了分析。结果表明,研究区表层土壤中OCPs的检出率达到95.2%,残留量最高值达到111.67 ng·g-1,平均值26.91 ng·g-1,其中以六六六(HCHs)和滴滴涕(DDTs)为主。与国内其他城市土壤中OCPs含量相比,沈阳郊区表层土壤HCHs和DDTs残留属于较低水平,但HCB残留属于较高水平。研究区OCPs的来源解析表明OCPs主要来自环境中的早期残留和近期林丹的使用,六氯苯(HCB)的来源还应包括工业生产。相关性分析说明土壤中总有机碳和水溶盐含量是影响OCPs残留的重要因素。生态风险评价显示表层土壤中DDTs类有机氯农药对该区生物可能仍存在生态风险。  相似文献   

5.
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   

6.
广西桂林大岩洞岩溶洞穴土壤中有机氯农药的分布特征   总被引:2,自引:0,他引:2  
首次对桂林岩溶区洞穴土壤中有机氯农药的污染状况进行了研究。结果表明,洞穴土壤受到了有机氯农药的轻度污染,其中大气传输对有机氯农药的贡献起主导作用。在17种有机氯农药中,以DDTs、HCHs和氯丹污染为主。在洞穴内部OCP总量为1.19~11.18 ng/g,远低于洞外土壤中的含量(11.41~23.62 ng/g)。在洞内土壤中,HCHs含量高于DDTs,在HCH四种同分异构体中,β-HCH占HCHs的比例远高于其他3种同分异构体。除β-HCH外,其他3种同分异构体的含量分布均匀,可能是由洞穴环境稳定、气候分带等因素造成的。在洞外土壤中,异构体百分比和示踪标志物比值表明周围可能有林丹扣三氯杀螨醇的新近输入。研究区六六六和滴滴涕主要来源于历史上使用的农药的残留。  相似文献   

7.
广西百朗地下河水和沉积物中有机氯农药的分布特征   总被引:4,自引:2,他引:2  
为了解典型岩溶地区广西乐业百朗地下河表层水和沉积物中有机氯农药的分布特征,采集地下河不同断面的水和沉积物样品,利用气相色谱仪测定了19种有机氯农药。结果表明:(1)百朗地下河表层水中19种有机氯农药总量(∑OCPs)浓度为1.95~71.45ng/L,HCHs和DDTs浓度分别为未检出至58.40ng/L和未检出至0.44ng/L;(2)沉积物中∑OCPs浓度为0.75~14.85ng/g,HCHs和DDTs浓度分别为0.11~3.52ng/g和0.03~2.90ng/g;(3)地下河表层水和沉积物中有机氯农药的分布与吸附作用、环境温度以及和地下河连通的天坑的底部的土壤侵蚀有关,即因温差作用,大气沉降的有机氯农药易富集在天坑底部(“冷陷阱效应”),并在土壤侵蚀作用下向水体移动,使地下河沉积物中有机氯农药浓度升高;(4)百朗地下河出口沉积物吸附系数最低,但水中有机氯农药浓度较高且种类最多,推测可能是地下河沉积物中因有机氯农药被释放而引起二次污染;(5)表层沉积物中大多数断面的异狄氏剂浓度及乐业县城附近断面的DDTs和DDD浓度在风险评估低值与风险评估中值之间,表明百朗地下河处于较低的生态风险水平;(6)目前,流域部分断面尚有新的γ-HCH(林丹)和DDTs农药输入。由于有机氯农药长期累积,可能对地下河生态系统造成危害,应采取防治措施。   相似文献   

8.
吉林省洁净地区长白山表层土壤中有机氯农药(OCPs)和多氯联苯(PCBs)总体上污染较轻,但高于一些其他地区。表层土壤的OCPs和PCBs表现出明显的随海拔高度增大的趋势,初步显示了高山冷凝捕集效应的影响。长白山旅游地区表层土壤受到轻微HCHs和DDTs的污染(平均值分别为12.4 ng/g和12.3 ng/g)。长白山附近较低海拔地区表层土壤中OCPs含量要略高一些,表明农业活动逐渐增大。HCHs和DDTs都未超过国家土壤环境质量标准的一级,但个别地点DDTs可能对鸟类和土壤生物具有一定的潜在生态风险。不排除在个别采样点有林丹和三氯杀螨醇被使用的可能性。长白山及附近地区表层土壤样品中∑7PCBs含量为7.3~31.9ng/g,平均17.2 ng/g。PCBs污染主要集中在海拔1450 m和1800 m处。7种PCBs异构体的含量依次为:PCB 28>PCB 52>PCB 180>PCB 138>PCB 101>PCB 153>PCB 118。  相似文献   

9.
以重庆市南川区不同农业活动强度下的3个表层岩溶泉为例,通过分析泉点水化学变化特征来估算不同泉点的DIC损失量(△DIC)和探讨农业活动对岩溶碳汇的影响。研究结果表明:柏树湾泉水温变幅较小,电导率、pH值相对兰花沟泉、后沟泉较低。由于农业活动的影响,兰花沟泉、后沟泉Ca2+ 浓度偏高,而HCO3-浓度偏低。NO3-、SO42-浓度也因农业活动干扰,表现出后沟泉、兰花沟泉远大于柏树湾泉。随农业活动强度的增加,△DIC也逐渐增大,表现为:柏树湾泉(1.64 mmol/L)<兰花沟泉(4.28 mmol/L)<后沟泉(4.36 mmol/L)。△DIC与(SO42-+NO3-)呈正相关,表明农业活动越强烈,DIC损失量越大,岩溶碳汇的损失也随之增大。   相似文献   

10.
柳州岩溶地下河水体有机氯农药分布特征   总被引:6,自引:3,他引:3  
采用气相色谱(配ECD检测器)对柳州鸡喇和龙寨两条岩溶地下河不同位置水体中18种有机氯农药(OCPs)组分进行分析。结果表明,除异狄氏剂醛外,其余17种OCPs均有不同程度检出,OCPs浓度变化范围为107.68~1101.55ng/L,均值为532.515ng/L。OCPs主要组分为:α-HCH、β-HCH、γ-HCH、δ-HCH、p,p'-DDE、o,p'-DDT、p,p'-DDD、p,p'-DDT、六氯苯、七氯、艾氏剂。其中DDTs和HCHs含量最高,二者之和占到总OCPs的75.8%~96%。对其污染源进行分析,发现地下河水体中DDTs主要源自土壤。HCHs来源相对复杂,可能源于工业品或者长距离大气运输,也可能是近期有林丹的输入使其浓度增高。与国内外各水体相比,本次研究的两条岩溶地下河有机氯农药含量相对较高。   相似文献   

11.
Surface soil and sediment samples were collected from the surroundings of the Ittehad Chemical Industries Kalashah Kaku industrial zone to assess residual level of 19 organochlorine pesticides (OCPs) and identify their sources. DDTs and HCHs were most prevalent OCPs and general pattern of contamination followed the order: ∑DDT > ∑HCH > dicofol > endrin > heptachlor > dieldrin > endosulfan II. Total measured concentrations of HCHs (6.38–121.71 ng/g) and DDTs (759.65–1811.98 ng/g) were greater in the soil samples collected from fodder/rice fields irrigated with the factory effluents and in the surrounding of waste disposal site. Ratios of β to γ-HCH highlighted an old mixed source of technical HCH and lindane in surface soils. Predominance of p,p′-DDT and p,p′-DDE among isomers and metabolites showed that large quantity of technical grade DDT is still present in the surrounding surface soils. Six soil samples were categorized as heavy polluted soils (class III category of DDT > 1,000 ng/g), two soil samples into less polluted soil between class I and II (50–500 ng/g) and 28 soil samples as non-polluted (<50 ng/g) according to environmental quality standards for surface soils. Six soil samples were categorized as less polluted between class I and II of HCHs (50–500 ng/g). Greater concentration of DDTs and HCHs above quality guideline poses potential exposure risk to biological organisms, safety of agricultural products and human health in the surrounding of the Ittehad Chemical Industries.  相似文献   

12.
表层岩溶带土壤中多环芳烃分布特征及来源解析   总被引:3,自引:0,他引:3  
利用气相色谱-质谱联用仪(GC-MS)对表层岩溶泉域土壤中的16种优控的多环芳烃(Polycyclic Aromatic Hydrocarbons, PAHs)含量进行了分析,并对其组成、污染水平和来源进行了探讨。结果表明,16种优控PAHs在表层岩溶泉域土壤中的检出率为100%,其含量介于439.19~3329.72ng/g之间,平均值为1392.44ng/g,7种致癌性PAHs占总量的26%。PAHs的组成特征受地形的控制,随着海拔升高,低环PAHs所占比例升高,高环PAHs比例降低。同分异构体比值分析表明,研究区土壤中的PAHs主要来自于煤、生物质和石油的燃烧排放。研究区土壤中16种PAHs的TEQcarc值介于18.65~501.13ng/g,平均值为140.57ng/g。7种致癌性PAHs占总TEQcarc的比例达到96.8%。研究区表土中,后沟泉域的污染程度最大,次之是兰花沟泉域和柏树湾泉域,水房泉泉域的污染程度最小,但由于柏树湾泉域松针落叶中BaP、PAHs含量较高,松针落叶中PAHs含量分别高达36.36ng/g和2370.1ng/g,土壤生态风险评价中应考虑松针落叶层的潜在影响。   相似文献   

13.
This research was conducted in an attempt to assess the concentration levels and potential sources of organochlorine pesticides (OCPs) in the karst soils of Dashiwei tiankeng, southwest China. The tiankeng is a karst surface expression that can act as a focal point for introduction of contaminants to groundwater system, which may serve as condenser and receiver for semi-volatile persistent organic pollutants such as OCPs. In this study, surface soil samples from Dashiwei tiankeng were collected and 23 organochlorine pesticide compounds were analyzed. The results showed that the concentration was 0.019–3.605 ng/g for DDTs (sum of p,p’-DDD, p,p’-DDE, o,p’-DDT, p,p’-DDT), 0.001–0.218 ng/g for HCHs (sum of α-, β-, γ-, δ-HCH), 0.003–0.290 ng/g for CHLs (sum of heptachlor, heptachlor epoxide, TC, CC and trans-nonachlor), 0.001–0.064 ng/g for endosulfan (sum of α-endosulfan and β-endosulfan), 0.008–1.630 ng/g for HCB and 0.023–0.928 ng/g for other OCPs (sum of aldrin, dieldrin, methoxychlor, endrin, endrin aldehyde and endrin ketone). The total OCPs concentrations varied from 0.055 to 5.216 ng/g. The ratio of DDT/(DDE + DDD) in the floor soils of Dashiwei tiankeng ranged from 0.434 to 0.797, suggesting a mostly historical residue of technical DDT contamination. However, the ratio of DDT/(DDE + DDD) in the upper rim soils was higher than one, which that there was fresh DDT application nearby. Both the floor and upper rim soils of Dashiwei tiankeng had high ratios of o,p’-DDT/p,p’-DDT (range of 0.016–10.833 with mean of 5.424 and 4.667–7.714 with mean of 5.723, respectively), which implied that the primary source of DDTs was probably from dicofol-type DDT products. The average ratios of α-/γ-HCH were 24.435 in the floor soils and 1.067 in the upper rim soils, together with the averaged percentages of β-HCH among the total HCH isomers (accounting for 33.772 %), indicating that the HCHs were a dominant contribution from technical HCH usage in the past.  相似文献   

14.
Surface soil samples were collected in two karst Tiankengs, Dashiwei and Datuo, situated within the Dashiwei Tiankeng group, located in Leye County of Guangxi province, South China. The soil samples were analyzed for 23 kinds of organochlorine pesticides (OCPs) using a gas chromatography electron capture detector device. The results showed that the concentrations of OCPs in soils of Dashiwei Tiankeng ranged from 0.03 to 5.13 ng/g for total OCPs, not detectable (ND) to 0.22 ng/g for Hexachlorocyclohexane (HCHs), and 0.01 to 3.61 ng/g for Dichlorodiphenyltrichloroethane and metabolites (DDTs). Concentration of the total OCPs in soils of Datuo Tiankeng ranged from 0.13 to 14.36 ng/g, ND to 0.39 ng/g for HCHs, and 0.01 to 3.28 ng/g for DDTs. These concentrations indicated that there could be new inputs of HCHs and DDTs from recent application of lindane and dicofol in this area. Further analysis also revealed that the concentration of OCPs at the bottom of both Tiankengs was higher than the top. The variability in concentrations between the top and the bottom was attributed to the “cold trapping effect” for persistent organic pollutants (POPs) in karst Tiankeng topography. The difference in temperature between the top and bottom of Tiankeng is a predominating factor which can cause a POPs “cold trapping effect.” Other environmental factors are proposed to explain the difference in concentration such as humidity, topography (or slope), wind speed, wind direction, solar radiation, vegetation cover, and soil organic matter. The environmental condition of Dashiwei Tiankeng appears to favor the accumulation of OCPs than that of Datuo Tiankeng because Dashiwei Tiankeng is a matured Tiankeng but Datuo Tiankeng is a degraded one. Thus, there is the need for further studies on the environmental factors influencing distribution of OCPs in karst Tiankeng.  相似文献   

15.
广州市公园表层土壤中有机氯农药的分布特征   总被引:5,自引:4,他引:1  
通过测定广州市典型公园的冬季和夏季表层土壤样品中有机氯农药(OCPs)含量,研究了OCPs的残留现状和潜在生态风险,并与附近地区相比较,结合当地所处的地理位置对土壤中OCPs的分布特征进行了探讨。冬季和夏季土壤中,六六六类(HCHs)的残留水平分别为0.29~6.26 ng/g和0.60~8.07ng/g,平均值分别为2.06和2.44 ng/g;滴滴涕类(DDTs)的残留水平分别为3.27~38.8 ng/g和1.46~35.5 ng/g,平均值分别为12.4和12.5 ng/g。两类OCPs都未超过国家土壤环境质量标准一级自然背景值。较低的α-HCH/γ-HCH比值和γ-HCH>β-HCH,有可能仍有林丹的使用所致。一些公园可能有新的外源DDTs的输入。历史悠久且距离市中心较近的公园土壤中OCPs含量明显偏高。对于大多数新建且相对偏僻的公园而言,表层土壤一般都未见明显的OCPs污染。  相似文献   

16.
Soil residual concentration of organochlorine pesticides (OCPs) were determined in 245 agricultural surface soil samples collected from Chengdu Economic Region, Sichuan Province, Southwest China, in order to investigate their spatial distribution and the controlling environmental factors. Results showed that detectable ratios of hexachlorocyclohexane (HCH) and dichlorodiphenyltrichloroethane (DDT) were very high, ranging from 88.16 (for δ-HCH) to 97.96% (for p,p′-DDE). The concentrations of DDTs were higher than HCHs, which were consistent with their historical usage in China. OCPs concentrations in the economically developed regions (Chengdu Plain) were higher than in the less developed, mountainous region around Chengdu Plain. The metabolite to parent ratio analysis of HCHs and DDTs indicated there were new pesticide inputs, possibly from the use of lindane (γ-HCH) and dicofol in some regions although they have banned for agricultural use since 1983. Also, the distribution of OCP congeners in soil was mainly governed by their individual physical and chemical characteristic, historical usage amount and patterns, and the environmental conditions, such as, temperature, landform, soil type, etc.  相似文献   

17.
为研究不同土壤类型中有机氯农药的残留特征、降解程度和来源途径,采集了山东烟台9个不同地质单元苹果园根系土壤和剖面土壤样品,用电子捕获检测器气相色谱法测定其中的滴滴涕(DDTs)和六六六(HCHs)。结果表明,研究区所有类型根系土壤中DDTs和HCHs均未超出《土壤环境质量标准》的二级土壤限值(500 ng/g);土壤中DDTs的残留量及检出率均高于HCHs,DDTs检出率为100%,平均残留量为71.7ng/g,而HCHs的检出率为19.70%,平均残留量为7.9 ng/g;根系土壤中DDTs各异构体平均浓度依次为p,p’-DDT>p,p’-DDE>o,p’-DDT>p,p’-DDD,而HCHs大部分以α-HCH形式存在,部分以β-HCH、γ-HCH存在。不同类型土壤中有机氯农药残留分布特征明显不同:DDTs在棕壤土(臧家庄)中最高(145.5 ng/g),在中粗粒砂土(武宁)中最低(24.1 ng/g);而HCHs在细砂质壤土(蛇窝泊)中最高(27.9ng/g)。各剖面土壤DDTs均在<20 cm层位中残留最高。DDTs和HCHs来源解析表明:研究区土壤为好氧条件;麻砂棕壤(官道和桃村)、黏细壤土(牟平)、细砂质壤土(蛇窝泊)和棕壤土(臧家庄)近年来仍有新的DDTs输入;大部分根系土壤均未发现HCHs新来源,但麻砂棕壤(桃村)在HCHs禁用后可能仍存在林丹的使用。  相似文献   

18.
广州市海珠区有机氯农药污染状况及其土-气交换   总被引:5,自引:3,他引:2  
通过在冬夏两季对广州市海珠区表层土壤和空气样品中有机氯农药的采样和分析,对有机氯农药残留现状和潜在生态风险进行了研究。结果表明,土壤中六六六类(HCHs)含量水平在2007年冬季和2008年夏季分别为0.57~8.77 ng/g和0.30~14.9 ng/g,平均值分别为2.87 ng/g和3.04 ng/g,都未超过国家土壤环境质量标准的一级自然背景值。冬季和夏季滴滴涕类(DDTs)含量水平分别为3.69~697.7 ng/g和0.88~263.3 ng/g,平均值分别为85.5 ng/g和39.4 ng/g。海珠区部分地点DDTs超过国家土壤环境质量标准的一级自然背景值。DDTs为该区域表层土壤中主要的有机氯农药残留。在研究区域对逸度模型进行了初步应用。  相似文献   

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