山东单县浅层高氟高碘地下水的水化学特征及成因分析

氟和碘作为人体必需的微量元素,过少或过多摄入都会影响人身健康,相较于缺氟、缺碘,高氟高碘地下水对人体的危害更加难以控制。该研究选择单县作为典型的水源型高氟高碘地区,通过对浅层高氟高碘地下水进行采样测试,采用箱线图、Piper图及双变量相关性分析等多元统计技术剖析了该区域浅层地下水的水环境特征;采用R型因子分析揭示了水化学成分之间的相互关系,探讨了该区浅层高氟高碘地下水的成因。结果表明:①单县浅层地下水中的氟化物和碘化物的质量浓度均值分别为1.2 mg/L和391 μg/L。②随着氟化物浓度的增加,水化学类型偏向于向HCO₃-Na型和HCO₃-Na·Mg型集中,而随着碘化物浓度的增加,水化学类型则倾向于以HCO₃-Na·Mg为主。③该区域强烈的蒸发浓缩作用是控制单县浅层地下水化学成分的最重要因子;萤石平衡控制作用是控制单县浅层地下水高氟背景的因子;水-有机沉积物相互作用是控制单县浅层地下水高碘背景的因子。     

长兴入太湖河网水文变化特征与水质时空差异

以长兴县入太湖的泗安塘-合溪-乌溪河网为研究对象，将入湖河网划分为水源区、河网区、西苕溪区和入湖区，于2018年8月和2019年1月分别对长兴县入太湖河网丰水期和枯水期的水质状况进行了调查，采用空间聚类法、水质标识指数对水质的时空分布进行评价。结果表明，长兴入太湖河网不同片区氨氮（NH₃-N）和总氮（TN）的质量浓度平均值呈现枯水期较丰水期高的特征，而高锰酸盐指数（COD_Mn）和总磷（TP）则呈现丰水期较枯水期高的特征。空间聚类分析结果表明，水质指标分布具有明显的空间差异性，呈现水源区>西苕溪区>河网区>入湖区的分布特征，入湖区是污染物聚集的主要区域。综合水质标识指数分析结果表明，长兴入太湖河网主要以Ⅱ类和Ⅲ类水为主；单因子水质标识指数分析结果表明，溶解氧（DO）、COD_Mn、NH₃-N、TP指标均优于Ⅲ类水标准，TN是入太湖河网的特征污染物，且在丰水期和枯水期质量浓度平均值分别达到2.24,3.49 mg/L。因此，进一步削减氮污染是缓解其河网富营养化的关键。     

骆马湖地区水体、沉积物中农药筛查和分布特征

采用气相色谱/质谱（GC/MS）非靶向筛查技术,分别于2019年11月5—7日（枯水期）、2020年4月24—26日（平水期）和2020年7月15—16日（丰水期）对骆马湖地区水体和沉积物中的农药残留进行了筛查并对其空间分布特征进行研究。结果表明,水中筛查出主要农药13种,除草剂占比62%,检出率＞95%的农药有丁草胺、环嗪酮、异丙甲草胺、多效唑、噻氟菌胺、稻瘟灵、毒死蜱、阿特拉津、避蚊胺和莠灭净,阿特拉津检出质量浓度最高（ND～10 599 ng/L,平均值为725.5 ng/L）,其次为多效唑（ND～2 089 ng/L,平均值为237.0 ng/L）和噻氟菌胺（ND～1 991 ng/L,平均值为237.2 ng/L）。与国内其他地区相比,骆马湖地区水中农药污染处于中等水平,其中阿特拉津、稻瘟灵和毒死蜱的生态风险值得重点关注。骆马湖及入湖河流水中农药总质量浓度呈现丰水期＞平水期＞枯水期的特点,与地表径流、农药的性质及其在水体中的释放等因素有关,丰水期入湖口和省界来水中农药对饮用水水源地的影响较大。沉积物中筛查出9种农药,总体含量不高,且仅扑灭净和避蚊胺检出率>95%,其余<20%。     

沙颍河流域抗生素污染特征与生态风险评价

于2018年7月 (丰水期)、11月 (枯水期) 和2019年3月(平水期)对沙颍河流域5种抗生素磺胺吡啶(SPD)、磺胺氯哒嗪(SCP)、磺胺嘧啶(SDZ)、环丙沙星(CIP)和四环素(TCL)的污染状况和空间分布进行了研究，并对其生态风险进行了评价。结果表明，沙颍河流域5种抗生素在丰水期、枯水期和平水期均有检出，丰水期CIP、枯水期SPD和SDZ以及平水期SCP的检出率均>50%，平水期SCP的检出率最高达到70.97%，CIP在丰水期的检出值最高(655 ng/L)，5种抗生素累积浓度为：丰水期>平水期>枯水期。对比国内其他地区水体环境，沙颍河流域5种抗生素浓度总体处于一般水平，但丰水期CIP检出浓度较高。相关性分析显示抗生素浓度与水质参数硬度、NH₃-N和电导率显著相关。5种抗生素的水生态风险为：丰水期>枯水期>平水期，其中CIP和TCL均为高风险。提出，应加强监测评估与预警管理，有效控制其水生态风险。     

沧州地区氟元素在不同介质中的分布

以沧州地区的地下水、土壤和小麦中的氟元素为研究对象,探讨氟元素在地下水、土壤和小麦等不同介质中的含量、空间分布与来源成因。通过绘制各介质中氟元素分布图,获得氟元素在各介质中不同深度的含量及水平空间上的分布特征。结果显示,当地深层地下水氟含量平均为2.25 mg/L,高于浅层地下水的平均值0.80 mg/L;深层和浅层土壤氟含量接近,平均值分别为557.18、569.20 mg/kg;小麦中的氟含量最高值为0.96 mg/kg,当地小麦氟含量均低于国家标准限值(1.0 mg/kg)。根据氟元素的分布特点分析,当地深层地下水与土壤的氟元素来源一致,而不同于浅层地下水中的氟;小麦的氟元素分布受浅层土壤氟影响较大。     

上海市土壤氟含量风险管控限值探讨

受工业活动影响,上海市典型工业区表层土壤氟中位值普遍高于"七五"背景值。针对工业企业场地土壤氟化物高值现象,目前仍缺乏相关的管理标准体系,且基于总量的评估分析方法已无法满足日益增长的精细化管理需求。详细梳理了国内外氟化物相关标准体系,并对上海市土壤氟限值进行了探讨。基于上海市典型工业场地特征参数计算得到的土壤氟化物筛选值高于上海市土壤"七五"背景值,与上海市工业场地调查得到的土壤氟化物高值基本持平;第一类、第二类用地的氟化物筛选建议值分别为1 980、10 000 mg/kg。与氟化物相比,水溶态氟化物是影响作物体内氟含量的重要因素,且在淋溶等作用下会对地下水安全构成威胁。考虑到水溶态氟化物的环境行为与风险,建议针对农田土壤开展水溶性氟化物含量限值研究。     

江苏某县地下水邻苯二甲酸酯类的检测与风险评价

在江苏某癌症高发区对地下水进行布点,采用固相萃取与气相色谱-质谱联用方法测定深层地下水和浅层地下水中邻苯二甲酸酯类(PAEs)的浓度。检测结果表明,地下水中PAEs污染程度较严重,邻苯二甲酸二丁酯(DBP)和邻苯二甲酸二(2-乙基己基)酯(DEHP)均有超标现象,其中,丰水期深层地下水和枯水期浅层地下水中DBP超标率达到100%,最大超标10.7倍。PAEs总质量浓度均值为10 034.56~14 872.91 ng/L,丰水期总浓度均值大于枯水期,浅层地下水的总浓度均值大于深层地下水。采用优化的USEPA风险评价模型,对PAEs进行人体健康风险评价,评价结果表明,该地区52.5% 地下水的PAEs总致癌风险超过10^-6的水质监控值,总非致癌风险在可接受范围内。     

某铝厂邻近自然村环境氟污染现状监测及分析评价

通过对某铝冶炼厂邻近自然村地下水、地表水、土壤中氟化物含量进行监测,并对其氟污染程度进行分析及评价.结果表明,自然村地下水、地表水、土壤都不同程度地受到了氟污染,从平均质量指数来看,地下水受到了中度氟污染,地表水受到了重度氟污染,土壤受到轻度氟污染.氟是对植物、动物、人类有较高毒性的积累性污染物,为防止自然村地下水、地表水、土壤的氟污染现状进一步恶化,应当从源头上对氟污染源进行治理及控制,及时有效地解决当地铝冶炼造成的环境氟污染.     

广州主要工业源排放的气态污染物扩散模拟研究

以广州省控工业污染源排放的气态污染物(SO₂、NO_x为主要研究对象,通过中尺度气象模式MM5与空气质量模式CALPUFF耦合,模拟11月典型气象条件下, SO₂和NO_x的扩散传输过程,研究其时空分布特征,并分析省控工业污染源排放对特定区域(主要针对2010年亚运场馆)空气质量的影响。结果表明,主要受典型风速的影响,SO₂和NO_x浓度具有明显的时空分布不均匀性。浓度高峰值主要出现在晚间至凌晨时段,而浓度低峰值主要出现在白天至中午时段。受污染源分布、排放高度和风向的影响,荔湾区和越秀区污染物浓度较高,且在广州西南部形成较明显的污染带;且这些省控污染源对南沙体育馆空气质量有较大影响。 研究结果对广州空气污染来源分析具有一定参考意义。     

大连市中心城区地下水“三氮”污染分析

依据《地下水质量标准》(GB/T 14848-1993),对大连市中心城区2006-2010年地下水"三氮"监测资料进行分析。结果表明,"三氮"的检出率(最高为100%)和超标率(最高为58.8%)都较高,其中亚硝酸盐氮超标显著。氨氮浓度各年均值均超标,呈波动变化;亚硝酸盐氮浓度各年均值均超标,并呈上升趋势;硝酸盐氮各年均值波动变化,总体呈上升趋势。除2009年以外,其他4年中丰水期的硝酸盐氮浓度都比枯水期高;除2007年外,其他4年中的丰水期氨氮浓度都比枯水期低。"三氮"最高浓度值主要出现在中心城区周边区域。     

Assessment on Seasonal Variation of Groundwater Quality of Phreatic Aquifers – a River Basin System

Spatial distribution of pH, electrical conductivity (EC), total dissolved solids (TDS), fluoride and total iron content of ground water samples collected from the muvattupuzha river basin, Kerala, India, has been studied for pre monsoon and post monsoon periods of year 2001. Results showed the groundwater of the basin is acidic for which the pH values ranged between 5.5 and 8.0. Average EC was found to be less than 100 μS/cm, for most of the study region. The pre monsoon minimum and maximum TDS were found as 25.6 and 227.84 mg/L respectively, where as post monsoon values ranged between 16 and 162.56 mg/L. The relatively low EC and TDS values found both during the seasons in the lateritic terrain of the river basin signifies the lower residence time of ground water with the country rock. This makes the groundwater quality of this river basin as good. Pre monsoon season samples showed high total iron content than that during the post monsoon period. During the study period values of the fluoride contents were found to be within the permissible limits.     

Analysis of spatial–temporal distributions of nitrate-N concentration in Shitoukoumen catchment in northeast China

This article discusses the generation and migration process of nitrate-N pollution in shallow groundwater caused by agricultural nonpoint source pollution in the catchment area of Shitoukoumen Reservoir in northeast China. By monitoring the shallow groundwater nitrate-N in the low-water period, the normal season, and high-flow period in the study area for a year, it was found that the nitrate-N concentration in the shallow groundwater of this area had a seasonal variation in both spatial and time distribution. In the time distribution, the peak value appeared in July, the high-flow period, and the valley value appeared in April, the low-water period, and showed a significant correlation with the time distribution of fertilization rate and rainfall. In the spatial distribution of nitrate-N pollution, when the distribution in shallow groundwater was analyzed separately in the three different periods (low-water period, the normal season, and high-flow period) and the discipline transference and enrichment of nitrate-N pollution in shallow groundwater was determined, this indicated that the region in the southeast study area where runoff conditions were better was less contaminated, and the region where runoff conditions were poor, as well as the region along the river were seriously polluted. The nitrate-N concentration in shallow groundwater was distributed mainly along the path of groundwater flow and was excreted in the drainage region. This showed that the spatial distribution of nitrate-N concentration in the shallow groundwater of the entire region was mainly controlled by the groundwater flow system. At the same time, in the middle and lower reaches of the study area, the seasonal changes in the recharged–excreted relationship between groundwater and river caused seasonal differences in the spatial distribution of nitrate-N pollution in groundwater. The combined effects of the groundwater mobility and the surface river resulted in a poor correlation between the groundwater nitrate-N concentration and land-use types. Only in the plain area where there was little influence from groundwater runoff and the surface river did the groundwater nitrate-N concentration correlate with land-use types. The spatial and time distribution of nitrate-N concentration in the shallow groundwater of the study area was impacted by agricultural nonpoint source pollution, the groundwater flow system, and the surface river and formed a concentration response system which uses basins as a unit.     

Distribution of Iron, Manganese, Zinc and Atrazine in Groundwater in Parts of Palar and Cheyyar River Basins, South India

A study was carried out in a part of Palar and Cheyyar river basin to evaluate the current status of iron, manganese, zinc and atrazine concentrations, their origin and distribution in groundwater. Groundwater samples were collected during post-monsoon (March 1998 and February 1999) and pre-monsoon (June 1999) periods from 41 sampling wells distributed throughout the study area. The groundwater samples were analyzed for trace metals using AAS and atrazine using HPLC. The concentration of the trace elements in groundwater is predominant during pre-monsoon period. Distribution pattern indicates that the concentration of these elements increases from west to northeast and towards Palar river. Lower concentrations in the central part may be due to recharge of fresh water from the lakes located here. During most of the months, as there is no flow in Palar river, the concentrations of trace elements in groundwater are high. Drinking water standards indicate that Mn and Zn cross the permissible limit recommended by EPA during the pre-monsoon period. A comparison of groundwater data with trace element chemistry of rock samples shows the abundance of trace elements both in the rock and water in the order of Fe > Mn > Zn and Fe > Zn > Mn. This indicates that iron in groundwater is derived from lithogenic origin. Further, Fe, Mn and Zn have good correlation in rock samples, while it is reverse in the case of water samples, indicating the non-lithogenic origin of Mn and Zn. Atrazine (a herbicide) was not detected in any of the groundwater samples in the study area, perhaps due to low-application rate and adsorption in the soil materials.     

Fluorine contamination in groundwater: a major challenge

Fluoride in high concentration in groundwater has been reported from many parts of India. However, a systematic study is required to understand the behavior of fluoride in natural water in terms of local hydrogeological setting, climatic conditions, and agricultural practices. The present study is an attempt to assess hydrogeochemistry of groundwater in parts of Palar river basin pertaining to Kancheepuram district Tamil Nadu to understand the fluoride abundance in groundwater and to deduce the chemical parameters responsible for the dissolution activity of fluoride. The study area is geologically occupied by partly sedimentary and partly crystalline formations. A total of 50 dug cum borewell-water samples, representing an area of 2,628.92 km². The results of the chemical analyses in September 2009 show fluoride abundance in the range of 1 to 3.24 mg/l with 86% of the samples in excess of the permissible limit of 1.5 mg/l. Presence of fluoride-bearing minerals in the host rock, chemical properties like decomposition, dissociation, and dissolution, and their interaction with water are considered to be the main causes for fluoride in groundwater. Chemical weathering with relatively high alkalinity favors high concentration of fluoride in groundwater. Villagers who consume nonpotable high fluoride water may suffer from yellow, cracked teeth; joint pains; and crippled limbs and also age rapidly.     

Groundwater Quality Assessment of Tehsil Kheragarh, Agra (India) with Special Reference to Fluoride

Fluoride concentration and other parameters in groundwater from 261 villages in Tehsil Kheragarh of District Agra were assessed and attempts were made to observe the relationship between fluoride and other water quality parameters. Of 658 groundwater samples (collected from separate sources) analysed for fluoride, 27% were in the range of 0–1.0 mg/L, 25% in 1.0–1.5 mg/L, 32% in1.5–3.0 mg/L and 16% above 3.0 mg/L. The highest fluoride concentration recorded was 12.80 mg/L. Significant correlation of fluoride with pH, alkalinity, Na, SiO₂ and PO₄ were observed. Factor analysis was also attempted in order to identify the contributing sources.     

黑龙江省松花江流域河流中高锰酸盐指数非点源污染负荷分析

采用3种方法分析黑龙江省松花江流域高锰酸盐指数非点源污染的负荷。分析结果显示,非点源污染造成的松花江流域高锰酸盐指数负荷约为70%;松花江流域支流源头属于高高锰酸盐指数河段,本底值约为5mg/L,河流流经1000Km非点源污染会增加高锰酸盐指数约1mg/L;松花江流域河流中高锰酸盐指数含量高的主要原因是流域内土壤有机质含量高。     

The occurrence and hydrochemistry of fluoride and boron in carbonate aquifer system, central and western Estonia

Silurian–Ordovician (S–O) aquifer system is an important drinking water source of central and western Estonia. The fluoride and boron contents of groundwater in aquifer system vary considerably. The fluoride concentration in 60 collected groundwater samples ranged from 0.1 to 6.1 mg/l with a mean of 1.95 mg/l in the study area. Boron content in groundwater varied from 0.05 mg/l to 2.1 mg/l with a mean value of 0.66 mg/l. Considering the requirements of EU Directive 98/83/EC and the Estonian requirements for drinking water quality, the limit value for fluoride (1.5 mg/l) and for boron (1.0 mg/l) is exceeded in 47 and 28 % of wells, respectively. Groundwater with high fluoride and boron concentrations is found mainly in western Estonia and deeper portion of aquifer system, where groundwater chemical type is HCO₃–Cl–Na–Mg–Ca, water is alkaline, and its Ca²⁺ content is low. Groundwater of the study area is undersaturated with respect to fluorite and near to equilibrium phase with respect to calcite. The comparison of TDS versus Na/(Na?+?Ca) and Cl/(Cl?+?HCO₃) points to the dominance of rock weathering as the main process, which promotes the availability of fluoride and boron in the groundwater. The geological sources of B in S–O aquifer system have not been studied so far, but the dissolution of fluorides from carbonate rocks (F?=?100–400 mg/kg) and K-bentonites (F?=?2,800–4,500 mg/kg) contributes to the formation of F-rich groundwater.     

Lead (Pb) and arsenic (As) bioaccessibility in various soils from south China

Serious problems are faced in several parts of the world due to the presence of high concentration of fluoride in drinking water which causes dental and skeletal fluorosis to humans. Nalgonda district in Andhra Pradesh, India is one such region where high concentration of fluoride is present in groundwater. Since there are no major studies in the recent past, the present study was carried out to understand the present status of groundwater quality in Nalgonda and also to assess the possible causes for high concentration of fluoride in groundwater. Samples from 45 wells were collected once every 2 months and analyzed for fluoride concentration using an ion chromatograph. The fluoride concentration in groundwater of this region ranged from 0.1 to 8.8 mg/l with a mean of 1.3 mg/l. About 52% of the samples collected were suitable for human consumption. However, 18% of the samples were having less than the required limit of 0.6 mg/l, and 30% of the samples possessed high concentration of fluoride, i.e., above 1.5 mg/l. Weathering of rocks and evaporation of groundwater are responsible for high fluoride concentration in groundwater of this area apart from anthropogenic activities including irrigation which accelerates weathering of rocks.     

Occurrence and behaviour of nonylphenol and octylphenol in Nanming River, Guiyang City, China

Occurrence, variation and behaviour of nonylphenol (NP) and octylphenol (OP) were studied in surface water and groundwater in Guiyang, Guizhou Province, southwestern China. Discharge of wastewater from Guiyang City was the main source of alkylphenols (APs) entering the aquatic environment. The concentrations of NP and OP in river water ranged from 40 to 1582 ng L(-1) and from below the lowest limit of detection (LOD) to 67 ng L(-1), respectively. NP and OP were also detected in groundwater. Both NP and OP exhibited spatial and temporal variations in river water and groundwater. It was found that concentrations of NP and OP in river water was low upstream and dramatically increased downstream, and higher concentration of NP was found in winter compared to that in summer. Proportions of NP and OP were trapped by suspended particulate matter (SPM), which accounted for 7.6-50.0% and 3.4-25.6% of their total concentration in the river water system, respectively. Seasonal changes in water flow were responsible for the temporal variations of APs. To determine the behaviour of APs along the river, a mass balance equation based on chloride was used. The results showed that a mixing process was the predominant factor to determine upstream APs concentrations; while the discharge of wastewater controlled the concentrations of APs downstream. Considering the adverse effect of APs on organisms, combined effect modeling was used to assess the toxicity to fish. It was found that the predicted mixture effect for APs in river water on fish vitellogenin induction was low upstream and medium downstream, respectively.     

Fluoride contamination in drinking water in rural habitations of Northern Rajasthan, India

This study was carried out to assess the fluoride concentration in groundwater in some villages of northern Rajasthan, India, where groundwater is the main source of drinking water. Water samples collected form deep aquifer based hand-pumps were analysed for fluoride content. Fluoride in presently studied sites was recorded in the ranges of 4.78 and 1.01 mg/l. The average fluoride concentration for this region was recorded 2.82 mg/l. As per the desirable and maximum permissible limit for fluoride in drinking water, determined by WHO or by Bureau of Indian Standards, the groundwater of about 95 of the studied sites is unfit for drinking purposes. Due to the higher fluoride level in drinking water several cases of dental and skeletal fluorosis have appeared at alarming rate in this region. The middle and eastern parts of the Hanumangarh, a northern most district of the state, can be classified as higher risk area for fluorosis; due to relatively high concentrations of fluoride (3-4 mg/l) in groundwater of this region. After evaluating the data of this study it is concluded that there is an instant need to take ameliorative steps in this region to prevent the population from fluorosis.