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1.
分析济南幅黄泛平原区浅层孔隙水的补给来源、地下水流场形态变化、地下水排泄途径及水化学多年变化特征,并结合区内浅层地下水开采强度资料综合研究认为,引起济南幅黄泛平原区浅层孔隙水动力场变化的主要原因是地下水开采量的变化与天然补给源的减少。研究表明,局部水位下降甚至产生超采漏斗主要是由于地下水长期过量开采引起的,并对区域地下水流场形态影响较大,区内已形成地下水分水岭。  相似文献   

2.
分析济南幅黄泛平原区浅层孔隙水的补给来源、地下水流场形态变化、地下水排泄途径及水化学多年变化特征,并结合区内浅层地下水开采强度资料综合研究认为,引起济南幅黄泛平原区浅层孔隙水动力场变化的主要原因是地下水开采量的变化与天然补给源的减少.研究表明,局部水位下降甚至产生超采漏斗主要是由于地下水长期过量开采引起的,并对区域地下水流场形态影响较大,区内已形成地下水分水岭.  相似文献   

3.
为了解鲁西南地区地下水中锰的含量及其成因,采集并分析了276组地下水样和18组地表水样,结果表明,鲁西南平原区浅层地下水中锰含量在未检出至2.84mg/L之间,平均浓度为0.35mg/L,超标率达41%。鲁西南地区地下水中锰含量的分布与该区的工业化程度以及所处的补、径、排条件密切相关。影响地下水中锰含量分布的因素主要有表层土壤、地下水径流条件及含水层介质和地下水矿化度等。  相似文献   

4.
大同盆地是典型的高氟地下水分布区,其分布规律和成因在类似地区具有代表性。在对盆地地下水水化学特征和空间
变化特征分析的基础上,深入讨论了高氟地下水的空间分布规律、控制因素及其形成的水文地球化学过程。结果表明,整个盆地
浅层孔隙水中的氟质量浓度普遍较高,变化范围为0.29~6.22mg/L,平均值为1.82mg/L。氟质量浓度高值区主要分布于盆地
中部和北部,呈现出由盆地边缘至盆地中心,质量浓度趋向于升高的变化规律。强烈的蒸发浓缩作用以及高pH、高碱度、高钠低
钙含量的水化学特征有利于氟富集。大同盆地高氟地下水的形成是含氟矿物的溶解、离子交换和蒸发浓缩作用等水文地球化学
过程共同作用的结果。   相似文献   

5.
在对汶泗河冲洪积平原水文地质条件和污染源现状进行阐述的基础上,对不同含水岩组无机组分指标进行了分析,表明浅层孔隙水和部分地区岩溶裂隙水无机组分含量大幅增高,深层孔隙水无机物含量则变化不大。在有机污染方面,浅层孔隙水有机物检出率26.8%,但含量很低,远未达到饮用水标准限值;岩溶裂隙水有机物检出率46.7%,检出率相对较高,局部地段有机物超标;深层孔隙水有机物基本未检出。该区地下水污染评价结果表明,浅层孔隙水和岩溶裂隙水无机污染呈面状污染特征,且污染程度较重,而有机污染则呈现点状污染特征,且污染程度总体较轻。对研究区地下水污染现状,提出了地下水安全供水对策。  相似文献   

6.
平阴县浅层地下水调查采样密度为1点/16km2,分析测试27项指标的含量变化规律后,认为调查区浅层地下水中除K,Mn,NO-2等指标含量变化较大,局部富集外,其他指标含量变化小,在浅层地下水中分布较均匀.选择As,Ba,Be,Cd,Co,Cu,Fe,Hg,Mn,Mo,Ni,Pb,Se,Zn,F-,Cl-,Cr6+,NO-2,COD,pH等20项指标,按<地下水质量标准>对浅层地下水环境质量进行的单因子和综合评价,结果显示较好级以上者达88.4%,而较差级仅占11.6%,无极差级分布,调查区内浅层地下水环境质量状况良好.  相似文献   

7.
浅层地下水是陆地水资源的重要组成部分,与人类生产生活密切相关。基于生态地球化学调查项目,按照1点/16km2的密度对滕州市浅层地下水进行调查,共采集地下水样品95件,分析Fe、Mn等35项指标。结果表明,研究区浅层地下水质量总体较好,pH、CN-、Cr6+、溶解性总固体等21项指标含量基本符合《地下水质量标准》(GB/T 14848-2017)中Ⅲ类地下水规定的阀值,适用于集中式生活饮用水水源及工农业用水。影响研究区浅层地下水质量的主要因子是Fe和总硬度,由原生地质环境及人类活动引起。研究结果可为研究区经济社会发展和用水安全提供基础性资料和决策依据。  相似文献   

8.
高氟地下水是一种典型劣质水源,长期饮用可致人体患地方性高氟病。本次研究以禹城—平原地区为研究对象,对区内地下水进行氟含量、水化学类型和氟离子的影响因子等研究。结果表明,浅层地下水氟离子含量大部分不超过1.0mg/L,其水化学类型主要有HCO3-Na和Cl·SO4-Na型,深层地下水氟离子含量大部分均超过1.0mg/L,其水化学类型为HCO3·SO4-Na和HCO3·Cl-Na型。通过对pH和地下水水化学演化因素的研究,认为碱性环境一定程度能够促使氟离子聚集,但并不是唯一决定因子,高氟水的形成机制主要是水-岩相互作用和蒸发浓缩作用。  相似文献   

9.
为查明控制大同盆地高氟地下水形成的主要地球化学过程,对大同盆地地下水高氟区31个水样进行了水化学特征及
因子分析研究。结果表明,研究区浅层和深层地下水中均检测出氟,且氟含量高,最大ρ(F)达10.37mg/L。该区高氟地下水以
Na-HCO3 型水为主,具有典型的富Na特征。PHREEQC饱和指数计算结果表明,地下水中萤石为不饱和状态,地下水中ρ(F)主
要受到萤石溶解影响。因子分析研究表明,水-岩相互作用、碳酸盐矿物溶解沉淀及Na-Ca离子交换作用是控制大同盆地地下
水氟富集的主要水化学过程。   相似文献   

10.
在内陆干旱区,作为重要饮用水源的地下水常面临氟含量超标问题。查明内陆干旱区高氟地下水的分布规律,了解氟在地下水中的富集过程及其影响因素,既可丰富高氟地下水的研究体系,也是保证内陆干旱区饮水安全的重要基础。以新疆阿克苏地区典型山前洪积扇——依格齐艾肯河-喀拉玉尔滚河河间地带为研究区,基于水文地球化学调查结果,刻画了高氟地下水的分布区;结合氟离子含量与特征性水化学指标间的关系,揭示了高氟地下水的成因机制。结果表明:①地下水中氟含量的变化范围为0.8~6.1 mg/L,83%的水样氟含量超过《生活饮用水卫生标准》(GB 5749-2006)规定的上限(1.0 mg/L);②总体上,氟含量沿地下水流动路径逐渐增大,低氟地下水(ρ(F-)≤1.0 mg/L)分布在国道314以北的补给区,高氟地下水(ρ(F-)>1.0 mg/L)分布在国道314以南的径流区和排泄区;③高氟地下水的水化学类型以Cl·HCO3-Na型为主,而低氟地下水则以Cl·SO4-Na型为主,高氟地下水相比于低氟地下水优势阴离子偏向于HCO3-;④地下水的pH值范围为7.9~8.9(均值为8.4),表明其处于弱碱环境中。地下水中ρ(F-)与pH值呈正相关,此外构成浅层含水层的上更新统沉积物中含有黑云母、氟磷灰石等矿物,其表面存在一定数量的可交换F-,这表明水中OH-与矿物表面F-间的阴离子交换可能对氟的富集有一定贡献;⑤地下水的F-含量与Ca2+含量呈负相关,即高氟地下水中ρ(Ca2+)小于低氟地下水。考虑到氟化钙(CaF2)是自然界中的主要含氟矿物,也是地下水中氟的主要来源,ρ(F-)与ρ(Ca2+)间的这种负相关指示着高氟地下水中可能存在去Ca2+、Mg2+作用,如阳离子交替吸附或碳酸盐岩沉淀等。研究区地下水样中ρ(F-)与ρ(Mg2+)间也呈负相关关系,且和ρ(F-)与ρ(Ca2+)间的关系高度相似,也佐证了高氟地下水中去Ca2+、Mg2+作用的存在;⑥绝大部分地下水样品都位于氯碱性指数图的负值区域,且ρ(F-)与CAI-1和CAI-2均呈较好负相关,CAI-1和CAI-2都随ρ(F-)的增大而减小,这表明高氟地下水中存在Ca2+、Mg2+与Na+间更强的交换作用,对氟富集起着重要作用。地下水中ρ(F-)与SAR间呈较好正相关关系,且高氟地下水样的SAR均值(5.71)远大于低氟地下水SAR均值(1.67),这也进一步证明高氟地下水中的Ca2+、Mg2+与含水介质的Na+间存在强烈的交替作用,对氟的富集起着重要作用;⑦所有地下水样中的萤石均处于未饱和状态,且萤石的饱和指数(SI)与F-含量间呈现较好的正相关,这表明地下水对含氟矿物(主要是萤石)的持续溶解应是导致研究区地下水中氟富集的主要原因。与之相反,研究区所有地下水样中的方解石均处于过饱和状态(SI>0)。这表明CaCO3的沉淀可能促进了CaF2的溶解,导致地下水中氟离子质量浓度增高;⑧研究区低氟地下水的δ18O值介于-11.20‰~-10.67‰间,平均值为-10.94‰,而高氟地下水的δ18O值介于-11.65‰~-11.21‰间,平均值为-11.49‰,即低氟地下水较高氟地下水富集δ18O。此外,F-质量浓度较低(ρ(F-)≤3.0 mg/L)的地下水样中δ18O值与F-质量浓度呈负相关,即低氟地下水具有更正的δ18O值;F-质量浓度较高(ρ(F-)≥4.8 mg/L)的地下水样中δ18O值与F-质量浓度的相关性不显著,随F-质量浓度的增高,δ18O值基本维持不变。以上表明蒸发浓缩作用对地下水中氟的富集贡献较小;⑨研究区地下水中ρ(F-)/ρ(Cl-)比值与ρ(F-)间呈现正相关,即ρ(F-)/ρ(Cl-)比值随ρ(F-)增高呈增大趋势,这也说明地下水中氟富集的主要原因是含氟矿物的溶解,而不是蒸发浓缩作用。此外,Gibbs图也提供了证据:研究区地下水样基本处于水岩作用主导区域,表明地下水化学特征(包括氟的富集)主要受水岩作用控制,蒸发浓缩影响很小。总之,地下水中氟的富集主要由溶解作用引起,OH-与矿物表面F-间的交换也有贡献,但蒸发浓缩作用影响微弱。含氟矿物持续溶解的驱动机制是阳离子交替吸附(地下水中Ca2+与岩土颗粒表面Na+之间)及方解石沉淀所引起的地下水中Ca2+的衰减。   相似文献   

11.
12.
归纳总结了四川盆地珍珠冲组植物化石7类50属128种,须家河组植物化石10类71属267种,并将珍珠冲组植物群划分为上、下两个组合.通过分析两组植物群的发育特点及演化规律,结合区域有关资料,对侏罗系与三叠系界线进行了厘定.在四川盆地北部大巴山前缘地区,依据珍珠冲组(白田坝组)的岩性特征和所含植物化石特征,将侏罗系与三叠系的界线置于含Coniopteris植物化石的珍珠冲组(白田坝组)底部石英质砾岩或石英砂岩之下的假整合面或剥蚀面上;在四川盆地东北部的云阳、奉节及长江以南万县地区,侏罗系与三叠系的界线划在云阳南溪剖面上含Coniopteris murrayana植物化石8.3 m之下的珍珠冲组黄绿色泥质粉砂岩夹粉砂质泥岩地层之底.  相似文献   

13.
Impact factors on the salinity budget,especially the eddy salt fluxes and smaller-scale diffusive salt fluxes for the upper 50 m of the Bay of Bengal(BoB) in 2014 are investigated using a box model based on the Regional Ocean Modeling System(ROMS) daily outputs.The model results reproduce that the precipitation and river runoffs are the dominant factors modulating the sharp salinity decrease during the summer monsoon season.The analysis shows that the salinity increase after the summer monsoon is mostly due to the meridional advective and diffusive salt fluxes.The vertical advective salt flux,which is sensitive to the different signals of the wind stress curl,plays an important role in balancing the salinity change induced by the meridional advective salt flux during both the summer and winter monsoon seasons.Distinctive spatial mesosc ale structures are presented in the eddy salt flux throughout the year,and their contributions are sizeable(over 30% in the meridional direction and about 10%-30% in the vertical direction).The meridional eddy salt flux is larger in the monsoon seasons than that in the inter-monsoon seasons,and in a positive pattern near the western boundary during the winter monsoon and autumn inter-monsoon.The vertical eddy salt flux makes an important contribution to the salinity budget,especially along the coastal area and around the Andaman and Nicobar Islands.The vertical eddy salt flux becomes large when a tropical cyclone passes the area.  相似文献   

14.
应用分形法对桐柏山-大别山地区进行了钼元素地球化学异常筛选与靶区预测,以期实现该地区的找矿新突破。研究
最终在桐柏-大别地区圈定出25个有利钼异常区及5个靶区,分别是枣扒靶区、吴山靶区、墨斗关靶区、两路口靶区、烈马咀靶
区。其中,重点对两路口靶区进行了勘查工作,并且在该地区新发现了小型钨矿体。综合说明,分形法对桐柏山-大别山地区的
异常筛选工作优于传统方法,本次研究的成果对桐柏山-大别山地区寻找钼、钨矿床具有较强的指导意义。   相似文献   

15.
Among the factors influencing tourist trail network development are political issues, including the presence of state borders, the possibility of crossing them and the accessibility of border zones. In the article, it was decided to look at changes in the offer of tourist trails(hiking and cycling) along the entire border of the Czech Republic after the extension of the Schengen area(within this area, crossing the border is possible anywhere, and not only at official border crossings). It should be emphasized here that the borders of the Czech Republic over most of their length run through mountainous areas and, apart from political factors, natural features should have a major impact on the development of tourist routes. In order to determine the coherence of the current network of trails on both sides of the Czech Republic state border, modern tourist maps have been analyzed, determining the number of places where it is possible to cross the state border with the help of a marked tourist trail. Based on that, two indicators were introduced to determine the degree of openness with all neighboring countries as regards the opportunity to cross on a tourist trail. Changes in the historical situation, a comparison of the accessibility of the border area before entering the Schengen area and 2019, were analyzed for two study areas using archival maps. Over a decade after the extension of the Schengen area, the number of places where tourist trails of neighboring countries approach the border has clearly increased. Crossing is more often made possible using hiking trails than cycling routes(trails of the first type cross the border every 7.91 km, while the latter every 13.3 km), but considering the speed of movement, it can be assessed that the openness for cyclists is higher than for hikers. Moreover, in many places there is still significant potential for further integration of tourist trail networks as trails created in one country often do not have a continuation on the other side of the border.  相似文献   

16.
介绍了泰州市在推进国土资源管理走上法制化轨道的过程中采取的一系列措施.从健全规章制度,规范执法行为,实行责任追究制度,制约行政权力到严格考核奖惩,确保各项措施落到实处,便民服务,公开接受社会监督等,取得了明显的成效.  相似文献   

17.
Habitat richness influences and even determines biological diversity. Plant habitat suitability assessment can provide technical guidance and information support for ecological restoration. Thirteen factors in three categories of terrain, meteorology and soil were chosen to build a habitat suitability assessment index framework in the Upper Reaches of the Min River, based on the local natural environment and the actual influencing factors of vegetative growth. Combined with the Analytic Hierarchy Process(AHP) and entropy method, which were used to calculate weights of indexes, habitat suitability was studied by using a multi-objective linear weighting model and geographic information systems(GIS) spatial analysis techniques. The assessment results are as follows: Altitude, soil stability, aspect and slope have more important effects on plant habitat suitability in the Upper Reaches of the Min River, and their weights are 0.311, 0.260, 0.198 and 0.125, respectively. Suitable and sub-suitable habitats cover 4431.80 km2 and 6171.12 km2, respectively; most of which are distributed along both sides of rivers and have higher suitability. Unsuitable habitats cover the largest area(6679.76 km2), accounting for 29.83% of the whole area; and the worst unsuitable habitats are 5107.23 km2(22.81%); they account for more than half of the studyarea. These results indicate that the plant habitat in the Upper Reaches of the Min River is poor and ecological restoration is both urgent and difficult. Therefore, based on the principle of taking measures suitable to the habitat in ecological restoration projects, ecological and engineering measures should be combined to have better effects, while increasing the strength of ecological protection.  相似文献   

18.
对广东省中山市三角镇的低盐度鱼虾混养池进行连续采样分析,结果表明,混养池中的蓝藻主要有螺旋藻(Spirulina sp.),鱼腥藻(Anabaena sp.),颤藻(Oscillatoria sp.)、铜绿微囊藻(Microcystis aeruginosa)等,其中盐泽螺旋藻的优势度为0.52~0.73。蓝藻是水体中的优势微藻种群,蓝藻细胞数量占微藻细胞数量的88%~99%,蓝藻细胞数为0.99×10~9~5.89×l0~9 cell/L。混养池微藻多样性指数(H’)为1.16~2.49,养殖水体处于中度污染状态。溶解性无机氮的质量浓度为0.13~2.30 mg/L,正磷酸盐质量浓度为0.25~2.39 mg/L,化学需氧量的质量浓度为1.94~13.79 mg/L。微囊藻毒素(MC-LR)在水中质量浓度为0.18~0.79μg/L。蓝藻细胞数量与化学需氧量之间呈显著的正相关关系,表明蓝藻的生长情况与养殖池中的有机污染程度有密切联系,低盐度的富营养化的水体能促进蓝藻的生长,成为微藻群落中的优势种群。MC-LR的质量浓度与蓝藻细胞数量之间无显著相关。  相似文献   

19.
CTD data on standard levels coolected during July and December in 1998 and the cubic spline interpolating method were used to study the characteristics of the transition layer temperature and salinity.The thermocline undergoes remarkable seasonal variation in the South China Sea (SCS),and especially in the region of the north shelf where the thermocline disappears in december.The thermocline is stronger and thicker in July than in December,There is no obvious seasonal variation in the halocline.Due to the upper Ekman transport caused by monsoon over the SCS,the thermocline slopes upward in July and downward in december from east to west in the northern SCS.The characteristics of the thermocline and halocline are influenced by local eddies in the SCS.The Zhujiang diluted flow influences significantly the SCS shelf‘s halocline.  相似文献   

20.
Based on the analysis of Levitus data, the climatic states of the warm pool in the Indian Ocean (WPIO) and in the Pacific Ocean (WPPO) are studied. it is found that WPIO has a relatively smaller area, a shallower bottom and a slightly lower seawater temperature than those of WPPO. The horizontal area at different depths, volumes, central positions, and bottom depths of both WPIO and WPPO show quite apparent signals of seasonal variation. The maximum amplitude of WPIO surface area’s seasonal variation is 58% larger over the annual mean value. WPIO’s maximum volume variation amplitude is 66% larger over the annual mean value. The maximum variation amplitudes of the surface area and volume of WPPO are 20.9% and 20.6% larger over the annual mean value respectively. WPIO and WPPO show different temporal and spatial characteristics mainly due to the different wind fields and restriction of ocean basin geometry. For instance, seasonal northern displacement of WPIO is, to some extent, constrained by the basin of the Indian Ocean, while WPPO moves relatively freely in the longitudinal direction. The influence of WPIO and WPPO over the atmospheric motion must be quite different.  相似文献   

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