砂岩热储地热尾水回灌悬浮物堵塞研究

砂岩热储人工回灌过程中介质堵塞问题严重影响到回灌效率,为查明回灌过程中悬浮物堵塞对回灌效率的影响。试验依据德城区鲁北院内回灌井现场尾水中悬浮物粒径分布特征,并以市政自来水为水源,粘性土颗粒为入渗介质,配制0.038 mm和0.050 mm的不同悬浮物粒径和0 mg/L、20 mg/L、50 mg/L、60 mg/L、100 mg/L的不同悬浮物浓度开展一维砂柱模拟回灌试验。试验结果表明:悬浮物堵塞会引起整柱相对渗透系数呈现"快速下降-趋于稳定"的趋势,且堵塞主要发生在表层,可能在一定程度上抑制了悬浮物颗粒向下迁移;悬浮物粒径的大小和浓度均可以影响热储介质堵塞发生时间,悬浮物粒径越大堵塞发生时间越早,浓度越高,堵塞时间越短。试验针对悬浮物堵塞试验研究成果及现实情况,提出了一些针对性的治理措施:(1)设计一级除砂器,除砂器不仅可以沉降颗粒较大的悬浮物,降低悬浮物浓度,也能对尾水进行降温,有益于缓解物理悬浮物堵塞。(2)经过除砂器后,尾水进入二级过滤器,设计粗过滤器的过滤级为50μm,而精过滤器的过滤级为10μm,过滤器的个数可以根据尾水回灌量确定。     

地下水人工回灌过程中多孔介质悬浮物堵塞实验

地下水人工回灌技术的发展与推广常因其回灌过程中物理、化学及生物作用产生的入渗介质堵塞现象而受到严重制约。针对堵塞现象中最常见且最主要的悬浮物堵塞问题,采用室内模拟实验方法,通过将悬浊水连续注入均质的石英砂柱中,来刻画多孔介质中悬浮物堵塞的现象及发生的过程,并分析其发展规律,同时量化计算了堵塞速率。实验结果表明：回灌15 h左右表层介质渗透系数开始降低,即堵塞在表层开始发生,并随时间增加不断向深部发展;连续回灌100 h后表层渗透系数趋于稳定,进入介质内部悬浮物的量减少,内部堵塞发展也趋于稳定,此时堵塞主要在入渗深度10 cm左右的范围内。计算不同堵塞层的堵塞速率λ:表层0～1 cm的λ最大,为0.038 3 h^-1,λ随入渗深度增加而减小。对于介质整体的渗透性而言,其降低明显滞后于表层介质,但随时间发展主要受堵塞层的控制。     

地下水位抬升对人工回灌中悬浮物堵塞的影响

为了研究人工回灌条件下地下水位抬升对悬浮颗粒在含水层中的迁移-沉积的影响机理,在室内模拟实验中,采用100 mg/L的金刚砂悬浊水回灌中粒石英砂介质,分别研究了不同抬升速率(0、2、4cm/h)条件下人工回灌过程中的悬浮物堵塞规律。实验结果表明:地下水位抬升速率对堵塞位置和堵塞位置处悬浮物的级配影响不大,悬浮物主要淤积在0~2cm深度处;在26h前地下水位抬升引起的入渗量比地下水位固定的入渗量小,在26h后二者相反;水位抬升使介质表层堵塞发展速度减慢,非堵塞层渗流状态出现非饱和时刻滞后;在堵塞层0~2cm处地下水位抬升使堵塞速率小于地下水位固定的堵塞速率。     

雨洪资源地下回灌促渗技术的实验研究

针对雨洪资源地下回灌工程易堵塞、效率低、寿命短等问题,以入渗池为例,开展室内模拟实验。实验通过模拟雨洪资源地下回灌条件和过程、设定渗透介质的表面形态和回灌的工程工艺方法,观测渗透速率随时间的变化规律,分析堵塞层悬浮物的分布规律;通过对比相同目标补给层、不同回灌工程工艺方法对入渗速率的影响,分析促渗机理,评价堵塞的形成机制和管理方法,探索促渗关键技术。提出了局部高位入渗方法、垄沟池底方法、间歇回灌方法三种有效的促渗技术,对雨洪资源地下回灌的工程实践具有一定的借鉴意义。     

卵砾石沙波临界水流条件的水槽试验

以往对沙波的研究多针对河流中下游、河口海岸段的细沙(粒径D<1 mm),而长江上游等卵砾石输移河段(D>2 mm)是否会出现沙波以及卵砾石沙波的临界条件,尚需开展进一步研究。通过长江上游九堆子、筲箕背等卵石滩的现场踏勘,观察到明显的天然沙波形态。采用中值粒径D₅₀=1.8 mm和5.3 mm的天然沙和D₅₀=4.8 mm的轻质沙进行水槽试验,成功模拟出砾石沙波。根据恒定均匀流条件下,产生沙波的比降、水位、流量等水流条件及试验沙的粒径、比重,提出卵砾石沙波的临界条件公式。结果表明,卵砾石沙波的临界条件可以用量纲起动功率w_* 、R／D及比降S表达,并据此提出判别系数G_Dcr。当研究河段的卵砾石输移带上的水流条件满足判别系数G_Dcr,则可以判断能够产生沙波现象。     

碰撞作用下单个阶梯-深潭稳定性模型

阶梯-深潭系统是山区河流广泛分布的控制性河床结构,泥沙输移过程中大颗粒碰撞阶梯关键石块,使其发生位移,强烈影响阶梯-深潭的稳定性。以单个阶梯-深潭的关键石块为研究对象,重点考虑碰撞对阶梯-深潭的影响,量化来沙中大颗粒碰撞作用并改进稳定性理论模型,利用新模型分析阶梯-深潭的临界条件和破坏机制。来沙颗粒对关键石块的碰撞作用受自身粒径、运动速度和阶梯下游冲刷程度影响且皆为正相关关系。颗粒撞击减小阶梯失稳临界流量,且参与碰撞的石块粒径越大,减小作用越明显。当η> 0.55时（η=D₁/D,D₁为碰撞石块粒径,D为关键石块粒径）,临界流量下降幅度达到50%以上,表明来沙中卵石漂石对阶梯-深潭稳定性发挥主要影响。山区河流发生低频率洪水或滑坡泥石流,向下游河道输运大粒径石块并与阶梯碰撞,显著增大转动合力矩并降低失稳临界流量,使得单个阶梯-深潭更易达到临界条件发生破坏。     

中中新世以来阿尔金断裂走滑未造成柴达木盆地整体旋转

通过柴达木盆地南八仙剖面磁性地层学研究,建立了部分上油砂山组磁极性序列,认为该剖面时代为7.5~9.0 Ma。从320块样品的古地磁数据分析,揭示了一组高温特征剩磁分量,在95%置信度下通过倒转检验(B级),说明这组高温分量很可能代表岩石形成时的原生剩磁,其特征剩磁方向为:地理坐标下为D_g=358.5°, I_g=40.5°, k=28.5,α₉₅=4.2,层面坐标下为D_s=1.0°, I_s=41.5°, k=34.0,α₉₅=3.8;相应的极位置为λ_p=75.9°N, φ_p=270.5°E, d_p=2.8°, d_m=4.6°。通过与同时代柴达木盆地及邻区的古地磁极对比,说明中中新世以来柴达木地块整体上没有经历明显旋转运动,阿尔金断裂活动致使肃北等毗邻断裂带地区发生了构造旋转。     

微淹没圆形射流空化特性减压试验

空化空蚀和掺气减蚀机理的研究是高速射流研究的重要方面。在微淹没条件下,保证闸室面积与射流出口面积比不变,对设置门槽的有压矩形闸室后接圆管射流的突扩突跌消力池空化特性进行减压试验,其中跌坎高度S（5.5 m和4.0 m）和圆管长度L₂（L₂/d=2、1和0,d为圆管直径）。跌坎高度S从5.5 m降低至4.0 m,门槽及圆管射流出口处消力池边墙发生空化的可能性变化仅10%。圆管长度L₂/d=2和0时门槽发生空化的可能性比L₂/d=1时高出40%~60%;而L₂/d=0时圆管射流出口处边墙的空化可能性比L₂/d=1时可高出260%,L₂继续增加对空化特性的不利影响有限。增加跌坎高度S有利于水流掺气,为达到良好的掺气减蚀效果,不宜过低。因此,跌坎高度S对门槽及圆管射流出口处消力池边墙空化特性影响较小,而圆管长度L₂对其空化特性影响较大。     

沙粒当量粗糙度的分形表达

沙粒当量粗糙度k_s的准确确定是计算沙粒阻力的关键。针对沙粒轮廓剖面具有自相似精细结构的特点,提出采用分形维数对其复杂性及不规则性进行定量描述;通过粘沙平整床面、初始静平整床面和清水冲刷粗化床面的沙粒阻力试验研究k_s的分形表达方法,建立了静平整床面时k_s的分形表达式,并对公式进行了验证、比较和讨论;结果表明,公式引入的中值粒径d₅₀、分形维数D和弗劳德数Fr 3个参数,可定量地综合反映床沙颗粒大小、级配组成、随机排列以及水流条件对k_s的影响。     

含水层人工回灌物理堵塞的实验与数值模拟

以地表水体和雨洪水作为回灌水源,人工补给地下含水层过程中会发生含水层堵塞问题(特别是物理堵塞),将严重影响人工回灌的效果.采用模拟实验系统研究了悬浮固体颗粒对含水介质堵塞的机理,并用数学模型预测了含水介质物理堵塞的发生和发展过程.研究表明,含水介质的渗透性在回灌初期不断下降,随着回灌时间的延长逐渐趋于稳定;另外,悬浮物堵塞会导致介质的非均质性,渗透距离越小的砂层,堵塞越严重.建议将回灌液悬浮物浓度控制在25mg/L之内,在雨季悬浮物浓度较高时要进行周期性反冲洗,其频率为1次/d.     

人工回灌物理堵塞特征试验及渗滤经验公式推导

人工回灌是提高水资源利用水平的重要工程措施,然而回灌过程中的堵塞问题会影响入渗效率和入渗工程的使用寿命。为了深入研究堵塞的机理,以控制堵塞问题,通过砂柱试验模拟了地下水人工回灌物理堵塞过程,通过测定含水率的变化分析了由堵塞引起的砂柱饱和-非饱和状态的转化。试验中出流速率经过了迅速增大到一峰值后快速减小,然后又缓慢变小的过程,即：仅经过72 h的回灌,砂柱的出流速率减小为2.18 m/d;72 h后砂样出流速率的减小明显放缓;192 h时,砂样出流速率为0.81 m/d,约为出流速率最大值的1/10。试验结果表明：回灌水悬浮物颗粒进入砂样空隙中引起渗透性减弱,和逐渐沉积在砂柱顶部形成的淤泥层是造成堵塞的直接原因,而淤泥层的形成是造成渗滤速率迅速下降的关键因素;淤泥层的弱透水性使砂样由上至下含水率发生了变化,导致了砂样导水率和水力梯度都降低,促使回灌渗滤速率迅速减小;回灌时间越长,淤泥层厚度越大,出流速率越小。由10组对比试验的结果,综合考虑引起雨洪渗滤系统堵塞的各种因素,建立了无砾石滤料雨洪水回灌过程计算渗滤速率变化的经验模型,拟合结果决定性系数为0.932。     

地下水人工回灌气相堵塞特征的试验研究

地下水人工回灌可以高效地利用雨季丰沛的水量来缓解地下水过量开采造成的海水入侵、泉水断流等环境水文地质问题,但回灌堵塞一直是制约人工回灌效率的关键问题。针对雨洪水回灌携带的大量气泡问题,设计室内砂柱试验模拟装置,利用曝气水进行人工回灌,定时记录试验过程中测压管读数及出流流量,利用达西定律计算各层渗透系数,研究气相堵塞的发展过程和规律。结果表明:回灌过程中由于气相堵塞导致含水层渗透系数随时间呈指数衰减,气相堵塞主要发生在介质浅表层（0~30 cm）,且随时间有向下发展的趋势,堵塞速率随深度的增加逐渐减小,在回灌过程中适时停灌进行排气有利于减小气相堵塞对回灌效率的影响。     

Clogging mechanisms and preventive measures in artificial recharge systems

Groundwater which occurs in fractured rock or porous aquifers or other geological weak zones such as faults and fractures is usually extracted via boreholes, hand wells or other sources such as springs.Water scarcity has become a severe problem due to many factors, such as an alarming increase in population and per capita water consumption, over exploitation of groundwater resources and abrupt global climatic change along with its related eco-environmental geological problems. In such situation, application of artificial recharge systems(e.g. surface recharge basin and deep injection well systems) can help to effectively manage and augment the unitization of groundwater resources. However, the clogging problem,which may be caused by a complex interdependent mechanisms of physical, chemical and biological has been a challenge for the efficacy and the implementation of recharge facilities. Clogging can reduce the permeability, recharge rate and longevity of recharge facilities and increase the operational and maintenance costs. Major influencing factors associated with the occurrence of clogging include the chemical composition of groundwater(both the recharge water and native groundwater), aquifer medium and microbial diversity, together with other environmental factors such as temperature, pressure, total dissolved solids, total soluble salts, pH, Eh, nutrients, gases, carbonates and others; these factors ultimately increase the piezometric head but reduce the permeability and infiltration rates of porous/seepage media.Pretreatment of recharge water can minimize the potential clogging. In the case of clogged wells,rehabilitation methods need to be deployed. In the meantime, there is an urgent needs to understand the basic causes and developmental processes/mechanisms of clogging in order to mitigate this problem. This paper reviews the major clogging mechanisms and their possible preventive measures and redevelopments in artificial recharge systems.     

Artificial recharge of groundwater: hydrogeology and engineering

Artificial recharge of groundwater is achieved by putting surface water in basins, furrows, ditches, or other facilities where it infiltrates into the soil and moves downward to recharge aquifers. Artificial recharge is increasingly used for short- or long-term underground storage, where it has several advantages over surface storage, and in water reuse. Artificial recharge requires permeable surface soils. Where these are not available, trenches or shafts in the unsaturated zone can be used, or water can be directly injected into aquifers through wells. To design a system for artificial recharge of groundwater, infiltration rates of the soil must be determined and the unsaturated zone between land surface and the aquifer must be checked for adequate permeability and absence of polluted areas. The aquifer should be sufficiently transmissive to avoid excessive buildup of groundwater mounds. Knowledge of these conditions requires field investigations and, if no fatal flaws are detected, test basins to predict system performance. Water-quality issues must be evaluated, especially with respect to formation of clogging layers on basin bottoms or other infiltration surfaces, and to geochemical reactions in the aquifer. Clogging layers are managed by desilting or other pretreatment of the water, and by remedial techniques in the infiltration system, such as drying, scraping, disking, ripping, or other tillage. Recharge wells should be pumped periodically to backwash clogging layers. Electronic supplementary material to this paper can be obtained by using the Springer LINK server located at http://dx.doi.org/10.1007/s10040-001-0182-4. Electronic Publication     

Column test-based features analysis of clogging in artificial recharge of groundwater in Beijing

With the completion of South-North Water Transfer Project in China, plenty of high quality water will be transported to Beijing. To restore the groundwater level in Beijing, part of transferred water is planned to be used for artificial recharge. Clogging is an unavoidable challenge in the artificial recharge process. Therefore, a test is designed to analyse clogging duration and scope of influence and to test the reinjection properties of different recharge media. The test employs the self-designed sand column system with variable spacing and section monitoring, composed of four parts: Sand column, water-supply system, pressure-test system and flow-test system, to simulate the clogging of artificial recharge of sand and gravel pits. The hydraulic conductivity levels of all sand column sections are obtained to analyse the clogging of the injection of different concentrations in media of different particle sizes. In this experiment, two kinds of media are used–round gravel from sand and gravel pit in Xihuang village and the sand from sand and gravel pit by the Yongding River. The concentrations of recharge fluid are respectively 0.5 g/L and 1 g/L. The results show that clogging usually lasts for 20 hrs., and the hydraulic conductivity drops to the original 10%. Clogging usually occurs at 0–12 cm section of the sand column. The scope of influence is 0–60 cm. In column 3 and 4, whose average particle sizes are larger, section 20–50 cm also suffers from clogging, apart from section 0–12 cm. The effective recharge times are respectively 33 hrs. in column 1, 14 hrs. in column 2, 12 hrs. in column 3 and 12 hrs. in column 4. The larger the average particle size is, the quicker the clogging occurs. In media of larger particles, the change in suspension concentration does not have significant influence on the development of clogging. In conclusion, it is suggested that during artificial recharge, the conditions of reinjection medium should be fully considered and effective method of recharge be employed in order to improve effective recharge time.     

干湿交替条件下包气带土柱中氮素迁移转化规律实验

干湿交替的回灌方法常被用于解决地面回灌补给地下水的堵塞问题。研究干湿交替条件下地面回灌对地下水的影响对于指导再生水回灌地下水具有重要实际意义。通过室内土柱模拟实验,在入渗强度为10.5 mm/h的条件下,日均进水量3 888 mL;用干湿交替的地面回灌模式持续运行136 d,累计灌入氨氮含量为5 mg/L的模拟再生水23 894 L,研究包气带土柱对氨氮的去除效果及氮素在包气带中的迁移转化规律。研究表明,充分利用包气带的好氧、兼氧和厌氧环境,生物脱氮是地下水回灌过程中脱氮的主要途径。包气带对氨氮的去除机理主要为土壤对氨氮的吸附作用和微生物的降解作用。回灌过程中累积在土颗粒表面的氨氮在干期发生硝化作用,干湿交替会加强氮素在包气带的迁移转化,导致干期后的回灌初期大量硝态氮迁移到饱和带地下水中。     

黑河流域中游盆地地表水与地下水转化机制研究

地表水与地下水相互转化是中国西北干旱内流盆地水循环的显著特征,转化机制研究是盆地水循环规律认知和水资源可持续管理的重要基础。以我国西北干旱内流河黑河流域中游的张掖盆地和盐池盆地为研究区,建立了黑河主干河道时变水平衡模型和地表水地下水耦合数值模型,研究了长周期水文变化和人类活动双重影响下地表水与地下水转化机制,得到如下认识:（1）补给条件由以天然条件下河流渗漏为主的线状补给演变为以河流与引水渠道渗漏的线状补给和灌区田间入渗面状补给,排泄条件由以泉水溢出和天然湿地排泄演变为以泉水溢出与地下水开采为主的排泄。（2）张掖盆地黑河干流河道入渗段和溢出段大致以G312 大桥为界,亦称为地表水与地下水转化的转折点。莺落峡—G312 大桥段为悬河渗漏段,河道入渗补给主要受控于进入河道的实际过水量。其中,莺落峡—草滩庄段河道入渗补给率为28.20 %;草滩庄—G312 大桥段河道入渗补给量与河道过水量的关系可用分段函数表达,河道过水量大于或等于0.37×108 m3/mon时呈幂函数关系,小于则呈线性函数关系。G312 大桥—正义峡段为地下水溢出段,其中G312大桥—平川大桥段地下水溢出量约占全部溢出量的70%,溢出峰值出现在高崖水文站下游约6 km处,其单长溢出量可达0.46 m3/(s·km)。（3）研究区是一个相对完整的河流—含水层系统,近31年来经历了连枯和连丰的水文变化,地下水补给排泄条件及与地表水转化机制均发生了相应的变化。地表水与地下水转化最强烈的地区为张掖盆地中部的黑河—梨园河倾斜平原。1990—2001 年连枯期,灌区引水量总体逐年减少,以河道入渗和渠系渗漏为主的补给量平均以0.06×108 m3/a速率减少,农田灌溉面积增加导致灌溉用水增加,地下水开采量显著增加,地下水水位逐年下降,储存量累计减少5.77×108 m3,地下水溢出量平均减少0.16×108 m3/a;而2002—2020 年连丰期,灌区引水量总体逐年减少,河道入渗量呈增加趋势,地下水总补给量平均增加0.15×108 m3/a,灌溉面积继续扩大,农灌开采量随之增加,以河道入渗量增加为主导,地下水水位持续上升,储存量累计增加5.45×108 m3,地下水溢出量平均增加0.08×108 m3/a。总之,补给和排泄条件变化较大,地下水储存量先减后增,地下水溢出总量变化较为平缓,反映了该区巨厚含水层系统的巨大调蓄功能。（4）位于张掖盆地东部的诸河倾斜平原地下水水位长期处于持续下降状态,这是由于地表水开发过度,补给量锐减。黑河侵蚀堆积平原地下水水位基本稳定。30 多年来盐池盆地倾斜平原地下水水位长期处于持续下降状态,这是由于移民开垦导致地下水过量开采。（5）内流盆地天然悬河入渗段是珍贵的地下水补给通道,无论连枯期还是连丰期,河道实际过水量是河道渗漏补给量的关键,保护上游天然河道和一定的河道实际过水量是内流盆地水资源可持续管理的关键。     

Stormwater harvesting in ephemeral streams: how to bypass clogging and unsaturated layers

To cope with water scarcity in drylands, stormwater is often collected in surface basins and subsequently stored in shallow aquifers via infiltration. These stormwater harvesting systems are often accompanied by high evaporation rates and hygiene problems. This is commonly a consequence of low infiltration rates, which are caused by clogging layers that form on top of the soil profile and the presence of a thick vadose zone. The present study aims to develop a conceptual solution to increase groundwater recharge rates in stormwater harvesting systems. The efficiency of vadose-zone wells and infiltration trenches is tested using analytical equations, numerical models, and sensitivity analyses. Dams built in the channel of ephemeral streams (wadis) are selected as a study case to construct the numerical simulations. The modelling demonstrated that vadose-zone wells and infiltration trenches contribute to effective bypassing of the clogging layer. By implementing these solutions, recharge begins 2250–8100% faster than via infiltration from the bed surface of the wadi reservoir. The sensitivity analysis showed that the recharge rates are especially responsive to well length and trench depth. In terms of recharge quantity, the well had the best performance; it can infiltrate up to 1642% more water than the reservoir, and between 336 and 825% more than the trench. Moreover, the well can yield the highest cumulative recharge per dollar and high recharge rates when there are limitations to the available area. The methods investigated here significantly increased recharge rates, providing practical solutions to enhance aquifer water storage in drylands.