CN107190613A - Drainage system is oozed after a kind of first water storage in underground slowly - Google Patents
Drainage system is oozed after a kind of first water storage in underground slowly Download PDFInfo
- Publication number
- CN107190613A CN107190613A CN201710538090.3A CN201710538090A CN107190613A CN 107190613 A CN107190613 A CN 107190613A CN 201710538090 A CN201710538090 A CN 201710538090A CN 107190613 A CN107190613 A CN 107190613A
- Authority
- CN
- China
- Prior art keywords
- slow
- seepage
- seepage drainage
- slow seepage
- drainage structure
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 104
- 238000003860 storage Methods 0.000 title claims abstract description 32
- 239000000463 material Substances 0.000 claims abstract description 39
- 238000005192 partition Methods 0.000 claims description 14
- 239000002245 particle Substances 0.000 claims description 10
- 230000035699 permeability Effects 0.000 claims description 9
- 239000004746 geotextile Substances 0.000 claims description 5
- 230000000694 effects Effects 0.000 claims description 4
- 239000004567 concrete Substances 0.000 abstract description 14
- 239000003673 groundwater Substances 0.000 abstract description 12
- 238000001914 filtration Methods 0.000 abstract description 3
- 230000002787 reinforcement Effects 0.000 abstract 2
- 230000002265 prevention Effects 0.000 abstract 1
- 230000000717 retained effect Effects 0.000 abstract 1
- 239000002689 soil Substances 0.000 description 9
- 239000004568 cement Substances 0.000 description 7
- 238000010586 diagram Methods 0.000 description 5
- 238000001764 infiltration Methods 0.000 description 5
- 238000000034 method Methods 0.000 description 4
- 238000011161 development Methods 0.000 description 3
- 230000008595 infiltration Effects 0.000 description 3
- 239000011398 Portland cement Substances 0.000 description 2
- 238000012423 maintenance Methods 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- -1 roofs Substances 0.000 description 2
- 239000004576 sand Substances 0.000 description 2
- 238000007792 addition Methods 0.000 description 1
- 239000010426 asphalt Substances 0.000 description 1
- 230000004888 barrier function Effects 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000011449 brick Substances 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000012217 deletion Methods 0.000 description 1
- 230000037430 deletion Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 238000011065 in-situ storage Methods 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000011380 pervious concrete Substances 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 230000036962 time dependent Effects 0.000 description 1
- 238000012876 topography Methods 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 238000000844 transformation Methods 0.000 description 1
Classifications
-
- E—FIXED CONSTRUCTIONS
- E01—CONSTRUCTION OF ROADS, RAILWAYS, OR BRIDGES
- E01C—CONSTRUCTION OF, OR SURFACES FOR, ROADS, SPORTS GROUNDS, OR THE LIKE; MACHINES OR AUXILIARY TOOLS FOR CONSTRUCTION OR REPAIR
- E01C11/00—Details of pavings
- E01C11/22—Gutters; Kerbs ; Surface drainage of streets, roads or like traffic areas
- E01C11/224—Surface drainage of streets
- E01C11/227—Gutters; Channels ; Roof drainage discharge ducts set in sidewalks
-
- E—FIXED CONSTRUCTIONS
- E03—WATER SUPPLY; SEWERAGE
- E03F—SEWERS; CESSPOOLS
- E03F1/00—Methods, systems, or installations for draining-off sewage or storm water
- E03F1/002—Methods, systems, or installations for draining-off sewage or storm water with disposal into the ground, e.g. via dry wells
-
- E—FIXED CONSTRUCTIONS
- E03—WATER SUPPLY; SEWERAGE
- E03F—SEWERS; CESSPOOLS
- E03F5/00—Sewerage structures
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/40—Protecting water resources
Landscapes
- Engineering & Computer Science (AREA)
- Health & Medical Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Public Health (AREA)
- Water Supply & Treatment (AREA)
- Architecture (AREA)
- Civil Engineering (AREA)
- Structural Engineering (AREA)
- Sewage (AREA)
Abstract
Description
技术领域technical field
本发明涉及海绵城市、城市排水、市政工程领域,特别是一种地下先储水后慢渗排水系统。The invention relates to the fields of sponge city, urban drainage and municipal engineering, in particular to an underground water storage first and then slow seepage drainage system.
背景技术Background technique
在城市内部,大部分的地表土层、草坪被屋顶、沥青、混凝土石板材或水泥砖等硬质材料替代。由于此类硬质材料不透水,雨水不能有效地渗入地下土层,落在硬质不透水铺面的雨水形成地面径流。当地面径流量超过城市下水道系统的排水量时,导致城市内涝;同时,由于地下水位上涨,且高处的地下水向低处快速汇集,使得低处地下水位迅速抬升,雨水无法通过地下排水系统及时有效排除而形成内涝。为解决此问题,有在城市内设置临时储水池或水塘,收集水雨和地面径流,减少城市内涝,但此类临时储水设施占地面积大,加剧城市开发用地问题。Inside cities, most of the surface soil and lawns are replaced by hard materials such as roofs, asphalt, concrete stone slabs or cement bricks. Due to the impermeability of such hard materials, rainwater cannot effectively penetrate into the underground soil layer, and the rainwater falling on the hard impermeable pavement forms ground runoff. When the surface runoff exceeds the drainage capacity of the urban sewer system, urban waterlogging is caused; at the same time, due to the rising groundwater level and the rapid collection of groundwater from high places to low places, the groundwater level at low places rises rapidly, and rainwater cannot pass through the underground drainage system in a timely and effective manner. Excluded to form waterlogging. To solve this problem, temporary water storage pools or ponds are set up in cities to collect rainwater and ground runoff to reduce urban waterlogging. However, such temporary water storage facilities occupy a large area and aggravate the problem of urban development land.
近年来城市设计者使用透水混凝土铺路来缓解城市内涝。透水混凝土渗水速度高达0.01-5厘米/秒,落在其上的雨水以及来自高处的地面径流能快速排入地下土层,从而减少城市内涝。但是透水铺面的排水速率取决于基层以下土壤的排水速率和储水能力,如果透水铺面下层土壤的即时储排水量低于进入透水铺面的径流量和降雨量之和,则在透水铺面表面将形成死水,即出现内涝。如果透水混凝土的排水速率过快,则地下水位迅速上升,潜水面的自由水会向低处流,导致低洼处积水形成内涝。此外,透水铺面容易被砂尘和其它小颗粒阻塞,透水铺面需要定期维护以维持高透水率,其维护成本高,难度大。再次,透水铺面和传统密实铺面相比,其强度和耐久性相对较低,因此透水铺面只能运用于低交通铺面(例如停车场)而不是城市内部的主要街道。In recent years, urban designers have used pervious concrete paving to alleviate urban waterlogging. The water seepage speed of permeable concrete is as high as 0.01-5 cm/s, and the rainwater falling on it and the ground runoff from high places can be quickly discharged into the underground soil layer, thereby reducing urban waterlogging. However, the drainage rate of the permeable pavement depends on the drainage rate and water storage capacity of the soil below the base layer. If the immediate storage and drainage of the soil under the permeable pavement is lower than the sum of runoff and rainfall entering the permeable pavement, stagnant water will form on the surface of the permeable pavement , that is, waterlogging occurs. If the drainage rate of permeable concrete is too fast, the groundwater table will rise rapidly, and the free water on the water surface will flow to the lower place, resulting in waterlogging in the low-lying place. In addition, the permeable pavement is easily blocked by sand and other small particles, and the permeable pavement requires regular maintenance to maintain a high water permeability, which is costly and difficult to maintain. Thirdly, permeable pavement has relatively low strength and durability compared with traditional dense pavement, so permeable pavement can only be applied to low-traffic pavements (such as parking lots) rather than main streets in inner cities.
因此需要提供一个新型储排水系统,使其具有:(1)降雨时能就地临时储存雨水和地面径流,并在雨后逐渐自动排放到地下水,到下一次降雨时该系统内部没有积水以便再次就地临时储存雨水和地面径流,(2)降雨时此系统附近地下水位不显著提升,降低低洼处形成内涝的概率,(3)此系统不占用地面上部空间,既可埋设于人行道、停车场或是其它地面活动场所下部,又可布设于道路两边替代传统道路的排水系统,(4)此系统的储排水功能不需要(或是很少需用)人工定期维护。开发此类系统,实为城市提供新型海绵体,是减少城市内涝值得发展的一大课题。Therefore need to provide a new type storage and drainage system, it has: (1) can store rainwater and surface runoff temporarily on the spot during rainfall, and discharge to groundwater automatically gradually after rain, when next rainfall, there is no accumulated water inside the system so that Temporary storage of rainwater and surface runoff on the spot again, (2) the groundwater level near the system does not increase significantly during rainfall, reducing the probability of waterlogging in low-lying areas, (3) the system does not occupy the upper space of the ground, and can be buried on sidewalks, parking lots, etc. (4) The storage and drainage function of this system does not require (or rarely requires) manual maintenance on a regular basis. The development of such systems can actually provide cities with new types of sponges, which is a worthy development topic for reducing urban waterlogging.
发明内容Contents of the invention
本发明主要解决的技术问题是提供一种地下先储水后慢渗排水系统,能够将雨水和地面径流暂时收集于慢渗排水结构,在雨后若干天内将储存于慢渗排水结构内部的水分逐渐地自动排到地下,不显著提升地下水位,减少城市地下管道排水压力。The technical problem mainly solved by the present invention is to provide an underground water storage first and then slow seepage drainage system, which can temporarily collect rainwater and surface runoff in the slow seepage drainage structure, and release the water stored in the slow seepage drainage structure within a few days after the rain Gradually and automatically drain to the ground without significantly raising the groundwater level, reducing the drainage pressure of urban underground pipes.
为解决上述技术问题,本发明采用的一个技术方案是:一种地下先储水后慢渗排水系统,包括带过滤材料的慢渗排水结构、加筋顶盖、若干个透水进水口和若干个隔板,具体结构为:设有为阻止地面径流所携带的悬浮颗粒进入慢渗材料内部而铺设在慢渗排水结构内的过滤材料;设有可作为人行道、停车场或是其它地面活动场所的慢渗排水结构上部加筋顶盖;设有可阻止地面径流所携带的大颗粒进入慢渗排水结构的透水进水口;设有可就地分隔慢渗排水结构内雨水的隔板,防止雨水未就地慢渗排空而流入低洼处。In order to solve the above technical problems, a technical solution adopted by the present invention is: an underground water storage first and then slow seepage drainage system, including a slow seepage drainage structure with filter materials, a reinforced top cover, several permeable water inlets and several The specific structure of the clapboard is: there is a filter material laid in the slow seepage drainage structure to prevent the suspended particles carried by the ground runoff from entering the slow seepage material; there is a barrier that can be used as a sidewalk, a parking lot or other ground activities. The upper part of the slow seepage drainage structure is reinforced with a top cover; there is a permeable water inlet that can prevent the large particles carried by the ground runoff from entering the slow seepage drainage structure; In-situ slow seepage emptying and flowing into low-lying places.
所述慢渗排水结构的壁面、底面都可同时为慢渗材料,或是其中一面为慢渗材料,即慢渗排水结构可为底渗式、壁渗式、底壁双渗式的任何一种,优选壁渗式。Both the wall surface and the bottom surface of the slow seepage drainage structure can be made of slow seepage material at the same time, or one side thereof can be made of slow seepage material, that is, the slow seepage drainage structure can be any one of bottom seepage type, wall seepage type, and bottom wall double seepage type. Type, preferably wall infiltration.
所述慢渗材料的截面形式依据地形设定,可为梯形、圆形或矩形等。慢渗排水结构可为长条形、圆柱形、方形等几何结构。The cross-sectional form of the slow permeation material is set according to the topography and can be trapezoidal, circular or rectangular. Slow seepage drainage structure can be rectangular, cylindrical, square and other geometric structures.
所述慢渗排水结构壁面和底面铺设有过滤材料,以过滤掉地面径流所携带的小颗粒,防止慢渗材料被堵塞。过滤材料优先选用土工布。Filter materials are laid on the wall and bottom of the slow seepage drainage structure to filter out small particles carried by ground runoff and prevent slow seepage materials from being blocked. The filter material is preferably geotextile.
所述慢渗排水结构边缘安放有若干个进水口,进水口为高透水材料,其透水速率约为0.1-10厘米/秒。优选0.5-2厘米/秒。Several water inlets are arranged on the edge of the slow seepage drainage structure, and the water inlets are made of highly permeable materials with a water permeability rate of about 0.1-10 cm/s. Preferably 0.5-2 cm/sec.
所述加筋顶盖由加筋透水材料构成,能滤掉地面径流所携带的大颗粒,允许雨水和地面径流快速进入慢渗排水结构。The reinforced top cover is made of reinforced permeable material, which can filter out large particles carried by ground runoff, allowing rainwater and ground runoff to quickly enter the slow seepage drainage structure.
所述隔板的高度略低于慢渗排水结构的净高,超过隔板高度的水分可以流向河流或其它截水设施。隔板的纵向距离主要依据当地坡度,降雨量、地面径流量等因素共同决定。The height of the partition is slightly lower than the net height of the slow seepage drainage structure, and the water exceeding the height of the partition can flow to rivers or other water interception facilities. The longitudinal distance of the clapboard is mainly determined by the local slope, rainfall, surface runoff and other factors.
所述慢渗排水结构的渗水速率为5-50厘米/天。The water seepage rate of the slow seepage drainage structure is 5-50 cm/day.
本发明的有益效果是:The beneficial effects of the present invention are:
1、传统水沟将雨水和地面径流直接导入水池或河流,当地面径流量超过排水设施的容许值,导致内涝。而慢渗排水结构可将雨水就地截留,然后以慢渗形式在降雨后逐渐将截留水排入地下,更大限度的调控地面径流。1. Traditional ditches direct rainwater and surface runoff into pools or rivers, where the surface runoff exceeds the allowable value of the drainage facility, resulting in waterlogging. The slow seepage drainage structure can intercept rainwater on the spot, and then gradually discharge the intercepted water into the ground in the form of slow seepage after rainfall, so as to control the surface runoff to a greater extent.
2、慢渗排水结构的排水方式有别于透水铺面,透水铺面将雨水和地面径流快速排入基层,透水混凝土渗透速度高达0.01-5厘米/秒,雨水直接进入下层土壤,提升地下水位,加速高处水流往低处,加速低洼处水位上涨,导致低处形成内涝。密实铺面则直接形成地面径流,而慢渗排水结构首先将雨水和地面径流暂时就地截取,不显著地增大地下水位,阻止高处地面径流流向低处,减少低洼地带内涝;同时慢渗排水结构就地将其所截取雨水和地面径流在一定时间内(优选1-7天)以渗透的形式自动排干,无需人工干预,以备再次暂时地收集降雨期形成的地面径流。因此地下先储水后慢渗排水系统具有海绵的功能,是透水铺面和密实结构所不具有的。2. The drainage method of the slow seepage drainage structure is different from the permeable pavement. The permeable pavement quickly drains rainwater and ground runoff into the base layer. The permeable concrete seepage speed is as high as 0.01-5 cm/s, and the rainwater directly enters the subsoil, raising the groundwater level and accelerating Water from high places flows to low places, accelerating the rise of water levels in low-lying places, leading to waterlogging in low-lying places. The dense pavement directly forms ground runoff, while the slow seepage drainage structure first temporarily intercepts rainwater and ground runoff on the spot, does not significantly increase the groundwater level, prevents high ground runoff from flowing to low places, and reduces waterlogging in low-lying areas; at the same time, slow seepage drainage The structure automatically drains the intercepted rainwater and surface runoff in the form of infiltration within a certain period of time (preferably 1-7 days) without manual intervention, in order to temporarily collect the surface runoff formed during the rainfall period again. Therefore, the underground water storage first and then the slow seepage drainage system has the function of a sponge, which is not available in permeable pavements and dense structures.
3、慢渗排水结构可作为道路排水沟,也可作为安放在停车场、人行道底部的水箱。该慢渗排水结构的进水口可用透水混凝土或者其它相似的透水材料制成,以阻止地面径流所携带的大颗粒进入慢渗排水结构。该慢渗排水结构的顶面可为加筋盖板,可作为人行道、停车位或是其它地面活动所需的场所。在慢渗排水结构内设有若干隔板,依据设置区域的坡度、径流量等因素确定隔板的纵向距离,实现就地截留地面径流,控制流往低处的水量。3. The slow seepage drainage structure can be used as a road drainage ditch, or as a water tank placed at the bottom of the parking lot and sidewalk. The water inlet of the slow-seepage drainage structure can be made of permeable concrete or other similar water-permeable materials to prevent large particles carried by ground runoff from entering the slow-seepage drainage structure. The top surface of the slow seepage drainage structure can be a reinforced cover plate, which can be used as a sidewalk, a parking space or other places required for ground activities. There are several partitions in the slow seepage drainage structure, and the longitudinal distance of the partitions is determined according to the slope and runoff of the setting area, so as to realize the local interception of ground runoff and control the amount of water flowing to low places.
4、提供一种新的城市海绵技术,有助于降低甚至根除城市内涝。4. Provide a new urban sponge technology, which helps to reduce or even eradicate urban waterlogging.
附图说明Description of drawings
图1为本发明所述的地下先储水后慢渗排水系统的立体图。Fig. 1 is a perspective view of the underground water storage first and then slow seepage drainage system according to the present invention.
图2为本发明所述的地下先储水后慢渗排水系统的立体剖面图。Fig. 2 is a three-dimensional sectional view of the underground water storage first and then slow seepage drainage system according to the present invention.
图3为本发明所述的地下先储水后慢渗排水系统的平面剖面图。Fig. 3 is a plane sectional view of the underground water storage first and then slow seepage drainage system according to the present invention.
图4为本发明所述的地下先储水后慢渗排水系统的装配图。Fig. 4 is an assembly diagram of the underground water storage first and then slow seepage drainage system according to the present invention.
图5为地下先储水后慢渗排水系统停车场应用示意图Figure 5 is a schematic diagram of the parking lot application of the underground water storage first and then the slow seepage drainage system
图6为地下先储水后慢渗排水系统人行道应用示意图Figure 6 is a schematic diagram of the sidewalk application of the underground water storage first and then the slow seepage drainage system
图7为底渗式、壁渗式、底壁双渗式排水结构的排水效果。Figure 7 shows the drainage effect of bottom seepage, wall seepage and bottom wall double seepage drainage structures.
具体实施方式detailed description
以下通过附图和实施例对本发明的技术方案作进一步描述。The technical solutions of the present invention will be further described below through the accompanying drawings and embodiments.
实施例1Example 1
如图1至图4所示,本发明所述的地下先储水后慢渗排水系统的一个实例,设于小区、停车场、公园等低负荷场所底部,应用示意图如图5所示,充分利用这些场所的底部空间进行雨水调蓄。其中,盖在慢渗排水结构2上部的加筋顶盖7作为地面结构,并为主要的进水口。在慢渗排水结构2内部布设可滤水的过滤材料3,只允许水通过不让砂土通过。慢渗排水结构2为底渗式、壁渗式、底壁双渗式三种形式中的一种,慢渗结构透水率应为5-50厘米/天,优选5厘米/天。为使慢渗排水结构2内部水能有效地渗入土层,在慢渗排水结构2外部加铺一定厚度的碎石层4。As shown in Figures 1 to 4, an example of the underground water storage first and then slow seepage drainage system according to the present invention is located at the bottom of low-load places such as residential quarters, parking lots, parks, etc., and the application schematic diagram is shown in Figure 5, fully Use the bottom space of these places for rainwater regulation and storage. Among them, the reinforced top cover 7 covering the top of the slow seepage drainage structure 2 is used as the ground structure and is the main water inlet. A water-filtering filter material 3 is arranged inside the slow-seepage drainage structure 2 to allow only water to pass through and sand and soil to pass through. The slow seepage drainage structure 2 is one of three forms: bottom seepage, wall seepage, and bottom wall double seepage. The water permeability of the slow seepage structure should be 5-50 cm/day, preferably 5 cm/day. In order to make the water inside the slow seepage drainage structure 2 effectively infiltrate into the soil layer, a gravel layer 4 of a certain thickness is paved outside the slow seepage drainage structure 2 .
实施例2Example 2
本实施例是在城市道路或其它线性工程侧方,布设地下先储水后慢渗排水系统,代替传统的排水沟,应用示意图如图6所示。慢渗排水结构2的侧面布设若干个透水路缘石6当作进水口,其用透水率为0.1-5厘米/秒的透水材料制成。进水口的开孔距、开孔大小、单边或双边开孔情况可依实际工况而定。地面径流经透水路缘石6进入慢渗排水结构。慢渗排水结构顶部的透水加筋顶盖7作为城市道路两旁人行道使用,允许雨水或是地面径流进入慢渗排水结构2。In this embodiment, on the side of urban roads or other linear projects, an underground water storage and then slow seepage drainage system is arranged to replace the traditional drainage ditches. The application diagram is shown in Figure 6. A number of permeable curbstones 6 are arranged on the side of the slow seepage drainage structure 2 as water inlets, which are made of permeable materials with a water permeability of 0.1-5 cm/s. The opening distance, opening size, single-side or double-side opening of the water inlet can be determined according to the actual working conditions. Ground runoff enters the slow seepage drainage structure through the permeable curbstone 6 . The permeable and reinforced roof 7 on the top of the slow seepage drainage structure is used as sidewalks on both sides of urban roads, allowing rainwater or ground runoff to enter the slow seepage drainage structure 2 .
加筋透水盖7与慢渗排水结构2分离,以备定期更换过滤材料3(优选土工布)或者定期清理残留在慢渗排水结构内的渣土。The reinforced permeable cover 7 is separated from the slow seepage drainage structure 2 for regular replacement of the filter material 3 (preferably geotextile) or regular cleaning of the residue remaining in the slow seepage drainage structure.
实施例3Example 3
如图1所示,本发明所述的地下先储水后慢渗排水系统的另一个应用实例。利用慢渗混凝土制备的慢渗排水结构2,慢渗混凝土的配合比:4-9毫米骨料80-100重量份,2-4毫米骨料46-58重量份,1-2毫米骨料50-63重量份,小于1毫米细粉24-30重量份,水泥胶凝材料40-50重量份,水17-21重量份。优选:4-9毫米骨料90重量份,2-4毫米骨料52重量份,1-2毫米骨料56重量份,小于1毫米细粉27重量份,水泥45重量份,水19重量份。所述水泥为42.5级普通硅酸盐水泥,严格控制混凝土拌合物的坍落度为0厘米,试制成慢渗混凝土。试制30厘米×50厘米×6厘米样品,养护7天后将该样品试制作为一个水箱的底面,将水箱充满水后,观测水箱水位随时间下降的关系,反算样品的渗水率。测试慢渗混凝土的渗水率约为9.12+0.005厘米/天。As shown in Figure 1, another application example of the underground water storage first and then slow seepage drainage system according to the present invention. The slow seepage drainage structure 2 prepared by using slow seepage concrete, the mixing ratio of the slow seepage concrete: 80-100 parts by weight of 4-9 mm aggregate, 46-58 parts by weight of 2-4 mm aggregate, 50 parts by weight of 1-2 mm aggregate -63 parts by weight, 24-30 parts by weight of fine powder less than 1 mm, 40-50 parts by weight of cement gelling material, and 17-21 parts by weight of water. Preferably: 90 parts by weight of aggregates of 4-9 mm, 52 parts by weight of aggregates of 2-4 mm, 56 parts by weight of aggregates of 1-2 mm, 27 parts by weight of fine powder less than 1 mm, 45 parts by weight of cement, and 19 parts by weight of water . The cement is 42.5 grade ordinary Portland cement, the slump of the concrete mixture is strictly controlled to be 0 cm, and the slow permeable concrete is trial-produced. A sample of 30 cm × 50 cm × 6 cm was trial-produced, and after 7 days of curing, the sample was trial-produced as the bottom surface of a water tank. After the water tank was filled with water, the relationship between the water level of the water tank and the time-dependent decline was observed, and the water permeability of the sample was back-calculated. The water permeability of slow permeable concrete is about 9.12+0.005 cm/day.
透水路缘石6和透水加筋顶盖7由透水混凝土构成,其原料制配:5-10毫米骨料50-70重量份,水泥9-15重量份,水3-5重量份。优选的:5-10毫米骨料60重量份,水泥12分,水分4重量份。所述的水泥为42.5级普通硅酸盐水泥,在严格控制混凝土拌合物的坍落度为0厘米。The permeable curb 6 and the permeable reinforced top cover 7 are made of permeable concrete. The raw materials are: 50-70 parts by weight of 5-10 mm aggregate, 9-15 parts by weight of cement, and 3-5 parts by weight of water. Preferably: 60 parts by weight of 5-10 mm aggregate, 12 parts by weight of cement, and 4 parts by weight of water. The cement is 42.5 grade ordinary Portland cement, and the slump of the concrete mixture under strict control is 0 cm.
根据上述制成的慢渗混凝土,用Hydrus 2D软件分别模拟底渗式、壁渗式、底壁双渗式三种慢渗排水结构2的排水速率。模拟的慢渗排水结构2底长为50厘米,高为50厘米的水平长条形结构。假设每一种慢渗排水结构2的内部放置过滤材料3均为土工布,即细颗粒无法进入慢渗材料内部,保证慢渗材料的渗水速率不变。为研究最差基层排水条件下慢渗排水结构2的排水速率,假设慢渗排水箱放置于淤泥地层,淤泥的饱和渗水速率约为6厘米/天,在淤泥层和箱子外边之间填充2-5厘米的碎石,并用土工布将碎石和淤泥隔开。相对于慢渗排水结构2,碎石的排水速率视为无穷大。假设慢渗排水结构2内充50厘米高的雨水,模拟慢渗排水结构2内部水位随时间下降的规律如图7所示。底壁双渗式的慢渗排水结构2渗水速率快,约25个小时可渗完50厘米的水量;底渗式的慢渗排水结构2渗水速率其次,约50多个小时可渗完50厘米的水量;壁渗式的慢渗排水结构2渗水速率刚开始较快,主要因为刚开始水压大且两壁渗出面积较大,后期壁渗式慢渗排水结构2渗水速率极慢,主要因为结构内水位降低之后,侧壁的水压相对较低且渗水面积减小。经过约120个小时(5天),壁渗式结构内剩余水量约1厘米。因此,虽然底渗式、壁渗式、底壁双渗式的慢渗排水结构2排水方式有所不同,但慢渗排水结构2都可在1-7天内基本渗完结构内所有积水。According to the above-mentioned slow-seepage concrete, the drainage rate of the three slow-seepage drainage structures 2 of bottom seepage type, wall seepage type and bottom wall double seepage type were respectively simulated by Hydrus 2D software. The simulated slow seepage drainage structure 2 is a horizontal strip structure with a base length of 50 cm and a height of 50 cm. It is assumed that the filter material 3 placed inside each slow seepage drainage structure 2 is a geotextile, that is, fine particles cannot enter the slow seepage material, so that the water seepage rate of the slow seepage material remains unchanged. In order to study the drainage rate of the slow-seepage drainage structure 2 under the worst base drainage conditions, it is assumed that the slow-seepage drainage box is placed on a silt formation, and the saturated water seepage rate of the silt is about 6 cm/day, and a 2- 5 cm of gravel, and use geotextiles to separate the gravel and silt. Compared with the slow seepage drainage structure 2, the drainage rate of gravel is regarded as infinite. Assuming that the slow seepage drainage structure 2 is filled with rainwater at a height of 50 cm, the law of the simulated slow seepage drainage structure 2 internal water level falling over time is shown in Figure 7. The bottom wall double seepage slow seepage drainage structure 2 has a fast water seepage rate, and can seep 50 cm of water in about 25 hours; the bottom seepage slow seepage drainage structure 2 has the second water seepage rate, and can seep 50 cm in about 50 hours The water infiltration rate of the wall-infiltration drainage structure 2 is relatively fast at the beginning, mainly because the water pressure is high at the beginning and the seepage area of the two walls is large. Because after the water level in the structure is lowered, the water pressure on the side wall is relatively low and the seepage area is reduced. After about 120 hours (5 days), the remaining water in the wall-infiltration structure is about 1 cm. Therefore, although the drainage methods of the slow seepage drainage structure 2 of the bottom seepage type, the wall seepage type, and the bottom wall double seepage type are different, the slow seepage drainage structure 2 can basically infiltrate all the accumulated water in the structure within 1-7 days.
应该注意到,底渗式、壁渗式、底壁双渗式慢渗排水结构2的排水速率与结构的尺寸、慢渗材料的渗水率、慢渗材料的尺寸、结构内积水高度等因素有关。只要设计合适,底渗式、壁渗式、底壁双渗式慢渗排水结构2都可在预定的时间内自动将结构内积水排干,以备再次暂时地储存地面径流和雨水。It should be noted that the drainage rate of the bottom seepage type, wall seepage type, and bottom wall double seepage type slow seepage drainage structure 2 is related to the size of the structure, the water permeability of the slow seepage material, the size of the slow seepage material, and the height of the accumulated water in the structure. related. As long as the design is appropriate, the bottom seepage type, wall seepage type, and bottom wall double seepage slow seepage drainage structure 2 can automatically drain the accumulated water in the structure within a predetermined time, so as to temporarily store surface runoff and rainwater again.
工作原理working principle
降雨时,雨水和地面径流通过透水加筋顶盖7和进水口6或者二者之一进入慢渗排水结构2,由于慢渗排水结构2渗水速率5-50厘米/天,慢渗排水结构2内的水将逐渐地排放到地下土壤,在降雨时和其后在一定时间内都不显著提升慢渗排水结构2附近地下水位。依据慢渗排水结构2所在位置的坡度,在慢渗排水结构2内设置若干个隔板8,由此将慢渗排水结构2分隔为若干个慢渗集水箱。当降水量较小时,慢渗排水结构2内部的水位若没超过隔板的高度,每个慢渗集水箱内部截留的水分将会逐渐地排放到地下土壤,并在预定的时间自动排干。当降雨量较大或是从其它高处径流而来的地表水进入慢渗排水结构2,导致慢渗排水结构2内水位高度超内部隔板8的高度,超过部分可排到河流或其它截水设施,从而降低城市内涝的风险。When it rains, rainwater and ground runoff enter the slow seepage drainage structure 2 through the permeable reinforced roof 7 and the water inlet 6 or either of them. Since the slow seepage drainage structure 2 has a water seepage rate of 5-50 cm/day, the slow seepage drainage structure 2 The water inside will be gradually discharged to the underground soil, and the groundwater level near the slow seepage drainage structure 2 will not be significantly raised during the rainfall and thereafter within a certain period of time. According to the gradient of the location of the slow seepage drainage structure 2, several partitions 8 are arranged in the slow seepage drainage structure 2, thereby dividing the slow seepage drainage structure 2 into several slow seepage water collection tanks. When the precipitation is small, if the water level inside the slow seepage drainage structure 2 does not exceed the height of the dividing plate, the water intercepted in each slow seepage collection tank will be gradually discharged to the underground soil, and will be automatically drained at a predetermined time. When the rainfall is large or surface water runoff from other high places enters the slow-seepage drainage structure 2, the water level in the slow-seepage drainage structure 2 exceeds the height of the internal partition 8, and the excess part can be discharged to rivers or other cut-offs. Water facilities, thereby reducing the risk of urban flooding.
当慢渗排水结构2内有淤积有一定的渣土时,可以打开加筋顶盖7对慢渗排水结构内进行清淤或是更换过滤材料3。When a certain amount of muck is deposited in the slow seepage drainage structure 2 , the reinforced top cover 7 can be opened to desilt or replace the filter material 3 in the slow seepage drainage structure 2 .
具体慢渗排水结构2的高度、宽度、进水口大小和距离、隔板8距离、隔板高度等参数将由当地坡度、地下水位高度、预期地表径流量以及相邻两次降雨的间隔和大小等因素共同决定。The specific parameters such as the height, width, water inlet size and distance of the slow seepage drainage structure 2, the distance of the partition 8, and the height of the partition will be determined by the local slope, the height of the groundwater table, the expected surface runoff, and the interval and size of two adjacent rainfalls. factors are determined together.
以上所述仅为本发明的实施例,并非因此限制本发明的专利范围,凡是利用本发明说明书及附图内容所作的等效结构、等效流程变换、在适当删减或增加,或直接或间接运用在其他相关的技术领域,均同理包括在本发明的保护范围内。The above description is only an embodiment of the present invention, and does not limit the patent scope of the present invention. All equivalent structures, equivalent process transformations, appropriate deletions or additions, or direct or Indirect applications in other related technical fields are equally included in the protection scope of the present invention.
Claims (10)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201710538090.3A CN107190613A (en) | 2017-07-04 | 2017-07-04 | Drainage system is oozed after a kind of first water storage in underground slowly |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201710538090.3A CN107190613A (en) | 2017-07-04 | 2017-07-04 | Drainage system is oozed after a kind of first water storage in underground slowly |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN107190613A true CN107190613A (en) | 2017-09-22 |
Family
ID=59881464
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201710538090.3A Pending CN107190613A (en) | 2017-07-04 | 2017-07-04 | Drainage system is oozed after a kind of first water storage in underground slowly |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN107190613A (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108178441A (en) * | 2018-01-03 | 2018-06-19 | 北京师范大学 | A kind of permeable decontamination material assembly module of sponge urban construction |
| CN109356278A (en) * | 2018-09-28 | 2019-02-19 | 广西城居乐科技有限公司 | A kind of filter device suitable for slow discharge outlet |
| CN109403450A (en) * | 2018-10-12 | 2019-03-01 | 河海大学 | A kind of environment-friendly type underground aqua storage tank for road drainage under Rainfall Condition |
| CN109577569A (en) * | 2018-05-29 | 2019-04-05 | 怀化沃普环保科技有限公司 | Open waterproof system |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN2806567Y (en) * | 2005-03-25 | 2006-08-16 | 张益时 | Water well system for collecting rainwater to the ground |
| KR20120005874U (en) * | 2011-02-11 | 2012-08-21 | 정춘식 | boundary stone |
| CN105648873A (en) * | 2016-03-04 | 2016-06-08 | 广州市合信方园工业设备有限公司 | Cabin storage type border stone |
| CN105794523A (en) * | 2016-04-11 | 2016-07-27 | 重庆大学 | Tree pool device with rainwater infiltration, storage and purification functions |
| CN106400946A (en) * | 2016-11-21 | 2017-02-15 | 衡阳市农业科学研究所 | Water storage structure capable of improving moisture content in underground soil of urban street trees |
-
2017
- 2017-07-04 CN CN201710538090.3A patent/CN107190613A/en active Pending
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN2806567Y (en) * | 2005-03-25 | 2006-08-16 | 张益时 | Water well system for collecting rainwater to the ground |
| KR20120005874U (en) * | 2011-02-11 | 2012-08-21 | 정춘식 | boundary stone |
| CN105648873A (en) * | 2016-03-04 | 2016-06-08 | 广州市合信方园工业设备有限公司 | Cabin storage type border stone |
| CN105794523A (en) * | 2016-04-11 | 2016-07-27 | 重庆大学 | Tree pool device with rainwater infiltration, storage and purification functions |
| CN106400946A (en) * | 2016-11-21 | 2017-02-15 | 衡阳市农业科学研究所 | Water storage structure capable of improving moisture content in underground soil of urban street trees |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108178441A (en) * | 2018-01-03 | 2018-06-19 | 北京师范大学 | A kind of permeable decontamination material assembly module of sponge urban construction |
| CN108178441B (en) * | 2018-01-03 | 2020-06-19 | 北京师范大学 | A permeable and decontamination material assembly module for sponge city construction |
| CN109577569A (en) * | 2018-05-29 | 2019-04-05 | 怀化沃普环保科技有限公司 | Open waterproof system |
| CN109356278A (en) * | 2018-09-28 | 2019-02-19 | 广西城居乐科技有限公司 | A kind of filter device suitable for slow discharge outlet |
| CN109403450A (en) * | 2018-10-12 | 2019-03-01 | 河海大学 | A kind of environment-friendly type underground aqua storage tank for road drainage under Rainfall Condition |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN110453565A (en) | A road rainwater collection system for a sponge city | |
| CN105297872A (en) | LID type city rainwater closed conduit with functions of water permeating, storing, purifying and draining | |
| CN105908588A (en) | Permeable pavement system for weakly-permeable soil regions | |
| CN205171305U (en) | Bituminous paving with drainage structures | |
| CN107190613A (en) | Drainage system is oozed after a kind of first water storage in underground slowly | |
| CN209024909U (en) | A Sponge City Multifunctional Pavement Structure | |
| CN107044081B (en) | Ecological street drainage structure | |
| CN211199978U (en) | A permeable pavement pavement structure | |
| CN113550397A (en) | Road water storage and drainage system and road construction method | |
| CN205224230U (en) | LID type urban rainwater oozes and holds clean drainage closed conduit | |
| CN209099101U (en) | Suitable for permeable pavement in areas with high water table | |
| CN209759936U (en) | Permeable pavement structure based on building rubbish crushed aggregates | |
| CN110700386A (en) | Sponge city construction has rainwater well of supply groundwater function | |
| CN206448131U (en) | Pavement underdrain structure | |
| CN214530022U (en) | Hard pavement surface runoff storage and seepage tree pit and storage and seepage system | |
| CN212388714U (en) | Rainwater infiltration system for sponge city | |
| CN212389098U (en) | Ecological parking lot adopting green cutting technology | |
| CN212895755U (en) | Urban road sidewalk drainage device | |
| CN116025045A (en) | A sinking road green belt regulation and storage system based on sponge city | |
| CN221218372U (en) | Road side zoning drainage structure adopting sinking green land | |
| CN114635487A (en) | Highway evaporation plant with deodorant function | |
| CN219862180U (en) | Grass planting ditch | |
| CN211421356U (en) | A sunken green belt with grit chamber | |
| CN116219823B (en) | Ecological permeable pavement structure and construction method for collapsible loess green land | |
| CN114319556B (en) | Concealed type water purification drainage ditch and construction method thereof |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| WD01 | Invention patent application deemed withdrawn after publication | ||
| WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20170922 |