CN106835890A - Concave herbaceous field system and construction method based on sponge city - Google Patents
Concave herbaceous field system and construction method based on sponge city Download PDFInfo
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- 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
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- 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
- E01C11/221—Kerbs or like edging members, e.g. flush kerbs, shoulder retaining means ; Joint members, connecting or load-transfer means specially for kerbs
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- 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
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- E—FIXED CONSTRUCTIONS
- E03—WATER SUPPLY; SEWERAGE
- E03B—INSTALLATIONS OR METHODS FOR OBTAINING, COLLECTING, OR DISTRIBUTING WATER
- E03B3/00—Methods or installations for obtaining or collecting drinking water or tap water
- E03B3/02—Methods or installations for obtaining or collecting drinking water or tap water from rain-water
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- 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
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- E—FIXED CONSTRUCTIONS
- E03—WATER SUPPLY; SEWERAGE
- E03F—SEWERS; CESSPOOLS
- E03F5/00—Sewerage structures
- E03F5/04—Gullies inlets, road sinks, floor drains with or without odour seals or sediment traps
- E03F5/0401—Gullies for use in roads or pavements
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- E—FIXED CONSTRUCTIONS
- E03—WATER SUPPLY; SEWERAGE
- E03F—SEWERS; CESSPOOLS
- E03F5/00—Sewerage structures
- E03F5/04—Gullies inlets, road sinks, floor drains with or without odour seals or sediment traps
- E03F5/046—Gullies inlets, road sinks, floor drains with or without odour seals or sediment traps adapted to be used with kerbs
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- E—FIXED CONSTRUCTIONS
- E03—WATER SUPPLY; SEWERAGE
- E03F—SEWERS; CESSPOOLS
- E03F5/00—Sewerage structures
- E03F5/14—Devices for separating liquid or solid substances from sewage, e.g. sand or sludge traps, rakes or grates
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- 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
- Y02A20/108—Rainwater harvesting
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- 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
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Abstract
本发明公开了一种基于海绵城市的下凹式绿地系统,包括消能层、下凹式绿化带、防渗层、碎石盲沟;消能层包括路侧缘石、卵石消能池、细石混凝土,卵石消能池置于路侧缘石内侧,路侧缘石、卵石消能池置于细石混凝土上;在下凹式绿化带的最低点处设有溢流雨水口;在下凹式绿化带上还设有沉沙井;防渗层包括从上往下依次设置的水泥砂浆、沥青、防渗复合土工膜;碎石盲沟置于防渗层的最低处,在碎石盲沟内设有横向排水管和与软式透水管;在碎石盲沟内从上往下依次填充粗砂垫层、碎石层。本发明还提供一种基于海绵城市的下凹式绿地系统的施工方法。本发明能实现海绵城市的渗、蓄、滞、用、排功能,达到良好的雨水排放、收集利用效果。
The invention discloses a concave green space system based on a sponge city, which includes an energy dissipation layer, a concave green belt, an anti-seepage layer, and a gravel blind ditch; the energy dissipation layer includes roadside curbs, pebble energy dissipation pools, fine Stone concrete and pebble energy dissipation pools are placed inside the roadside curb stones, and roadside curb stones and pebble energy dissipation pools are placed on fine stone concrete; an overflow rainwater outlet is provided at the lowest point of the sunken green belt; There is also a settling well; the anti-seepage layer includes cement mortar, asphalt, and anti-seepage composite geomembrane arranged in sequence from top to bottom; the gravel blind ditch is placed at the lowest point of the anti-seepage layer, and there is a Horizontal drainage pipes and soft permeable pipes; fill the gravel blind ditch with coarse sand cushion and gravel layer from top to bottom. The invention also provides a construction method of the sunken green space system based on the sponge city. The invention can realize the infiltration, storage, stagnation, utilization and drainage functions of the sponge city, and achieve good rainwater discharge, collection and utilization effects.
Description
技术领域technical field
本发明属于市政工程建设技术领域,具体涉及一种基于海绵城市的下凹式绿地系统及施工方法。The invention belongs to the technical field of municipal engineering construction, and in particular relates to a sponge city-based sunken green space system and a construction method.
背景技术Background technique
近年来,一些城市在强降雨天气后,积涝问题突出,严重影响了城市的正常运转,造成了人民生命财产的严重损失。在传统的“以排为主”的雨洪管理理念指导下,城镇将收集到的大多数雨水通过市政雨水管网迅速排入受纳水体,对于雨水几乎不考虑下渗入土壤、资源化利用等途径。城市硬化地面造成雨水径流加剧,随着雨水在地表的冲刷,雨水径流污染问题也被提上研究日程。In recent years, some cities have experienced serious waterlogging problems after heavy rainfall, which has seriously affected the normal operation of the city and caused serious losses of people's lives and property. Under the guidance of the traditional "drainage-based" stormwater management concept, most of the rainwater collected by cities and towns is quickly discharged into the receiving water body through the municipal rainwater pipe network, and the rainwater is hardly considered infiltration into the soil, resource utilization, etc. . The hardening of the ground in the city has intensified the runoff of rainwater. As the rainwater scours the surface, the pollution of rainwater runoff has also been put on the research agenda.
目前,通过设置路基路面排水系统对路面水、地下水通过聚集、阻拦、隔通、疏通等方式排除到路基所覆盖地面的范围以外。现有的路基路面排水系统通常采用横向漫坡法和拦水带。横向漫坡法主要用于汇水容量较小、路面堤高较低、坡度高低不同且路基坡面有较强抗冲刷能力的路面。拦水带一般适用于水流冲刷力较大,能快速排出地表水的场合。目前还有一种排水方式—中央分隔排水。中央分隔排水通常分为两种:其一,当中央分隔带的宽度小于3m时,使用设有铺面的横断面模式对中间分隔带两端采用双向横坡的方式,把道路水从中间流入到道路两端的路面上,使之汇入到统一排水系统中。其二,当中间分隔的宽度大于3m时,设置向内侵水的横向坡度,通过集中地表水汇入到中间凹陷地段后,坡度惯性将其排入横向路基中。上述几种处理方法均以“排”为主,对雨水的收集,净化,回用缺乏考虑。At present, road surface water and groundwater are excluded from the scope of the ground covered by the subgrade by setting up subgrade pavement drainage systems through accumulation, blocking, isolation, and dredging. The existing subgrade pavement drainage system usually adopts the transverse slope method and the water retaining strip. The transverse ramp method is mainly used for pavements with small water catchment capacity, low embankment height, different slopes and strong anti-scouring ability of the subgrade slope. The water blocking belt is generally suitable for occasions where the water flow has a large scouring force and can quickly discharge surface water. At present, there is another drainage method-central partition drainage. Central partition drainage is usually divided into two types: first, when the width of the central partition is less than 3m, use the cross-section mode with pavement to adopt two-way transverse slopes at both ends of the central partition to flow road water from the middle to the The pavement at both ends of the road, so that it merges into the unified drainage system. Second, when the width of the middle partition is greater than 3m, set a lateral slope for water intrusion, and after concentrating the surface water into the middle depression, the slope inertia will drain it into the lateral subgrade. The above-mentioned treatment methods are all based on "drainage", and lack of consideration for the collection, purification and reuse of rainwater.
鉴于目前排水现状及问题,国内外许多城市开始实践新型雨洪管理概念,将雨洪渗蓄技术与城市道路相结合设计,构建以自然积存、自然渗透、自然净化为目标的“海绵城市”。《国务院关于加强城市基础设施建设的意见》(国发[2013]36号)中明确指出,建设下沉式绿地及城市湿地公园,提升城市绿地汇聚雨水、蓄洪排涝、补充地下水、净化生态功能。可见下沉式绿地对提升城市绿地的水文调蓄功能具有重要的意义。In view of the current status and problems of drainage, many cities at home and abroad have begun to practice new stormwater management concepts, combining stormwater infiltration storage technology with urban road design, and building "sponge cities" with the goals of natural accumulation, natural infiltration, and natural purification. The "Opinions of the State Council on Strengthening Urban Infrastructure Construction" (Guofa [2013] No. 36) clearly pointed out that the construction of sunken green spaces and urban wetland parks will enhance the functions of urban green spaces to gather rainwater, flood storage and drainage, replenish groundwater, and purify ecological functions. It can be seen that the sunken green space is of great significance to improve the hydrological regulation and storage function of urban green space.
发明内容Contents of the invention
本发明的目的在于提供一种基于海绵城市的下凹式绿地系统及施工方法,该系统和方法能实现海绵城市的渗、蓄、滞、用、排功能,达到良好的雨水排放、收集利用效果。The purpose of the present invention is to provide a sponge city-based concave green space system and construction method, the system and method can realize the functions of seepage, storage, stagnation, utilization and drainage of the sponge city, and achieve good rainwater discharge, collection and utilization effects .
本发明所采用的技术方案是:The technical scheme adopted in the present invention is:
一种基于海绵城市的下凹式绿地系统,置于机动车道、非机动车道之间,包括消能层、下凹式绿化带、防渗层、碎石盲沟;A sunken green space system based on sponge city, placed between motor vehicle lanes and non-motor vehicle lanes, including energy dissipation layer, sunken green belt, anti-seepage layer, gravel blind ditch;
所述消能层有两个,分别置于机动车道和非机动车道边缘,包括路侧缘石、卵石消能池、细石混凝土,卵石消能池置于路侧缘石内侧,且路侧缘石、卵石消能池置于细石混凝土上;There are two energy-dissipating layers, which are respectively placed on the edge of the motor vehicle lane and the non-motor vehicle lane, including roadside curbs, pebble energy dissipation pools, and fine stone concrete. The pebble energy dissipation pool is placed on the fine stone concrete;
所述下凹式绿化带置于两个消能层之间,在下凹式绿化带的最低点处设有与地下排水系统连接的溢流雨水口;在下凹式绿化带上还设有沉沙井,所述沉沙井靠近机动车道一侧;The sunken green belt is placed between two energy-dissipating layers, and an overflow rainwater outlet connected to the underground drainage system is provided at the lowest point of the sunken green belt; sand sinking wells are also arranged on the sunken green belt , the sand sinking well is close to the side of the motorway;
所述防渗层置于下凹式绿化带下方,呈下凹形,包括从上往下依次设置的水泥砂浆、沥青、防渗复合土工膜;The anti-seepage layer is placed under the concave green belt and is in a concave shape, including cement mortar, asphalt, and anti-seepage composite geomembrane arranged sequentially from top to bottom;
所述碎石盲沟置于防渗层的最低处,所述碎石盲沟内设有横向排水管和与横向排水管连接的软式透水管;在碎石盲沟内从上往下依次填充有粗砂垫层、碎石层。The crushed stone blind ditch is placed at the lowest point of the anti-seepage layer, and the crushed stone blind ditch is provided with a horizontal drain pipe and a soft permeable pipe connected with the horizontal drain pipe; in the crushed stone blind ditch from top to bottom Filled with coarse sand cushion, gravel layer.
在路侧缘石上设有多个进水口,相邻进水口的间距为40m,以方便雨水进入下凹式绿地,也确保路侧缘石强度,提高道路使用寿命。There are multiple water inlets on the roadside curbs, and the distance between adjacent water inlets is 40m to facilitate rainwater entering the concave green space, and also to ensure the strength of the roadside curbs and improve the service life of the road.
下凹式绿化带呈弧形,其最低点比机动车道的路面边缘低0.1-0.3m,以使本系统达到最优的蓄、排功能。The sunken green belt is arc-shaped, and its lowest point is 0.1-0.3m lower than the edge of the road surface of the motorway, so that the system can achieve optimal storage and discharge functions.
所述卵石消能池的宽度为0.2-0.3m,以最小宽度减少雨水对道路冲刷,消减路面径流,消减洪峰流量,缓解道路因暴雨引发的滞洪灾害。The width of the pebble energy dissipation pool is 0.2-0.3m, and the minimum width is used to reduce the erosion of rainwater on the road, reduce road surface runoff, reduce flood peak flow, and alleviate the flood detention disaster caused by heavy rain on the road.
沉沙井顶标高低于机动车道的路面边缘0.1m;溢流雨水口有多个,相邻溢流雨水口的间距为4m,以在最少的投入下实现使多余雨水的良好排出。The elevation of the top of the sand settling well is 0.1m lower than the edge of the road surface of the motorway; there are multiple overflow rainwater outlets, and the distance between adjacent overflow rainwater outlets is 4m, so as to achieve good drainage of excess rainwater with the least input.
本发明还提供上述基于海绵城市的下凹式绿地系统的施工方法,包括如下步骤:The present invention also provides the construction method of the above-mentioned concave green space system based on the sponge city, comprising the following steps:
第一步、完成碎石盲沟的修建The first step is to complete the construction of the gravel blind ditch
碎石盲沟内填充有粗砂和碎石,碎石盲沟内包裹软式透水管和与软式透水管连接的横向排水管;The crushed stone blind ditch is filled with coarse sand and gravel, and the crushed stone blind ditch is wrapped with a soft permeable pipe and a horizontal drainage pipe connected with the soft permeable pipe;
第二步、防渗层的修建The second step, the construction of anti-seepage layer
修建第一层水泥稳定碎石基层后,摊铺防渗复合土工膜,在防渗复合土工膜上涂一层沥青,再覆盖水泥砂浆;After building the first layer of cement-stabilized gravel base, pave the anti-seepage composite geomembrane, coat a layer of asphalt on the anti-seepage composite geomembrane, and then cover it with cement mortar;
第三步、完成消能层的修建The third step is to complete the construction of the energy dissipation layer
完成机动车道和非机动车道的路面摊铺后铺设细石混凝土,在细石混凝土上安设路侧缘石,在路侧缘石的内侧铺设卵石消能池;After paving the motorway and non-motorized lanes, lay fine stone concrete, install curb stones on the fine stone concrete, and lay pebble energy dissipation pools inside the curb stones;
第四步、完成下凹式绿化带的修建The fourth step is to complete the construction of the sunken green belt
下凹式绿化带的最低点比机动车道的路面边缘低,并在最低点设置溢流雨水口;在下凹式绿化带内靠近机动车道一侧设置沉沙井。The lowest point of the sunken green belt is lower than the edge of the road surface of the motorway, and an overflow rainwater outlet is set at the lowest point; sand sinking wells are set on the side of the sunken green belt near the motorway.
本发明响应了“海绵城市”的理念,将城市道路排水系统与下凹式绿地系统结合,对雨水进行“渗”、“蓄”、“排”,是一种生态的雨水渗蓄设施。其主要优点为:一是通过卵石消能池减少雨水对道路冲刷,消减路面径流,消减洪峰流量,缓解道路因暴雨引发的滞洪灾害;二是通过下凹式绿化带(生态雨水过滤)将雨水净化,减轻道路扬尘,减轻路面污染;三是通过下凹式绿化带、碎石盲沟节约绿地灌溉用水,储蓄降水和路面径流,补充土壤水资源和地下水资源,结合绿化带中溢流雨水口、碎石盲沟的排水管道设施(横向排水管、软式透水管),当地面径流较大,绿化带储蓄能力不足时,雨水可以通过高出绿化带高程而低于路面高程的溢流雨水口进入地下排水系统,碎石盲沟的排水管道设施也可以将下凹式绿化带内多余的水排出;实现了雨水“蓄”、“排”功能,也实现了防止内涝、水资源利用、景观美化的多重效益。The invention responds to the concept of "sponge city", combines the urban road drainage system with the concave green space system, and "infiltrates", "stores" and "drains" rainwater, and is an ecological rainwater infiltration and storage facility. Its main advantages are as follows: firstly, the pebble energy dissipation pool can reduce the erosion of rainwater on the road, reduce road surface runoff, reduce flood peak flow, and alleviate the flood detention disaster caused by heavy rain on the road; Purify, reduce road dust, reduce road pollution; the third is to save green irrigation water, save precipitation and road runoff, replenish soil water resources and groundwater resources, and combine overflow rainwater outlets in green belts 1. The drainage pipeline facilities (horizontal drainage pipe, soft permeable pipe) of gravel blind ditch. When the surface runoff is large and the storage capacity of the green belt is insufficient, the rainwater can pass through the overflow rainwater that is higher than the elevation of the green belt and lower than the elevation of the road surface. The drainage pipe facilities of gravel blind ditch can also discharge excess water in the sunken green belt; the function of "storage" and "drainage" of rainwater is realized, and the prevention of waterlogging, utilization of water resources, The multiple benefits of landscaping.
附图说明Description of drawings
下面将结合附图及实施例对本发明作进一步说明,附图中:The present invention will be further described below in conjunction with accompanying drawing and embodiment, in the accompanying drawing:
图1是本发明基于海绵城市的下凹式绿地系统的结构示意图;Fig. 1 is the structural representation of the sunken green space system based on the sponge city of the present invention;
图2是下凹式绿地的俯视结构示意图;Fig. 2 is a top view structure schematic diagram of a concave green space;
其中:1、卵石消能池,2、下凹式绿地,3、溢流雨水口,4、沉沙井,5、横向排水管,6、软式透水管,7、粗砂垫层,8、碎石层,9、防渗层,10、细石混凝土,11、机动车道,12、非机动车道,13、路侧缘石。Among them: 1. Pebble energy dissipation pool, 2. Recessed green space, 3. Overflow rainwater outlet, 4. Sand sinking well, 5. Horizontal drainage pipe, 6, Soft permeable pipe, 7. Coarse sand cushion, 8. Gravel layer, 9. Anti-seepage layer, 10. Fine stone concrete, 11. Motor vehicle lane, 12. Non-motor vehicle lane, 13. Curb stone.
具体实施方式detailed description
为了使本发明的目的、技术方案及优点更加清楚明白,以下结合附图及实施例,对本发明进行进一步详细说明。应当理解,此处所描述的具体实施例仅用以解释本发明,并不用于限定本发明。In order to make the object, technical solution and advantages of the present invention clearer, the present invention will be further described in detail below in conjunction with the accompanying drawings and embodiments. It should be understood that the specific embodiments described here are only used to explain the present invention, not to limit the present invention.
参见图1和图2,一种基于海绵城市的下凹式绿地系统,置于机动车道11、非机动车道12之间,包括消能层、下凹式绿化带2、防渗层9、碎石盲沟。消能层有两个,分别置于机动车道11和非机动车道12边缘,包括路侧缘石13、宽度为0.2-0.3m的卵石消能池1、细石混凝土10;路侧缘石13上设有间距为40m的进水口;卵石消能池1置于路侧缘石13内侧,且路侧缘石13、卵石消能池1置于细石混凝土10上。下凹式绿化带2置于两个消能层之间,呈弧形,其最低点比机动车道11的路面边缘低0.1-0.3m,在较佳实施例中,下凹式绿化带2的最低点比机动车道11的路面边缘低0.2m;在下凹式绿化带2的最低点处设有多个与地下排水系统连接的溢流雨水口3,相邻溢流雨水口3的间距为4m;溢流雨水口3高出下凹式绿化带2的最低点而低于路面(机动车道和非机动车道)高程,以便于雨水的排出;在下凹式绿化带2上,靠近机动车道11一侧还设有沉沙井4,沉沙井4顶标高低于机动车道11边缘0.1m,用于过滤、净化雨水。防渗层9置于下凹式绿化带2下方,呈下凹形,包括从上往下依次设置的水泥砂浆、沥青、防渗复合土工膜,水泥砂浆为2cm厚的M5水泥砂浆。碎石盲沟置于防渗层的最低处,且位于溢流雨水口3的正下方;碎石盲沟内设有横向排水管5和与横向排水管5连接的软式透水管6;在碎石盲沟内从上往下依次填充有5cm厚的粗砂垫层7、30cm厚的碎石层8。Referring to Fig. 1 and Fig. 2, a sunken green space system based on sponge city is placed between motor vehicle lane 11 and non-motor vehicle lane 12, including energy dissipation layer, sunken green belt 2, anti-seepage layer 9, crushed Stone Blind Ditch. There are two energy-dissipating layers, which are respectively placed on the edge of motor vehicle lane 11 and non-motor vehicle lane 12, including curb stone 13, a pebble energy dissipation pool 1 with a width of 0.2-0.3m, and fine stone concrete 10; There are water inlets with a distance of 40m; the pebble energy dissipation pool 1 is placed inside the roadside curb 13, and the roadside curb 13 and the pebble energy dissipation pool 1 are placed on the fine stone concrete 10. The sunken green belt 2 is placed between two energy-dissipating layers and is arc-shaped, and its lowest point is 0.1-0.3m lower than the road surface edge of the motorway 11. In a preferred embodiment, the sunken green belt 2 The lowest point is 0.2m lower than the edge of the road surface of the motorway 11; at the lowest point of the sunken green belt 2, there are multiple overflow stormwater outlets 3 connected to the underground drainage system, and the distance between adjacent overflow rainwater outlets 3 is 4m The overflow rainwater outlet 3 is higher than the lowest point of the sunken green belt 2 and lower than the road surface (motor vehicle lane and non-motor vehicle lane) elevation, so as to discharge rainwater; on the sunken green belt 2, it is close to the motor lane 11- The side is also provided with sinking wells 4, and the elevation of the tops of the sinking wells 4 is 0.1m lower than the edge of the motorway 11 for filtering and purifying rainwater. The anti-seepage layer 9 is placed below the concave green belt 2 and is in a concave shape, including cement mortar, asphalt, and anti-seepage composite geomembrane arranged sequentially from top to bottom, and the cement mortar is M5 cement mortar with a thickness of 2 cm. The gravel blind ditch is placed at the lowest point of the anti-seepage layer and directly below the overflow rainwater outlet 3; Lateral drains 5 and with Horizontal drain pipe 5 connected to Soft permeable pipe 6; the gravel blind ditch is filled with a 5cm-thick coarse sand cushion layer 7 and a 30cm-thick gravel layer 8 sequentially from top to bottom.
上述基于海绵城市的下凹式绿地系统的施工方法,包括如下步骤:The construction method of the above-mentioned concave green space system based on the sponge city includes the following steps:
第一步、完成碎石盲沟的修建The first step is to complete the construction of the gravel blind ditch
碎石盲沟内填充有防渗土工膜满包粗砂(厚5cm)和30cm厚的碎石,碎石盲沟内还包裹有软式透水管,该软式透水管与横向排水管5连接;The gravel blind ditch is filled with anti-seepage geomembrane full of coarse sand (5cm thick) and 30cm thick gravel, and the gravel blind ditch is also wrapped with flexible permeable pipe, the Flexible permeable pipe and Horizontal drainage pipe 5 is connected;
第二步、防渗层的修建The second step, the construction of anti-seepage layer
修建第一层水泥稳定碎石基层后,摊铺防渗复合土工膜,在防渗复合土工膜上涂一层沥青,再覆盖2cmM5水泥砂浆;After building the first layer of cement-stabilized gravel base, spread the anti-seepage composite geomembrane, coat a layer of asphalt on the anti-seepage composite geomembrane, and then cover with 2cmM5 cement mortar;
第三步、完成消能层的修建The third step is to complete the construction of the energy dissipation layer
完成机动车道和非机动车道的路面摊铺后铺设细石混凝土,在细石混凝土上安设路侧缘石,在路侧缘石的内侧铺设卵石消能池,消能池用于减少雨水本身能量,避免雨水流速大对泥土造成强冲刷;After paving the motorway and non-motorized lanes, pave fine stone concrete, install roadside curbstones on the finestone concrete, and lay pebble energy dissipation pools inside the roadside curbstones. The energy dissipation pools are used to reduce the energy of rainwater itself. Avoid the strong erosion of the soil caused by the high flow rate of rainwater;
第四步、完成下凹式绿化带的修建The fourth step is to complete the construction of the sunken green belt
下凹式绿化带的最低点比机动车道的路面边缘低0.1-0.3m,最低点根据需要设置在绿化带中间或其他位置,在最低点设置间距为4m的溢流雨水口,用于收集雨水;在下凹式绿化带内靠近机动车道一侧设置沉沙井,以便于净化雨水。The lowest point of the sunken green belt is 0.1-0.3m lower than the edge of the road surface of the motorway, and the lowest point is set in the middle of the green belt or other positions according to the needs, and the overflow rainwater outlet with a distance of 4m is set at the lowest point to collect rainwater ; Set up sand sinks on the side of the concave green belt near the motorway to purify rainwater.
本发明中,路面和周边雨水排入绿化带、然后通过绿化带过滤和净化,当绿化带储蓄能力不足时,雨水通过溢流雨水口进入地下排水系统,收集的雨水可以用于绿化带养护及路面清理。本发明具有蓄、渗雨水,消减洪峰流量、减轻地表径流、污染等优点。In the present invention, the road surface and surrounding rainwater is discharged into the green belt, and then filtered and purified by the green belt. When the storage capacity of the green belt is insufficient, the rainwater enters the underground drainage system through the overflow rainwater outlet, and the collected rainwater can be used for maintenance of the green belt and maintenance of the green belt. Road clearing. The invention has the advantages of storing and infiltrating rainwater, reducing flood peak flow, reducing surface runoff and pollution, and the like.
下凹式绿地水量平衡分析:Water balance analysis of sunken green space:
下凹式绿地通过渗透、蒸发、蓄积等处理集水区内部分雨水,超出绿地渗蓄能力的雨水就近排入雨水管道,计算时段内存在以下水量平衡关系式:The sunken green space treats part of the rainwater in the catchment area through infiltration, evaporation, storage, etc., and the rainwater that exceeds the green space's infiltration and storage capacity is discharged into the nearby rainwater pipe. The following water balance relationship exists in the calculation period:
P0+U0=D+E+S+U1+Q (1)P 0 +U 0 =D+E+S+U 1 +Q (1)
式中:P0—降雨总量,m3;U0—初始蓄水量,m3;D—径流损失量,m3;E—蒸发量,m3;S—下渗量,m3;U1—结束时绿地蓄水量,m3;Q—溢流外排水量,m3。In the formula: P 0 —total rainfall, m 3 ; U 0 —initial water storage, m 3 ; D—runoff loss, m 3 ; E—evapotranspiration, m 3 ; S—infiltration amount, m 3 ; U 1 —the water storage capacity of the green space at the end, m 3 ; Q—the overflow discharge, m 3 .
下凹式绿雨水渗蓄能力计算:Calculation of concave green rainwater seepage storage capacity:
下凹式绿地雨水渗蓄率是降雨过程中绿地渗透、蓄积雨水的量占进入绿地总雨水径流量的百分比,用N表示。可通过式(2)计算,由于时段内蒸发量E较小,因此计算中未考虑;通过对雨水径流渗蓄率的计算,可以反映下凹式绿地的雨水渗蓄能力;The rainwater infiltration rate of the sunken green space is the percentage of the infiltration and accumulation of rainwater in the green space to the total rainwater runoff entering the green space during the rainfall process, expressed in N. It can be calculated by formula (2), because the evaporation amount E in the time period is small, so it is not considered in the calculation; through the calculation of the rainwater runoff seepage storage rate, it can reflect the rainwater seepage storage capacity of the sunken green space;
式中:Pz—降雨量,mm;F1—绿地服务区域面积(即集水区面积),m2;F2—下凹式绿地面积,m2;Cn—绿地服务区域的径流系数。In the formula: P z —rainfall, mm; F 1 —area of green space service area (i.e. catchment area), m 2 ; F 2 —concave green area, m 2 ; C n —runoff coefficient of green space service area .
下渗量S计算公式:Infiltration amount S calculation formula:
S=60KJF2T (3)S=60KJF 2 T (3)
式中:K—土壤稳定入渗速率,m/s;J—水力坡度,垂直下渗时,J=1;T—渗蓄计算时段,min。In the formula: K—Soil stable infiltration rate, m/s; J—Hydraulic slope, when vertical infiltration, J=1; T—Infiltration storage calculation period, min.
下凹式绿地蓄水量U1计算公式为:The formula for calculating the water storage capacity U 1 of the sunken green space is:
U1=F2Δh (4)U 1 =F 2 Δh (4)
式中△h—下凹深度,即下凹式绿地与溢流口或路面之间的高差,cm。In the formula, △h—the depth of the depression, that is, the height difference between the concave green space and the overflow port or the road surface, cm.
根据当地降雨强度q(t),单位时间内的降雨量Pz可通过对降雨强度求积分获得;武汉地区降雨强度公式:According to the local rainfall intensity q( t ), the rainfall Pz per unit time can be obtained by integrating the rainfall intensity; the formula of rainfall intensity in Wuhan is:
式中:q(t)—设计暴雨强度,mm/min;P—设计暴雨重现期,a;t—降雨历时,min,武汉地区按照60min计算。In the formula: q(t)—design rainstorm intensity, mm/min; P—design rainstorm return period, a; t—rainfall duration, min, calculated as 60 minutes in Wuhan area.
根据公式(2)、(3)、(4),当绿化率达到最大控制容积时,即N=100%时,可以推算出临界值的降雨量公式如(7),绿化带所需的下沉深度如公式(8):According to the formulas (2), (3) and (4), when the greening rate reaches the maximum control volume, that is, when N=100%, the rainfall formula of the critical value can be deduced, such as (7), the required lowering of the green belt The sinking depth is as formula (8):
实例:Example:
为定量描述下凹式绿地对雨水径流的渗蓄效应,以某封闭区域A为例,区域除去绿地以外面积的径流系数Cn为0.9,假定蒸发量E和下凹式绿地的前期蓄水量U0均为零。以该区域实测土壤稳定入渗速率K的最大和最小值,即5×10-5m/s和3×10-7m/s为代表结合武汉市雨水系统专业规划规定,选择一般情况下一年、三年和五年一遇设计暴雨重现期,即1h降雨量分别为35.5mm,49.6mm和56.3mm的情况,根据式(1)~式(6),计算1h内不同绿地面积比f(f=F1/F2)、下凹深度Δh条件下的绿地雨水渗蓄率N,计算结果见表,结果显示,当K=5×10-5m/s时,f=25%,Δh≥0.1m的下凹式绿地,对于一年、三年和五年一遇的设计暴雨重现期,持续1h的降雨可被下凹式绿地渗蓄;对于K=3×10-7m/s的情况,以f=35%Δh=0.3m为例,一年一遇的暴雨可被渗蓄,对于三年和五年一遇的暴雨,N可达94%和81%。In order to quantitatively describe the infiltration and storage effect of the sunken green space on rainwater runoff, taking a certain closed area A as an example, the runoff coefficient C n of the area except the green space is 0.9, assuming that the evaporation amount E and the initial water storage capacity of the sunken green space U 0 are all zero. Taking the maximum and minimum values of the measured soil stable infiltration rate K in this area, that is, 5×10 -5 m/s and 3×10 -7 m/s as representatives, combined with the professional planning regulations of Wuhan's rainwater system, choose a Design return periods of rainstorms once in one year, three years and five years, that is, when the rainfall in 1 hour is 35.5mm, 49.6mm and 56.3mm respectively, according to formula (1) ~ formula (6), calculate the ratio of different green areas within 1 hour f(f=F 1 /F 2 ), the rainwater infiltration rate N of the green space under the conditions of the concave depth Δh, the calculation results are shown in the table, and the results show that when K=5×10 -5 m/s, f=25% , Δh ≥ 0.1m sunken green space, for the one-year, three-year and five-year design rainstorm return period, the rainfall lasting 1 hour can be infiltrated by the sunken green space; for K=3×10 -7 In the case of m/s, taking f=35%Δh=0.3m as an example, the once-a-year torrential rain can be infiltrated. For the three-year and five-year torrential rain, N can reach 94% and 81%.
从计算实例可以看出:It can be seen from the calculation example that:
选择不同设计参数,雨水渗蓄能力也不同。如配合适当的工程措施,可成为城市雨洪管理的重要生态措施。下凹式绿地功能发挥受诸多因素影响,其中下凹式绿地面积比例f、绿地下凹深度△h、绿地土壤稳定入渗速率K和设计暴雨重现期P是影响下凹式绿地对雨水渗蓄效率的重要影响因子。设计选用合适的参数有非常重要的意义。With different design parameters, the rainwater seepage and storage capacity is also different. With appropriate engineering measures, it can become an important ecological measure for urban stormwater management. The function of the sunken green space is affected by many factors, among which the area ratio f of the sunken green space, the depth of the green depression △h, the stable infiltration rate of the green space soil K and the design rainstorm return period P are the factors that affect the rainwater infiltration of the sunken green space. An important factor affecting storage efficiency. It is very important to design and select appropriate parameters.
1、竖向设计1. Vertical design
下沉式道路绿化带竖向设计要考虑地形条件、土壤条件、降雨量和绿化带而积比率以及植物的选择类型等因素,进行合理设计和布局。下沉深度太小,雨水大量外排,不能起到调蓄雨水功能的作用,下沉深度过大,雨水在绿化带中大量渗蓄,一旦超过植被的耐淹时间将会带来灾害。所以,为了定量描述绿化带的竖向设计,以武汉地区为例,在一定的暴雨重现期下,假设N为100%,根据公式(5)和公式(6)可算出不同重现期武汉的降雨量H变化,当T取值为1、3、5、10a时,对应的武汉降雨量H分别为48.47、61.19、67.11、75.13mm,可见随着重现期的增加,降雨量也随之增加,但是增加趋势变缓。The vertical design of the sunken road green belt should consider factors such as terrain conditions, soil conditions, rainfall, green belt plot ratio, and plant selection types, and carry out reasonable design and layout. If the subsidence depth is too small, a large amount of rainwater will be discharged outside, which cannot play the role of regulating and storing rainwater. If the subsidence depth is too large, a large amount of rainwater will infiltrate and accumulate in the green belt. Therefore, in order to quantitatively describe the vertical design of the green belt, taking Wuhan as an example, under a certain rainstorm return period, assuming that N is 100%, according to formula (5) and formula (6), the different return periods of Wuhan can be calculated. When the values of T are 1, 3, 5, and 10a, the corresponding rainfall H in Wuhan is 48.47, 61.19, 67.11, and 75.13mm respectively. It can be seen that with the increase of the return period, the rainfall also increases with increased, but the increasing trend slowed down.
选择3a的重现期,设其土壤稳定入渗系数K为1.5×10-6m/s,路面径流系数为0.9,水利坡度J设为垂直下渗为1,时间t取60min,下沉深度△h取10、15、20、25、30cm,可推算所需的道路绿化率f分别为56.4%、,37.3%、27.9%、22.2%、18.5%。Choose the return period of 3 years, set the soil stable infiltration coefficient K as 1.5×10 -6 m/s, the pavement runoff coefficient as 0.9, the water conservancy slope J as vertical infiltration as 1, the time t as 60min, and the subsidence depth △h takes 10, 15, 20, 25, and 30 cm, and the required road greening rate f can be estimated to be 56.4%, 37.3%, 27.9%, 22.2%, and 18.5%, respectively.
可见,当道路绿化带下沉深度在10~30cm时就能满足雨水渗蓄需求,设计少于20cm的也能吸收一定量的雨水,剩余的雨水可以通过溢流口进入存蓄装置,也可以排入雨水管道。武汉城区的地势较为平坦,道路设计坡度也较小,比较适合设计下沉式道路绿化带,最好将道路设计在较高地势处,有利于雨水流向地势较低的下沉式绿化带和周边绿地。为了减少地表径流,在人行道和非机动车道处采取生态路面处理,而且需要合理设计下沉式绿化带与路面及溢流雨水口的衔接方式。首先,路缘侧石设计高度最好不高于路面,尽量与路面平齐,如需高出路面也要设计缺口以保证雨水流入下沉绿地;其次,在绿化带近路面侧要铺20~30cm宽的卵石,防止绿化带土壤被冲刷,土层层次从下到上采用砾石、沙、土壤、覆盖物进行铺设能更有利于雨水下渗;最后,雨水溢流口的高程应低于路面,可设计在绿化带中间或两侧,而且要做防堵塞处理。It can be seen that when the sinking depth of the road green belt is 10-30cm, it can meet the demand for rainwater infiltration and storage, and the design is less than 20cm can also absorb a certain amount of rainwater, and the remaining rainwater can enter the storage device through the overflow port, or it can Drain into storm sewers. The urban terrain of Wuhan is relatively flat, and the slope of the road design is relatively small. It is more suitable for the design of the sunken road green belt. It is better to design the road at a higher terrain, which is conducive to the flow of rainwater to the lower terrain of the sunken green belt and surrounding areas. green space. In order to reduce surface runoff, ecological pavement treatment is adopted on sidewalks and non-motorized vehicle lanes, and the connection between sunken green belts, road surfaces and overflow stormwater outlets needs to be reasonably designed. First of all, the design height of the curb side stone should not be higher than the road surface, and it should be as flush with the road surface as possible. If it needs to be higher than the road surface, a gap should be designed to ensure that the rainwater flows into the sunken green space; Pebbles with a width of 30cm prevent the soil of the green belt from being scoured. The soil layer is laid from bottom to top with gravel, sand, soil, and mulch, which is more conducive to the infiltration of rainwater; finally, the elevation of the rainwater overflow should be lower than the road surface , can be designed in the middle or both sides of the green belt, and anti-clogging treatment must be done.
2、下凹式绿地面积比f2. Area ratio of concave green space f
下沉式绿化带占全部面积的百分比对雨水的排水率影响特别明显,根据公式(8),设其土壤稳定入渗系数K为1.5×10-6m/s,路面径流系数中为0.9,水利坡度J设为垂直下渗为1,时间t取60min,变量绿化带比率f分别取值10%、20%、30%、40%、50%,得出不同的暴雨重现期下道路绿化带的下沉深度h。The percentage of the sunken green belt in the total area has a particularly obvious impact on the drainage rate of rainwater. According to the formula (8), the stable soil infiltration coefficient K is set to 1.5×10 -6 m/s, and the runoff coefficient of the pavement is 0.9. The water conservancy slope J is set to be 1 for vertical infiltration, the time t is set to be 60 minutes, and the variable green belt ratio f is set to be 10%, 20%, 30%, 40%, and 50%, respectively, to obtain road greening under different rainstorm recurrence periods The sinking depth h of the belt.
随着绿化率的增加,所需要的下沉深度减小,且在前面降幅大于后面,当f达到30%以上时下沉深度减少较少。当道路绿化率低于20%时所需要的下沉深度超过下沉绿化带设计的临界值,可能不利于植物的生长。而最符合武汉道路绿化率标准也能满足下沉式绿化带功能需求的绿化率是30%左右。当f为35%时,满足暴雨重现期1、3、5、10a的下沉深度分别为14.7、18.6、20.4、22.9cm,符合下沉深度规范设计,渗蓄效果明显。而在武汉大部分地区,道路绿化率普遍高于20%,很多地区都达到30%,但是基本属于高程绿地,无法渗蓄路面雨水,设计只需要将现有的绿地改造成下沉式绿化带就能留住大部分道路80%的雨水。With the increase of the greening rate, the required sinking depth decreases, and the decrease in the front is larger than that in the back, and the sinking depth decreases less when f reaches more than 30%. When the road greening rate is lower than 20%, the required sinking depth exceeds the critical value of the sinking green belt design, which may not be conducive to the growth of plants. The greening rate that most meets the road greening rate standard in Wuhan and can also meet the functional requirements of the sunken green belt is about 30%. When f is 35%, the subsidence depths that meet the rainstorm return periods 1, 3, 5, and 10a are 14.7, 18.6, 20.4, and 22.9 cm, respectively, which meet the standard design of subsidence depth, and the infiltration and storage effect is obvious. In most areas of Wuhan, the road greening rate is generally higher than 20%, and in many areas it reaches 30%, but it is basically an elevated green space, which cannot infiltrate rainwater on the road surface. The design only needs to transform the existing green space into a sunken green belt 80% of the rainwater on most roads can be retained.
应当理解的是,对本领域普通技术人员来说,可以根据上述说明加以改进或变换,而所有这些改进和变换都应属于本发明所附权利要求的保护范围。It should be understood that those skilled in the art can make improvements or changes based on the above description, and all these improvements and changes should belong to the protection scope of the appended claims of the present invention.
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| CN107869183A (en) * | 2017-11-30 | 2018-04-03 | 中国电建集团成都勘测设计研究院有限公司 | Concave herbaceous field structure |
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| CN114182600A (en) * | 2021-11-29 | 2022-03-15 | 青海省交通规划设计研究院有限公司 | Quick drainage system in green's road surface |
| CN116949965A (en) * | 2023-07-13 | 2023-10-27 | 同济大学建筑设计研究院(集团)有限公司 | A concave deceleration strip structure for wisdom sponge city |
| CN117230874A (en) * | 2023-10-27 | 2023-12-15 | 中铁十九局集团第六工程有限公司 | A park sponge city seepage and drainage structure and its construction technology |
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