CN111328489A - A system and method for efficient rainwater improvement of coastal sticky and heavy saline soil - Google Patents

A system and method for efficient rainwater improvement of coastal sticky and heavy saline soil Download PDF

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CN111328489A
CN111328489A CN202010060710.9A CN202010060710A CN111328489A CN 111328489 A CN111328489 A CN 111328489A CN 202010060710 A CN202010060710 A CN 202010060710A CN 111328489 A CN111328489 A CN 111328489A
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soil
water
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saline soil
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周国华
陈亮
郭祺忠
练继建
马莎莎
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    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01BSOIL WORKING IN AGRICULTURE OR FORESTRY; PARTS, DETAILS, OR ACCESSORIES OF AGRICULTURAL MACHINES OR IMPLEMENTS, IN GENERAL
    • A01B77/00Machines for lifting and treating soil
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01BSOIL WORKING IN AGRICULTURE OR FORESTRY; PARTS, DETAILS, OR ACCESSORIES OF AGRICULTURAL MACHINES OR IMPLEMENTS, IN GENERAL
    • A01B79/00Methods for working soil
    • A01B79/02Methods for working soil combined with other agricultural processing, e.g. fertilising, planting
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G24/00Growth substrates; Culture media; Apparatus or methods therefor
    • A01G24/40Growth substrates; Culture media; Apparatus or methods therefor characterised by their structure
    • A01G24/44Growth substrates; Culture media; Apparatus or methods therefor characterised by their structure in block, mat or sheet form
    • A01G24/46Growth substrates; Culture media; Apparatus or methods therefor characterised by their structure in block, mat or sheet form multi-layered
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G25/00Watering gardens, fields, sports grounds or the like
    • A01G25/02Watering arrangements located above the soil which make use of perforated pipe-lines or pipe-lines with dispensing fittings, e.g. for drip irrigation
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F3/00Fertilisers from human or animal excrements, e.g. manure
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    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K17/00Soil-conditioning materials or soil-stabilising materials
    • C09K17/40Soil-conditioning materials or soil-stabilising materials containing mixtures of inorganic and organic compounds
    • EFIXED CONSTRUCTIONS
    • E03WATER SUPPLY; SEWERAGE
    • E03FSEWERS; CESSPOOLS
    • E03F1/00Methods, systems, or installations for draining-off sewage or storm water
    • EFIXED CONSTRUCTIONS
    • E03WATER SUPPLY; SEWERAGE
    • E03FSEWERS; CESSPOOLS
    • E03F5/00Sewerage structures
    • E03F5/10Collecting-tanks; Equalising-tanks for regulating the run-off; Laying-up basins
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K2101/00Agricultural use

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  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Soil Sciences (AREA)
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  • Hydrology & Water Resources (AREA)
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  • Inorganic Chemistry (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Materials Engineering (AREA)
  • Cultivation Of Plants (AREA)

Abstract

本发明公开了一种雨水高效改良滨海黏重盐渍土的系统和方法,系统包括土壤本体、蓄水井和智能控制系统;所述土壤本体包括从上到下依次设置的待改良重黏盐碱土、透水膜层、蓄水层、防水层、盐碱土层;所述蓄水井的井底设有取水窝,蓄水井内设有取水管,该取水管进水口设有抽水泵并一直延伸到取水窝内,取水管出口端水平设置在待改良黏重盐碱土表面下方,所述取水管出口端一头设有向上伸出待改良黏重盐碱土的喷灌装置,一头连接弃流装置。本发明系统和方法可将渗透进入蓄水井的水循环淋洗盐渍土,操作简便,自动控制,实现了水资源的循环利用,可高效利用降雨对盐碱土淋洗,实现一个雨季完成盐碱土改良的效果,利用雨期节约工期,节约了淡水资源,改良成本较低。

Figure 202010060710

The invention discloses a system and method for efficiently improving coastal sticky and heavy saline soil by rainwater. The system includes a soil body, a water storage well and an intelligent control system; the soil body includes heavy sticky salts to be improved that are arranged in sequence from top to bottom Alkaline soil, permeable membrane layer, water storage layer, waterproof layer and saline-alkali soil layer; the bottom of the water storage well is provided with a water intake pit, and a water intake pipe is provided in the water storage well, and the water intake of the water intake pipe is provided with a pumping pump and is continuously Extending into the water intake socket, the outlet end of the water intake pipe is horizontally arranged below the surface of the sticky and heavy saline-alkali soil to be improved. The system and method of the invention can circulate the water infiltrated into the water storage well to wash the saline soil, the operation is simple and the automatic control, the recycling of water resources is realized, the rainfall can be efficiently used to wash the saline-alkali soil, and the saline-alkali soil can be washed in one rainy season. The effect of improvement is that the rain period is used to save the construction period, fresh water resources are saved, and the improvement cost is low.

Figure 202010060710

Description

一种雨水高效改良滨海黏重盐渍土的系统和方法A system and method for efficient rainwater improvement of coastal sticky and heavy saline soil

技术领域technical field

本发明属于水资源利用和盐碱地改良工程技术领域,尤其是涉及一种雨水高效改良滨海 黏重盐渍土的系统和方法。The invention belongs to the technical field of water resource utilization and saline-alkali land improvement engineering, and in particular relates to a system and method for efficiently improving coastal sticky and heavy saline soil by rainwater.

背景技术Background technique

我国滨海盐渍土总面积达500×104hm2,随着经济的发展和城市建设对土地资源需求的日 益紧迫,盐碱地的改良利用成为开发后备土地资源的重要方向,利用吹填淤泥围海造陆的吹 填土工程蓬勃发展。至2007年底,全国吹填土面积己达540km2,至2015年中国吹填土面积 已达到1500km2以上,仅天津滨海新区和河北曹妃甸至2020年就计划吹填面积达到600km2, 滨海盐渍土的面积近一步扩大。滨海盐渍土,尤其是黏重盐渍土,含盐量高、土质黏重、渗 透性极低(一般数量级不超过10-7cm/s)、高土壤钠吸附比(水分饱和后土壤颗粒膨胀结构破 坏孔隙关闭,不透水、气盐分难以淋洗。)、养分贫乏、易碱化、地下水矿化度高且埋藏浅等 特点严重影响着城镇绿化和农林业生产,在寸草不生的吹填土上绿化一直是国际公认的“世界 性难题”。The total area of coastal saline soil in China is 500×104hm 2 . With the increasingly urgent demand for land resources in economic development and urban construction, the improvement and utilization of saline-alkali land has become an important direction for the development of reserve land resources. Blowing and filling works are booming. By the end of 2007, the area of reclamation nationwide had reached 540km 2 , and by 2015, the area of reclamation in China had reached more than 1,500km 2 . Only Tianjin Binhai New Area and Caofeidian in Hebei planned to reclaim 600km 2 by 2020. area further expanded. Coastal saline soils, especially heavy-heavy saline soils, are characterized by high salt content, heavy soil texture, extremely low permeability (generally, the order of magnitude does not exceed 10 -7 cm/s), and high soil sodium adsorption ratio (soil particles after water saturation) Expansion structure destroys pores and closes, impermeable, gas and salt are difficult to wash.), nutrient-poor, easy to alkalize, groundwater with high salinity and shallow burial, etc., seriously affect urban greening and agricultural and forestry production. Greening has always been an internationally recognized "worldwide problem".

为了探索不同自然环境、城市形态下的海绵城市建设路径,国家开展了两批共30个海绵 城市试点建设,目前海绵城市建设已经如火如荼的在全国开展,针对各种不同下垫面采用不 同的雨水收集净化和利用的技术和产品层出不穷。雨水是一种非常珍贵的淡水资源,尤其针 对滨海盐碱地,这种严重缺水区域,收集与利用雨水,那更是难能可贵。盐碱地因为土壤中 含盐量超出了植物的承受能力,形成了盐害。盐随水来,盐随水去,所以必须充分收集和高 效利用淡水资源,盐渍土地资源才能做到可持续利用。In order to explore the construction paths of sponge cities under different natural environments and urban forms, the country has carried out two batches of pilot construction of 30 sponge cities. At present, the construction of sponge cities has been carried out in full swing across the country. Different types of rainwater are used for different underlying surfaces. Technologies and products for collection, purification and utilization emerge in an endless stream. Rainwater is a very precious freshwater resource, especially for coastal saline-alkali land, which is severely water-deficient, collecting and utilizing rainwater is even more valuable. In saline-alkali land, salt damage occurs because the salt content in the soil exceeds the capacity of plants. Salt comes and goes with water. Therefore, freshwater resources must be fully collected and efficiently utilized to achieve sustainable utilization of saline land resources.

农田用的灌排洗盐控盐的方法,因改良深度有限,且容易反复,不适宜城市绿化,目前, 我国盐碱地城市绿化普遍采用“工程避盐+客土置换”的工程措施。工程避盐一般是采用物理措 施改善土壤的盐碱状况,即通过改变土壤物理结构达到调控土壤水盐运动、抑制土壤蒸发、 提高入渗淋盐的目的。淋层隔盐与盲管排盐组合的方法是目前较为常用的物理改良措施,淋 层隔盐是通过设置大孔隙的介质,促进土体排盐,切断盐随毛管水上升的途径,从而避免客 土盐渍化的作用。暗管排盐是在淋层下通过设置暗沟,在暗沟中安放塑料波纹暗管,通过暗 管的排水作用,达到将盐分排出的作用。客土置换,是用外购的种植土代替原状盐渍土,从 而保证盐分含量达标,可以直接进行绿化栽植。淋层隔盐、暗管排盐、客土栽植技术一种成 熟的盐碱地治理方法,见效快、效果好、成本适中,在我国滨海地区也有广泛应用。The method of irrigation, drainage, washing and salt control used in farmland is not suitable for urban greening due to the limited improvement depth and easy repetition. At present, the engineering measures of “project salt avoidance + foreign soil replacement” are generally adopted in urban greening of saline-alkali land in my country. Salt avoidance in engineering generally uses physical measures to improve soil salinity, that is, by changing soil physical structure to achieve the purpose of regulating soil water and salt movement, inhibiting soil evaporation, and improving infiltration and leaching of salt. The method of combining the salt barrier with the blind pipe is the most commonly used physical improvement measure at present. The salt barrier by setting the medium with large pores promotes the salt discharge from the soil and cuts off the way for the salt to rise with the capillary water, thereby avoiding the The role of soil salinization. Underdrain salt drainage is to set underdrain under the coating layer, and place plastic corrugated underdrain in the underditch to discharge the salt through the drainage effect of the underdrain. The replacement of foreign soil is to replace the original saline soil with purchased planting soil, so as to ensure that the salt content reaches the standard, and greening can be directly carried out. The technology of drenching the salt layer, draining the salt through the hidden pipe, and planting the foreign soil is a mature saline-alkali land treatment method, which has quick effect, good effect and moderate cost.

虽然“工程避盐+客土置换”的工程措施在一定程度上都能达到排盐降盐的作用,但是这种 技术还有以下几方面的缺点。Although the engineering measures of "project salt avoidance + foreign soil replacement" can achieve the effect of salt discharge and salt reduction to a certain extent, this technology has the following shortcomings.

第一、这个技术虽然采用了物理隔排盐措施,但是其主要依赖客土资源,通过挖除其他 地方的种植土,来满足盐碱地域绿化建设需求,种植土资源是一种珍贵的土壤资源,一旦挖 除对当地的生态环境尤其是土壤环境是一大破坏,这是一种不生态的建设方法。First, although this technology adopts the measures of physical separation and discharge of salt, it mainly relies on foreign soil resources. By excavating planting soil in other places, it can meet the needs of greening construction in saline-alkali areas. Planting soil resources are a kind of precious soil resources. Once excavation is a major damage to the local ecological environment, especially the soil environment, this is an unecological construction method.

第二、该种技术没有降低原状盐渍土的含盐量。放弃了对原状盐渍土的利用,造成大量 盐渍土资源的浪费。Second, this technology did not reduce the salinity of the undisturbed saline soil. The utilization of undisturbed saline soil has been abandoned, resulting in the waste of a large amount of saline soil resources.

第三、目前随着盐碱地域的城市绿化建设,客土资源原来越少,购买运距越来越远,成 本原来越高。Third, with the current urban greening construction in saline-alkali areas, the original less passenger and soil resources, the longer the purchase distance, the higher the cost.

第四、该技术应用范围都是在地下水位之上,如果埋深超过地下水位,就不能抵挡地下 咸水的反渗和侧渗,不能起到排盐降盐的作用。而滨海地区地下水位受到气候、海水等多因 素影响,往往波动很大,越靠近海边变化越大,对土体的影响越大。Fourth, the application range of this technology is above the groundwater level. If the burial depth exceeds the groundwater level, it cannot resist the reverse osmosis and lateral seepage of the underground salt water, and cannot play the role of salt discharge and salt reduction. The groundwater level in coastal areas is affected by climate, seawater and other factors, and often fluctuates greatly.

第五、现用的客土栽植暗管排盐技术,还存在雨水资源利用不充分的问题,降雨后的雨 水渗透入土壤后,经石屑层直接排入了市政排水管网或渗入地下盐渍土层,雨水不能有效的 利用,Fifth, the currently used technology of underground salt drainage for soil planting still has the problem of insufficient utilization of rainwater resources. After the rainwater penetrates into the soil, it is directly discharged into the municipal drainage pipe network through the stone chip layer or seeps into the underground salt. Soil layer, rainwater cannot be used effectively,

第六、施肥过程中,大量的氮磷钾等营养物质也随排盐水排入了市政雨水系统,造成植 物养分不足,长势不佳,还造成下游水体的富营养化。Sixth, during the fertilization process, a large amount of nitrogen, phosphorus, potassium and other nutrients are also discharged into the municipal rainwater system with the brine, resulting in insufficient plant nutrients, poor growth, and eutrophication of downstream water bodies.

此外工程上常在客土栽植暗管排盐技术的基础上结合抬高地形的方法来解决地下水位埋 深过浅、波动大的问题,在地形上起坡将绿地高程抬高,一般在原高程上再抬高1-2m,进一 步远离地下高盐地下水,减少高盐毛细水的影响,从而保证客土不再被盐渍化,可以正常做 绿化。但是该做法存在以下缺点,绿地抬高需要增加土方量,不经济,且绿地抬高后,降雨 时径流雨水,流入周边道路等周边设施,增加道路排水压力和内涝风险,同时绿地泥土随径 流冲刷路面,造成道路雨后留泥等径流污染问题。In addition, in engineering, the method of raising the terrain is often combined with the method of raising the terrain on the basis of the technology of planting the underground pipe to solve the problem of the groundwater level being too shallow and fluctuating. Raise it by 1-2m, further away from underground high-salinity groundwater, and reduce the influence of high-salt capillary water, so as to ensure that the guest soil is no longer salinized and can be greened normally. However, this method has the following disadvantages. The elevation of green space requires an increase in the amount of earthwork, which is uneconomical, and after the elevation of green space, rainwater will flow into surrounding roads and other surrounding facilities during rainfall, increasing road drainage pressure and the risk of waterlogging. road surface, resulting in runoff pollution problems such as mud left on the road after rain.

发明内容SUMMARY OF THE INVENTION

为了解决现有技术中存在的问题,本发明提供一种雨水高效改良滨海黏重盐渍土的系统 和方法,解决滨海黏重盐渍土渗透性差、水资源消耗大、养分缺乏,和现有技术盐渍土客土 资源紧缺、成本高、盐渍土资源浪费、受地下水影响大、雨水资源利用不充分、养分流失以 及径流污染等问题。In order to solve the problems existing in the prior art, the present invention provides a system and method for efficiently improving the coastal sticky and heavy saline soil with rainwater, which solves the problems of poor permeability, large water consumption, and lack of nutrients in the coastal sticky and heavy saline soil. Technical saline soils suffer from shortage of guest soil resources, high cost, waste of saline soil resources, great influence by groundwater, insufficient utilization of rainwater resources, nutrient loss and runoff pollution.

本发明的技术方案为:一种雨水高效改良滨海黏重盐渍土的系统,包括土壤本体、蓄水 井和智能控制系统;所述土壤本体包括从上到下依次设置的待改良黏重盐渍土、透水膜层、 蓄水层、防水层、盐渍土层和通气装置;所述蓄水层下表面设有突入盐渍土层的沟槽,该沟 槽内设有暗管;所述暗管坡向连接相通蓄水井;所述蓄水井间隔设置在土壤本体内,其深度 自上而下延伸至沟槽下方;所述通气装置,包括土壤中设置通气管、井中设置通气孔;在该 系统高程低于周边地面5-20cm或将该系统周边起垄,垄高5-20cm,与周边建筑或构筑物的 交接处采用侧向防水层反包;所述蓄水井的井底设有取水窝,蓄水井内设有取水管,该取水 管进水口设有抽水泵并一直延伸到取水窝内,取水管出口端水平设置在待改良黏重盐渍土表 面上方,所述取水管出口端一头设有向上伸出待改良黏重盐渍土的喷灌装置,另一头设有弃 流装置;所述智能控制系统包含信息采集模块、分析模块、弃流模块和淋洗模块;所述信息 采集模块包含土壤及蓄水的盐度、PH值在线采集器,控制分析模块包括信息处理器和比对处 理器以及控制器,通过对采集的信息进行处理并与设定的阈值进行比对,做出淋洗和弃流的 决策,并将控制信号传递给弃流模块和淋洗模块;淋洗模块用于接收控制分析模块控制淋洗 阀门的开启或关闭信号,来执行给待改良土壤供水淋洗,弃流模块用于接收控制分析模块控 制弃流阀门的开启或关闭信号,来执行对超标水的弃流;智能控制系统悬挂在蓄水井侧壁或 立于蓄水井旁,在线采集器探头分别插入土壤中和取水井底部水中。The technical scheme of the present invention is as follows: a system for efficiently improving coastal sticky and heavy saline soil by rainwater, comprising a soil body, a water storage well and an intelligent control system; the soil body comprises the sticky and heavy salt to be improved sequentially arranged from top to bottom soaking soil, permeable membrane layer, water storage layer, waterproof layer, saline soil layer and ventilation device; the lower surface of the aquifer layer is provided with a groove protruding into the saline soil layer, and a hidden pipe is arranged in the groove; The hidden pipes are connected to the water storage wells in the slope direction; the water storage wells are arranged in the soil body at intervals, and the depth of the water storage wells extends from top to bottom to the bottom of the groove; Air holes; the system elevation is 5-20cm lower than the surrounding ground, or the system is ridged, the ridge height is 5-20cm, and the junction with the surrounding buildings or structures is reverse-wrapped with a lateral waterproof layer; the well of the water storage well There is a water intake hole at the bottom, and a water intake pipe is arranged in the water storage well. The water intake of the water intake pipe is provided with a pump and extends into the water intake pocket. One end of the outlet end of the water intake pipe is provided with a sprinkler irrigation device extending upwards for the sticky and heavy saline soil to be improved, and the other end is provided with a discarding device; the intelligent control system includes an information collection module, an analysis module, a discarding module and a rinsing module The information acquisition module includes an online collector of salinity and PH value of soil and water storage, and the control analysis module includes an information processor, a comparison processor and a controller. Carry out comparison, make decisions on rinsing and discarding, and transmit control signals to the discarding module and the rinsing module; To be improved soil water supply and leaching, the abandoned flow module is used to receive the open or closed signal of the control analysis module to control the abandoned flow valve to perform the abandonment of the excess water; the intelligent control system is suspended on the side wall of the water storage well or stands on the water storage Beside the well, the probe of the online collector is inserted into the soil and the bottom water of the water intake well.

所述待改良黏重盐渍土掺拌渗透性改良剂。所述渗透性改良剂为河沙和有机物,掺拌比 例为:盐渍土:河沙:有机物(0.5-0.85):(0.1-0.3):(0.05-0.3),所述有机物可以为椰糠、 绿化废弃枝干粉碎物、木质碎屑等一种或两种以上组合。The viscous and heavy saline soil to be improved is mixed with a permeability modifier. The permeability modifier is river sand and organic matter, and the mixing ratio is: saline soil: river sand: organic matter (0.5-0.85): (0.1-0.3): (0.05-0.3), and the organic matter can be coconut bran , One or more combinations of greening waste branches and trunks, wood debris, etc.

所述待改良黏重盐渍土厚度为60-140cm。The thickness of the sticky and heavy saline soil to be improved is 60-140 cm.

还设置有通气孔,所述通气孔自土壤本体的待改良黏重盐渍土向下延伸到透水膜层。A ventilation hole is also provided, and the ventilation hole extends downward from the sticky heavy saline soil to be improved in the soil body to the water permeable membrane layer.

一种雨水高效改良滨海黏重盐渍土的方法,包括以下步骤:A method for efficiently improving coastal sticky and heavy saline soil with rainwater, comprising the following steps:

(1)对待改良滨海黏重盐渍土进行渗透性改良;(1) Permeability improvement of the coastal sticky and heavy saline soil to be improved;

(2)降雨时通过蓄水井收集雨水,当蓄水井中的水位达到控制水位上沿,智能控制系统 将淋洗模块开启,进行待改良黏重盐渍土淋洗,雨水再次通过下渗淋洗进入到蓄水层和蓄水井,如此循环往复浇洒淋洗待改良黏重盐渍土;(2) Collect rainwater through the water storage well when it rains. When the water level in the water storage well reaches the upper edge of the control water level, the intelligent control system turns on the rinsing module to perform the leaching of the sticky and heavy saline soil to be improved, and the rainwater passes through the infiltration again. Washed into the aquifer and water storage well, so that the watering and rinsing is repeated in a cycle to improve the sticky and heavy saline soil;

(3)当智能控制系统显示蓄水层的水含盐量超过待改良盐渍土含盐量时,启动弃流装 置,将弃流水排至市政排水系统或周边盐碱湿地湖泊等水系,下次降雨来临后可再次循环淋洗,直至土壤含盐量指标≤3g/kg,完成淋洗,达到脱盐目的;(3) When the intelligent control system shows that the salt content of the water in the aquifer exceeds the salt content of the saline soil to be improved, the abandoned flow device is activated, and the abandoned flow is discharged to the municipal drainage system or the surrounding saline-alkali wetland lakes and other water systems. After the first rainfall, the leaching cycle can be repeated until the soil salinity index is less than or equal to 3g/kg, and the leaching is completed to achieve the purpose of desalination;

(4)最后对脱盐后的土壤添加土壤养分改良剂,达到改良目的,栽植适生植物。(4) Finally, a soil nutrient improver is added to the desalinated soil to achieve the purpose of improvement, and suitable plants are planted.

所述步骤(1)待改良黏重盐渍土渗透性改良包括掺拌渗透性改良剂或深垄。In the step (1), the permeability improvement of the sticky and heavy saline soil to be improved includes mixing a permeability modifier or a deep ridge.

所述渗透性改良剂为河沙和有机物,掺拌比例为:盐渍土:河沙:有机物(0.5-0.85): (0.1-0.3):(0.05-0.3),所述有机物可以为椰糠、绿化废弃枝干粉碎物、木质碎屑等一种或 两种以上组合。The permeability modifier is river sand and organic matter, and the mixing ratio is: saline soil: river sand: organic matter (0.5-0.85): (0.1-0.3): (0.05-0.3), and the organic matter can be coconut bran , One or more combinations of greening waste branches and trunks, wood debris, etc.

所述步骤(4)土壤养分改良剂包括牛粪、醋糟、食用菌菌渣和绿化粉碎废料。养分改良 剂占待改良土壤比例不小于1%,与表层土壤搅拌均匀。The soil nutrient modifier in the step (4) includes cow dung, vinegar lees, edible fungus residue and greening crushed waste. The proportion of nutrient improver in the soil to be improved should not be less than 1%, and it should be mixed with the surface soil evenly.

所述牛粪、醋糟、食用菌菌渣和绿化粉碎废料的体积比为(15-30):(15:45):(30-45): (15:45)。The volume ratio of the cow dung, vinegar lees, edible fungus residue and greening pulverized waste is (15-30):(15:45):(30-45):(15:45).

本发明有益效果:1、快速高效淋洗盐渍土,实现水资源循环利用,最大程度节约水资 源。2、本发明技术操作简单,智能控制,系统构建完成后,自动处理,可实现无人工值守。3、本发明适用含盐量超过3g/kg以上的盐渍土,含盐量越高,效果越显著。4、本发明经济 效益显著,相对于现有技术成本较低。5、工期短,仅需要一个雨季即可完成盐渍土改良,不 耽误工期。6、该系统可以重复使用,不断淋洗不同的盐渍土。7、该系统亦可以直接作为长 期绿化的结构,不会让下层盐渍土及地下水盐分返至系统内,且能很好的实现养分的保持,有利于植物生长。Beneficial effects of the present invention: 1. Rapid and efficient leaching of saline soil, realizing the recycling of water resources and saving water resources to the greatest extent. 2. The technology of the present invention is simple in operation and intelligently controlled. After the system is constructed, it is automatically processed and can be realized without manual duty. 3. The present invention is suitable for saline soil with a salt content of more than 3 g/kg. The higher the salt content, the more significant the effect. 4. The economic benefit of the present invention is remarkable, and the cost is lower compared to the prior art. 5. The construction period is short, and the saline soil improvement can be completed in only one rainy season, without delaying the construction period. 6. The system can be reused to continuously rinse different saline soils. 7. The system can also be directly used as a long-term greening structure, which will not allow the lower saline soil and groundwater salt to return to the system, and can well achieve nutrient retention, which is beneficial to plant growth.

附图说明Description of drawings

图1为本发明的整体结构示意图;Fig. 1 is the overall structure schematic diagram of the present invention;

图2为本发明另一种实施方式带有通气孔的结构示意图;FIG. 2 is a schematic structural diagram of another embodiment of the present invention with ventilation holes;

其中:1-蓄水井;2-智能控制系统;3-待改良黏重盐渍土;4-透水膜层;5-蓄水层;6-防水层; 7-取水窝;8-取水管;9-抽水泵;10-喷灌装置;11-喷灌阀门;12-弃流装置阀门;13-第一盐 度及PH值采集器;14-第二盐度及PH值采集器;15-沟槽;16-暗管;17-水;18-盐渍土层; 19-液位计;20-通气孔。Among them: 1-water storage well; 2-intelligent control system; 3-viscous and heavy saline soil to be improved; 4-permeable membrane layer; 5-water storage layer; 6-waterproof layer; 7-water intake hole; 8-water intake pipe ;9-water pump;10-sprinkler irrigation device;11-sprinkler irrigation valve;12-discharge device valve;13-first salinity and PH value collector; 14-second salinity and PH value collector; 15-ditch tank; 16-dark pipe; 17-water; 18-saline soil layer; 19-liquid level gauge; 20-vent hole.

具体实施方式Detailed ways

为了更清楚地说明本发明,下面结合优选实施例对本发明做进一步的说明。本领域技术 人员应当理解,下面所具体描述的内容是说明性的而非限制性的,不应以此限制本发明的保 护范围。In order to illustrate the present invention more clearly, the present invention will be further described below with reference to the preferred embodiments. Those skilled in the art should understand that the content specifically described below is illustrative rather than restrictive, and should not limit the protection scope of the present invention.

参见图1,本发明一种雨水高效改良滨海黏重盐渍土的系统,包括土壤本体、蓄水井1 和智能控制系统2;所述土壤本体包括从上到下依次设置的待改良黏重盐渍土3、透水膜层4、 蓄水层5、防水层6、盐渍土层18;Referring to FIG. 1 , a system for efficiently improving coastal clay-heavy saline soil by rainwater according to the present invention includes a soil body, a water storage well 1 and an intelligent control system 2; Saline soil 3, permeable membrane layer 4, aquifer layer 5, waterproof layer 6, saline soil layer 18;

所述蓄水层5下表面设有突入盐渍土层18的沟槽15,该沟槽15内设有暗管16;所述暗 管16坡向连接相通蓄水井1;所述蓄水井1间隔设置在土壤本体内,其深度自上而下延伸至 沟槽15下方,且所述蓄水井1与蓄水层5接触部分井壁为透气孔结构;在该系统高程低于周 边地面5-20cm或将该系统周边起垄,垄高5-20cm,与周边建筑或构筑物的交接处采用侧向 防水层反包;所述蓄水井5的井底设有取水窝7,蓄水井5内设有取水管8,该取水管8进水口设有抽水泵9并一直延伸到取水窝7内,取水管8出口端水平设置在待改良黏重盐渍土3表面下方,所述取水管8出口端设三通一头设有向上伸出待改良黏重盐渍土的喷灌装置10,另一头设有弃流装置,所述智能控制系统包含信息采集模块、分析模块、弃流模块和淋洗模块。所述信息采集模块包含土壤及蓄水的盐度、酸碱度在线采集器,控制分析模块包括信息处理器和比对处理器以及控制器,通过对采集的信息进行处理并与设定的阈值进行比对,做 出淋洗和弃流的决策,并将控制信号传递给弃流模块和淋洗模块;淋洗模块为,用于接收控 制分析模块控制淋洗阀门的开启或关闭信号,来执行给待改良土壤供水淋洗,弃流模块用于 接收控制分析模块控制弃流阀门的开启或关闭信号,来执行对超标水的弃流。智能智能控制 系统2悬挂在蓄水井1侧壁或立于蓄水井1旁,在线采集器探头13、14分别插入土壤中和蓄 水井底部水中。The lower surface of the water storage layer 5 is provided with a groove 15 protruding into the saline soil layer 18, and a hidden pipe 16 is arranged in the groove 15; the hidden pipe 16 is connected to the water storage well 1 in the slope direction; The well 1 is arranged in the soil body at intervals, and its depth extends from top to bottom to the bottom of the groove 15, and the wall of the well 1 in contact with the aquifer 5 is a vent structure; in the system elevation is lower than the surrounding 5-20cm on the ground or ridges around the system, the height of the ridge is 5-20cm, and the junction with surrounding buildings or structures adopts a lateral waterproof layer to be reversed; The water well 5 is provided with a water intake pipe 8, and the water intake of the water intake pipe 8 is provided with a pump 9 and extends into the water intake pocket 7, and the outlet end of the water intake pipe 8 is horizontally arranged below the surface of the sticky and heavy saline soil 3 to be improved. The outlet end of the water intake pipe 8 is provided with a tee, and one end is provided with a sprinkler irrigation device 10 extending upward for the sticky and heavy saline soil to be improved, and the other end is provided with a discarding device. The intelligent control system includes an information acquisition module, an analysis module, a discarded flow module and rinse module. The information acquisition module includes an online collector of salinity and pH of soil and water storage, and the control and analysis module includes an information processor, a comparison processor and a controller, by processing the collected information and comparing it with a set threshold. Yes, make decisions on rinsing and discarding, and transmit the control signal to the discarding module and the rinsing module; When the soil to be improved is supplied with water for leaching, the discarding flow module is used to receive the open or close signal of the control analysis module to control the discarding flow valve, so as to carry out the discarding of the excess water. The intelligent intelligent control system 2 is suspended on the side wall of the water storage well 1 or stands beside the water storage well 1, and the online collector probes 13 and 14 are respectively inserted into the soil and the water at the bottom of the water storage well.

根据本发明优选地实施方式,所述透水膜层4为透水无纺布。According to a preferred embodiment of the present invention, the water-permeable membrane layer 4 is a water-permeable nonwoven fabric.

根据本发明优选地实施方式,所述蓄水层5为18-60cm厚的石屑或碎石或pp模块等大孔 隙材料。According to a preferred embodiment of the present invention, the aquifer 5 is a 18-60 cm thick stone chip or crushed stone or pp module and other macroporous materials.

根据本发明优选地实施方式,所述防水层6优选为透气防渗层,包括上防水土工布层、 防水膜层和下防水土工层,在蓄水井1处延伸至井底下方;防水层6的设置不仅能够保证雨 水渗透到蓄水层5后通过暗管16排到蓄水井1内,不至于雨水直接渗透到下方的盐渍土层 18流失;还能保证盐渍土层18的盐水不至反渗到蓄水层5,甚至反渗到待改良盐渍土3,从 而对待改良盐渍土3造成破坏;所述防水层6在蓄水井1处同样隔离了蓄水层5和盐渍土层 18之间的相互渗水问题。另外,上防水土工布层还有助于加强防水层的韧性和强度,防止上 层的碎石等损坏防水膜层;同样,下防水土工层有助于防止下层盐渍土层18对防水膜层的损 坏。According to a preferred embodiment of the present invention, the waterproof layer 6 is preferably a breathable and impermeable layer, including an upper waterproof geotextile layer, a waterproof membrane layer and a lower waterproof geotechnical layer, extending to the bottom of the well at the water storage well 1; the waterproof layer The setting of 6 can not only ensure that the rainwater penetrates into the aquifer 5 and is discharged into the water storage well 1 through the hidden pipe 16, so that the rainwater will not directly penetrate into the saline soil layer 18 below to be lost; Salt water does not reverse seep into the aquifer 5, even reverse osmosis to the saline soil 3 to be improved, thereby causing damage to the saline soil 3 to be improved; the waterproof layer 6 also isolates the aquifer 5 at the water storage well 1 Mutual seepage between the soil layer and the saline soil layer 18. In addition, the upper waterproof geotextile layer also helps to strengthen the toughness and strength of the waterproof layer, preventing the crushed stone on the upper layer from damaging the waterproof membrane layer; similarly, the lower waterproof geotextile layer helps to prevent the lower saline soil layer from 18 pairs of waterproof membrane layers of damage.

根据本发明优选地实施方式,所述暗管16每间隔6-8米设置;所述暗管16为PVC渗管 且2%坡向连通蓄水井1;为防止暗管渗孔堵塞,所述暗管16外包覆透水土工布;本发明暗 管16圆周上可开出多排窄条形渗水孔,可以通过控制开孔率,满足不同环刚度和渗透率要求; 在暗管16外包覆透水土工布,既能起到渗透水作用,又能避免泥沙进入暗管16造成堵塞。According to a preferred embodiment of the present invention, the hidden pipes 16 are arranged at intervals of 6-8 meters; the hidden pipes 16 are PVC seepage pipes and are connected to the water storage well 1 in a 2% slope direction; in order to prevent the seepage holes of the hidden pipes from being blocked, the The hidden pipe 16 is covered with water-permeable geotextile; the circumference of the hidden pipe 16 of the present invention can be opened with multiple rows of narrow strip-shaped water seepage holes, which can meet the requirements of different ring stiffness and permeability by controlling the opening rate; outside the hidden pipe 16 Covering the water-permeable geotextile can not only play the role of water infiltration, but also prevent sediment from entering the hidden pipe 16 and causing blockage.

根据本发明优选地实施方式,在该系统与周边建筑或构筑物等交接处,为防止水流失和 对渗水对其他构筑物等的影响,在该系统边界采用侧向防水层6反包进行保水和防渗。According to a preferred embodiment of the present invention, at the junction of the system and surrounding buildings or structures, in order to prevent water loss and the impact of water seepage on other structures, etc., a lateral waterproof layer 6 is used at the boundary of the system to protect water and prevent water. seep.

根据本发明优选地实施方式,对于绿地面积非常大时,为便于管理和控制,所述系统可 以划分为多个汇水区,不同汇水区间可用防水土工布反包进行分隔;反包高度一般超过蓄水 层5上方50cm。According to a preferred embodiment of the present invention, when the green space is very large, in order to facilitate management and control, the system can be divided into multiple catchment areas, and different catchment areas can be separated by reverse wrapping with waterproof geotextiles; More than 50cm above the aquifer 5.

优选地,所述待改良黏重盐渍土3掺拌渗透性改良剂。Preferably, the viscous and heavy saline soil 3 to be improved is mixed with a permeability modifier.

优选地,所述渗透性改良剂为河沙和有机物(椰糠、木屑、绿化废弃枝干粉碎料等), 掺拌比例为:盐渍土:河沙:有机物(0.5-0.7):(0.2-0.3):(0.1-0.3)。Preferably, the permeability modifier is river sand and organic matter (coconut chaff, sawdust, and crushed green waste branches, etc.), and the mixing ratio is: saline soil: river sand: organic matter (0.5-0.7): (0.2 -0.3): (0.1-0.3).

优选地,所述待改良黏重盐渍土厚度为60-140cm。Preferably, the thickness of the sticky and heavy saline soil to be improved is 60-140 cm.

优选地,如图2所示,本系统还可以设置有通气孔,通气孔自土壤本体的待改良黏重盐 渍土层3向下延伸到透水膜层4;当蓄水井1里储存较多水,不再方便排气,会导致土壤本 体表面的水资源不再往下渗透,需要通气孔进行排气;本发明中的通气孔可以直接在土壤本 体中打孔,或者用带有透气孔的管道插入到土壤本体中实现。Preferably, as shown in FIG. 2, the system can also be provided with ventilation holes, which extend downward from the sticky and heavy saline soil layer 3 of the soil body to be improved to the permeable membrane layer 4; Too much water, it is no longer convenient to exhaust, which will cause the water resources on the surface of the soil body to no longer penetrate downward, and ventilation holes are required for exhausting; the ventilation holes in the present invention can be directly punched in the soil body, or use a ventilation The hole is achieved by inserting the pipe into the soil body.

本发明一种雨水高效改良滨海黏重盐渍土的方法,包括以下步骤:A method for efficiently improving coastal sticky heavy saline soil by rainwater of the present invention comprises the following steps:

(1)对待改良滨海黏重盐渍土进行渗透性改良;包括掺拌渗透性改良剂,渗透性改良剂为 河沙和有机物,有机物包括椰糠、木屑、绿化废弃枝干粉碎料等,掺拌比例为:盐渍土:河沙:有机物(0.5-0.7):(0.2-0.3):(0.1-0.3)。(1) Permeability improvement of coastal sticky and heavy saline soil to be improved; including mixing permeability improver, which is river sand and organic matter, organic matter includes coconut bran, sawdust, green waste branch and trunk crushed material, etc. The mixing ratio is: saline soil: river sand: organic matter (0.5-0.7): (0.2-0.3): (0.1-0.3).

(2)降雨时通过蓄水井收集雨水,当蓄水井1内的水位升高,达到设定水位阈值—蓄水层上 沿,智能控制系统2发出打开淋洗模块指令,抽水泵9阀门打开,同时喷灌阀门11打开,抽 水泵开启,喷灌装置10开始对待改良盐渍土进行喷洒浇水;水位降低至设定水位阈值下线水 底15cm时,智能控制系统2发出淋洗结束指令,水泵阀门关闭,抽水泵9停止运行。当蓄 水井1内的水位再次升高到设定水位阈值—蓄水层上沿,智能控制系统2再次启动淋洗模块, 进行待改良黏重盐渍土淋洗,如此循环往复浇洒淋洗待改良黏重盐渍土;(2) Collect rainwater through the water storage well when it rains. When the water level in the water storage well 1 rises and reaches the set water level threshold—the upper edge of the aquifer, the intelligent control system 2 issues an instruction to open the rinsing module, and the pump 9 valve At the same time, the sprinkler irrigation valve 11 is opened, the water pump is opened, and the sprinkler irrigation device 10 starts to spray and water the saline soil to be improved; when the water level drops to 15 cm below the set water level threshold, the intelligent control system 2 sends out a rinsing end command, and the pump The valve is closed and the suction pump 9 stops running. When the water level in the water storage well 1 rises again to the set water level threshold—the upper edge of the aquifer, the intelligent control system 2 starts the rinsing module again to perform the rinsing of the sticky and heavy saline soil to be improved. Washed to improve sticky heavy saline soil;

(3)当智能控制系统显示蓄水层5的水含盐量超过待改良盐渍土,且水位达到设定弃流阈值 上限时将发出弃流指令,弃流模块启动,送水管路切换弃流装置,将超标雨水排至市政排水 系统或周边盐碱湿地湖泊等水系,下次降雨来临后可再次循环淋洗,直至含盐量达到0.3%, 完成淋洗,达到脱盐目的;(3) When the intelligent control system shows that the salt content of the water in the aquifer 5 exceeds the saline soil to be improved, and the water level reaches the upper limit of the set flow abandonment threshold, the flow abandonment command will be issued, the flow abandonment module will be activated, and the water supply pipeline will be switched to abandon flow. A flow device is used to discharge the excess rainwater to the municipal drainage system or the surrounding saline-alkali wetland lakes and other water systems. After the next rainfall comes, it can be recycled again until the salt content reaches 0.3%, and the leaching is completed to achieve the purpose of desalination;

(4)最后对脱盐后的土壤添加土壤养分改良剂,最后种植植物。养分改良剂占待改良土壤比 例不小于1%,与表层土壤搅拌均匀。土壤养分改良剂包括牛粪、醋糟、食用菌菌渣和绿化粉 碎废料。所述牛粪、醋糟、食用菌菌渣和绿化粉碎废料的体积比为(15-30):(15:45): (30-45):(15:45)。(4) Finally, a soil nutrient improver is added to the desalinated soil, and plants are finally planted. The proportion of nutrient improver in the soil to be improved should not be less than 1%, and it should be mixed with the surface soil evenly. Soil nutrient amendments include cow dung, vinegar residue, edible fungus residue and greening and crushed waste. The volume ratio of the cow dung, vinegar waste, edible fungus residue and greening pulverized waste is (15-30):(15:45):(30-45):(15:45).

本发明所用的雨水淋洗也可用自来水、湖泊、河水等其他淡水代替,同样能够实现盐渍土改 良的效果。The rainwater leaching used in the present invention can also be replaced by other fresh water such as tap water, lake water, river water, etc., and the effect of improving saline soil can also be realized.

显然,本发明的上述实施例仅仅是为清楚地说明本发明所作的举例,而并非是对本发明 的实施方式的限定。对于所属领域的普通技术人员来说,在上述说明的基础上还可以做出其 它不同形式的变化或变动。这里无法对所有的实施方式予以穷举。凡是属于本发明的技术方 案所引伸出的显而易见的变化或变动仍处于本发明的保护范围之列。Obviously, the above-mentioned embodiments of the present invention are only examples for clearly illustrating the present invention, and are not intended to limit the embodiments of the present invention. For those of ordinary skill in the art, other changes or modifications in different forms can also be made on the basis of the above description. Not all implementations can be exhaustive here. Any obvious changes or changes derived from the technical solutions of the present invention are still within the protection scope of the present invention.

Claims (10)

1.一种雨水高效改良滨海黏重盐渍土的系统,其特征在于,包括土壤本体、蓄水井和智能控制系统;所述土壤本体包括从上到下依次设置的待改良黏重盐渍土、透水膜层、蓄水层、防水层、盐渍土层和透气装置;所述蓄水层下表面设有突入盐渍土层的沟槽,该沟槽内设有暗管;所述暗管坡向连接相通蓄水井;所述蓄水井间隔设置在土壤本体内,其深度自上而下延伸至沟槽下方;所述通气装置,包括土壤中设置通气管、井中设置通气孔;在该系统高程低于周边地面5-20cm或将该系统周边起垄,垄高5-20cm,与周边建筑或构筑物的交接处采用侧向防水层反包;所述蓄水井的井底设有取水窝,蓄水井内设有取水管,该取水管进水口设有抽水泵并一直延伸到取水窝内,取水管出口端水平设置在待改良黏重盐渍土表面上方,所述取水管出口端一头设有向上伸出待改良黏重盐渍土的喷灌装置,另一头设有弃流装置;所述智能控制系统包含信息采集模块、分析模块、弃流模块和淋洗模块;所述信息采集模块包含土壤及蓄水的盐度、PH值在线采集器,控制分析模块包括信息处理器和比对处理器以及控制器,通过对采集的信息进行处理并与设定的阈值进行比对,做出淋洗和弃流的决策,并将控制信号传递给弃流模块和淋洗模块;淋洗模块用于接收控制分析模块控制淋洗阀门的开启或关闭信号,来执行给待改良土壤供水淋洗,弃流模块用于接收控制分析模块控制弃流阀门的开启或关闭信号,来执行对超标水的弃流;智能控制系统悬挂在蓄水井侧壁或立于蓄水井旁,在线采集器探头分别插入土壤中和取水井底部水中。1. a system for the efficient improvement of coastal sticky and heavy saline soil by rainwater, is characterized in that, comprises soil body, water storage well and intelligent control system; Described soil body comprises the sticky and heavy saline soil to be improved that is set sequentially from top to bottom soil, permeable membrane layer, water storage layer, waterproof layer, saline soil layer and ventilation device; the lower surface of the aquifer layer is provided with a groove protruding into the saline soil layer, and a hidden pipe is arranged in the groove; the The hidden pipes are connected to the water storage wells in the slope direction; the water storage wells are arranged in the soil body at intervals, and the depth of the water storage wells extends from top to bottom to the bottom of the groove; the ventilation device includes a ventilation pipe provided in the soil and a ventilation hole provided in the well ; The system elevation is 5-20cm lower than the surrounding ground or ridges are raised around the system, the ridge height is 5-20cm, and the junction with the surrounding buildings or structures adopts a lateral waterproof layer to reverse the package; the bottom of the water storage well There is a water intake pit, a water intake pipe is arranged in the water storage well, the water intake of the water intake pipe is provided with a pump and extends into the water intake pit, and the outlet end of the water intake pipe is horizontally arranged above the surface of the sticky and heavy saline soil to be improved. One end of the outlet end of the water intake pipe is provided with a sprinkler irrigation device extending upwards for the sticky and heavy saline soil to be improved, and the other end is provided with a discarding device; the intelligent control system includes an information collection module, an analysis module, a discarding module and a rinsing module; The information acquisition module includes an online collector of salinity and PH value of soil and water storage, and the control analysis module includes an information processor, a comparison processor and a controller. Compare, make decisions on rinsing and discarding, and transmit the control signal to the discarding module and the rinsing module; the rinsing module is used to receive the opening or closing signal of the control analysis module to control the rinsing valve to execute the control signal to the rinsing valve. Improve soil water supply and leaching, the abandonment module is used to receive the open or close signal of the control analysis module to control the abandonment valve to perform the abandonment of the excess water; the intelligent control system is suspended on the side wall of the water storage well or stands on the water storage well Next to it, the probes of the online collector are inserted into the soil and the bottom water of the water well. 2.根据权利要求1所述雨水高效改良滨海黏重盐渍土的系统,其特征在于,所述待改良黏重盐渍土掺拌渗透性改良剂。2 . The system for efficiently improving coastal viscous and heavy saline soil according to claim 1 , wherein the to-be-improved viscous and heavy saline soil is mixed with a permeability modifier. 3 . 3.根据权利要求2所述雨水高效改良滨海黏重盐渍土的系统,其特征在于,所述渗透性改良剂为河沙和有机物,掺拌比例为:盐渍土:河沙:有机物(0.5-0.85):(0.1-0.3):(0.05-0.3),所述有机物包括椰糠、绿化废弃枝干粉碎物、木质碎屑等一种或两种以上组合。3. the system that rainwater efficiently improves coastal sticky heavy saline soil according to claim 2, is characterized in that, described permeability modifier is river sand and organic matter, and the mixing ratio is: saline soil: river sand: organic matter ( 0.5-0.85): (0.1-0.3): (0.05-0.3), and the organic matter includes one or more combinations of coconut bran, green waste branch and trunk pulverized material, and wood debris. 4.根据权利要求1所述雨水高效改良滨海黏重盐渍土的系统,其特征在于,所述待改良黏重盐渍土厚度为60-140cm。4 . The system for efficiently improving coastal sticky and heavy saline soil according to claim 1 , wherein the thickness of the sticky and heavy saline soil to be improved is 60-140 cm. 5 . 5.根据权利要求1所述雨水高效改良滨海黏重盐渍土的系统,其特征在于,还设置有通气孔,所述通气孔自土壤本体的待改良黏重盐渍土向下延伸到透水膜层。5. The system for efficiently improving coastal viscous and heavy saline soil by rainwater according to claim 1, characterized in that, a vent hole is also provided, and the vent hole extends downward from the sticky and heavy saline soil to be improved in the soil body to the water permeable film layer. 6.一种雨水高效改良滨海黏重盐渍土的方法,其特征在于,包括以下步骤:6. a method of rainwater efficient improvement of coastal sticky heavy saline soil, is characterized in that, comprises the following steps: (1)对待改良滨海黏重盐渍土进行渗透性改良;(1) Permeability improvement of the coastal sticky and heavy saline soil to be improved; (2)降雨时通过蓄水井收集雨水,当蓄水井中的水位达到控制水位上沿,智能控制系统将淋洗模块开启,进行待改良黏重盐渍土淋洗,雨水再次通过下渗淋洗进入到蓄水层和蓄水井,如此循环往复浇洒淋洗待改良黏重盐渍土;(2) Collect rainwater through the water storage well when it rains. When the water level in the water storage well reaches the upper edge of the control water level, the intelligent control system turns on the rinsing module to perform the leaching of the sticky and heavy saline soil to be improved, and the rainwater passes through the infiltration again. Washed into the aquifer and water storage well, so that the watering and rinsing is repeated in a cycle to improve the sticky and heavy saline soil; (3)当智能控制系统显示蓄水层的水含盐量或盐渍土含盐量不在变化时,启动弃流装置,将弃流水排至市政排水系统或周边盐碱湿地湖泊水系,下次降雨来临后可再次循环淋洗,如此循环往复,直至土壤含盐量指标≤3g/kg,完成淋洗,达到脱盐目的;(3) When the intelligent control system shows that the salinity content of the water in the aquifer or the salinity content of the saline soil does not change, start the waste flow device and discharge the waste flow to the municipal drainage system or the surrounding saline-alkali wetland lake water system. After the rainfall comes, the leaching cycle can be repeated again and again, until the soil salinity index is less than or equal to 3g/kg, the leaching is completed, and the purpose of desalination is achieved; (4)最后对脱盐后的土壤添加土壤养分改良剂,达到改良目的,栽植适生植物。(4) Finally, a soil nutrient improver is added to the desalinated soil to achieve the purpose of improvement, and suitable plants are planted. 7.根据权利要求6所述雨水高效改良滨海黏重盐渍土的方法,其特征在于,所述步骤(1)待改良黏重盐渍土渗透性改良包括掺拌渗透性改良剂或深垄。7. The method for efficiently improving coastal sticky and heavy saline soil by rainwater according to claim 6, wherein the step (1) to improve the permeability improvement of the sticky and heavy saline soil comprises mixing a permeability modifier or a deep ridge . 8.根据权利要求7所述雨水高效改良滨海黏重盐渍土的方法,其特征在于,所述渗透性改良剂为河沙和有机物,掺拌比例为:盐渍土:河沙:有机物(0.5-0.85):(0.1-0.3):(0.05-0.3),所述有机物可以为椰糠、绿化废弃枝干粉碎物、木质碎屑等一种或两种以上组合。8. the method for the efficient improvement of coastal viscous saline soil by rainwater according to claim 7, is characterized in that, described permeability modifier is river sand and organic matter, and the mixing ratio is: saline soil: river sand: organic matter ( 0.5-0.85): (0.1-0.3): (0.05-0.3), and the organic matter can be one or more combinations of coconut bran, green waste branch and trunk pulverized material, and wood debris. 9.根据权利要求6所述雨水高效改良滨海黏重盐渍土的方法,其特征在于,所述步骤(4)土壤养分改良剂包括牛粪、醋糟、食用菌菌渣和绿化粉碎废料,施加量不小于待改良土壤体积的1%,与表层土壤搅拌均匀。9. the method for the efficient improvement of coastal sticky saline soil by rainwater according to claim 6, is characterized in that, described step (4) soil nutrient modifier comprises cow dung, vinegar lees, edible fungus residue and greening pulverized waste, The application amount is not less than 1% of the volume of the soil to be improved, and it is evenly mixed with the surface soil. 10.根据权利要求9所述雨水高效改良滨海黏重盐渍土的方法,其特征在于,所述牛粪、醋糟、食用菌菌渣和绿化粉碎废料的体积比为(15-30):(15:45):(30-45):(15:45)。10. according to the described method of claim 9, rainwater efficient improvement coastal sticky heavy saline soil is characterized in that, the volume ratio of described cow dung, vinegar grains, edible fungus residue and greening pulverized waste is (15-30): (15:45):(30-45):(15:45).
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Application publication date: 20200626

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