CN203256709U - Efficient ecological intercepting ditch suitable for dry land farmland - Google Patents
Efficient ecological intercepting ditch suitable for dry land farmland Download PDFInfo
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Abstract
本实用新型涉及面源污染控制工程领域,公开了一种适用于旱地农田的高效生态拦截沟渠,沟渠横断面为梯形,所述沟渠两侧的渠壁表面铺设有带孔洞的水泥板,沟渠的渠底铺设有植草砖,所述植草砖的形状为8字形。水泥板采用钢筋混凝土结构,水泥板表面间隔均布6-9个孔洞,所述孔洞中种植香菇草。本实用新型简单高效、实用经济、易于维护、便于推广,可有效解决旱地农田种植过程N、P等营养元素流失大量大,周边水体富营养化严重的问题。
The utility model relates to the field of non-point source pollution control engineering, and discloses a high-efficiency ecological interception ditch suitable for dry land farmland. The cross section of the ditch is trapezoidal. The bottom of the canal is laid with grass-planting bricks, and the shape of the grass-planting bricks is figure 8. The cement board adopts a reinforced concrete structure, and 6-9 holes are evenly distributed on the surface of the cement board, and mushroom grass is planted in the holes. The utility model is simple, efficient, practical and economical, easy to maintain and easy to popularize, and can effectively solve the problems of large loss of nutrients such as N and P in the planting process of dry land farmland and serious eutrophication of surrounding water bodies.
Description
技术领域 technical field
本实用新型涉及面源污染控制工程领域,尤其涉及了一种适用于旱地农田的高效生态拦截沟渠。 The utility model relates to the field of surface source pollution control engineering, in particular to a high-efficiency ecological interception ditch suitable for dry farmland. the
背景技术 Background technique
农田面源污染是指在农田生产活动中,氮素和磷素等营养物质、农药以及其他有机或无机污染物质,随着降水或灌溉过程,通过农田的地表径流和农田渗漏而形成的环境污染,主要包括化肥污染、农药污染、畜禽粪便污染、农田固体废弃物污染等。随着农田种植过程中肥料用量的不断增加,农田土壤中氮、磷含量及氮、磷流失量不断增加,造成了农田土壤及水体环境污染加剧。目前,农业面源污染已成为我国湖泊、河流等水体富营养化的主要原因,而农田面源污染由于区域大、范围广、难治理,成为农业面源污染中重要因素。相关研究表明,农田氮、磷的流失主要是通过农田径流流失或淋洗渗漏流失等途径,控制农田径流污染的生态拦截技术是从迁移途经上对农田面源污染进行控制,主要包括湿地工程技术、生态沟渠技术、滨岸缓冲带控制技术和人工多水塘技术等,其中湿地工程技术、及人工多水塘技术对农田周边自然环境要求较高,且需占据大量农田土地,投入成本也较高。近年来,针对农田生态拦截技术研究较多,如:例如:公开号为CN102094407A的发明专利,申请号为201010616311,名称为农田径流污染生态拦截沟渠,涉及一种集农田排水与防控农田非点源污染于一体的农田径流污染生态拦截沟渠,但该沟渠系统结构较复杂,在大面积农田应用成本较高;公开号为CN102211820A的发明专利,申请号为201110079288,名称为一种面源污染治理方法,涉及一种采用菌根技术治理面源污染的方法,能够强化面源污染截留工程中植物营养物质吸收能力和吸收效率,但此发明中菌根技术的生产、应用与推广性均有很强限制性;公开号为CN1823564A的发明专利,申请号为200610037908.5,名称为菜地土壤氮磷径流控制生态拦截方法,涉及一种菜地土壤氮磷径流控制生态拦截方法,采用构建生态拦截带及拦截沟,但生态拦截带建造需占用较多的土地面积。以上研究应用局限性较大,技术投入成本较高,推广难度较大。在我国,旱地种植业是农田种植业的核心部分,其具有农田地块面积较大、区域水资源较少,农田排水以降雨及灌溉产生农田径流为主,非降雨期及灌溉时农田沟渠水量较少,目前针对旱地农田面源污染的生态拦截措施研究较少,且现阶段的生态拦截措施对水资源要求较高,很难在旱地农田中应用。 Farmland non-point source pollution refers to the environment formed by the surface runoff and seepage of farmland through the surface runoff and farmland seepage of nutrients such as nitrogen and phosphorus, pesticides, and other organic or inorganic pollutants during farmland production activities. Pollution mainly includes chemical fertilizer pollution, pesticide pollution, livestock and poultry manure pollution, farmland solid waste pollution, etc. With the continuous increase of fertilizer consumption in the process of farmland planting, the content of nitrogen and phosphorus in farmland soil and the loss of nitrogen and phosphorus continue to increase, resulting in increased environmental pollution of farmland soil and water bodies. At present, agricultural non-point source pollution has become the main cause of eutrophication in lakes, rivers and other water bodies in my country, and farmland non-point source pollution has become an important factor in agricultural non-point source pollution due to its large area, wide range and difficult treatment. Relevant studies have shown that the loss of nitrogen and phosphorus in farmland is mainly through farmland runoff loss or leaching seepage loss. The ecological interception technology to control farmland runoff pollution is to control farmland non-point source pollution from the migration route, mainly including wetland engineering. technology, ecological ditch technology, coastal buffer zone control technology and artificial multi-pond technology, etc. Among them, wetland engineering technology and artificial multi-water pond technology have higher requirements on the natural environment around the farmland, and they need to occupy a large amount of farmland land, and the input cost is also high. higher. In recent years, there have been many studies on farmland ecological interception technology, such as: for example: the invention patent with the publication number CN102094407A, the application number is 201010616311, and the name is farmland runoff pollution ecological interception ditch, which involves a collection of farmland drainage and prevention and control of farmland non-point Farmland runoff pollution ecological interception ditches integrating source pollution, but the structure of the ditch system is relatively complex, and the cost of application in large-scale farmland is relatively high; the invention patent with the publication number CN102211820A, the application number is 201110079288, and the name is a non-point source pollution control The method relates to a method of using mycorrhizal technology to control non-point source pollution, which can strengthen the absorption capacity and absorption efficiency of plant nutrients in the non-point source pollution interception project, but the production, application and promotion of mycorrhizal technology in this invention have great potential. Strong restriction; Publication No. is CN1823564A invention patent, application number is 200610037908.5, the name is called vegetable field soil nitrogen and phosphorus runoff control ecological interception method, relates to a kind of vegetable field soil nitrogen and phosphorus runoff control ecological interception method, adopts the construction of ecological interception zone and interception ditch, but the construction of the ecological interception belt needs to occupy more land area. The application of the above research is limited, the technology investment cost is high, and the promotion is difficult. In my country, dryland planting is the core part of farmland planting. It has large farmland plots and less regional water resources. Farmland drainage is mainly farmland runoff generated by rainfall and irrigation. At present, there are few studies on ecological interception measures for non-point source pollution in dryland farmland, and the current ecological interception measures have high requirements for water resources, so it is difficult to apply them in dryland farmland. the
发明内容 Contents of the invention
本实用新型针对现有技术中存在的缺陷,提供了一种简单高效、实用经济、易于维护、便于推广的适用于旱地农田面源污染的高效生态拦截沟渠,可有效解决旱地农田种植过程N、P等营养元素流失大量大,周边水体富营养化严重的问题。 Aiming at the defects in the prior art, the utility model provides a simple, efficient, practical, economical, easy-to-maintain, and easy-to-promote high-efficiency ecological interception ditch suitable for dryland farmland non-point source pollution, which can effectively solve dryland farmland planting process N, Nutrient elements such as P are lost in a large amount, and the surrounding water body is seriously eutrophic. the
为了解决上述技术问题,本实用新型通过下述技术方案得以解决: In order to solve the above technical problems, the utility model is solved through the following technical solutions:
适用于旱地农田的高效生态拦截沟渠,所述的沟渠横断面为梯形,所述沟渠两侧的渠壁表面铺设有带孔洞的水泥板,沟渠的渠底铺设有植草砖,所述植草砖的形状为8字形。 A high-efficiency ecological interception ditch suitable for dry farmland, the cross section of the ditch is trapezoidal, the surface of the ditch wall on both sides of the ditch is covered with cement boards with holes, and the bottom of the ditch is laid with grass-planting bricks. The shape is figure 8.
作为优选,所述的水泥板采用钢筋混凝土结构,水泥板表面间隔均布6-9个孔洞,所述孔洞中种植香菇草。所述孔洞的形状为矩形、菱形、圆形、三角形任一种或几种的组合。 As a preference, the cement board adopts a reinforced concrete structure, and 6-9 holes are evenly distributed on the surface of the cement board, and mushroom grass is planted in the holes. The shape of the hole is any one or a combination of rectangle, rhombus, circle and triangle. the
作为优选,所述的水泥板规格为:厚5 cm,长60 cm,宽60 cm;孔洞直径5-10cm,相邻两孔间距为15-20cm。 Preferably, the specifications of the cement board are: 5 cm thick, 60 cm long, and 60 cm wide; the hole diameter is 5-10 cm, and the distance between two adjacent holes is 15-20 cm. the
作为优选,所述的植草砖的规格为:厚8cm,长40cm,宽20cm。 As a preference, the specification of the grass planting brick is: thickness 8cm, length 40cm, width 20cm. the
作为优选,所述的植草砖内种植有聚草。 As a preference, grasses are planted in the grass-planting bricks. the
作为优选,所述的沟渠内设置有拦截过滤网,此过滤网设置在渠道起始端,可对农田径流水进行初步拦截过滤,且可降低水体流速。 Preferably, the ditch is provided with an interception filter, which is arranged at the beginning of the channel, and can perform preliminary interception and filtration of farmland runoff water, and can reduce the flow velocity of the water body. the
渠壁带空洞水泥板及渠底植草砖能够有效降低因降雨而引起的渠道水土流失;渠壁及渠底种植的大量植物,既可以直接从水体和自身拦截的颗粒物中吸收生长所需氮、磷等营养元素,又可以起到减缓水流,延长水力停留时间的作用,从而进一步促进植物自身对氮、磷的吸收;另外,生态沟渠中植物能够有效拦截经雨水冲刷带走的农田土壤颗粒,此部分土壤颗粒沉积在渠道底部,对氮、磷等营养元素也有一定的吸附作用。因此,此生态沟渠对农田径流水氮、磷素表现出很强的拦截、去除能力。 Hollow cement boards on the canal wall and grass-planting bricks at the canal bottom can effectively reduce the water and soil loss in the canal caused by rainfall; a large number of plants planted on the canal wall and canal bottom can absorb the nitrogen needed for growth directly from the water body and the particulate matter intercepted by itself. Phosphorus and other nutrients can also slow down the water flow and prolong the hydraulic retention time, thereby further promoting the absorption of nitrogen and phosphorus by the plants themselves; in addition, the plants in the ecological ditch can effectively intercept the farmland soil particles washed away by the rainwater, This part of the soil particles is deposited at the bottom of the channel, which also has a certain adsorption effect on nitrogen, phosphorus and other nutrients. Therefore, this ecological ditch has a strong ability to intercept and remove nitrogen and phosphorus in farmland runoff. the
本实用新型由于采用了以上技术方案,具有显著的技术效果: Due to the adoption of the above technical scheme, the utility model has remarkable technical effects:
(1)沟渠设计简单、实用,可以与农田沟渠相结合,在现有渠道基础上进行改造,不需另外占用农田土地,且建造成本合理。 (1) The design of the ditches is simple and practical, and can be combined with farmland ditches to transform existing canals without occupying additional farmland land, and the construction cost is reasonable.
(2)所选草种有着很强的环境适应能力、繁殖能力、氮磷吸收能力,并有着较好的耐受性,能适应从水到旱、从强光到荫蔽等多种生存环境,对渠道中水量要求较小,且种植成本较低,易于收割、维护,景观美化性强,能够提升生态沟渠对氮、磷等营养元素的消纳能力。 (2) The selected grass species have strong environmental adaptability, reproductive ability, nitrogen and phosphorus absorption ability, and good tolerance, and can adapt to various living environments from water to drought, from strong light to shade, etc. It requires less water in the channel, and the planting cost is lower. It is easy to harvest and maintain, and has strong landscaping properties. It can improve the absorption capacity of ecological ditches for nitrogen, phosphorus and other nutrients. the
(3)生态沟渠中植物能够有效拦截经雨水冲刷带走的农田土壤颗粒,此部分土壤颗粒沉积在渠道底部,对氮、磷也有一定的吸附作用;同时,渠壁带空洞水泥板及渠底植草砖能够有效降低农田沟渠因强降雨而引起的水土流失。 (3) The plants in the ecological ditch can effectively intercept the farmland soil particles washed away by the rainwater. This part of the soil particles is deposited at the bottom of the ditch and has a certain adsorption effect on nitrogen and phosphorus. Grass planting bricks can effectively reduce soil erosion caused by heavy rainfall in farmland ditches. the
(4)本实用新型应用性强,适用范围广,日常运行、维护成本合理,简单便捷,具有很强的推广价值,可应用与不同旱地农田,如蔬菜田、麦田、花卉田、茶园、苗木田等。 (4) The utility model has strong applicability, wide application range, reasonable daily operation and maintenance costs, simple and convenient, and has strong promotion value. It can be applied to different dry land farmlands, such as vegetable fields, wheat fields, flower fields, tea gardens, seedlings Tian et al. the
附图说明 Description of drawings
图1为高效农田生态沟渠剖面图; Figure 1 is a section view of an efficient farmland ecological ditch;
图2为孔洞水泥板结构平面图; Fig. 2 is a structure plan view of a hole cement board;
图3 为植草砖平面图。 Figure 3 is a plan view of the grass planting brick.
具体实施方式 Detailed ways
下面结合附图1至附图3与实施例对本实用新型作进一步详细描述:
Below in conjunction with accompanying
实施例1Example 1
本实例以太湖流域某典型蔬菜集约化种植基地为示范对象。 This example takes a typical vegetable intensive planting base in the Taihu Lake Basin as the demonstration object.
如图1所示,将原有农田沟渠改造成横断面为梯形的渠道,沟渠两侧渠壁1平行铺设带孔洞的水泥板,渠底2平行铺设8字形的植草砖。 As shown in Figure 1, the original farmland ditch was transformed into a channel with a trapezoidal cross section. Cement boards with holes were laid in parallel on both sides of the ditch, and 8-shaped grass-planting bricks were laid in parallel on the bottom 2 of the ditch. the
如图2所示,渠壁带孔洞水泥板板厚5 cm,长60 cm,宽60 cm,圆孔直径8 cm,孔间距为20 cm,为钢筋混凝土结构,在孔洞中,种植对N、P等营养元素具有高效吸收能力且环境适应性强的多年生植物,选用多年生挺水植物——香菇草(Hydrocotyle vulgaris)。 As shown in Figure 2, the cement slab with holes on the canal wall is 5 cm thick, 60 cm long, and 60 cm wide. The diameter of the round hole is 8 cm, and the hole spacing is 20 cm. It is a reinforced concrete structure. As a perennial plant with high absorption capacity of nutrients such as P and strong environmental adaptability, a perennial emergent plant—Hydrocotyle vulgaris ( Hydrocotyle vulgaris ) is selected.
如图3所示,渠底铺设8字形植草砖,砖厚8cm,长40cm,宽20cm,在孔洞中,种植对N、P等营养元素具有高效吸收能力且环境适应性强的多年生植物,选用多年生水草——聚草(Myriophyllumspicatum) As shown in Figure 3, 8-shaped grass-planting bricks are laid on the bottom of the canal. The bricks are 8cm thick, 40cm long, and 20cm wide. Perennial Aquatic Grass - Myriophyllum spicatum
该蔬菜基地总面积1100亩,其中种植区域面积520亩,主要进行设施与露地蔬菜种植。示范工程建设前菜地废水不经任何有效处理而直接排放,总排水口总氮浓度在6.83 mgL-1~4.65 mgL-1之间,总磷浓度在1.93 mgL-1~1.43 mgL-1之间,分别为《地表水环境质量标准(GB3838-2002)》中Ⅴ类水质标准的3.41~2.33倍、4.87~3.58倍,蔬菜地面源污染问题日益严重。依据此发明,在示范区经过两年有效的运行、维护,该蔬菜地总排水水质得到明显提升,2011年、2012年总氮浓度分别削减为4.18 mgL-1~2.33 mgL-1及3.41 mgL-1~1.56 mgL-1,与2010年同月份相比,去除率分别达0.33~0.52、0.43~0.67;2011年、2012年总磷浓度分别削减为1.88 mgL-1~0.59 mgL-1及1.12 mgL-1~0.28 mgL-1,去除率分别达0.23~0.59、0.43~0.82。在农田原有沟渠基础上进行生态沟渠改造,不仅有效改善示范区农田排水水质,节约农田土地资源,同时防止农田水土流失,达到因地制宜、成本合理、实用高效、保持水土、维护便捷的效果。 The total area of the vegetable base is 1100 mu, of which the planting area is 520 mu, mainly for facilities and open field vegetable planting. Before the construction of the demonstration project, the vegetable field wastewater was directly discharged without any effective treatment. The total nitrogen concentration at the total outlet was between 6.83 mgL -1 and 4.65 mgL -1 , and the total phosphorus concentration was between 1.93 mgL -1 and 1.43 mgL -1 . They are respectively 3.41 to 2.33 times and 4.87 to 3.58 times that of the Class V water quality standard in the Environmental Quality Standard for Surface Water (GB3838-2002), and the problem of vegetable ground source pollution is becoming more and more serious. According to this invention, after two years of effective operation and maintenance in the demonstration area, the total drainage water quality of the vegetable field has been significantly improved. In 2011 and 2012, the total nitrogen concentration was reduced to 4.18 mgL -1 ~ 2.33 mgL -1 and 3.41 mgL - 1 ~ 1.56 mgL -1 , compared with the same month in 2010, the removal rates reached 0.33 ~ 0.52, 0.43 ~ 0.67 respectively; in 2011 and 2012, the total phosphorus concentration was reduced to 1.88 mgL -1 ~ 0.59 mgL -1 and 1.12 mgL -1 to 0.28 mgL -1 , the removal rates were 0.23 to 0.59 and 0.43 to 0.82, respectively. Reconstruction of ecological ditches on the basis of the original ditches in the farmland can not only effectively improve the drainage water quality of the farmland in the demonstration area, save farmland land resources, but also prevent soil erosion in the farmland, and achieve the effects of adapting measures to local conditions, reasonable cost, practical and efficient, water and soil conservation, and convenient maintenance.
总之,以上所述仅为本实用新型的较佳实施例,凡依本实用新型申请专利范围所作的均等变化与修饰,皆应属本实用新型专利的涵盖范围。 In a word, the above descriptions are only preferred embodiments of the present utility model, and all equal changes and modifications made according to the patent scope of the utility model should fall within the scope of the utility model patent. the
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103233449A (en) * | 2013-04-18 | 2013-08-07 | 浙江大学 | Efficient ecological interception ditch suitable for dry land farmlands |
| CN106978797A (en) * | 2017-05-09 | 2017-07-25 | 恩施清江茶业有限责任公司 | One kind is applied to tea place escape canal and its application method |
| CN113582448A (en) * | 2021-07-29 | 2021-11-02 | 长三角(义乌)生态环境研究中心 | Processing system for reducing farmland non-point source pollution |
| CN117839289A (en) * | 2024-03-07 | 2024-04-09 | 安徽省农业科学院土壤肥料研究所 | Ecological intercepting device for agricultural non-point source pollutant |
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2013
- 2013-04-18 CN CN2013201957251U patent/CN203256709U/en not_active Expired - Lifetime
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103233449A (en) * | 2013-04-18 | 2013-08-07 | 浙江大学 | Efficient ecological interception ditch suitable for dry land farmlands |
| CN106978797A (en) * | 2017-05-09 | 2017-07-25 | 恩施清江茶业有限责任公司 | One kind is applied to tea place escape canal and its application method |
| CN113582448A (en) * | 2021-07-29 | 2021-11-02 | 长三角(义乌)生态环境研究中心 | Processing system for reducing farmland non-point source pollution |
| CN117839289A (en) * | 2024-03-07 | 2024-04-09 | 安徽省农业科学院土壤肥料研究所 | Ecological intercepting device for agricultural non-point source pollutant |
| CN117839289B (en) * | 2024-03-07 | 2024-05-24 | 安徽省农业科学院土壤肥料研究所 | Ecological intercepting device for agricultural non-point source pollutant |
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