CN102603071A - Construction method for nitrogen and phosphorus loss system of greenhouse soil of intercept river network area - Google Patents
Construction method for nitrogen and phosphorus loss system of greenhouse soil of intercept river network area Download PDFInfo
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- CN102603071A CN102603071A CN2011104193438A CN201110419343A CN102603071A CN 102603071 A CN102603071 A CN 102603071A CN 2011104193438 A CN2011104193438 A CN 2011104193438A CN 201110419343 A CN201110419343 A CN 201110419343A CN 102603071 A CN102603071 A CN 102603071A
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- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 title claims abstract description 75
- 229910052757 nitrogen Inorganic materials 0.000 title claims abstract description 39
- 229910052698 phosphorus Inorganic materials 0.000 title claims abstract description 38
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 title claims abstract description 37
- 239000011574 phosphorus Substances 0.000 title claims abstract description 37
- 238000010276 construction Methods 0.000 title claims abstract description 12
- 239000002689 soil Substances 0.000 title abstract description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 41
- 241000209094 Oryza Species 0.000 claims abstract description 17
- 235000007164 Oryza sativa Nutrition 0.000 claims abstract description 17
- 235000009566 rice Nutrition 0.000 claims abstract description 17
- 241000196324 Embryophyta Species 0.000 claims abstract description 15
- 239000001963 growth medium Substances 0.000 claims abstract description 7
- 239000003818 cinder Substances 0.000 claims abstract description 4
- 235000013311 vegetables Nutrition 0.000 claims description 45
- 239000004568 cement Substances 0.000 claims description 8
- 244000052363 Cynodon dactylon Species 0.000 claims description 4
- 238000003860 storage Methods 0.000 claims description 3
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 claims 1
- 235000015097 nutrients Nutrition 0.000 abstract description 15
- 238000012851 eutrophication Methods 0.000 abstract description 3
- 239000003245 coal Substances 0.000 abstract 1
- 239000000126 substance Substances 0.000 abstract 1
- 238000010586 diagram Methods 0.000 description 14
- 238000005516 engineering process Methods 0.000 description 8
- 238000000034 method Methods 0.000 description 7
- 230000008878 coupling Effects 0.000 description 6
- 238000010168 coupling process Methods 0.000 description 6
- 238000005859 coupling reaction Methods 0.000 description 6
- 230000000694 effects Effects 0.000 description 6
- 238000001179 sorption measurement Methods 0.000 description 6
- 210000001503 joint Anatomy 0.000 description 4
- 238000012423 maintenance Methods 0.000 description 4
- 238000010521 absorption reaction Methods 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- 239000000618 nitrogen fertilizer Substances 0.000 description 3
- 244000025254 Cannabis sativa Species 0.000 description 2
- 238000012271 agricultural production Methods 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 230000004720 fertilization Effects 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 239000013049 sediment Substances 0.000 description 2
- 230000004083 survival effect Effects 0.000 description 2
- MMDJDBSEMBIJBB-UHFFFAOYSA-N [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] Chemical compound [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] MMDJDBSEMBIJBB-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000003628 erosive effect Effects 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 238000003973 irrigation Methods 0.000 description 1
- 230000002262 irrigation Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 230000001932 seasonal effect Effects 0.000 description 1
- 238000004162 soil erosion Methods 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
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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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
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Abstract
Description
the
技术领域 technical field
本发明技术属于设施菜地给排水技术领域,它能针对设施菜地径流污染进行生态沟渠拦截处理,同时利用湿地稻田系统对经过生态沟渠拦截处理过的菜地排水中富余养分进行吸收再利用,尤其对氮、磷等污染物质有很强的削减作用。 The technology of the present invention belongs to the technical field of water supply and drainage of facility vegetable fields. It can carry out ecological ditch interception treatment for the runoff pollution of facility vegetable fields, and at the same time use the wetland paddy field system to absorb and reuse the surplus nutrients in the vegetable field drainage that has been intercepted by ecological ditch. In particular, it has a strong reduction effect on pollutants such as nitrogen and phosphorus.
the
背景技术 Background technique
面源(non-point又称非点源)污染是当今世界上普遍存在的一个严重环境问题,美国、欧盟等发达国家研究表明:农业活动是最大的面源污染源。1985年美国进行了迄今最广泛的面源污染调查,调查结果显示,受面源污染的河流和湖泊中,农业面源污染贡献率分别为64%和57%。农田地表径流N、P流失是导致地表水体富营养化的主要原因,在农业生产过程中,由于降雨等因素导致的养分流失不可避免,降雨形成的地表径流是河湖水体污染物汇集的主要途径之一。因而对农田流失中的营养成分进行生物吸收、固定和循环再利用成为了生态环境研究中的重要内容。 Non-point source (also known as non-point source) pollution is a serious environmental problem that exists in the world today. Studies in developed countries such as the United States and the European Union have shown that agricultural activities are the largest source of non-point source pollution. In 1985, the United States conducted the most extensive survey of non-point source pollution so far. The survey results showed that among the rivers and lakes polluted by non-point sources, the contribution rates of agricultural non-point source pollution were 64% and 57%, respectively. The loss of N and P in farmland surface runoff is the main cause of eutrophication in surface water bodies. In the process of agricultural production, nutrient loss due to factors such as rainfall is inevitable, and surface runoff formed by rainfall is the main way for rivers and lakes to collect pollutants. one. Therefore, the bioabsorption, immobilization and recycling of nutrients lost in farmland has become an important content in the study of ecological environment.
在我国,设施菜地排水沟渠主要有土质沟渠和混凝土沟渠两种类型。土质沟渠由于存在水土流失和丛生杂草的问题,会对受纳水体产生污染;混凝土沟渠存在的主要问题一是水速较快,难以较完全地沉降排水中的泥沙;二是缺少植物和微生物,不能吸收、吸附和降解排水中的氮磷。针对农田径流,目前已有生态沟渠拦截技术,能有效拦截农田排水中的氮磷,但对设施菜地径流污染控制方面还未有此类技术。地表径流是面源污染向水体输出氮磷主要途径之一,针对菜地径流已有的防治技术主要有生态草带拦截技术,其可以有效地吸收和截留来自蔬菜地地表径流和地下径流中的氮磷养分(李国栋,2006),但生态草带由于占用一定的耕地面积而难以在大范围内推广,同时存在中等强度以上降雨情况下拦截效果差,养分再利用率低等缺点,且由于植物生长的季节性差异,在其枯萎季节植被枯萎腐烂,自身所含养分释放而增加了流失养分负荷。 In my country, there are mainly two types of drainage ditches for facility vegetable fields: soil ditches and concrete ditches. Due to the problems of soil erosion and overgrown weeds, soil ditches will pollute the receiving water body; the main problems of concrete ditches are that the water velocity is fast and it is difficult to settle the sediment in the drainage completely; the second is the lack of plants and Microorganisms cannot absorb, adsorb and degrade nitrogen and phosphorus in wastewater. For farmland runoff, there is currently an ecological ditch interception technology that can effectively intercept nitrogen and phosphorus in farmland drainage, but there is no such technology for the control of runoff pollution from facility vegetable fields. Surface runoff is one of the main ways for non-point source pollution to export nitrogen and phosphorus to water bodies. The existing control technology for vegetable runoff mainly includes ecological grass belt interception technology, which can effectively absorb and intercept the nitrogen and phosphorus from vegetable surface runoff and underground runoff. Nitrogen and phosphorus nutrients (Li Guodong, 2006), but the ecological grass belt is difficult to promote on a large scale because it occupies a certain area of cultivated land. At the same time, there are disadvantages such as poor interception effect and low nutrient reuse rate under the condition of moderate rainfall and above. Seasonal differences in growth, vegetation withers and rots in its withering season, and the release of nutrients contained in itself increases the load of lost nutrients.
the
发明内容 Contents of the invention
解决的技术问题:本发明的目的在于提供一种拦截水网区设施菜地氮磷流失系统的构建方法,其主要是解决水网区设施菜地径流污染问题。 Technical problem to be solved: The purpose of this invention is to provide a construction method for intercepting the loss of nitrogen and phosphorus in the vegetable field in the water network area, which mainly solves the runoff pollution of the vegetable field in the water network area.
技术方案:Technical solutions:
拦截水网区设施菜地氮磷流失系统的构建方法,步骤为:在设施菜地地表构建生态沟渠,所述生态沟渠由横断面为“U”形的管道拼接而成,U型管底部用水泥浇筑,每两个“U”形管之间的侧壁连接处,设有空隙,空隙内种有植物;生态沟渠的底部设置生长箱,生长箱内装有生长介质并种有植物,所述生长介质为煤渣、碎石或陶粒;所述生态沟渠与集水池相连通,集水池与湿地稻田相连,所述湿地稻田的两端为缓冲带,缓冲带所夹中间地带种植水稻,从集水池流出的蓄水经缓冲带流入湿地稻田,再由湿地稻田另一端的缓冲带流出。 A method for constructing a system for intercepting nitrogen and phosphorus loss in a facility vegetable field in a water network area. The steps include: constructing an ecological ditch on the surface of the facility vegetable field. Concrete pouring, there is a gap at the side wall connection between every two "U"-shaped pipes, and plants are planted in the gap; a growth box is set at the bottom of the ecological ditch, and the growth medium is installed in the growth box and plants are planted. The growth medium is cinder, crushed stone or ceramsite; the ecological ditch is connected to the sump, and the sump is connected to the wetland paddy field. The stored water flowing out of the pool flows into the wetland paddy field through the buffer zone, and then flows out from the buffer zone at the other end of the wetland paddy field.
上述“U”形管的中间结合部留空宽30cm。 The middle junction of the above-mentioned "U"-shaped pipe is left open with a width of 30 cm.
上述生态沟渠侧壁种植的植物为狗牙根,生长箱内种植的植物为氮高效水稻桂单4号。 The plant planted on the side wall of the ecological ditch is Bermudagrass, and the plant planted in the growth box is the nitrogen-efficient rice Guidan No. 4.
上述生长箱的排列间距为80cm。 The arrangement pitch of the above-mentioned growth boxes is 80 cm.
上述“U”形的管道为水泥浇筑而成。 The above-mentioned "U" shaped pipeline is formed by pouring cement.
上述集水池内设有提升泵,蓄水经提升泵流入湿地稻田。 A lifting pump is arranged in the above sump, and the stored water flows into the wetland paddy field through the lifting pump.
上述生长箱外壁布满孔。 The outer wall of the growth box is covered with holes.
有益效果:本发明可以有效削减氮磷等营养物质的负荷,有效降低设施菜地径流负荷,能够解决设施菜地附近河网水体的富营养化问题。利用本发明提供的水网区设施菜地氮磷流失生态沟渠与湿地稻田耦联拦截方法,一是能有效拦截设施菜地径流中的氮磷,拦截率分别达80%和85%以上;二是可减少湿地稻田20%~30%氮肥投入,且对产量没有影响;三是能充分利用原有农田排水沟渠,解决了生态工程占用较多耕地的问题;四是生态沟渠两壁植物种植更加方便,成活率高;五是工程造价和维护成本低、操作维护简单、便于大面积推广应用。 Beneficial effects: the invention can effectively reduce the load of nutrients such as nitrogen and phosphorus, effectively reduce the runoff load of the facility vegetable field, and can solve the eutrophication problem of the river network water body near the facility vegetable field. Utilize the method for intercepting the nitrogen and phosphorus loss ecological ditch in the facility vegetable field provided by the present invention and the wetland paddy field coupling interception method, one can effectively intercept the nitrogen and phosphorus in the runoff of the facility vegetable field, and the interception rate reaches more than 80% and 85% respectively; First, it can reduce 20%~30% nitrogen fertilizer input in wetland rice fields, and has no effect on yield; third, it can make full use of the original farmland drainage ditches, which solves the problem of ecological engineering occupying more cultivated land; fourth, planting plants on both walls of ecological ditches is easier It is convenient and has a high survival rate; fifthly, the construction cost and maintenance cost are low, the operation and maintenance are simple, and it is convenient for large-scale promotion and application.
the
附图说明 Description of drawings
图1为水网区设施菜地氮磷流失生态沟渠与湿地稻田耦联拦截系统的整体结构及水流方向示意图; Figure 1 is a schematic diagram of the overall structure and water flow direction of the ecological ditch for nitrogen and phosphorus loss in the facility vegetable field and the wetland rice field coupling interception system in the water network area;
图2为生态沟渠横断面示意图; Figure 2 is a schematic diagram of the cross-section of the ecological ditch;
图3为生态沟渠构造示意图 Figure 3 is a schematic diagram of the ecological ditch structure
图4为生态沟渠的侧壁和底部结构的示意图; Fig. 4 is the schematic diagram of the side wall and bottom structure of ecological ditch;
图5为生态沟渠生长箱及其在沟渠底部排列方式示意图; Fig. 5 is a schematic diagram of an ecological ditch growth box and its arrangement at the bottom of the ditch;
图6为集水池结构示意图; Fig. 6 is a schematic diagram of the structure of the sump;
图7为湿地稻田结构示意图。 Figure 7 is a schematic diagram of the wetland paddy field structure.
the
具体实施方式 Detailed ways
为了更详细地介绍本发明技术,下面结合实施例子来说明: In order to describe the technology of the present invention in more detail, it is illustrated below in conjunction with the implementation examples:
实施例1: Embodiment 1 :
太湖流域面积36 900平方公里,以平原为主,占总面积的4/6,水面占1/6,其余为丘陵和山地。项目示范区位于无锡市滨湖区。随着农业结构的调整,设施栽培特别是大棚蔬菜栽培面积不断扩大,大棚蔬菜生产已成为当地农业生产的重要组成部分之一。对于太湖地区而言,设施蔬菜多由水稻田改种而来,同一区域内稻田菜地共存的现象普遍存在。太湖地区河网密布,许多设施菜地与水体相邻,肥料在雨水冲刷下易通过径流进入水体,因此蔬菜地氮磷径流流失是一个重要的污染源。太湖区降雨主要集中在春夏季节,同时春夏季也是蔬菜施肥频繁时期,而设施菜地在夏季处于揭棚期,因此夏季设施菜地径流是全年径流的主要部分。 The Taihu Lake Basin covers an area of 36 900 square kilometers, mainly plains, accounting for 4/6 of the total area, water surface accounts for 1/6, and the rest is hills and mountains. The project demonstration area is located in Binhu District, Wuxi City. With the adjustment of the agricultural structure, facility cultivation, especially greenhouse vegetable cultivation area has been expanding, and greenhouse vegetable production has become one of the important components of local agricultural production. For the Taihu Lake area, most of the protected vegetables are replanted from rice fields, and the coexistence of rice fields and vegetable fields in the same area is common. The Taihu Lake area is densely covered with river networks, and many facility vegetable fields are adjacent to water bodies. Fertilizers easily enter the water bodies through runoff under the erosion of rainwater. Therefore, nitrogen and phosphorus runoff from vegetable fields is an important source of pollution. Rainfall in the Taihu Lake area is mainly concentrated in spring and summer, which are also the periods of frequent fertilization of vegetables, and the protected vegetable fields are in the period of uncovering the sheds in summer, so the runoff of the protected vegetable fields in summer is the main part of the annual runoff.
工程实施例实施在无锡市滨湖区胡埭镇龙延村,水网区设施菜地氮磷流失生态沟渠与湿地稻田耦联拦截技术设计说明: The implementation of the project is carried out in Longyan Village, Hudai Town, Binhu District, Wuxi City. Design description of the coupling interception technology of ecological ditches and wetland paddy fields for nitrogen and phosphorus loss in the water network area:
参照图1,其为水网区设施菜地氮磷流失生态沟渠与湿地稻田耦联拦截系统的整体结构及水流方向示意图。将原来设施菜地径流直接入河改造为经生态沟渠拦截处理后汇入集水池,再经集水池中的蓄水通过提升泵泵进湿地稻田,经稻田吸收再利用后排入河流。 Referring to Figure 1, it is a schematic diagram of the overall structure and water flow direction of the ecological ditch for the loss of nitrogen and phosphorus in the vegetable field of the water network area and the coupling interception system of the wetland paddy field. The runoff from the original facility vegetable field is transformed into the river after being intercepted and treated by the ecological ditch, and then the water stored in the sump is pumped into the wetland paddy field through the lift pump, and then discharged into the river after being absorbed and reused by the paddy field.
参照图2,其为生态拦截沟渠横断面示意图。在原有的农田土质排水沟渠中每隔30cm放置一个长×宽×高=40×50×60(cm)的U型水泥管,将其改造成横断面为U形的混凝土沟渠。 Referring to Fig. 2, it is a schematic diagram of a cross-section of an ecological interception ditch. Place a U-shaped cement pipe with length × width × height = 40 × 50 × 60 (cm) every 30 cm in the original farmland soil drainage ditch, and transform it into a U-shaped concrete ditch in cross section.
参照图3,其为生态拦截沟渠构造示意图。每两个U型管连接处的底部3用水泥浇筑连接,沟渠的两侧壁1分布多个30cm宽的留空中间结合部4。
Referring to Fig. 3, it is a schematic diagram of the structure of an ecological interception ditch. The bottom 3 of every two U-shaped pipe joints is connected by pouring cement, and a plurality of 30 cm wide empty
参照图4,其为生态拦截沟渠侧壁和底部结构的示意图,从图4中可以看出,侧壁1上设置有若干留空中间结合部4。在侧壁1的留空中间结合部4中种植对氮磷具有较强吸收能力的狗牙根5。
Referring to FIG. 4 , it is a schematic diagram of the side wall and bottom structure of an ecological interception ditch. It can be seen from FIG. 4 that a number of empty
参照图5,其为生长箱及其在沟渠底部排列方式示意图,每隔80 cm放置的生长箱6,彼此有间隔地排列在沟渠的底部2,生长箱6的外壁上布满孔7,生长箱6内充对氮磷具有较强吸附能力的吸附材料,并在生长箱中种植氮高效水稻桂单4号8。
With reference to Fig. 5, it is the schematic diagram of the growth box and its arrangement at the bottom of the ditch, the
参照图6,其为集水池示意图,经过生态沟渠拦截处理后的菜地排水进入集水池9,通过提升泵10将集水池中的蓄水泵入湿地稻田。
Referring to FIG. 6 , it is a schematic diagram of a sump. After being intercepted by an ecological ditch, the vegetable field drains into the sump 9 , and the water stored in the sump is pumped into the wetland paddy field through a
参照图7,其为湿地稻田示意图,通过提升泵10将集水池中的蓄水泵入湿地稻田缓冲带11,经过缓冲带分流均匀进入稻田12,富余养分被水稻吸收利用后通过缓冲带13排入河流。
Referring to Figure 7, it is a schematic diagram of a wetland paddy field. The water storage in the sump is pumped into the
本工程于2010年5月施工建设,2010年6月运行,利用本发明提供的水网区设施菜地氮磷流失生态沟渠与湿地稻田耦联拦截方法,在整个水稻生长季(2010年6月20日至2010年11月5日)可有效拦截工程示范区内设施菜地径流氮磷排放。本发明共削减示范区内设施菜地径流排放中硝态氮15 kg/hm2,总氮16.81kg/hm2,总磷0.16 kg/hm2,对TN、TP的削减分别达到87%、89%。另外,可将降雨中(30 min)设施菜地径流排放中的TN、TP 平均浓度分别由11.31mg/L 、0.05mg/L降低到2.59mg/L、0.04 mg/L,平均阻控率达到45% 、52%;而降雨后TN、TP平均浓度分别由12.38mg/L、0.06 mg/L降低到2.9mg/L、0.03 mg/L,平均阻控率达到81%、64%。与当地推荐施肥量相比,湿地稻田可减少20 %氮肥投入,且对产量无影响。本发明可有效提高养分再利用率,充分利用原有土质排水沟渠,解决了生态工程占用较多耕地的问题。与生态沟渠预制板留空相比,U型水泥管的使用具有成本低、沟壁植物种植方便且成活率高的优点。本发明具有控污效果好、工程造价和维护成本低、操作维护简单、便于大面积推广应用等特点。 This project was constructed in May 2010 and started operation in June 2010. Using the ecological ditch for the loss of nitrogen and phosphorus in the water network area facilities and vegetable fields provided by the present invention and the wetland paddy field coupling interception method, the whole rice growing season (June 2010) 20th to November 5th, 2010) can effectively intercept the discharge of nitrogen and phosphorus from the vegetable field runoff in the project demonstration area. The present invention reduces 15 kg/hm 2 of nitrate nitrogen, 16.81 kg/hm 2 of total nitrogen, and 0.16 kg/hm 2 of total phosphorus in runoff discharge from facility vegetable fields in the demonstration area, and reduces TN and TP by 87% and 89% respectively. %. In addition, the average concentration of TN and TP in the runoff discharge from vegetable fields during rainfall (30 min) can be reduced from 11.31 mg/L and 0.05 mg/L to 2.59 mg/L and 0.04 mg/L respectively, and the average resistance control rate reaches After the rainfall, the average concentration of TN and TP decreased from 12.38 mg/L and 0.06 mg/L to 2.9 mg/L and 0.03 mg/L respectively, and the average resistance and control rate reached 81% and 64%. Compared with the local recommended fertilization rate, wetland paddy field can reduce nitrogen fertilizer input by 20%, and has no effect on yield. The invention can effectively improve the nutrient reutilization rate, make full use of the original soil drainage ditches, and solve the problem that more cultivated land is occupied by ecological projects. Compared with the prefabricated slab in the ecological ditch, the use of U-shaped cement pipe has the advantages of low cost, convenient planting of ditch wall plants and high survival rate. The invention has the characteristics of good pollution control effect, low engineering cost and maintenance cost, simple operation and maintenance, and easy popularization and application in a large area.
the
实施例2Example 2
拦截水网区设施菜地氮磷流失系统的构建方法:将设施菜地径流引入生态沟渠中,通过生态沟渠吸收径流中的氮磷、降低水速、沉降泥沙;沟渠的横断面呈U型,沟渠由多个长×宽×高=40×50×60(cm)的U型水泥管排列组成,每两个U型管的中间结合部底部用水泥浇筑连接,侧壁留空30cm宽土壤,沟渠底部相隔80cm距离放置一个内充对氮磷具有较强吸附能力的吸附材料的生长箱,沟渠两壁的留空中间结合部和底部的生长箱中分别种植对氮磷具有较强吸收能力的狗牙根和氮高效水稻桂单4号; 通过生态沟渠拦截处理后的设施菜地排水再汇入集水池中,通过泵提升将集水池中的蓄水泵入湿地稻田中进行吸收再利用,对富余养分进行吸收再利用,提高养分再利用率。其水流方向参见附图1。所述生长箱,是一个外壁布满孔、内充对氮磷具有较强吸附能力的吸附材料的箱体,并在生长箱中种植对氮磷具有较强吸收能力的氮高效水稻桂单4号。
The construction method of intercepting the nitrogen and phosphorus loss system of the facility vegetable field in the water network area: introduce the runoff of the facility vegetable field into the ecological ditch, absorb the nitrogen and phosphorus in the runoff through the ecological ditch, reduce the water speed, and settle the sediment; the cross section of the ditch is U-shaped , The ditch is composed of a plurality of U-shaped cement pipes arranged in length × width × height = 40 × 50 × 60 (cm), and the bottom of the middle junction of every two U-shaped pipes is connected by cement pouring, and the side wall is left with a 30cm wide soil At the bottom of the ditch, a growth box filled with adsorption materials with strong adsorption capacity for nitrogen and phosphorus is placed at a distance of 80 cm. Bermudagrass and nitrogen-efficient rice Guidan No. 4; the drainage of the treated vegetable field is intercepted by the ecological ditch and then poured into the sump, and the water in the sump is pumped into the wetland paddy field for absorption and reuse through pump lifting. Absorb and reuse surplus nutrients to improve nutrient reutilization rate. Its flow direction is referring to accompanying
水网区设施菜地氮磷流失生态沟渠与湿地稻田耦联拦截系统基本工艺与工作原理:工艺路线如下:设施菜地径流-生态沟渠-集水池-湿地稻田—河流。工作原理:生态沟渠中沟壁和沟底生长箱中种植高效吸收氮磷的植物,生长箱中的生长介质选择煤渣、碎石、陶粒等;集水池收集经生态沟渠拦截处理后的菜地排水;减少湿地稻田氮肥投入,通过灌溉集水池中的蓄水补足养分。 The basic technology and working principle of the nitrogen and phosphorus loss ecological ditch and wetland paddy field coupling interception system in the water network area: the process route is as follows: runoff from the facility vegetable field - ecological ditch - catchment pond - wetland paddy field - river. Working principle: plants that absorb nitrogen and phosphorus efficiently are planted in the ditch wall and ditch bottom growth box in the ecological ditch, and the growth medium in the growth box is cinder, gravel, ceramsite, etc.; the collection pool collects the vegetable field intercepted by the ecological ditch Drainage: reduce the input of nitrogen fertilizer in wetland paddy fields, and replenish nutrients through the water storage in the irrigation sump.
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| CN102910739A (en) * | 2012-10-22 | 2013-02-06 | 中国科学院沈阳应用生态研究所 | Purification method of drainage outside rice field in estuarine area |
| CN103435165A (en) * | 2013-09-18 | 2013-12-11 | 浙江省农业科学院 | Method for blocking and absorbing nitrogen and phosphorus flowing away from paddy field by utilizing water discharging channel |
| CN104345131A (en) * | 2014-11-06 | 2015-02-11 | 浙江大学 | Rice field nitrogen and phosphorus runoff loss load field scale estimation and calculation method |
| CN104355410A (en) * | 2014-11-07 | 2015-02-18 | 上海交通大学 | Ecological interception and blocking system for controlling non-point source pollution of rice field |
| CN105706691A (en) * | 2016-02-18 | 2016-06-29 | 广东省生态环境与土壤研究所 | Method for reducing farmland drainage canal nitrogen and phosphorus loss through charcoal |
| CN106115925A (en) * | 2016-08-19 | 2016-11-16 | 中国科学院、水利部成都山地灾害与环境研究所 | The widespread pollution from the overuse of fertilizers and pesticides in rural area cleaning system that step rice field organically combines with ecological canal |
| CN107902842A (en) * | 2017-11-25 | 2018-04-13 | 南京林业大学 | A kind of ecological purification band in situ of multibank capability |
| CN107902842B (en) * | 2017-11-25 | 2024-01-30 | 南京林业大学 | In-situ ecological purification belt with multiple functions |
| CN109851050A (en) * | 2019-01-03 | 2019-06-07 | 浙江省农业科学院 | Multi-stage nutrient absorption system and method for planting base runoff sewage |
| CN114532209A (en) * | 2022-02-23 | 2022-05-27 | 江西省农业科学院土壤肥料与资源环境研究所 | System for intercepting nitrogen and phosphorus loss of facility vegetable field in water network area |
| BE1032449B1 (en) * | 2024-12-26 | 2025-10-01 | Inst Soil Science Cas | Method for establishing a system to prevent and control nitrogen and phosphorus losses for vegetable fields in areas with a water network |
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