CN111392871A - An ecological grading interception and control method for hardened ditches in hilly and mountainous areas - Google Patents
An ecological grading interception and control method for hardened ditches in hilly and mountainous areas Download PDFInfo
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Abstract
本发明属于农田面源控制技术领域,针对现有技术中实施困难和维护效率低下的问题,提出一种丘陵山区硬化沟渠生态分级拦截阻控方法,包括:S1,分级拦截:推算出沉沙凼和拦水坝的建设位置和数量;S2,建设沉沙凼:选择上下级沟渠交结处,根据10年中单日24h内最大降雨量和原有排水沟的形状;S3,建设拦水坝:根据沟渠长度和径流量情况布设拦水坝;S4,制造生态浮床:包括床体,床体开有贯穿的种植槽,种植槽侧壁开有卡槽,卡槽内设有将种植槽封闭的泡沫块,泡沫块中开有种植孔,种植孔内种植挺水植物;当沟渠宽度小于1m时,种植孔内设有框架,框架内部布设有尼龙网,尼龙网的空隙内扦插有漂浮植物;上述植物均用于净化强富集水中NP污染物。
The invention belongs to the technical field of farmland non-point source control, and aims at the problems of difficulty in implementation and low maintenance efficiency in the prior art, and proposes an ecological graded interception and control method for hardened ditches in hilly and mountainous areas. and the construction location and quantity of the dams; S2, construction of the sinking dam: select the junction of the upper and lower ditches, according to the maximum rainfall within 24 hours in a single day in 10 years and the shape of the original drainage ditch; S3, construction of the dam: according to the ditch Arrange dams according to the length and runoff; S4, manufacturing ecological floating bed: including bed body, the bed body is provided with a planting groove that runs through, a clamping groove is formed on the side wall of the planting groove, and a foam block that closes the planting groove is arranged in the clamping groove. There are planting holes in the foam blocks, and emergent plants are planted in the planting holes; when the width of the ditch is less than 1m, a frame is arranged in the planting hole, a nylon mesh is arranged inside the frame, and floating plants are inserted into the gaps of the nylon mesh; the above plants are all Used to purify NP pollutants in strongly enriched water.
Description
技术领域technical field
本发明属于农田面源控制技术领域,具体涉及一种丘陵山区硬化沟渠生态分级拦截阻控方法。The invention belongs to the technical field of farmland non-point source control, and in particular relates to a method for ecological graded interception and control of hardened ditches in hilly and mountainous areas.
背景技术Background technique
随着世界工业化的飞速发展和农业集约化程度的进一步提高,控制和降低面源污染已经成为环境治理领域面临的主要问题。我国作为农业生产大国,农业面源污已经占面源污染总量的60%以上,导致流域水环境和水资源的恶化,并严重威胁到人们赖以生存的淡水资源。With the rapid development of world industrialization and the further improvement of agricultural intensification, controlling and reducing non-point source pollution has become a major problem in the field of environmental governance. As a major agricultural producing country, agricultural non-point source pollution has accounted for more than 60% of the total non-point source pollution, which leads to the deterioration of the water environment and water resources in the basin, and seriously threatens the freshwater resources that people rely on.
目前,农业面源污染已经成为我国河湖污染的第一大污染源,对生态系统功能、人类健康和经济发展等造成了严重的后果。农业面源污染具有随机性大、时空范围广、潜伏周期长、成因复杂等特点,使其近年来成为国内环境领域普遍关注的一个重要问题。At present, agricultural non-point source pollution has become the largest source of pollution in rivers and lakes in my country, causing serious consequences for ecosystem functions, human health and economic development. Agricultural non-point source pollution has the characteristics of large randomness, wide temporal and spatial scope, long incubation period, and complex causes, which make it an important issue of general concern in the domestic environmental field in recent years.
农业面源污染(ANPSP)是指在农业生产活动中,农田中的泥沙、营养盐、农药及其它污染物,在降水或灌溉过程中,通过农田地表径流、壤中流、农田排水和地下渗漏,进入水体而形成的面源污染。这些污染物主要来源于农田施肥、农药、畜禽及水产养殖和农村居民。农田土壤中未被作物吸收或土壤固定的氮和磷通过人为或自然途径进入水体是引起水体污染的一个因素。Agricultural non-point source pollution (ANPSP) refers to the sediment, nutrients, pesticides and other pollutants in farmland during agricultural production activities, through farmland surface runoff, soil flow, farmland drainage and underground seepage during precipitation or irrigation. Leakage and non-point source pollution caused by entering the water body. These pollutants mainly come from farmland fertilization, pesticides, livestock and aquaculture and rural residents. Nitrogen and phosphorus in farmland soil that are not absorbed by crops or fixed by soil enter water bodies through human or natural routes, which is a factor that causes water pollution.
生态渠道净化技术是目前广泛使用的一种污染物原位拦截技术,具有布置灵活、维护方便、投资少等优点。目前广泛使用的生态渠道净化方法主要分为两类,一类是生态分级拦截阻控,这种方式是在现有的农田排水沟渠中种植漂浮植物或布设一些净化装置,如生物净化箱等,利用水流通过净化装置时发生的物理化学反应来截留和降低污染物浓度。但由于布设路线长且分散,维护较为困难,有时会由于维护不及时而造成植物腐败后将污染物重新释放到水体中,造成二次污染。另一类方法是在农田排水沟渠中设置集中的生态净化池,这种方式维护较为简单方便,易于实施。但在实施时发现,净化池的容积直接决定了净化效果,占用大量耕地来建设大容量净化池是不合适的。The ecological channel purification technology is a widely used in-situ pollutant interception technology, which has the advantages of flexible layout, convenient maintenance, and low investment. At present, the widely used ecological channel purification methods are mainly divided into two categories. One is ecological hierarchical interception and control. This method is to plant floating plants in the existing farmland drainage ditches or arrange some purification devices, such as biological purification boxes. The physicochemical reactions that occur when the water flows through the purification device are used to trap and reduce the concentration of pollutants. However, due to the long and scattered routes, maintenance is difficult. Sometimes due to untimely maintenance, the plants will decay and the pollutants will be re-released into the water body, causing secondary pollution. Another method is to set up centralized ecological purification pools in farmland drainage ditches. This method is relatively simple and convenient to maintain and easy to implement. However, during the implementation, it was found that the volume of the purification pool directly determines the purification effect, and it is inappropriate to occupy a large amount of cultivated land to build a large-capacity purification pool.
在生态分级拦截阻控中,如何实现沟渠的快速改造和提高维护效率,是亟待现有技术人员进一步进行探究的。In the ecological hierarchical interception and control, how to realize the rapid transformation of ditches and improve the maintenance efficiency is an urgent need for existing technicians to further explore.
发明内容SUMMARY OF THE INVENTION
本发明提供了一种丘陵山区硬化沟渠生态分级拦截阻控方法,用于解决现有技术中,实施困难和维护效率低下的问题。The invention provides an ecological grading interception and control method for hardened ditches in hilly and mountainous areas, which is used to solve the problems of difficulty in implementation and low maintenance efficiency in the prior art.
本发明的基础方案为:一种丘陵山区硬化沟渠生态分级拦截阻控方法,包括以下步骤:The basic scheme of the present invention is: a method for ecological graded interception and control of hardened ditches in hilly and mountainous areas, comprising the following steps:
S1,分级拦截:根据丘陵山区农业生态系统中原有硬化沟渠的分布信息、面源径流污染物的时空变化信息,推算出沉沙凼和拦水坝的建设位置和数量;S1, graded interception: according to the distribution information of the original hardened ditches and the spatiotemporal variation information of non-point source runoff pollutants in the agro-ecosystem in the hills and mountains, calculate the construction location and quantity of the sand sink and the dam;
S2,建设沉沙凼:选择上下级沟渠交结处,提取当地10年中单日24h内最大降雨量信息,结合原有排水沟的形状,推算出最小改造量的沉沙凼形状,保证沉沙凼的进水口底部高度大于或等于出水口底部高度;S2. Construction of the sand sink: Select the junction of the upper and lower ditches, extract the local maximum rainfall information within 24 hours of a single day in the past 10 years, and combine the shape of the original drainage ditch to calculate the shape of the sand sink with the minimum amount of renovation to ensure sand sinking. The bottom height of the water inlet of Taipa is greater than or equal to the bottom height of the water outlet;
S3,建设拦水坝:选择坡度小于5的沟渠,制造高度为30cm的拦截物,所述拦截物具有吸附过滤功能,原则上沟渠每隔20米使用拦截物建造拦水坝;S3, build a dam: select a ditch with a slope less than 5, and make an interceptor with a height of 30cm, and the interceptor has the function of adsorption and filtration. In principle, the ditch uses the interceptor to build a dam every 20 meters;
S4,制造生态浮床:选择合适的轻型生物载体,利用轻型生物载体拼接、组合以及搭建成所需要的面积和几何形状,形成生态浮床;所述生态浮床中设有种植槽,种植槽内植入预设的漂浮载体,漂浮载体上种植经过筛选、驯化过的漂浮植物或挺水植物,所述漂浮植物或挺水植物用于强力吸收水中的NP污染物。S4, manufacturing an ecological floating bed: select a suitable light biological carrier, and use the light biological carrier to splicing, combining and building into the required area and geometric shape to form an ecological floating bed; the ecological floating bed is provided with a planting groove, which is implanted in the planting groove A preset floating carrier, on which screened and domesticated floating plants or emergent plants are planted, and the floating plants or emergent plants are used to strongly absorb NP pollutants in water.
本发明的原理及有益效果为:(1)本方案中,对沉沙凼和拦水坝的建设位置和数量进行了规划,相比于随意设计沉沙凼和拦水坝而言,便于推广,具有一定的标准性;并且在规划时考虑到了原有硬化沟渠的分布和每个沟渠径流污染物的流动情况,在充分考虑到了污染状况,做到沉沙凼和拦水坝距离和数量的灵活变通,同时,还会充分利用现有硬化沟渠进行改造以达到预设标准,从而尽可能的减少预算,避免劳民伤财。The principle and beneficial effects of the present invention are as follows: (1) In this scheme, the construction positions and quantities of the sand sink and the dam are planned. Compared with the random design of the sand sink and the dam, it is easy to promote and has A certain standard; and the distribution of the original hardened ditches and the flow of runoff pollutants in each ditches are considered in the planning, and the pollution conditions are fully considered, so that the distance and number of sand sinks and dams can be flexibly changed. At the same time, it will make full use of the existing hardened ditches for renovation to meet the preset standards, so as to reduce the budget as much as possible and avoid waste of money.
(2)本方案中,采用生态浮床来进行水的净化,相比于现有技术中直接种植而言,本方案更有利于管控植物的多少,便于整个生态浮床数量的调整,种植不同植物的生态浮床之间按照季节进行更替,实现整个生态净化的可控和便于管理;并且采用生态浮床可种植的植物不仅包含漂浮植物还包含了一些挺水植物,用于生态净化的植物种类范围更广,便于整体净化的实行。(2) In this scheme, the ecological floating bed is used to purify water. Compared with direct planting in the prior art, this scheme is more conducive to controlling the number of plants, facilitating the adjustment of the number of the entire ecological floating bed, and planting different plants. The ecological floating beds are replaced according to the seasons to realize the controllability and easy management of the entire ecological purification; and the plants that can be grown using the ecological floating beds include not only floating plants but also some emergent plants, and the range of plants used for ecological purification is wider. , to facilitate the implementation of the overall purification.
(3)本方案中,采用分级的形式,根据具体情形来形成多级的沉沙凼和拦水坝,实现对于整体水质的过滤,保证生态分级的硬化沟渠末端的水质达到预计的水质标准;同时这种多级的形式,也对整个水体的淤泥进行了分级和筛选,将整个水体中的淤泥分摊到每个沉沙凼和拦水坝中,避免水体的堵塞,保证整个硬化沟渠中水流通畅。(3) In this scheme, the form of grading is adopted, and multi-level sand sinking and dams are formed according to the specific situation to realize the filtration of the overall water quality and ensure that the water quality at the end of the ecologically graded hardened ditch reaches the expected water quality standard; This multi-level form also classifies and screens the silt in the entire water body, and distributes the silt in the entire water body to each sand sink and dam to avoid blockage of the water body and ensure smooth water flow in the entire hardened ditch.
进一步,S4中,生态浮床上种植的挺水植物为西北利亚鸢尾、粉花美人蕉和伞草;生态浮床上种植的漂浮植物为狐尾藻和香菇草.Further, in S4, the emergent plants planted on the ecological floating bed were Iris iris, Canna japonica, and Umbrella; the floating plants planted on the ecological floating bed were foxtail algae and shiitake grass.
进一步,硬化沟渠中的植物由人工种植形成,沟中种植空心菜、水芹、香菇草。Further, the plants in the hardened ditch are formed by artificial planting, and water spinach, cress, and shiitake grass are planted in the ditch.
进一步,所有阻控方法中所种植的漂浮植物或挺水植物,根据漂浮植物和挺水植物的物候期进行收割、处置、利用,形成NP元素的循环利用。Further, the floating plants or emergent plants planted in all the resistance and control methods are harvested, disposed of and utilized according to the phenological period of the floating plants and emergent plants to form the recycling of NP elements.
进一步,所述轻型生物载体由紫色泥岩和生物质炭构成,紫色泥岩为主,生物质炭为辅;轻型生物载体根据其吸附情况,进行不定期的回收利用。Further, the light biological carrier is composed of purple mudstone and biomass charcoal, the purple mudstone is the main component, and the biomass charcoal is supplemented; the light biological carrier is recycled from time to time according to its adsorption condition.
本方案中,利用生物质炭吸收水中的细小颗粒,避免水底杂质堆积,提高水质的纯净度。In this scheme, the biomass charcoal is used to absorb fine particles in the water, so as to avoid the accumulation of impurities on the bottom of the water and improve the purity of the water quality.
进一步,S4中,漂浮载体为泡沫块,生态浮床包括床体,床体开有贯穿的种植槽,当沟渠宽度大于1m时,种植槽侧壁开有卡槽,卡槽内设有将种植槽封闭的泡沫块,泡沫块中开有种植孔,种植孔内种植挺水植物的幼苗;当沟渠宽度小于1m时,种植孔内设有框架,框架内部布设有尼龙网,尼龙网的空隙内扦插有漂浮植物的幼苗;Further, in S4, the floating carrier is a foam block, the ecological floating bed includes a bed body, and the bed body is provided with a planting groove running through it. When the width of the groove is greater than 1 m, a clamping groove is formed on the side wall of the planting groove, and the clamping groove is provided with a planting groove. A closed foam block, with a planting hole in the foam block, and seedlings of emerging plants are planted in the planting hole; when the width of the ditch is less than 1m, a frame is arranged in the planting hole, a nylon mesh is arranged inside the frame, and cuttings are inserted into the gaps of the nylon mesh. Seedlings with floating plants;
所述生态浮床上还设有定时器、太阳能电池片、控制器、告警灯、天线;太阳能电池片安装在生态浮床的上壁,用于将太阳能转化为电能进行供电,定时器用于在预设时间到时通过控制器控制告警灯点亮和天线向外界发送更换信息。The ecological floating bed is also provided with a timer, solar cells, a controller, an alarm light, and an antenna; the solar cells are installed on the upper wall of the ecological floating bed for converting solar energy into electrical energy for power supply, and the timer is used for preset When the time is up, the controller controls the warning light to light up and the antenna to send replacement information to the outside world.
本方案中,生态浮床的结构有两种,分别适用于沟渠宽度大于1m的情况和沟渠宽度小于1m的情况。In this scheme, there are two structures of the ecological floating bed, which are respectively suitable for the case where the width of the ditch is greater than 1m and the case where the width of the ditch is less than 1m.
在沟渠宽度大于1m时,生态浮床的体积可以设置得比较大,从而提供足够的空间来种植挺水植物,保证挺水植物的生长。挺水植物种植在种植槽内,在植物净化阶段完成后,可以直接将生态浮床进行更换,在更换时,生态浮床上的挺水植物也随之更换,有利于阶段更替。并且,由于泡沫块通常漂浮在水面上,借助泡沫块的浮力可以避免挺水植物完全沉入水底,提高挺水植物的成活率。When the width of the ditch is greater than 1m, the volume of the ecological floating bed can be set relatively large, thereby providing enough space for planting emergent plants and ensuring the growth of emergent plants. Emergent plants are planted in the planting tank. After the plant purification stage is completed, the ecological floating bed can be directly replaced. During the replacement, the emerging plants on the ecological floating bed are also replaced, which is conducive to stage replacement. In addition, since the foam blocks usually float on the water surface, the buoyancy of the foam blocks can prevent the emergent plants from sinking to the bottom completely and improve the survival rate of the emergent plants.
在沟渠宽度小于1m时,为节约空间,生态浮床通常设置的比较窄小,在生态浮床框体间的尼龙网网孔内种植漂浮植物,便于后续漂浮植物的打捞。When the width of the ditch is less than 1m, in order to save space, the ecological floating bed is usually set relatively narrow, and floating plants are planted in the nylon mesh meshes between the ecological floating bed frames to facilitate subsequent salvage of floating plants.
此外,本方案的生态浮床在投入使用后,定时器就已经启动,在达到预设时间后,控制器通过天线向外发射信号,从而通知远方的监控人员预设时间已到,工作人员赶往现场对生态浮床进行更换时,点亮的告警灯能够及时指明方向。In addition, after the ecological floating bed of this scheme is put into use, the timer has been started. After the preset time is reached, the controller transmits a signal through the antenna to notify the remote monitoring personnel that the preset time has come, and the staff rushes to When the ecological floating bed is replaced on site, the lit warning light can indicate the direction in time.
进一步,所述生态浮床底部设有固定杆和横杆,固定杆顶部与生态浮床底部固接,固定杆底部开有固定孔,横杆中部固接有中心轴,中心轴穿过固定孔,且中心轴与固定孔之间通过滚珠轴承连接,生态浮床上壁还设有旋转电机,旋转电机的端部同轴固设有齿轮,生态浮床还开有限位孔,限位杆竖直穿过限位孔,且限位杆的侧壁设有与齿轮啮合的齿条,限位杆底部铰接横杆的一端,横杆的另一端固接有可与泡沫块相抵的顶杆。Further, the bottom of the ecological floating bed is provided with a fixed rod and a horizontal rod, the top of the fixed rod is fixedly connected with the bottom of the ecological floating bed, the bottom of the fixed rod is provided with a fixed hole, the middle of the horizontal rod is fixed with a central shaft, and the central shaft passes through the fixed hole, and The central shaft and the fixing hole are connected by a ball bearing. The upper wall of the ecological floating bed is also provided with a rotating motor. The end of the rotating motor is coaxially fixed with a gear. The ecological floating bed also has a limit hole, and the limit rod vertically passes through the limiter. The side wall of the limit rod is provided with a rack meshing with the gear, the bottom of the limit rod is hinged to one end of the cross rod, and the other end of the cross rod is fixed with a top rod that can abut against the foam block.
本方案中,旋转电机会带动齿轮旋转,从而使得带齿条的限位杆向下移动,促使横杆摆动,横杆端部的顶杆向上顶起,考虑到泡沫块具有一定的收缩性能,顶杆的顶起会带动泡沫板脱离种植槽,或者直接破坏泡沫板,从而便于更换种植槽中所种的植物。In this solution, the rotating motor will drive the gear to rotate, so that the limit rod with the rack moves downward, causing the cross rod to swing, and the top rod at the end of the cross rod is lifted up. Considering that the foam block has a certain shrinkage performance, The lifting of the ejector rod will drive the foam board out of the planting trough, or directly destroy the foam board, so as to facilitate the replacement of the plants planted in the planting trough.
进一步,所述横杆的侧壁设有刀片。Further, the side wall of the cross bar is provided with a blade.
本方案中,考虑到植物的生长期间,根须生长状况各种各样,很有可能与横杆相铰,从而阻碍横杆的运动,因此,设计刀片在横杆运动期间对阻碍的根须进行切割,保证横杆运动的通畅。In this scheme, considering that the roots grow in various conditions during the growth of the plant, they are likely to be hinged with the crossbar, thereby hindering the movement of the crossbar. Therefore, the blade is designed to prevent the obstructed roots during the movement of the crossbar. Make the cut to ensure the smooth movement of the cross bar.
附图说明Description of drawings
图1为本发明一种丘陵山区硬化沟渠原生态分级拦截阻控方法实施例中生态浮床的结构示意图;1 is a schematic structural diagram of an ecological floating bed in the embodiment of a method for graded interception and resistance control of hardened ditches in hilly and mountainous areas of the present invention;
图2为本发明中沉沙凼的结构图;Fig. 2 is the structure diagram of Shensha Taipa in the present invention;
图3为本发明中拦水坝和沉沙凼分布示意图。Figure 3 is a schematic diagram of the distribution of dams and sand sinks in the present invention.
具体实施方式Detailed ways
下面通过具体实施方式进一步详细的说明:The following is a further detailed description through specific embodiments:
说明书附图中的附图标记包括:生态浮床1、种植槽2、泡沫块3、顶杆4、横杆5、固定杆6、限位杆7、齿轮8。The reference numerals in the accompanying drawings include: ecological floating bed 1 , planting tank 2 , foam block 3 , ejector rod 4 ,
实施例基本如附图1所示:The embodiment is basically as shown in Figure 1:
一种丘陵山区硬化沟渠生态分级拦截阻控方法,包括以下步骤:A method for ecological graded interception and control of hardened ditches in hilly and mountainous areas, comprising the following steps:
S1,分级拦截:根据丘陵山区农业生态系统中原有硬化沟渠的分布信息、面源径流污染物的时空变化信息,推算出沉沙凼和拦水坝的建设位置和数量;S1, graded interception: according to the distribution information of the original hardened ditches and the spatiotemporal variation information of non-point source runoff pollutants in the agro-ecosystem in the hills and mountains, calculate the construction location and quantity of the sand sink and the dam;
请参考图2和图3,S2,建设沉沙凼:选择上下级沟渠交接处,提取当地10年中单日24h内最大降雨量信息,结合原有排水沟的形状,推算出最小改造量的沉沙凼形状,保证沉沙凼的进水口底部高度大于或等于出水口底部高度;Please refer to Fig. 2 and Fig. 3, S2, to build a sand-sinking ditch: select the junction of the upper and lower ditches, extract the local maximum rainfall information within 24 hours of a single day in the past 10 years, and calculate the minimum transformation amount based on the shape of the original drainage ditch. The shape of the sand sink ensures that the bottom height of the water inlet of the sand sink is greater than or equal to the bottom height of the water outlet;
S3,建设拦水坝:选择坡度小于5的沟渠,制造高度为30cm的拦截物,所述拦截物具有吸附过滤功能,沟渠每隔20米使用拦截物建造拦水坝;S3, build a dam: select a ditch with a slope less than 5, and make an interceptor with a height of 30cm, the interceptor has an adsorption and filtering function, and the ditch uses the interceptor to build a dam every 20 meters;
S4,制造生态浮床1:选择合适的轻型生物载体,如板竹和毛竹,利用轻型生物载体拼接、组合以及搭建成所需要的面积和几何形状,形成生态浮床1;S4, manufacturing ecological floating bed 1: select suitable light biological carriers, such as bamboo and moso bamboo, and use light biological carriers to splicing, combining and building into the required area and geometric shape to form ecological floating bed 1;
生态浮床1包括床体,床体开有贯穿的种植槽2,种植槽具有两种设置分别对应沟渠宽度大于1m的情况和沟渠宽度小于1m的情况。沟渠宽度大于1m时生态浮床的结构如图1所示,种植槽2侧壁开有卡槽,卡槽内设有将种植槽2封闭的泡沫块3,泡沫块3中开有种植孔,种植孔内种植挺水植物,挺水植物的根茎允许穿过种植孔伸入到水面中,挺水植物为西北利亚鸢尾、粉花美人蕉和伞草等;当沟渠宽度小于1m时,种植槽2内壁设有环状的金属框架,金属框架内布设有尼龙网,在尼龙网的空隙处扦插有漂浮植物,漂浮植物有狐尾藻和香菇草等。The ecological floating bed 1 includes a bed body, and the bed body is provided with a planting groove 2 therethrough. The planting groove has two settings corresponding to the case where the width of the ditch is greater than 1m and the case where the width of the ditch is less than 1m. When the width of the ditch is greater than 1m, the structure of the ecological floating bed is shown in Figure 1. The side wall of the planting groove 2 is provided with a clamping groove, and the clamping groove is provided with a foam block 3 that closes the planting groove 2. Emergent plants are planted in the hole, and the rhizomes of the emergent plants are allowed to extend into the water surface through the planting hole. The emergent plants are iris, canna and umbrella grass, etc.; when the width of the ditch is less than 1m, the planting groove 2 A ring-shaped metal frame is arranged on the inner wall, a nylon net is arranged inside the metal frame, and floating plants are cut in the gaps of the nylon net.
此外,生态浮床1上还设有定时器、太阳能电池片、控制器、告警灯和天线;太阳能电池片安装在生态浮床1的上壁,用于将太阳能转化为电能进行供电,定时器用于在预设时间到时通过控制器控制告警灯点亮和天线向外界发送更换信息。并且,生态浮床1底部设有固定杆6和横杆5,横杆5的侧壁设有刀片,通过刀片在横杆5运动期间对阻碍的根须进行切割,避免植物根须与横杆5相铰,保证横杆5运动的通畅。固定杆6顶部与生态浮床1底部固接,固定杆6底部开有固定孔,横杆5中部固接有中心轴,中心轴穿过固定孔,且中心轴与固定孔之间通过滚珠轴承连接,生态浮床1上壁还设有旋转电机,旋转电机的端部同轴固设有齿轮8,生态浮床1还开有限位孔,限位杆7竖直穿过限位孔,且限位杆7的侧壁设有与齿轮8啮合的齿条,限位杆7底部铰接横杆5的一端,横杆5的另一端固接有可与泡沫块3相抵的顶杆4。In addition, the ecological floating bed 1 is also provided with a timer, solar cells, a controller, an alarm light and an antenna; the solar cells are installed on the upper wall of the ecological floating bed 1 to convert solar energy into electrical energy for power supply, and the timer is used for When the preset time expires, the controller controls the warning light to light up and the antenna to send replacement information to the outside world. And, the bottom of the ecological floating bed 1 is provided with a fixed
请参考图2,在实施期间,本方案对沉沙凼和拦水坝的建设位置和数量进行了规划,便于推广,具有一定的标准性;在规划时考虑到了原有硬化沟渠的分布和每块沟渠径流污染物的流动情况,在充分考虑到了污染状况,做到沉沙凼和拦水坝距离和数量的灵活变通。同时,充分利用现有硬化沟渠进行改造以达到预设标准,从而尽可能的减少预算。采用分级的形式,根据具体情形来形成多级的沉沙凼和拦水坝,实现对于整体水质的过滤,保证最终所获得的末端水质达到预计的水质标准;同时这种多级的形式,也对整个水体的淤泥进行了分级和筛选,将整个水体中的淤泥分摊到每个沉沙凼和拦水坝中,避免水体的堵塞,保证整个硬化沟渠中水流通畅。Please refer to Figure 2. During the implementation period, the plan has planned the construction location and quantity of the sand dams and dams, which is convenient for promotion and has a certain standard; The flow of runoff pollutants in the ditches has been fully considered, and the distance and number of dams and dams can be adjusted flexibly. At the same time, make full use of the existing hardened ditches to retrofit to preset standards, so as to reduce the budget as much as possible. In the form of grading, multi-level sand sinks and dams are formed according to the specific situation to realize the filtration of the overall water quality and ensure that the final water quality obtained meets the expected water quality standards; at the same time, this multi-level form is also suitable for The silt in the entire water body is graded and screened, and the silt in the entire water body is apportioned to each sand sink and dam to avoid blockage of the water body and ensure smooth water flow in the entire hardened ditch.
生态浮床1来进行水的净化,有利于管控植物的多少,调整整体生态浮床1数量的,按照季节变化调整种有不同植物的生态浮床1。构成生态浮床1的生物质炭吸收水中的细小颗粒,避免水底杂质堆积,提高水质的纯净度。借助泡沫块3的浮力可以避免挺水植物完全沉入水底,借助尼龙网的支持力避免漂浮植物也完全沉入水底,提高种植槽内所种植的植物的成活率。生态浮床1投入使用后,定时器就已经启动,在达到预设时间后,控制器通过天线向外发射信号,从而通知远方的监控人员预设时间已到,工作人员赶往现场对生态浮床1进行更换时,点亮的告警灯能够及时指明方向。The ecological floating bed 1 is used for water purification, which is beneficial to control the number of plants. When adjusting the number of the overall ecological floating bed 1, the ecological floating bed 1 with different plants can be adjusted according to seasonal changes. The biomass charcoal constituting the ecological floating bed 1 absorbs fine particles in the water, avoids the accumulation of impurities on the bottom of the water, and improves the purity of the water quality. With the help of the buoyancy of the foam block 3, the emergent plants can be prevented from completely sinking to the bottom of the water, and the supporting force of the nylon net can prevent the floating plants from completely sinking to the bottom of the water, thereby improving the survival rate of the plants planted in the planting tank. After the ecological floating bed 1 is put into use, the timer has been started. After the preset time is reached, the controller transmits a signal through the antenna to notify the remote monitoring personnel that the preset time has come, and the staff rushes to the scene to monitor the ecological floating bed 1. When the replacement is carried out, the lit warning light can indicate the direction in time.
旋转电机会带动齿轮8旋转,从而使得带齿条的限位杆7向下移动,促使横杆5摆动,横杆5端部的顶杆4向上顶起,考虑到泡沫块3具有一定的收缩性能,顶杆4的顶起会带动泡沫板脱离种植槽2,或者直接破坏泡沫板,从而便于更换种植槽2中所种的植物。The rotating motor will drive the gear 8 to rotate, so that the limit rod 7 with the rack moves downward, causing the
以上所述的仅是本发明的实施例,方案中公知的具体结构及特性等常识在此未作过多描述,所属领域普通技术人员知晓申请日或者优先权日之前发明所属技术领域所有的普通技术知识,能够获知该领域中所有的现有技术,并且具有应用该日期之前常规实验手段的能力,所属领域普通技术人员可以在本申请给出的启示下,结合自身能力完善并实施本方案,一些典型的公知结构或者公知方法不应当成为所属领域普通技术人员实施本申请的障碍。应当指出,对于本领域的技术人员来说,在不脱离本发明结构的前提下,还可以作出若干变形和改进,这些也应该视为本发明的保护范围,这些都不会影响本发明实施的效果和专利的实用性。本申请要求的保护范围应当以其权利要求的内容为准,说明书中的具体实施方式等记载可以用于解释权利要求的内容。The above are only the embodiments of the present invention, and the common knowledge such as the well-known specific structures and characteristics in the scheme has not been described too much here. Those of ordinary skill in the art know that the invention belongs to the technical field before the filing date or the priority date. Technical knowledge, can know all the prior art in this field, and have the ability to apply conventional experimental means before the date, those of ordinary skill in the art can improve and implement this scheme in combination with their own ability under the enlightenment given in this application, Some typical well-known structures or well-known methods should not be an obstacle to those skilled in the art from practicing the present application. It should be pointed out that for those skilled in the art, some modifications and improvements can be made without departing from the structure of the present invention. These should also be regarded as the protection scope of the present invention, and these will not affect the implementation of the present invention. Effectiveness and utility of patents. The scope of protection claimed in this application shall be based on the content of the claims, and the descriptions of the specific implementation manners in the description can be used to interpret the content of the claims.
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Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112939231A (en) * | 2021-02-04 | 2021-06-11 | 福建昱勋建设有限公司 | Landscape ecological floating bed construction method |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2012255276A (en) * | 2011-06-08 | 2012-12-27 | Shimizu Corp | Sand removal method of dam sediment |
CN103183413A (en) * | 2011-12-30 | 2013-07-03 | 中国城市规划设计研究院 | Ecologic purifying system for water |
CN105776736A (en) * | 2016-03-17 | 2016-07-20 | 江西省环境保护科学研究院 | Method for treating agricultural non-point source pollution in hilly areas |
CN106698811A (en) * | 2016-11-25 | 2017-05-24 | 四川君和环保股份有限公司 | Surface runoff pollutant treatment system for small-catchment farmland |
CN107010787A (en) * | 2017-05-15 | 2017-08-04 | 河海大学 | It is a kind of to block the native dirty system of sand setting drop suitable for hills area dyke |
CN107278865A (en) * | 2017-07-28 | 2017-10-24 | 吴慧 | A kind of water plant for ecological water body purification floating bed automates implanted device |
CN210026106U (en) * | 2019-05-27 | 2020-02-07 | 东莞景欣塑胶制品有限公司 | Structure for replacing mold insert through lever pressing plate |
-
2020
- 2020-04-23 CN CN202010329153.6A patent/CN111392871A/en active Pending
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2012255276A (en) * | 2011-06-08 | 2012-12-27 | Shimizu Corp | Sand removal method of dam sediment |
CN103183413A (en) * | 2011-12-30 | 2013-07-03 | 中国城市规划设计研究院 | Ecologic purifying system for water |
CN105776736A (en) * | 2016-03-17 | 2016-07-20 | 江西省环境保护科学研究院 | Method for treating agricultural non-point source pollution in hilly areas |
CN106698811A (en) * | 2016-11-25 | 2017-05-24 | 四川君和环保股份有限公司 | Surface runoff pollutant treatment system for small-catchment farmland |
CN107010787A (en) * | 2017-05-15 | 2017-08-04 | 河海大学 | It is a kind of to block the native dirty system of sand setting drop suitable for hills area dyke |
CN107278865A (en) * | 2017-07-28 | 2017-10-24 | 吴慧 | A kind of water plant for ecological water body purification floating bed automates implanted device |
CN210026106U (en) * | 2019-05-27 | 2020-02-07 | 东莞景欣塑胶制品有限公司 | Structure for replacing mold insert through lever pressing plate |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112939231A (en) * | 2021-02-04 | 2021-06-11 | 福建昱勋建设有限公司 | Landscape ecological floating bed construction method |
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