CN210736329U - A three-dimensional rotating horizontal subsurface artificial wetland device - Google Patents
A three-dimensional rotating horizontal subsurface artificial wetland device Download PDFInfo
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Abstract
Description
技术领域technical field
本发明属于人工湿地领域,尤其涉及一种多层垂向布置的、污水依据重力水平回转流动的立体水平潜流人工湿地装置。The invention belongs to the field of constructed wetlands, and in particular relates to a three-dimensional horizontal submerged flow constructed wetland device with multi-layer vertical arrangement and horizontal rotary flow of sewage according to gravity.
背景技术Background technique
人工湿地通常指经过人工强化措施改造后的湿地系统,应用生态体系中物种共生、物质循环再生原理,按照结构与功能协调原则,促使污水在湿地的基质、植物以及微生物的物理、化学和生物作用下得到净化。Constructed wetlands usually refer to wetland systems transformed by artificial strengthening measures, applying the principles of species symbiosis and material recycling in the ecosystem, and in accordance with the principle of structure and function coordination, to promote the physical, chemical and biological effects of sewage on wetland substrates, plants and microorganisms. to be purified.
人工湿地由围护结构、基质、水生植物、微生物、污水等部分构成。按照进出水布水方式的不同,一般将人工湿地分为表面流人工湿地和潜流人工湿地,其中潜流人工湿地因其具有运行环境良好、污染物净化效能高的特点,因而得到了更为广泛的应用。潜流人工湿地按照内部的水流方向又可分为水平潜流人工湿地和垂直潜流人工湿地,相对垂直潜流人工湿地而言,水平潜流人工湿地内兼具好氧和缺氧环境,具有较好硝化和反硝化性能,故常在污水脱氮过程中得到应用。Constructed wetlands are composed of enclosure structures, substrates, aquatic plants, microorganisms, and sewage. Constructed wetlands are generally divided into surface-flow constructed wetlands and subsurface-flow constructed wetlands according to different ways of distributing water in and out application. According to the internal water flow direction, subsurface constructed wetlands can be divided into horizontal subsurface constructed wetlands and vertical subsurface constructed wetlands. Compared with vertical subsurface constructed wetlands, horizontal subsurface constructed wetlands have both aerobic and anoxic environments, and have better nitrification and reaction conditions. Nitrification performance, so it is often used in the process of sewage denitrification.
人工湿地生物处理技术能够对各种污染物例如氮、磷、悬浮物、有机物、重金属等进行有效的降解和转化。人工湿地系统通过对于自然生境的模拟,提供了生态景观及绿色植物,为野生动物提供了栖息场所,因而展现了良好的生态修复功能。但传统人工湿地的污染物去除负荷较小,往往需要大面积的土地供应以保障废水处理的规模和出水水质。因人工湿地占地面积过大,导致其通常被迫设置于远离人口集聚区的城市郊区。因此,长距离的污水输送,一方面增加了污水收集和排放系统的建设成本,另一方面增加了污水污染地下水的风险。人工湿地远离城区的设置,如考虑人工湿地处理水的回用问题,会使管网的建设成本成倍增加,并且使其作为滨水区亲水性景观功能的发挥受到了较大的限制。因此,提高人工湿地的单位土地面积的污染去除负荷,减小人工湿地的占地面积是推广和发展人工湿地生物处理技术,充分发挥其环境、经济和社会效益的关键所在。Constructed wetland biological treatment technology can effectively degrade and transform various pollutants such as nitrogen, phosphorus, suspended solids, organic matter, heavy metals, etc. By simulating the natural habitat, the artificial wetland system provides ecological landscape and green plants, and provides a habitat for wild animals, thus showing a good ecological restoration function. However, the pollutant removal load of traditional constructed wetlands is small, and a large area of land supply is often required to ensure the scale of wastewater treatment and effluent quality. Due to the large area of constructed wetlands, they are usually forced to be located in urban suburbs far away from population agglomeration areas. Therefore, long-distance sewage transportation increases the construction cost of sewage collection and discharge systems on the one hand, and increases the risk of sewage contamination of groundwater on the other hand. Constructed wetlands are set far away from urban areas, such as considering the reuse of treated water from constructed wetlands, which will double the construction cost of the pipeline network and greatly limit its function as a hydrophilic landscape in the waterfront area. Therefore, improving the pollution removal load per unit land area of constructed wetlands and reducing the area of constructed wetlands are the keys to popularize and develop the biological treatment technology of constructed wetlands and give full play to its environmental, economic and social benefits.
发明内容SUMMARY OF THE INVENTION
本发明是针对现有人工湿地生物处理技术存在的上述问题,提供一种耐冲击负荷、具有较高脱氮效能、较高单位土地面积的污染物去除负荷,因而能够减少其占地面积的新型水平潜流人工湿地装置。The present invention is aimed at the above-mentioned problems existing in the existing constructed wetland biological treatment technology, and provides a new type of pollutant removal load that is resistant to impact load, has higher denitrification efficiency, and higher unit land area, thereby reducing its floor space. Horizontal subsurface flow constructed wetland device.
本发明的目的可通过下列技术方案来实现。The object of the present invention can be achieved through the following technical solutions.
一种立体回转水平潜流人工湿地装置,可以分成上中下三层、左右对称两单元,包括上部右侧的上层人工湿地右单元、上部左侧的上层人工湿地左单元、中部右侧的中层人工湿地右单元、中部左侧的中层人工湿地左单元、下部右侧的下层人工湿地右单元、下部左侧的下层人工湿地左单元、人工湿地左右单元之间的左立柱、中立柱、右立柱。上层人工湿地右单元为上敞口的中空长方体结构。上右过水孔设置于上右过水隔板上部。上右单元进水管水平设置于上右单元左挡板左侧中心部位,右单元上中连接管上端水平短管的左端与上右单元右挡板中心连接,中右单元进水管水平设置于中右单元右挡板右侧下部中心位置,右单元上中连接管下端水平短管的左端与中右单元右挡板上部中心连接;右单元中下连接管上端水平短管的右端与中右单元左挡板的中心连接;下右单元进水管水平设置于下右单元左挡板的左侧下部中心位置;右单元中下连接管下端水平短管与下右单元左挡板上部左侧中心连接;下右单元出水管的水平短管的左端与下右单元右挡板的右侧中心连接。A three-dimensional rotating horizontal subsurface flow constructed wetland device can be divided into upper, middle and lower layers and two symmetrical units, including the upper constructed wetland right unit on the upper right side, the upper constructed wetland left unit on the upper left side, and the middle artificial wetland on the right side of the middle. The right unit of the wetland, the left unit of the middle constructed wetland on the left side of the middle, the right unit of the lower constructed wetland on the right side of the lower part, the left unit of the lower constructed wetland on the left side of the lower part, the left column, the middle column and the right column between the left and right units of the constructed wetland. The right unit of the upper constructed wetland is a hollow cuboid structure with an upper opening. The upper right water passage hole is arranged on the upper part of the upper right water passage partition plate. The water inlet pipe of the upper right unit is horizontally arranged at the left central part of the left baffle of the upper right unit, the left end of the horizontal short pipe at the upper end of the upper middle connecting pipe of the right unit is connected with the center of the right baffle of the upper right unit, and the water inlet pipe of the middle right unit is arranged horizontally in the middle The center position of the lower part of the right side of the right baffle of the right unit, the left end of the horizontal short pipe at the lower end of the upper middle connecting pipe of the right unit is connected with the upper center of the right baffle of the middle right unit; The center of the left baffle is connected; the water inlet pipe of the lower right unit is horizontally arranged at the lower center of the left side of the left baffle of the lower right unit; the horizontal short pipe at the lower end of the middle and lower connecting pipe of the right unit is connected with the upper left center of the left baffle of the lower right unit ; The left end of the horizontal short pipe of the water outlet pipe of the lower right unit is connected to the right center of the right baffle plate of the lower right unit.
所述的上层人工湿地右单元由上右单元前挡板、上右单元后挡板、上右单元左挡板、上右单元右挡板和上右单元底板围挡组成。The upper right unit of the constructed wetland is composed of the front baffle of the upper right unit, the rear baffle of the upper right unit, the left baffle of the upper right unit, the right baffle of the upper right unit and the bottom plate of the upper right unit.
所述的上右单元前挡板、上右单元后挡板、上右单元左挡板、上右单元右挡板和上右单元底板均为矩形平面薄板。The front baffle of the upper right unit, the rear baffle of the upper right unit, the left baffle of the upper right unit, the right baffle of the upper right unit and the bottom plate of the upper right unit are all rectangular flat thin plates.
所述上右过水孔均匀分布于上右过水隔板的上部,共三排,上排的上右过水孔距上右过水隔板上沿的中心距为上右过水隔板高度的1/4。且各排相邻上右过水孔之间的净距为其直径的1.5倍,上右过水孔的开孔总面积约占上右过水隔板面积的4%~6%。The upper and right water passage holes are evenly distributed on the upper part of the upper and right water passage baffles, and there are three rows in total. 1/4 of the height. And the clear distance between the adjacent upper and right water passages in each row is 1.5 times its diameter, and the total opening area of the upper and right water passages accounts for about 4% to 6% of the area of the upper and right water passages.
所述上右过水隔板共5块,左右两端上右过水隔板与相邻的上右单元左挡板、上右单元右挡板之间的区域分别为上右单元进水配水区和上右单元出水配水区,上右单元进水配水区和上右单元出水配水区的长度约为上层人工湿地右单元长度的1/10。相邻两块上右过水隔板之间的区域为上右单元水处理区,共4个上右单元水处理区,单个上右单元水处理区的长度为上层人工湿地右单元长度的1/5。The upper and right water-passing baffles are 5 pieces in total, and the areas between the upper-right water-passing baffles at the left and right ends and the adjacent upper-right unit left baffle and upper-right unit right baffle are respectively the upper and right unit water inlet and water distribution. The length of the upper right unit inlet water distribution area and the upper right unit outlet water distribution area is about 1/10 of the length of the upper constructed wetland right unit. The area between two adjacent upper-right water-passing partitions is the upper-right unit water treatment area. There are 4 upper-right unit water treatment areas in total. The length of a single upper-right unit water treatment area is 1 of the length of the upper-layer constructed wetland right unit. /5.
所述的右单元上中连接管、右单元中下连接管分别为“]”型、“[”型的两端敞口的圆柱形中空管道,其高度为上层人工湿地右单元1高度的1.0倍~1.2倍。右单元上中连接管、右单元中下连接管上下水平段长度相等;下右单元出水管为“L”型的两端敞口的圆柱形中空管道;下右单元出水管水平短管和垂直短管长度相等。本发明中各种管道的直径均与上右单元进水管相等。The upper and middle connecting pipes of the right unit and the middle and lower connecting pipes of the right unit are respectively “]” and “[”-shaped cylindrical hollow pipes with open ends, and their height is 1.0 of the height of the
所述的上层人工湿地左单元、中层人工湿地右单元、中层人工湿地左单元、下层人工湿地右单元、下层人工湿地左单元的箱体结构与尺寸均与上层人工湿地右单元一致,且上层人工湿地右单元与上层人工湿地左单元、中层人工湿地右单元与中层人工湿地左单元、下层人工湿地右单元与下层人工湿地左单元分别关于左立柱、中立柱、右立柱垂直中线形成的面构成前后对称关系。上层人工湿地右单元与中层人工湿地右单元、中层人工湿地右单元与下层人工湿地右单元之间的净距以及上层人工湿地左单元与中层人工湿地左单元、中层人工湿地左单元与下层人工湿地左单元之间的净距均相等,且为人工湿地单元高度的1.2倍~1.5倍。The upper constructed wetland left unit, the middle constructed wetland right unit, the middle constructed wetland left unit, the lower constructed wetland right unit, and the lower constructed wetland left unit have the same box structure and size as the upper constructed wetland right unit, and the upper constructed wetland The right unit of the wetland and the left unit of the upper constructed wetland, the right unit of the middle constructed wetland and the left unit of the middle constructed wetland, and the right unit of the lower constructed wetland and the left unit of the lower constructed wetland respectively constitute the front and rear of the plane formed by the vertical center line of the left column, the middle column and the right column. Symmetrical relationship. The clear distance between the upper constructed wetland right unit and the middle constructed wetland right unit, the middle constructed wetland right unit and the lower constructed wetland right unit, the upper constructed wetland left unit and the middle constructed wetland left unit, the middle constructed wetland left unit and the lower constructed wetland The clear distances between the left units are all equal, and are 1.2 to 1.5 times the height of the constructed wetland unit.
所述左立柱、中立柱和右立柱均为正方形的空心立柱,3根立柱分别装配于三层左右人工湿地单元之间形成的空隙的左端、中部和右端。各立柱的前后外壁与各单元的后挡板紧密贴合在一起。相邻立柱之间的中心距为人工湿地单元长度的2/5,左立柱和右立柱分别与人工湿地单元左右外壁的中心距为人工湿地单元长度的1/10。左立柱、中立柱和右立柱上设置有三角支撑分别支撑每层人工湿地单元,每个人工湿地单元共设置3个三角支撑,分别与左立柱、中立柱和右立柱单侧外壁紧密连接,共有18个。The left column, the middle column and the right column are all square hollow columns, and the three columns are respectively assembled at the left, middle and right ends of the gaps formed between the left and right constructed wetland units on the three floors. The front and rear outer walls of each upright are closely fitted with the rear baffles of each unit. The center distance between adjacent columns is 2/5 of the length of the constructed wetland unit, and the center distance between the left and right columns and the left and right outer walls of the constructed wetland unit respectively is 1/10 of the length of the constructed wetland unit. The left column, the middle column and the right column are provided with triangular supports to support the constructed wetland units on each floor respectively. Each constructed wetland unit is provided with 3 triangular supports, which are respectively closely connected with the one-sided outer wall of the left column, the middle column and the right column. 18 pcs.
与现有技术相比,本发明具有以下优点:(1)碳源均衡,耐冲击负荷。多点进水能够保证进水中携带的溶解氧和碳源在装置中较为均衡地分配,从而能够实现溶解氧供应与污染物负荷的较好匹配,因而可实现较好的硝化反应和反硝化反应;同时,可有效平抑进水水质变化对于人工湿地系统的冲击。(2)植物生物量显著增加。植物在人工湿地污染物去除过程中具有极为关键的作用。本发明的垂向多层设计,改变了传统人工湿地水生植物单层种植的固有模式,实现了植物生物量的多层积累,有利于更好地发挥植物在人工湿地污染物去除中的生态优势。(3)占地面积少。本发明的装置为立体垂直回转结构,多层串联,在提高了单位土地面积上的污染负荷和去除负荷的同时减少了土地占用面积。(4)减少管网建设成本,降低地下水污染风险。利用本发明具有占地面积较少的优势,可将本发明布置在污染源附近,能够较好地实现污水的源头处理,不但减少了污水收集管网的长距离输送,同时也避免了回用管网的大规模铺设,降低管网建设成本的同时也降低了污水渗漏对于地下水的污染风险。(5)充分呈现了生态景观功能。利用本发明占地面积较少、布置机动灵活的特性,可将其设置在居民集聚区附近,能够充分实现人工湿地的环境和社会效益。Compared with the prior art, the present invention has the following advantages: (1) The carbon source is balanced and the impact load is resistant. Multi-point inflow can ensure that the dissolved oxygen and carbon sources carried in the influent are distributed evenly in the device, so as to achieve a better match between the dissolved oxygen supply and the pollutant load, and thus achieve better nitrification reaction and denitrification. At the same time, it can effectively suppress the impact of changes in influent water quality on the constructed wetland system. (2) Plant biomass increased significantly. Plants play a crucial role in the removal of pollutants from constructed wetlands. The vertical multi-layer design of the present invention changes the inherent mode of single-layer planting of aquatic plants in traditional constructed wetlands, realizes multi-layer accumulation of plant biomass, and is conducive to better exerting the ecological advantages of plants in the removal of pollutants in constructed wetlands . (3) Small footprint. The device of the present invention is a three-dimensional vertical rotary structure, with multiple layers connected in series, which reduces the land occupation area while increasing the pollution load on a unit land area and removing the load. (4) Reduce the cost of pipeline network construction and reduce the risk of groundwater pollution. Using the present invention has the advantage of less floor space, the present invention can be arranged near the pollution source, and the source treatment of sewage can be better realized, which not only reduces the long-distance transportation of the sewage collection pipe network, but also avoids the reuse of pipes. The large-scale laying of the network reduces the construction cost of the pipeline network and also reduces the pollution risk of sewage leakage to groundwater. (5) The ecological landscape function is fully presented. Taking advantage of the characteristics of the invention with less floor space and flexible arrangement, it can be arranged near the residential area, and the environmental and social benefits of the constructed wetland can be fully realized.
附图说明Description of drawings
图1为本发明一种立体回转水平潜流人工湿地装置的俯视图。FIG. 1 is a top view of a three-dimensional rotating horizontal subsurface constructed wetland device according to the present invention.
图2为本发明一种立体回转水平潜流人工湿地装置的正视图。FIG. 2 is a front view of a three-dimensional rotating horizontal subsurface constructed wetland device of the present invention.
图3为本发明一种立体回转水平潜流人工湿地装置的侧视图。3 is a side view of a three-dimensional rotating horizontal subsurface constructed wetland device of the present invention.
图4为图1的Ⅰ-Ⅰ剖视图。Fig. 4 is a sectional view taken along line I-I of Fig. 1 .
图5为图1的Ⅱ-Ⅱ剖视图。FIG. 5 is a sectional view taken along line II-II of FIG. 1 .
图6为图5的A点大样图。FIG. 6 is a large sample view of point A in FIG. 5 .
具体实施方式Detailed ways
以下是本发明的具体实施例并结合附图1-6,对本发明的技术方案作进一步的描述,但本发明并不限于这些实施例。The following are specific embodiments of the present invention and the technical solutions of the present invention are further described with reference to the accompanying drawings 1-6, but the present invention is not limited to these embodiments.
一种立体回转水平潜流人工湿地装置,可以分成上中下三层、左右对称两单元。包括位于上部右侧的上层人工湿地右单元1、位于上部左侧的上层人工湿地左单元2、位于中部右侧的中层人工湿地右单元3、位于中部左侧的中层人工湿地左单元4、位于下部右侧的下层人工湿地右单元5、位于下部左侧的下层人工湿地左单元6、位于人工湿地左右单元之间的左立柱7、中立柱8、右立柱9。The utility model relates to a three-dimensional rotating horizontal subsurface constructed wetland device, which can be divided into upper, middle and lower layers and two symmetrical units. It includes the upper constructed
所述的上层人工湿地右单元1包括上右单元前挡板11、上右单元后挡板12、上右单元左挡板13、上右单元右挡板14、上右单元底板15、上右单元进水管16、右单元上中连接管17、上右单元过水隔板18。The upper constructed
上层人工湿地右单元1为上敞口的中空长方体,由上右单元前挡板11、上右单元后挡板12、上右单元左挡板13、上右单元右挡板14和上右单元底板15围挡而成,各挡板之间以及各挡板与底板之间均为紧密连接,各挡板和底板均为矩形平面薄板。The
所述的上右单元进水管16为两端敞口的圆柱形中空管道,水平设置于上右单元左挡板13左侧中心部位,其右端与上右单元左挡板13中心设置的相同直径的圆形孔洞紧密连接。The upper right unit
所述的右单元上中连接管17为“]”型的两端敞口的圆柱形中空管道,由两个90°弯头、两段水平短管和一段垂直短管连接组成,其高度为上层人工湿地右单元1高度的1.0倍~1.2倍。右单元上中连接管17上下水平段长度相等,且为垂直段部分长度的0.5倍,其垂直段部分长度为上层人工湿地右单元1高度的1倍。右单元上中连接管17上端水平短管的左端与上右单元右挡板14中心的相同直径的圆形开孔紧密连接。The connecting
所述的上右过水隔板18为矩形平面薄板,共有5块,垂直设置于上层人工湿地右单元1内。上右过水隔板18的上沿与上层人工湿地右单元1的上沿平齐,每块上右过水隔板18均与上右单元前挡板11、上右单元后挡板12、上右单元底板15均紧密连接。左右两端上右过水隔板18与相邻的上右单元左挡板13、上右单元右挡板14之间的区域分别为上右单元进水配水区101和上右单元出水配水区102,上右单元进水配水区101和上右单元出水配水区102的长度约为上层人工湿地右单元1长度的1/10。相邻两块上右过水隔板18之间的区域为上右单元水处理区103,共4个上右单元水处理区103,单个上右单元水处理区103的长度为上层人工湿地右单元1长度的1/5。上右过水隔板18上部设置有上右过水孔181。The upper and right water-passing
所述的上右过水孔181为圆形孔洞,均匀分布于上右过水隔板18的上部,共三排,上排的上右过水孔181距上右过水隔板18上沿的中心距为上右过水隔板18高度的1/4。且各排相邻上右过水孔181之间的净距为其直径的1.5倍,上右过水孔181的开孔总面积约占上右过水隔板18面积的4%~6%。The upper right
所述的上层人工湿地左单元2、中层人工湿地右单元3、中层人工湿地左单元4、下层人工湿地右单元5、下层人工湿地左单元6的箱体结构与尺寸均与上层人工湿地右单元1一致,且上层人工湿地右单元1与上层人工湿地左单元2、中层人工湿地右单元3与中层人工湿地左单元4、下层人工湿地右单元5与下层人工湿地左单元6分别关于左立柱7、中立柱8、右立柱9垂直中线形成的面构成前后对称关系。上层人工湿地右单元1与中层人工湿地右单元3、中层人工湿地右单元3与下层人工湿地右单元5之间的净距以及上层人工湿地左单元2与中层人工湿地左单元4、中层人工湿地左单元4与下层人工湿地左单元6之间的净距均相等,且为人工湿地单元高度的1.2倍~1.5倍。The upper constructed wetland left
所述的中右单元进水管36为两端敞口的圆柱形中空管道,水平设置于中右单元右挡板34右侧下部中心位置,其左端与中右单元右挡板34中心设置的相同直径的圆形孔洞紧密连接。中右单元进水管36的管中线与中右单元右挡板34下沿的距离为中右单元右挡板34高度的1/4。The middle-right unit
所述的右单元上中连接管17下端水平短管与中右单元右挡板34上部中心的相同直径的圆形开孔紧密连接,下端水平段的管中线与中右单元右挡板34上沿的距离为中右单元右挡板34高度的1/4。The horizontal short tube at the lower end of the upper-
所述的右单元中下连接管37 “[”型的两端敞口的圆柱形中空管道,由两个90°弯头、两段水平短管和一段垂直短管连接组成,其高度为上层人工湿地右单元1高度的1.5倍~2倍。右单元中下连接管37上下水平段长度相等,且为垂直段部分长度的0.5倍,其垂直段部分长度为上层人工湿地右单元1高度的1倍。右单元中下连接管37上端水平短管的右端与中右单元左挡板33的中心的开孔紧密连接。The middle and lower connecting
所述的下右单元进水管56为两端敞口的圆柱形中空管道,水平设置于下右单元左挡板53的左侧下部中心位置,其右端与下右单元左挡板53中心设置的相同直径的圆形孔洞紧密连接。下右单元进水管56的管中线与下右单元左挡板53下沿的距离为下右单元左挡板53高度的1/4。The lower right unit
所述的右单元中下连接管37下端水平短管与下右单元左挡板53上部左侧中心的开孔紧密连接,下端水平段的管中线与下右单元左挡板53上沿的距离为下右单元左挡板53高度的1/4。The horizontal short tube at the lower end of the middle and lower connecting
所述的下右单元出水管57 为“L”型的两端敞口的圆柱形中空管道,由一个90°弯头、一段水平短管和一段垂直短管连接组成。下右单元出水管57水平短管和垂直短管长度相等。下右单元出水管57的水平短管的左端与下右单元右挡板54的右侧中心的开孔紧密连接。The lower right unit
本发明中各种管道的直径均与上右单元进水管16相等。The diameters of various pipes in the present invention are all equal to the
所述的左立柱7、中立柱8和右立柱9均为正方形的空心立柱,3根立柱分别装配于三层左右人工湿地单元之间形成的空隙的左端、中部和右端。各立柱的前后外壁与各单元的后挡板紧密贴合在一起。相邻立柱之间的中心距为人工湿地单元长度的2/5,左立柱7和右立柱9分别与人工湿地单元左右外壁的中心距为人工湿地单元长度的1/10。左立柱7、中立柱8和右立柱9的顶端与上层人工湿地右单元1的上沿平齐。左立柱7、中立柱8和右立柱9的底端延伸出下层人工湿地右单元5下沿的尺寸为下层人工湿地右单元5高度的2倍。左立柱7、中立柱8和右立柱9的底端分别与左垫板71、中垫板81、右垫板91的中心部位紧密连接,其作用是分散各个立柱传导的压力,防止各个立柱的沉降。所述的左垫板71、中垫板81、右垫板91均为正方形薄板,其边长为立柱边长的5倍。左立柱7、中立柱8和右立柱9上设置有三角支撑789分别支撑每层人工湿地单元,每个人工湿地单元共设置3个三角支撑789,分别与左立柱7、中立柱8和右立柱9单侧外壁紧密连接,共有18个。The
另外,本发明的主体(上层人工湿地右单元1、上层人工湿地左单元2、中层人工湿地右单元3、中层人工湿地左单元4、下层人工湿地右单元5、下层人工湿地左单元6)可由8mm ~10mm厚的PE、PVC或PPP材料模压制成,也可由1mm~3mm厚的不锈钢板钣金焊接制成,左立柱7、中立柱8、右立柱9、左垫板71、中垫板81、右垫板91、三角支撑789等部件可由钢或不锈钢制成。各人工湿地单元箱体的长度均为2000mm~2200mm、宽度均为400mm~500mm、高度均为400mm~500mm。过水孔181的直径为6mm~8mm。上右单元进水管16、中右单元进水管36、下右单元进水管56的直径均为100mm,长度为200mm~300mm。右单元上中连接管17、右单元中下连接管37的水平段管长度均为200mm~300mm,直径均为100mm。下右单元出水管57的水平短管和垂直短管长度均为200mm~300mm。左立柱7、中立柱8和右立柱9的外边长均为100mm,高度在2700mm~2900mm之间。左垫板71、中垫板81、右垫板91厚度为5mm,边长为500mm。In addition, the main body of the present invention (the upper constructed
本发明的工作原理是:The working principle of the present invention is:
放置场所。本发明占地面积少,适用于对于人们日常生活污水的处理,可放置于街道、居民小区、河道边岸等场所。污水经本发明处理达到一定的出水水质标准后,可以就近排放或回用于冲厕、浇洒道路、洗车、建筑用水等。Place the place. The invention occupies less area, is suitable for the treatment of people's daily life sewage, and can be placed in places such as streets, residential quarters, river banks and the like. After the sewage is treated by the present invention and reaches a certain effluent quality standard, it can be discharged nearby or reused for flushing toilets, watering roads, washing cars, building water and the like.
填充基质。基质为人工湿地内微生物的生命活动提供微环境,同时也能够对某些污染物起到物理吸附作用。本发明组装完成后,直接填充基质于人工湿地单元的箱体内。基质的填充高度以350~450mm为宜。根据处理目标污染物的不同,可填充不同类型或不同尺寸的基质或基质组合,如水处理微电解铁碳球、页岩陶粒、卵石、沸石、生物炭等。Fill the matrix. The matrix provides a microenvironment for the life activities of microorganisms in the constructed wetland, and can also play a role in physical adsorption of certain pollutants. After the assembly of the present invention is completed, the matrix is directly filled in the box of the constructed wetland unit. The filling height of the matrix should be 350~450mm. Depending on the target pollutants to be treated, different types or sizes of substrates or combinations of substrates can be filled, such as water treatment micro-electrolysis iron carbon balls, shale ceramsite, pebbles, zeolite, biochar, etc.
栽种水生植物。完成基质填充后进行植物栽种。植物应栽种在水处理区内,植物优先选择本土、生命力强、对环境适应性好的品种。适当选择根系发达、生物量大的水生植物,更有利于污染物的去除。植物移栽度过缓苗期后,可配制营养液,促进植物的生长。Plant aquatic plants. Plants are planted after the substrate filling is completed. Plants should be planted in the water treatment area, and the plants should preferably choose native varieties with strong vitality and good adaptability to the environment. Appropriate selection of aquatic plants with developed root systems and large biomass is more conducive to the removal of pollutants. After the plant is transplanted to the slow seedling stage, a nutrient solution can be prepared to promote the growth of the plant.
启动。待植物生长稳定后,可由上右单元进水管16、中右单元进水管36、下右单元进水管56间歇性注入经预处理后的污水,直至按照正常水量进水。同时监测进出水水质。待出水水质稳定后可认为人工湿地完成启动阶段。如污水进水压力不能保证提升至上右单元进水管16、中右单元进水管36、下右单元进水管56,需要配置进水提升泵以满足进水的水压要求。start up. After the plants grow stably, the pretreated sewage can be injected intermittently through the upper right unit
运行。污水由上右单元进水管16进入上层人工湿地右单元1前端的上右单元进水配水区101,当进水水位分别超出上右过水隔板18的上右过水孔181的高度时,进入上右单元水处理区103内,污水中的污染物质在经过4个连续上右单元水处理区103内经过植物、微生物、基质等的物理、化学和生物联合作用后,进入上层人工湿地右单元1尾端的上右单元出水配水区102,经上右单元出水配水区102进行水力条件调配后,流出上层人工湿地右单元1,通过右单元上中连接管17流入中右单元进水配水区301,并在中层人工湿地右单元3中重复在上层人工湿地右单元1的处理流程。同理,经中层人工湿地右单元3处理后的污水经经右单元中下连接管37 流入下层人工湿地右单元5,经下层人工湿地右单元5处理后,经下右单元出水管57排出系统。需要说明的是,可以根据进水水质的变化程度、以及污水去除有机物以及脱氮反硝化过程中对于碳源需求的不同启用中右单元进水管36、下右单元进水管56,即可从上右单元进水管16、中右单元进水管36和下右单元进水管56同时或分别进水,以达到平衡污染负荷、合理分配碳源,提高系统耐冲击负荷和脱氮效能的作用。同时,可以根据出水水质标准的不同,结合环境温度的变化,通过调整进水流量,改变水力停留时间,达到改变污染负荷的目的,从而使出水水质满足要求。run. Sewage enters the upper right unit inlet
本文中所描述的具体实施例仅仅是对本发明的精神实质作举例说明。本发明所属技术领域的技术人员可以对所描述的具体实施例做各种各样的修改或补充或采用类似的方式替代,但并不会偏离本发明的精神或者超越所附权利要求书所定义的范围。The specific embodiments described herein are merely illustrative of the spirit of the invention. Those skilled in the art to which the present invention pertains can make various modifications or additions to the described specific embodiments or substitute in similar manners, but will not deviate from the spirit of the present invention or go beyond the definitions of the appended claims range.
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