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CN116655117A - A method for constructing water ecosystem balance - Google Patents

A method for constructing water ecosystem balance Download PDF

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CN116655117A
CN116655117A CN202310530386.6A CN202310530386A CN116655117A CN 116655117 A CN116655117 A CN 116655117A CN 202310530386 A CN202310530386 A CN 202310530386A CN 116655117 A CN116655117 A CN 116655117A
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刘春霄
季同利
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Ningxia Xiaoxia Ecological Technology Co ltd
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/008Sludge treatment by fixation or solidification
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/02Biological treatment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • C02F3/322Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae use of algae
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • C02F3/327Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae characterised by animals and plants
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/348Biological treatment of water, waste water, or sewage characterised by the microorganisms used characterised by the way or the form in which the microorganisms are added or dosed
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/007Contaminated open waterways, rivers, lakes or ponds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection

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  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Biotechnology (AREA)
  • Botany (AREA)
  • Health & Medical Sciences (AREA)
  • Molecular Biology (AREA)
  • Sewage (AREA)

Abstract

本申请公开了一种水生态系统平衡构建方法,包括污水来源阻断、水源预处理、底部淤泥处置、底质改良、沉水植物群落构建,水生群落构建、微生物群落构建、后期管护,污水来源阻断采用围网隔断技术,水源预处理采用湿地预净化技术,湿地预净化技术具体内容为,在经围网隔断技术处理后的污水流向水生态系统构建区域的前段设置的前置库内。通过对该地区生态环境、气象、水文、地质资料的收集,结合原位水生态系统平衡构建技术特点,论证了该技术在该地区的适用性,通过引进先进的地表水质净化技术,有效减缓现状生态环境的恶化,通过工程实践,逐步形成适合当地特点的生态工程修复技术,在区域内广泛推广,达到生态环境全面修复的目的。

This application discloses a method for constructing a water ecosystem balance, including blocking sewage sources, water source pretreatment, bottom sludge disposal, substrate improvement, submerged plant community construction, aquatic community construction, microbial community construction, post-management and protection, sewage Seine isolation technology is used for source blocking, and wetland pre-purification technology is used for water source pretreatment. The specific content of wetland pre-purification technology is that the sewage treated by the seine isolation technology flows to the front-end reservoir set up in the front section of the water ecosystem construction area. . Through the collection of ecological environment, meteorology, hydrology, and geological data of the area, combined with the technical characteristics of in-situ water ecosystem balance construction, the applicability of this technology in this area was demonstrated, and the current situation was effectively alleviated by introducing advanced surface water purification technology. For the deterioration of the ecological environment, through engineering practice, ecological engineering restoration technologies suitable for local characteristics are gradually formed, and widely promoted in the region to achieve the purpose of comprehensive restoration of the ecological environment.

Description

一种水生态系统平衡构建方法A method for constructing water ecosystem balance

技术领域technical field

本申请涉及水生态构建领域,尤其涉及水生态系统平衡构建方法。The present application relates to the field of water ecological construction, in particular to a method for constructing a water ecological system balance.

背景技术Background technique

我国某地区因蒸发强烈,气候干燥,日照充足,时间长,年降雨量72-215mm,年蒸发量1312-1924mm,年降雨量远远低于年蒸发量,使得湖库中水体因蒸发导致盐度上升或沉积后底泥盐碱化,为平衡水量蒸发,满足农业灌溉的需求,引黄灌区200余条排水沟,同时接纳了大量农田化肥、农药,氨氮、总磷、COD等污染物浓度严重超标,排水沟水质经检测TN浓度为0.17-8.72mg/L,TP浓度为0.14-1.02mg/L,面临水土的盐碱化和农业面源污染双重威胁,针对上述问题,设计一种水生态系统平衡构建方法。Due to strong evaporation, dry climate, sufficient sunshine and long time in a certain area of China, the annual rainfall is 72-215mm, and the annual evaporation is 1312-1924mm. In order to balance water evaporation and meet the needs of agricultural irrigation, more than 200 drainage ditches in the Yellow River irrigation area have received a large amount of farmland chemical fertilizers, pesticides, ammonia nitrogen, total phosphorus, COD and other pollutants. Severely exceeded the standard, the concentration of TN in the drainage ditch was tested to be 0.17-8.72mg/L, and the concentration of TP was 0.14-1.02mg/L, facing the double threat of salinization of water and soil and agricultural non-point source pollution. Ecosystem balance construction method.

发明内容Contents of the invention

本申请提供了一种水生态系统平衡构建方法,通过对该地区生态环境、气象、水文、地质资料的收集,结合原位水生态系统平衡构建技术特点,论证了该技术在该地区的适用性,通过引进先进的地表水质净化技术,有效减缓现状生态环境的恶化,通过工程实践,逐步形成适合当地特点的生态工程修复技术,在区域内广泛推广,达到生态环境全面修复的目的。This application provides a water ecosystem balance construction method. Through the collection of ecological environment, meteorology, hydrology, and geological data in this area, combined with the technical characteristics of in-situ water ecosystem balance construction, the applicability of this technology in this area is demonstrated , through the introduction of advanced surface water purification technology, the deterioration of the current ecological environment can be effectively slowed down, and through engineering practice, an ecological engineering restoration technology suitable for local characteristics is gradually formed, and it is widely promoted in the region to achieve the purpose of comprehensive restoration of the ecological environment.

本申请提供了一种水生态系统平衡构建方法,包括:污水来源阻断、水源预处理、底部淤泥处置、底质改良、沉水植物群落构建,水生群落构建、微生物群落构建、后期管护。The application provides a method for building a balanced water ecosystem, including: blocking of sewage sources, water source pretreatment, bottom sludge disposal, substrate improvement, submerged plant community building, aquatic community building, microbial community building, and post-management and protection.

进一步的,污水来源阻断采用围网隔断技术,围网隔断技术具体内容为:Furthermore, seine isolation technology is used to block the source of sewage, and the specific content of the seine isolation technology is as follows:

在污水输入处设置围网隔断,围网隔断包括:透水围隔骨架采用铝合金打桩固定,透水围网里层采用铝丝网加强,外层采用聚丙乙烯密目网装饰,超高层采用软性聚氨酯泡沫包裹于聚丙乙烯密目网中,有设定弹性空间内,可随水位变化自动调节高度。Set up a seine partition at the sewage input point. The seine partition includes: the permeable fence frame is fixed with aluminum alloy piles, the inner layer of the permeable fence is reinforced with aluminum wire mesh, the outer layer is decorated with polypropylene dense mesh, and the super high-rise is made of soft. Polyurethane foam is wrapped in polypropylene dense mesh, and there is a set elastic space, which can automatically adjust the height with the change of water level.

进一步的,水源预处理采用湿地预净化技术,湿地预净化技术具体内容为:Furthermore, wetland pre-purification technology is adopted for water source pretreatment, and the specific content of wetland pre-purification technology is as follows:

在经围网隔断技术处理后的污水流向水生态系统构建区域的前段设置的前置库内,前置库内部等密度栽植有挺水类植物,挺水类植物具体为芦苇,芦苇的栽植密度为16-20株每平米。In the pre-storage set in the front section where the sewage treated by the seine isolation technology flows to the water ecosystem construction area, emergent plants are planted at equal densities inside the front-storage. Emergent plants are specifically reeds. 16-20 plants per square meter.

进一步的,底部淤泥处置具体内容为:Further, the specific content of bottom sludge disposal is as follows:

将水生态系统构建区域的淤泥挖出,挖出后的淤泥进行消毒、降解、固化处理;Excavate the silt in the area where the water ecosystem is built, and then disinfect, degrade, and solidify the excavated silt;

水生态系统构建区域底部的淤泥清除后回填种植土,每亩回填的种植土体积相同。After the silt at the bottom of the water ecosystem construction area is removed, the planting soil is backfilled, and the volume of the planting soil backfilled per mu is the same.

进一步的,底质改良采用底泥底质改良技术,底泥底质改良技术具体内容包括:Further, the sediment improvement technology adopts the bottom mud bottom quality improvement technology, and the specific content of the bottom mud bottom quality improvement technology includes:

一:种植土消毒1: Planting soil disinfection

使用漂白粉作为消毒剂,具体操作步骤如下:Use bleach as a disinfectant, the specific steps are as follows:

准备足量的含氯量为25%~30%的漂白粉;Prepare a sufficient amount of bleaching powder with a chlorine content of 25% to 30%;

准备足量的尿素;Prepare enough urea;

对水生态系统构建区域面积进行测量;Measure the area of the water ecosystem construction area;

按照测量面积配制溶解有漂白粉的漂白液,按照每亩5-7千克的漂白粉比例配制,漂白液中漂白粉和水的比例为1:10;According to the measurement area, prepare the bleaching solution dissolved with bleaching powder, and prepare according to the ratio of 5-7 kilograms of bleaching powder per mu, and the ratio of bleaching powder and water in the bleaching solution is 1:10;

按照每亩66千克漂白液进行均匀泼洒,泼洒后静置24小时;Sprinkle evenly according to 66 kg of bleach per mu, and let it stand for 24 hours after splashing;

按照测量面积配置尿素溶液,按照每亩5-7千克的比例配制,尿素和水的比例为1:10;Configure urea solution according to the measurement area, according to the ratio of 5-7 kg per mu, the ratio of urea to water is 1:10;

按照每亩66千克尿素溶液均匀泼洒,泼洒后自然消毒5-6天;Sprinkle evenly according to 66 kg of urea solution per mu, and sterilize naturally for 5-6 days after splashing;

种植土消毒完成。Planting soil disinfection is complete.

二:底质改善Two: Substrate improvement

消毒完成后3-5天内,向水生态系统构建区域的底泥中投放定量的芽孢杆菌、光合细菌、硝化细菌、脱氮菌,每亩中的投放密度相同,其中芽孢杆菌、光合细菌、硝化细菌、脱氮菌的比例为1:1:1:1,使用专利号为CN200420109978.3,专利名称为一种向水体污泥投加微生物菌剂的装置进行芽孢杆菌、光合细菌、硝化细菌、脱氮菌向种植土中的投放。Within 3-5 days after the disinfection is completed, put a certain amount of Bacillus, photosynthetic bacteria, nitrifying bacteria, and denitrifying bacteria into the bottom mud of the water ecosystem construction area. The ratio of bacteria and nitrogen-removing bacteria is 1:1:1:1, and the patent number is CN200420109978.3, and the patent name is a device for adding microbial agents to water sludge for Bacillus, photosynthetic bacteria, nitrifying bacteria, The release of denitrification bacteria into the planting soil.

三:微量元素配比Three: Trace element ratio

向种植土中投加微量元素肥,微量元素肥在水生态系统构建区域等密度投放。Add trace element fertilizers to the planting soil, and put the trace element fertilizers in equal density in the water ecosystem construction area.

进一步的,沉水植物群落构建具体内容为:Further, the specific content of submerged plant community construction is as follows:

向水生态系统构建区域栽植苦草、伊乐藻、轮叶黑藻、金鱼藻,每亩中的栽植密度相同,其中苦草的栽植密度为40-60株每平米,伊乐藻的栽植密度为40株每平米,轮叶黑藻的栽植密度为10-15芽每从,25-36从每平米,金鱼藻栽植密度为7芽每从,10从每平米。Plant bitter grass, Elodea, Hydrilla verticillium, and hornwort in the area where the water ecosystem is constructed. Plant per square meter, the planting density of Hydrilla verticillium is 10-15 buds per bud, 25-36 buds per square meter, and the planting density of hornwort is 7 buds per bud, 10 buds per square meter.

进一步的,水生群落构建具体内容为:Further, the specific content of aquatic community construction is as follows:

向水生态系统构建区域投放螺类、蚌类、鱼类、枝角类水生动物,每亩中的投放密度相同,其中螺类的投放密度为2-3个每平方厘米,蚌类的投放密度为5-6个每平方厘米,鱼类的投放密度为10尾每平方米,枝角类的投放密度为1-2个每平方厘米。Put snails, mussels, fish, and cladocera aquatic animals into the water ecosystem construction area, and the stocking density in each mu is the same, wherein the stocking density of snails is 2-3 per square centimeter, and the stocking density of mussels is 2-3 per square centimeter. For 5-6 per square centimeter, the stocking density of fish is 10 tails per square meter, and the stocking density of cladocera is 1-2 per square centimeter.

进一步的,微生物群落构建具体内容为:Further, the specific content of microbial community construction is as follows:

向水生态系统构建区域投放有益复合微生物,每亩中的投放量相同。Add beneficial compound microorganisms to the area where the water ecosystem is built, with the same amount per mu.

进一步的,后期管护的具体内容为:Further, the specific content of post-management and protection is as follows:

对水质进行持续监测;Continuous monitoring of water quality;

根据水质实际情况定期进行底质改善;Regularly carry out bottom quality improvement according to the actual situation of water quality;

根据水质实际情况定期进行沉水植物栽植或者清理;Plant or clean submerged plants on a regular basis according to the actual water quality;

根据水质实际情况定期进行水生动物的投放及清理;According to the actual situation of water quality, release and clean up aquatic animals on a regular basis;

根据水质实际情况定期进行微生物群落的调整。Adjust the microbial community regularly according to the actual situation of water quality.

由以上技术方案可知,本申请提供了一种水生态系统平衡构建方法,水体的底质改善为其中重要步骤,具体的内容如下:底质改良采用底泥底质改良技术,底泥底质改善包括水体底质消毒与底质活化,其目的为消除或者减缓水体底质污染源对后期生态系统的负面影响。在工程实施前,根据需要对水体底泥进行消毒及活性淤泥处理等措施,其目的是杀灭原来富营养化水体底质中的病原体,改善底质酸碱度,并建立或者恢复底质有益微生物处理系统,促进沉水植物群落的生长及系统的恢复和稳定,提高水体水质净化效果。It can be known from the above technical solutions that this application provides a method for constructing a water ecosystem balance. The improvement of the bottom quality of the water body is an important step. The specific content is as follows: Including water bottom disinfection and bottom activation, the purpose is to eliminate or slow down the negative impact of water bottom pollution sources on the later ecosystem. Before the implementation of the project, measures such as disinfection and active sludge treatment should be carried out on the bottom mud of the water body according to the needs, the purpose of which is to kill the pathogens in the original eutrophic water bottom, improve the pH of the bottom, and establish or restore the treatment of beneficial microorganisms in the bottom system, promote the growth of submerged plant communities and the recovery and stability of the system, and improve the water quality purification effect.

底泥底质改良技术具体内容包括三个部分:The specific content of sediment improvement technology includes three parts:

一:种植土消毒1: Planting soil disinfection

使用漂白粉作为消毒剂,具体操作步骤如下:Use bleach as a disinfectant, the specific steps are as follows:

准备足量的含氯量为25%~30%的漂白粉;准备足量的尿素;对水生态系统构建区域面积进行测量;按照测量面积配制溶解有漂白粉的漂白液,按照每亩5-7千克的漂白粉比例配制,漂白液中漂白粉和水的比例为1:10;按照每亩66千克漂白液进行均匀泼洒,泼洒后静置24小时;按照测量面积配置尿素溶液,按照每亩5-7千克的比例配制,尿素和水的比例为1:10;按照每亩66千克尿素溶液均匀泼洒,泼洒后自然消毒5-6天;种植土消毒完成。Prepare a sufficient amount of bleaching powder with a chlorine content of 25% to 30%; prepare a sufficient amount of urea; measure the area of the water ecosystem construction area; prepare bleaching solution dissolved in bleaching powder according to the measured area, and use 5-7 kg per mu The ratio of bleaching powder is prepared, and the ratio of bleaching powder and water in the bleaching solution is 1:10; the bleaching solution is evenly splashed according to 66 kg per mu, and left to stand for 24 hours after splashing; the urea solution is configured according to the measurement area, and the urea solution is 5-7 kg per mu The ratio of urea to water is 1:10; 66 kg of urea solution per mu is evenly sprayed, and the natural disinfection is 5-6 days after spraying; the planting soil is disinfected.

生石灰结合尿素来消毒,与尿素发生化学反应生成氯胺(一种消毒效果很好的氧化剂,其所含的二氯胺和三氯胺具有非常强的毒性),能迅速杀灭池塘中的敌害生物和野杂鱼,是非常理想的消毒配方。Quicklime is combined with urea to disinfect, and chemically reacts with urea to generate chloramine (an oxidant with good disinfection effect, and the dichloramine and trichloramine contained in it are very toxic), which can quickly kill the enemies in the pond. It is an ideal disinfection formula for harmful organisms and wild fish.

底泥消毒工程是对底泥进行病原菌的杀灭工作,植物在起苗、打包、运输、栽植的过程中极易受到不同程度的创伤,对底泥消毒处理后,可有效提高植物成活率,保障构建初期即可快速呈现良好的水质净化效果。The bottom mud disinfection project is to kill pathogenic bacteria on the bottom mud. Plants are vulnerable to varying degrees of trauma during the process of seedling raising, packaging, transportation, and planting. After the bottom mud is disinfected, the survival rate of plants can be effectively improved. It is guaranteed that a good water purification effect can be quickly presented at the initial stage of construction.

二:底质改善Two: Substrate improvement

消毒完成后3-5天内,向水生态系统构建区域的底泥中投放定量的芽孢杆菌、光合细菌、硝化细菌、脱氮菌,每亩中的投放密度相同,其中芽孢杆菌、光合细菌、硝化细菌、脱氮菌的比例为1:1:1:1,使用专利号为CN200420109978.3,专利名称为一种向水体污泥投加微生物菌剂的装置进行芽孢杆菌、光合细菌、硝化细菌、脱氮菌向种植土中的投放。Within 3-5 days after the disinfection is completed, put a certain amount of Bacillus, photosynthetic bacteria, nitrifying bacteria, and denitrifying bacteria into the bottom mud of the water ecosystem construction area. The ratio of bacteria and nitrogen-removing bacteria is 1:1:1:1, and the patent number is CN200420109978.3, and the patent name is a device for adding microbial agents to water sludge for Bacillus, photosynthetic bacteria, nitrifying bacteria, The release of denitrification bacteria into the planting soil.

向底泥中投放芽孢杆菌、光合细菌、硝化细菌、脱氮菌等有益微生物菌落,主要通过微生物的呼吸发酵,将有机物等容易造成底泥的物质迅速分解成CO和HO或转化成无害物质,使污染水体得以净化。同时,能对底泥或水体中含氮物质进行有效分解。其中,芽孢杆菌可以分解产生恶臭气体的有机物质、有机硫化物、有机氮等,大大改善底泥环境光合细菌则一类以光作为能源、能在厌氧光照或好氧黑暗条件下利用自然界中的有机物、硫化物、氨等作为供氢体兼碳源进行光合作用的微生物,其广泛分布于自然界的土壤、水田、沼泽、湖泊、江海等处,主要分布于水生环境中光线能透射到的缺氧区。但是以上微生物制剂并不能持续保持净化效果,另外,由于投加微生物制剂,并不能修复湖体的水生态系统,恢复湖体的自净能力,因此,微生物制剂的选择只能作为湖体修复底泥处理的前期处理措施。Bacillus, photosynthetic bacteria, nitrifying bacteria, denitrifying bacteria and other beneficial microbial colonies are put into the bottom mud, mainly through the respiratory fermentation of microorganisms, the organic matter and other substances that are easy to cause bottom mud are quickly decomposed into CO and HO or converted into harmless substances , so that polluted water can be purified. At the same time, it can effectively decompose nitrogen-containing substances in sediment or water. Among them, Bacillus can decompose organic substances, organic sulfides, organic nitrogen, etc. that produce malodorous gases, greatly improving the sediment environment. Organic matter, sulfide, ammonia, etc. are used as hydrogen donors and carbon sources for photosynthetic microorganisms, which are widely distributed in natural soils, paddy fields, swamps, lakes, rivers and seas, etc., mainly distributed in aquatic environments where light can penetrate hypoxic zone. However, the above microbial preparations cannot maintain the purification effect continuously. In addition, because the addition of microbial preparations cannot restore the water ecosystem of the lake body and restore the self-purification ability of the lake body, the choice of microbial preparations can only be used as a lake for sediment restoration. Pre-processing measures for processing.

底泥底质改良工程应在底泥消毒工作结束后3-5天内进行,底泥底质改良主要作用:对土壤中的有机质、有害物质如硝酸盐、亚硝酸盐类、硫化物等进行分解,增进原土壤的肥效,促进植株的体的分蘖生殖。The sediment improvement project should be carried out within 3-5 days after the disinfection of the sediment. The main function of the sediment improvement is to decompose the organic matter and harmful substances in the soil, such as nitrate, nitrite, sulfide, etc. , improve the fertilizer efficiency of the original soil, and promote the tillering and reproduction of the plant body.

三:微量元素配比Three: Trace element ratio

向种植土中投加微量元素肥,微量元素肥在水生态系统构建区域等密度投放。Add trace element fertilizers to the planting soil, and put the trace element fertilizers in equal density in the water ecosystem construction area.

土壤微量元素工程主要是补充植物生长所必须的微量元素,微量元素可有效提高植株体的抗逆性、耐盐性、抗病能力,对植株体叶片具有增色作用,对植物的分蘖也有一定的促进作用。微量元素肥适用于水生植物的各个生长阶段,可显著提高植株体的光合作用,延长生命周期。Soil trace element engineering is mainly to supplement the trace elements necessary for plant growth. Trace elements can effectively improve the stress resistance, salt tolerance, and disease resistance of the plant body, enhance the color of the leaves of the plant body, and have a certain effect on the tillering of the plant. enhancement. Trace element fertilizers are suitable for all growth stages of aquatic plants, which can significantly improve the photosynthesis of plants and prolong their life cycle.

后期管护的过程也必不可少,对水质进行持续监测;The process of management and protection in the later stage is also essential, and continuous monitoring of water quality is carried out;

根据水质实际情况定期进行底质改善;Regularly carry out bottom quality improvement according to the actual situation of water quality;

根据水质实际情况定期进行沉水植物栽植或者清理;Plant or clean submerged plants on a regular basis according to the actual water quality;

根据水质实际情况定期进行水生动物的投放及清理;According to the actual situation of water quality, release and clean up aquatic animals on a regular basis;

根据水质实际情况定期进行微生物群落的调整,通过对底质的改善,沉水植物的调整,水生动物的调整,微生物群落的调整,使整个水生态系统构建区域始终保持在平衡状态下。Regularly adjust the microbial community according to the actual water quality. Through the improvement of the substrate, the adjustment of submerged plants, the adjustment of aquatic animals, and the adjustment of the microbial community, the entire water ecosystem construction area is always kept in a balanced state.

综上所述,本申请产生的有益效果如下:In summary, the beneficial effects produced by the application are as follows:

1、通过采用原位水生态系统平衡构建技术对其水质进行综合治理,目前,湖水水质保持在地表水环境质量标准的Ⅲ类,水体清澈透明,水景景观效果良好,驳岸植物景观营造也十分优美。1. By adopting in-situ water ecosystem balance construction technology to comprehensively control its water quality, at present, the water quality of the lake is maintained at Class III of the surface water environmental quality standard, the water body is clear and transparent, the water landscape effect is good, and the revetment plant landscape is also very beautiful .

2、底质改善过程对底泥进行有有效改良,将淤泥处理后回填种植土,种植土经消毒、改良、添加微量元素后适合水生植物的生长,有效保证水生植物的长势,维护整个水生态系统构建区域的生态平衡。2. The bottom quality improvement process effectively improves the bottom mud, and backfills the planting soil after treating the silt. The planting soil is suitable for the growth of aquatic plants after disinfection, improvement, and adding trace elements, effectively ensuring the growth of aquatic plants and maintaining the entire aquatic ecology The system builds the ecological balance of the region.

3、后期管护可以对整个水生态系统构建区域持续监测,在持续监测情况下可以对失衡后的水生态系统构建区域进行及时调节,保证水质。3. The post-management and protection can continuously monitor the entire water ecosystem construction area. Under continuous monitoring, the imbalanced water ecosystem construction area can be adjusted in time to ensure water quality.

附图说明Description of drawings

为了更清楚地说明本申请的技术方案,下面将对实施案例中所需要使用的附图作简单地介绍,显而易见地,对于本领域普通技术人员而言,在不付出创造性劳动性的前提下,还可以根据这些附图获得其他的附图。In order to illustrate the technical solution of the present application more clearly, the accompanying drawings used in the implementation cases will be briefly introduced below. Obviously, for those of ordinary skill in the art, on the premise of not paying creative labor, Additional drawings can also be derived from these drawings.

图1为本申请水生态系统平衡构建示意图。Figure 1 is a schematic diagram of the water ecosystem balance construction of the present application.

具体实施方式Detailed ways

为了使本技术领域的人员更好地理解本申请中的技术方案,下面将结合附图,对本申请实施例中的技术方案进行清楚、完整地描述。In order to enable those skilled in the art to better understand the technical solutions in the present application, the technical solutions in the embodiments of the present application will be clearly and completely described below in conjunction with the accompanying drawings.

由以上技术方案可知的参见图1。From the above technical solution, see Fig. 1 .

实施例1:Example 1:

一种水生态系统平衡构建方法,包括:污水来源阻断、水源预处理、底部淤泥处置、底质改良、沉水植物群落构建,水生群落构建、微生物群落构建、后期管护。A method for constructing a balanced aquatic ecosystem, including: blocking of sewage sources, water source pretreatment, bottom sludge disposal, substrate improvement, submerged plant community construction, aquatic community construction, microbial community construction, and post-management and protection.

作为优选的实施方式,污水来源阻断采用围网隔断技术,围网隔断技术具体内容为:As a preferred implementation mode, seine isolation technology is used to block the source of sewage, and the specific content of the seine isolation technology is:

在污水输入处设置围网隔断,围网隔断包括:透水围隔骨架采用铝合金打桩固定,透水围网里层采用铝丝网加强,外层采用聚丙乙烯密目网装饰,超高层采用软性聚氨酯泡沫包裹于聚丙乙烯密目网中,有设定弹性空间内,可随水位变化自动调节高度。Set up a seine partition at the sewage input point. The seine partition includes: the permeable fence frame is fixed with aluminum alloy piles, the inner layer of the permeable fence is reinforced with aluminum wire mesh, the outer layer is decorated with polypropylene dense mesh, and the super high-rise is made of soft. Polyurethane foam is wrapped in polypropylene dense mesh, and there is a set elastic space, which can automatically adjust the height with the change of water level.

作为优选的实施方式,水源预处理采用湿地预净化技术,湿地预净化技术具体内容为:As a preferred implementation mode, wetland pre-purification technology is used for water source pretreatment, and the specific content of wetland pre-purification technology is as follows:

在经围网隔断技术处理后的污水流向水生态系统构建区域的前段设置的前置库内,前置库内部等密度栽植有挺水类植物,挺水类植物具体为芦苇,芦苇的栽植密度为16-20株每平米。In the pre-storage set in the front section where the sewage treated by the seine isolation technology flows to the water ecosystem construction area, emergent plants are planted at equal densities inside the front-storage. Emergent plants are specifically reeds. 16-20 plants per square meter.

通常在水源不太理想的情况下,在水生态系统构建区域的前段设置前置库,库内规划适当的挺水类植物,该类植物能很好的吸收和吸附水中的有机质和悬浮物质、氮磷等元素,从而为后续生态系统的稳定运行提供一到天然的屏障。Usually, when the water source is not ideal, a front-end reservoir is set up in the front of the water ecosystem construction area, and appropriate emergent plants are planned in the reservoir, which can absorb and absorb organic matter and suspended matter in the water well. Nitrogen, phosphorus and other elements provide a natural barrier for the subsequent stable operation of the ecosystem.

作为优选的实施方式,底部淤泥处置具体内容为:As a preferred embodiment, the specific content of bottom sludge disposal is:

将水生态系统构建区域的淤泥挖出,挖出后的淤泥进行消毒、降解、固化处理;Excavate the silt in the area where the water ecosystem is built, and then disinfect, degrade, and solidify the excavated silt;

水生态系统构建区域底部的淤泥清除后回填种植土,每亩回填的种植土体积相同。After the silt at the bottom of the water ecosystem construction area is removed, the planting soil is backfilled, and the volume of the planting soil backfilled per mu is the same.

作为优选的实施方式,底质改良采用底泥底质改良技术,底泥底质改善包括水体底质消毒与底质活化,其目的为消除或者减缓水体底质污染源对后期生态系统的负面影响。在工程实施前,根据需要对水体底泥进行消毒及活性淤泥处理等措施,其目的是杀灭原来富营养化水体底质中的病原体,改善底质酸碱度,并建立或者恢复底质有益微生物处理系统,促进沉水植物群落的生长及系统的恢复和稳定,提高水体水质净化效果。As a preferred embodiment, the sediment improvement technology adopts the sediment improvement technology, and the sediment improvement includes disinfection and activation of the bottom of the water body, the purpose of which is to eliminate or slow down the negative impact of the pollution source of the bottom of the water body on the ecosystem in the later stage. Before the implementation of the project, measures such as disinfection and active sludge treatment should be carried out on the bottom mud of the water body according to the needs, the purpose of which is to kill the pathogens in the original eutrophic water bottom, improve the pH of the bottom, and establish or restore the treatment of beneficial microorganisms in the bottom system, promote the growth of submerged plant communities and the recovery and stability of the system, and improve the water quality purification effect.

底泥底质改良技术具体内容包括:The specific content of sediment improvement technology includes:

一:种植土消毒1: Planting soil disinfection

使用漂白粉作为消毒剂,具体操作步骤如下:Use bleach as a disinfectant, the specific steps are as follows:

准备足量的含氯量为25%~30%的漂白粉;Prepare a sufficient amount of bleaching powder with a chlorine content of 25% to 30%;

准备足量的尿素;Prepare enough urea;

对水生态系统构建区域面积进行测量;Measure the area of the water ecosystem construction area;

按照测量面积配制溶解有漂白粉的漂白液,按照每亩5-7千克的漂白粉比例配制,漂白液中漂白粉和水的比例为1:10;According to the measurement area, prepare the bleaching solution dissolved with bleaching powder, and prepare according to the ratio of 5-7 kilograms of bleaching powder per mu, and the ratio of bleaching powder and water in the bleaching solution is 1:10;

按照每亩66千克漂白液进行均匀泼洒,泼洒后静置24小时;Sprinkle evenly according to 66 kg of bleach per mu, and let it stand for 24 hours after splashing;

按照测量面积配置尿素溶液,按照每亩5-7千克的比例配制,尿素和水的比例为1:10;Configure urea solution according to the measurement area, according to the ratio of 5-7 kg per mu, the ratio of urea to water is 1:10;

按照每亩66千克尿素溶液均匀泼洒,泼洒后自然消毒5-6天;Sprinkle evenly according to 66 kg of urea solution per mu, and sterilize naturally for 5-6 days after splashing;

种植土消毒完成。Planting soil disinfection is complete.

生石灰结合尿素来消毒,与尿素发生化学反应生成氯胺(一种消毒效果很好的氧化剂,其所含的二氯胺和三氯胺具有非常强的毒性),能迅速杀灭池塘中的敌害生物和野杂鱼,是非常理想的消毒配方。Quicklime is combined with urea to disinfect, and chemically reacts with urea to generate chloramine (an oxidant with good disinfection effect, and the dichloramine and trichloramine contained in it are very toxic), which can quickly kill the enemies in the pond. It is an ideal disinfection formula for harmful organisms and wild fish.

底泥消毒工程是对底泥进行病原菌的杀灭工作,植物在起苗、打包、运输、栽植的过程中极易受到不同程度的创伤,对底泥消毒处理后,可有效提高植物成活率,保障构建初期即可快速呈现良好的水质净化效果。The bottom mud disinfection project is to kill pathogenic bacteria on the bottom mud. Plants are vulnerable to varying degrees of trauma during the process of seedling raising, packaging, transportation, and planting. After the bottom mud is disinfected, the survival rate of plants can be effectively improved. It is guaranteed that a good water purification effect can be quickly presented at the initial stage of construction.

二:底质改善Two: Substrate improvement

消毒完成后3-5天内,向水生态系统构建区域的底泥中投放定量的芽孢杆菌、光合细菌、硝化细菌、脱氮菌,每亩中的投放密度相同,其中芽孢杆菌、光合细菌、硝化细菌、脱氮菌的比例为1:1:1:1,使用专利号为CN200420109978.3,专利名称为一种向水体污泥投加微生物菌剂的装置进行芽孢杆菌、光合细菌、硝化细菌、脱氮菌向种植土中的投放。Within 3-5 days after the disinfection is completed, put a certain amount of Bacillus, photosynthetic bacteria, nitrifying bacteria, and denitrifying bacteria into the bottom mud of the water ecosystem construction area. The ratio of bacteria and nitrogen-removing bacteria is 1:1:1:1, and the patent number is CN200420109978.3, and the patent name is a device for adding microbial agents to water sludge for Bacillus, photosynthetic bacteria, nitrifying bacteria, The release of denitrification bacteria into the planting soil.

向底泥中投放芽孢杆菌、光合细菌、硝化细菌、脱氮菌等有益微生物菌落,主要通过微生物的呼吸发酵,将有机物等容易造成底泥的物质迅速分解成CO和HO或转化成无害物质,使污染水体得以净化。同时,能对底泥或水体中含氮物质进行有效分解。其中,芽孢杆菌可以分解产生恶臭气体的有机物质、有机硫化物、有机氮等,大大改善底泥环境光合细菌则一类以光作为能源、能在厌氧光照或好氧黑暗条件下利用自然界中的有机物、硫化物、氨等作为供氢体兼碳源进行光合作用的微生物,其广泛分布于自然界的土壤、水田、沼泽、湖泊、江海等处,主要分布于水生环境中光线能透射到的缺氧区。但是以上微生物制剂并不能持续保持净化效果,另外,由于投加微生物制剂,并不能修复湖体的水生态系统,恢复湖体的自净能力,因此,微生物制剂的选择只能作为湖体修复底泥处理的前期处理措施。Bacillus, photosynthetic bacteria, nitrifying bacteria, denitrifying bacteria and other beneficial microbial colonies are put into the bottom mud, mainly through the respiratory fermentation of microorganisms, the organic matter and other substances that are easy to cause bottom mud are quickly decomposed into CO and HO or converted into harmless substances , so that polluted water can be purified. At the same time, it can effectively decompose nitrogen-containing substances in sediment or water. Among them, Bacillus can decompose organic substances, organic sulfides, organic nitrogen, etc. that produce malodorous gases, greatly improving the sediment environment. Organic matter, sulfide, ammonia, etc. are used as hydrogen donors and carbon sources for photosynthetic microorganisms, which are widely distributed in soil, paddy fields, swamps, lakes, rivers and seas in nature, and are mainly distributed in aquatic environments where light can penetrate hypoxic zone. However, the above microbial preparations cannot maintain the purification effect continuously. In addition, the addition of microbial preparations cannot restore the water ecosystem of the lake and restore the self-purification ability of the lake. Therefore, the choice of microbial preparations can only be used as a lake to restore sediment Pre-processing measures for processing.

底泥底质改良工程应在底泥消毒工作结束后3-5天内进行,底泥底质改良主要作用:对土壤中的有机质、有害物质如硝酸盐、亚硝酸盐类、硫化物等进行分解,增进原土壤的肥效,促进植株的体的分蘖生殖。The sediment improvement project should be carried out within 3-5 days after the disinfection of the sediment. The main function of the sediment improvement is to decompose the organic matter and harmful substances in the soil, such as nitrate, nitrite, sulfide, etc. , improve the fertilizer efficiency of the original soil, and promote the tillering and reproduction of the plant body.

三:微量元素配比Three: Trace element ratio

向种植土中投加微量元素肥,微量元素肥在水生态系统构建区域等密度投放。Add trace element fertilizers to the planting soil, and put the trace element fertilizers in equal density in the water ecosystem construction area.

土壤微量元素工程主要是补充植物生长所必须的微量元素,微量元素可有效提高植株体的抗逆性、耐盐性、抗病能力,对植株体叶片具有增色作用,对植物的分蘖也有一定的促进作用。微量元素肥适用于水生植物的各个生长阶段,可显著提高植株体的光合作用,延长生命周期。Soil trace element engineering is mainly to supplement the trace elements necessary for plant growth. Trace elements can effectively improve the stress resistance, salt tolerance, and disease resistance of the plant body, have a color-enhancing effect on the leaves of the plant body, and have a certain effect on the tillering of the plant. enhancement. Trace element fertilizers are suitable for all growth stages of aquatic plants, which can significantly improve the photosynthesis of plants and prolong their life cycle.

作为优选的实施方式,沉水植物群落构建具体内容为:As a preferred embodiment, the specific content of submerged plant community construction is:

向水生态系统构建区域栽植苦草、伊乐藻、轮叶黑藻、金鱼藻,每亩中的栽植密度相同,其中苦草的栽植密度为40-60株每平米,伊乐藻的栽植密度为40株每平米,轮叶黑藻的栽植密度为10-15芽每从,25-36从每平米,金鱼藻栽植密度为7芽每从,10从每平米。Plant bitter grass, Elodea, Hydrilla verticillium, and hornwort in the area where the water ecosystem is constructed. Plant per square meter, the planting density of Hydrilla verticillium is 10-15 buds per bud, 25-36 buds per square meter, and the planting density of hornwort is 7 buds per bud, 10 buds per square meter.

水生植物种植是原位水生态系统构建的重要环节,是实现水体自净和生态修复的关键生物群落,也是展现美妙水体景观的重要的工程部分,因此设计配置适宜各不同水体和各个季节生长的多种水生植物,不仅增加了水体的景观效果,同时也保持生物多样性原则,增强生态系统的稳定性。沉水植物作为水体主要初级生产者,在水生生态系统中有着不可替代的作用。当沉水植物丰富时,水体表现为水质清澈、溶解氧高、藻类密度低、生物多样性高等特点。反之,当沉水植物消失,水体处于较高营养状态时,高温季节一般藻类密度高、生物多样性低、水质浑浊。沉水植物能够通过多种途径影响淡水生态系统。首先,它能消耗水体中大量的氮、磷等物质,促进营养物质的沉积,降低水体的营养物含量;还能吸收富集污染物质,提高水体的自净能力。其次,很多水生植物特别是沉水植物通过同生态位的竞争,释放生物因子,对有毒藻类的生长具有明显的抑制作用。同时大型沉水植物还能够为水体内本土物种和微生物生长提供附着表面,为水体中部分水生动物提供饵料和栖息、繁殖场所。此外,沉水植物光合作用所产生的次生氧能杀灭有害菌,强光合作用下更能使水中产生有机絮凝体,形成气浮效应,并使其快速氧化分解,降低水体中BOD;和COD。因此沉水植被是维护水生生态系统多样性的基础,在水生态系统中具有重要作用。The planting of aquatic plants is an important link in the construction of an in-situ water ecosystem. It is a key biological community to achieve water self-purification and ecological restoration, and is also an important part of the project to show a beautiful water landscape. Therefore, the design and configuration are suitable for various water bodies and various seasons. Planting aquatic plants not only increases the landscape effect of the water body, but also maintains the principle of biodiversity and enhances the stability of the ecosystem. As the main primary producers of water bodies, submerged plants play an irreplaceable role in aquatic ecosystems. When submerged plants are abundant, the water body is characterized by clear water quality, high dissolved oxygen, low algae density, and high biodiversity. Conversely, when submerged plants disappear and the water body is in a high nutrient state, the high-temperature season generally has high algae density, low biodiversity, and turbid water quality. Submerged plants can affect freshwater ecosystems in many ways. First of all, it can consume a large amount of nitrogen, phosphorus and other substances in the water body, promote the deposition of nutrients, reduce the nutrient content of the water body; it can also absorb and enrich pollutants, and improve the self-purification ability of the water body. Secondly, many aquatic plants, especially submerged plants, release biological factors through competition with the same ecological niche, which has a significant inhibitory effect on the growth of toxic algae. At the same time, large submerged plants can also provide attachment surfaces for the growth of native species and microorganisms in the water body, and provide bait, habitat and breeding places for some aquatic animals in the water body. In addition, the secondary oxygen produced by the photosynthesis of submerged plants can kill harmful bacteria. Under strong photosynthesis, organic flocs can be produced in the water, forming an air flotation effect, and making them oxidize and decompose quickly, reducing BOD in the water; and COD. Therefore, submerged vegetation is the basis for maintaining the diversity of aquatic ecosystems and plays an important role in aquatic ecosystems.

作为优选的实施方式,水生群落构建具体内容为:As a preferred embodiment, the specific content of aquatic community construction is:

向水生态系统构建区域投放螺类、蚌类、鱼类、枝角类水生动物,每亩中的投放密度相同,其中螺类的投放密度为2-3个每平方厘米,蚌类的投放密度为5-6个每平方厘米,鱼类的投放密度为10尾每平方米,枝角类的投放密度为1-2个每平方厘米。Put snails, mussels, fish, and cladocera aquatic animals into the water ecosystem construction area, and the stocking density in each mu is the same, wherein the stocking density of snails is 2-3 per square centimeter, and the stocking density of mussels is 2-3 per square centimeter. For 5-6 per square centimeter, the stocking density of fish is 10 tails per square meter, and the stocking density of cladocera is 1-2 per square centimeter.

水体的植被恢复后,引入水生动物丰富食物链,水生生物在水生态系统物质循环与流动中具有特殊的地位和作用。对于后期生态系统的平衡稳定具有重要的意义。因此,出于对良性水生态系统的构建以及水质保护的需要,构建合理的水生生物群落是十分必要的。After the vegetation of the water body is restored, aquatic animals are introduced to enrich the food chain. Aquatic organisms have a special status and role in the material circulation and flow of the aquatic ecosystem. It is of great significance to the balance and stability of the ecosystem in the later stage. Therefore, for the construction of benign aquatic ecosystems and the protection of water quality, it is very necessary to construct a reasonable aquatic biome.

水生动物的放养将充分考虑水生动物物种的配置结构(时空结构和营养结构),科学合理地设计水生动物的放养模式(种类、数量、雌雄比、个体大小、食性、生活习性、放养季节、放养顺序等)使各种群生物量和生物密度达到营养水平,利用肉食性鱼类-滤食性鱼类-浮游动物-藻类-营养物质的食物链关系所产生的生态学效应,达到消减营养物质、净化水质的作用。The stocking of aquatic animals will fully consider the configuration structure of aquatic animal species (spatial-temporal structure and nutritional structure), scientifically and rationally design the stocking mode of aquatic animals (species, quantity, sex ratio, individual size, feeding habits, living habits, stocking season, stocking season, etc.) Sequence, etc.) to make the biomass and biological density of various groups reach the nutritional level, and use the ecological effect produced by the food chain relationship of carnivorous fish-filter-feeding fish-zooplankton-algae-nutrient substances to reduce nutrients and purify The role of water quality.

作为优选的实施方式,微生物群落构建具体内容为:As a preferred embodiment, the specific content of microbial community construction is:

向水生态系统构建区域投放有益复合微生物,每亩中的投放量相同。Add beneficial compound microorganisms to the area where the water ecosystem is built, with the same amount per mu.

微生物是水生态系统的重要组成部分,位于食物链的前端和末端。它对水中的污染物进行分解、溶解氧消耗又恢复的循环过异氧细胞出现数量高峰PY生动物吸收、吸咐。它同时把其它生物无法吸收的有机物通过自身代谢作用,转化为无机成分,供水生植物利用。Microorganisms are an important part of aquatic ecosystems, located at the front and end of the food chain. It decomposes the pollutants in the water, consumes dissolved oxygen and recovers, and the number of circulating heterooxygen cells peaks to absorb and adsorb PY animals. At the same time, it converts organic matter that cannot be absorbed by other organisms into inorganic components through its own metabolism, which can be used by aquatic plants.

微生物在水体中的分布包括底泥微生物群和悬浮微生物群,前者对沉积物进行分解,后者对溶解性污染物进分解,二者生态位互补,形成立体净化功能。研究表明,一个新的景观水体缺乏足够量的分解者微生物,因此在水体中应该添加一定量的微生物制剂,使分解有机物的微生物占优势群落,可以促进水中有机质的矿化。微生物制剂必须含有一定量的活菌,一般要求每毫升含3亿个以上的活菌体,并且活力要强。该类生物尽量在本地获取种源后扩陪使用。The distribution of microorganisms in the water body includes sediment microbial groups and suspended microbial groups. The former decomposes sediments, while the latter decomposes dissolved pollutants. The ecological niches of the two complement each other to form a three-dimensional purification function. Studies have shown that a new landscape water body lacks a sufficient amount of decomposer microorganisms, so a certain amount of microbial preparations should be added to the water body, so that the microorganisms that decompose organic matter dominate the community, which can promote the mineralization of organic matter in water. Microbial preparations must contain a certain amount of live bacteria, generally requiring more than 300 million live bacteria per milliliter, and the vitality must be strong. This type of creature should be used as much as possible after obtaining the provenance locally.

作为优选的实施方式,后期管护的具体内容为:As a preferred implementation mode, the specific content of post-management and protection is:

对水质进行持续监测;Continuous monitoring of water quality;

根据水质实际情况定期进行底质改善;Regularly carry out bottom quality improvement according to the actual situation of water quality;

根据水质实际情况定期进行沉水植物栽植或者清理;Plant or clean submerged plants on a regular basis according to the actual water quality;

根据水质实际情况定期进行水生动物的投放及清理;According to the actual situation of water quality, release and clean up aquatic animals on a regular basis;

根据水质实际情况定期进行微生物群落的调整。Adjust the microbial community regularly according to the actual situation of water quality.

本领域技术人员在考虑说明书及实践这里公开的申请后,将容易想到本申请的其它实施方案。本申请旨在涵盖本申请的任何变型、用途或者适应性变化,这些变型、用途或者适应性变化遵循本申请的一般性原理并包括本申请未公开的本技术领域中的公知常识或惯用技术手段。说明书和实施例仅被视为示例性的,本申请的真正范围由权利要求指出。Other embodiments of the application will be readily apparent to those skilled in the art from consideration of the specification and practice of the application disclosed herein. This application is intended to cover any modification, use or adaptation of the application, these modifications, uses or adaptations follow the general principles of the application and include common knowledge or conventional technical means in the technical field not disclosed in the application . The specification and examples are to be considered exemplary only, with the true scope of the application indicated by the claims.

应当理解的是,本申请并不局限于上面已经描述并在附图中示出的精确结构,并且可以在不脱离其范围进行各种修改和改变。以上所述的本申请实施方式并不构成对本申请保护范围的限定。It should be understood that the present application is not limited to the precise constructions which have been described above and shown in the accompanying drawings, and various modifications and changes may be made without departing from the scope thereof. The embodiments of the present application described above are not intended to limit the scope of protection of the present application.

Claims (9)

1.一种水生态系统平衡构建方法,其特征在于,包括:污水来源阻断、水源预处理、底部淤泥处置、底质改良、沉水植物群落构建,水生群落构建、微生物群落构建、后期管护。1. A method for constructing a water ecosystem balance, characterized in that, comprising: blocking of sewage source, water source pretreatment, bottom sludge disposal, substrate improvement, submerged plant community construction, aquatic community construction, microbial community construction, post-management protect. 2.根据权利要求1所述的一种水生态系统平衡构建方法,其特征在于,所述污水来源阻断采用围网隔断技术,所述围网隔断技术具体内容为:2. A kind of water ecological system balance construction method according to claim 1, is characterized in that, described sewage source is blocked and adopts fence to cut off technology, and the specific content of described fence to cut off technology is: 在污水输入处设置围网隔断,围网隔断包括:透水围隔骨架采用铝合金打桩固定,透水围网里层采用铝丝网加强,外层采用聚丙乙烯密目网装饰,超高层采用软性聚氨酯泡沫包裹于聚丙乙烯密目网中,有设定弹性空间内,可随水位变化自动调节高度。Set up a seine partition at the sewage input point. The seine partition includes: the permeable fence frame is fixed with aluminum alloy piles, the inner layer of the permeable fence is reinforced with aluminum wire mesh, the outer layer is decorated with polypropylene dense mesh, and the super high-rise is made of soft. Polyurethane foam is wrapped in polypropylene dense mesh, and there is a set elastic space, which can automatically adjust the height with the change of water level. 3.根据权利要求1所述的一种水生态系统平衡构建方法,其特征在于,所述水源预处理采用湿地预净化技术,所述湿地预净化技术具体内容为:3. A method for constructing a water ecosystem balance according to claim 1, wherein the water source pretreatment adopts wetland pre-purification technology, and the specific content of the wetland pre-purification technology is: 在经围网隔断技术处理后的污水流向水生态系统构建区域的前段设置的前置库内,所述前置库内部等密度栽植有挺水类植物,所述挺水类植物具体为芦苇,所述芦苇的栽植密度为16-20株每平米。In the pre-storage set before the sewage treated by the seine isolation technology flows to the water ecosystem construction area, emergent plants are planted at equal densities in the front-storage, and the emergent plants are specifically reeds, The planting density of the reeds is 16-20 per square meter. 4.根据权利要求1所述的一种水生态系统平衡构建方法,其特征在于,所述底部淤泥处置具体内容为:4. a kind of water ecosystem balance construction method according to claim 1, is characterized in that, the specific content of described bottom silt disposal is: 将水生态系统构建区域的淤泥挖出,挖出后的淤泥进行消毒、降解、固化处理;Excavate the silt in the area where the water ecosystem is built, and then disinfect, degrade, and solidify the excavated silt; 水生态系统构建区域底部的淤泥清除后回填种植土,每亩回填的种植土体积相同。After the silt at the bottom of the water ecosystem construction area is removed, the planting soil is backfilled, and the volume of the planting soil backfilled per mu is the same. 5.根据权利要求1所述的一种水生态系统平衡构建方法,其特征在于,所述底质改良采用底泥底质改良技术,所述底泥底质改良技术具体内容包括:5. a kind of water ecosystem balance construction method according to claim 1, is characterized in that, described bottom quality improvement adopts bottom mud bottom quality improvement technology, and described bottom mud bottom quality improvement technology specific content comprises: 一:种植土消毒1: Planting soil disinfection 使用漂白粉作为消毒剂,具体操作步骤如下:Use bleach as a disinfectant, the specific steps are as follows: 准备足量的含氯量为25%~30%的漂白粉;Prepare a sufficient amount of bleaching powder with a chlorine content of 25% to 30%; 准备足量的尿素;Prepare enough urea; 对水生态系统构建区域面积进行测量;Measure the area of the water ecosystem construction area; 按照测量面积配制溶解有漂白粉的漂白液,按照每亩5-7千克的漂白粉比例配制,所述漂白液中漂白粉和水的比例为1:10;Prepare the bleaching solution dissolved with bleaching powder according to the measured area, prepare according to the bleaching powder ratio of 5-7 kilograms per mu, and the ratio of bleaching powder and water in the bleaching solution is 1:10; 按照每亩66千克所述漂白液进行均匀泼洒,泼洒后静置24小时;Sprinkle evenly according to 66 kilograms of bleach per mu, and let it stand for 24 hours after splashing; 按照测量面积配置尿素溶液,按照每亩5-7千克的比例配制,所述尿素和水的比例为1:10;Configure urea solution according to the measurement area, prepare according to the ratio of 5-7 kilograms per mu, and the ratio of urea and water is 1:10; 按照每亩66千克所述尿素溶液均匀泼洒,泼洒后自然消毒5-6天;Sprinkle evenly according to the urea solution of 66 kilograms per mu, and sterilize naturally for 5-6 days after splashing; 所述种植土消毒完成。The disinfection of the planting soil is completed. 二:底质改善Two: Substrate improvement 消毒完成后3-5天内,向水生态系统构建区域的底泥中投放定量的芽孢杆菌、光合细菌、硝化细菌、脱氮菌,每亩中的投放密度相同,其中芽孢杆菌、光合细菌、硝化细菌、脱氮菌的比例为1:1:1:1,使用专利号为CN200420109978.3,专利名称为一种向水体污泥投加微生物菌剂的装置进行芽孢杆菌、光合细菌、硝化细菌、脱氮菌向所述种植土中的投放。Within 3-5 days after the disinfection is completed, put a certain amount of Bacillus, photosynthetic bacteria, nitrifying bacteria, and denitrifying bacteria into the bottom mud of the water ecosystem construction area. The ratio of bacteria and nitrogen-removing bacteria is 1:1:1:1, and the patent number is CN200420109978.3, and the patent name is a device for adding microbial agents to water sludge for Bacillus, photosynthetic bacteria, nitrifying bacteria, The release of denitrification bacteria into the planting soil. 三:微量元素配比Three: Trace element ratio 向所述种植土中投加微量元素肥,所述微量元素肥在水生态系统构建区域等密度投放。Add trace element fertilizers to the planting soil, and the trace element fertilizers are placed in equal density in the area where the water ecosystem is constructed. 6.根据权利要求1所述的一种水生态系统平衡构建方法,其特征在于,所述沉水植物群落构建具体内容为:6. A kind of water ecosystem balance construction method according to claim 1, is characterized in that, the concrete content of described submerged plant community construction is: 向水生态系统构建区域栽植苦草、伊乐藻、轮叶黑藻、金鱼藻,每亩中的栽植密度相同,其中所述苦草的栽植密度为40-60株每平米,所述伊乐藻的栽植密度为40株每平米,所述轮叶黑藻的栽植密度为10-15芽每从,25-36从每平米,所述金鱼藻栽植密度为7芽每从,10从每平米。To the water ecosystem construction area planting balsamic grass, Elodea, Hydrilla verticillium, hornwort, the planting density in every mu is the same, wherein the planting density of said licorice is 40-60 strains per square meter, the planting density of said elodea The planting density is 40 plants per square meter, the planting density of the Hydrilla verticillium is 10-15 buds per bud, 25-36 buds per square meter, and the hornwort planting density is 7 buds per bud, 10 buds per square meter. 7.根据权利要求1所述的一种水生态系统平衡构建方法,其特征在于,所述水生群落构建具体内容为:7. A kind of water ecosystem balance construction method according to claim 1, is characterized in that, described aquatic community construction specific content is: 向水生态系统构建区域投放螺类、蚌类、鱼类、枝角类水生动物,每亩中的投放密度相同,其中所述螺类的投放密度为2-3个每平方厘米,所述蚌类的投放密度为5-6个每平方厘米,所述鱼类的投放密度为10尾每平方米,所述枝角类的投放密度为1-2个每平方厘米。Throw in snails, mussels, fish, and cladocera aquatic animals to the water ecosystem construction area, and the density of putting in every mu is the same, wherein the density of putting in the snails is 2-3 per square centimeter, and the mussels The stocking density of species is 5-6 per square centimeter, the stocking density of described fish is 10 tails per square meter, and the stocking density of described cladocera is 1-2 per square centimeter. 8.根据权利要求1所述的一种水生态系统平衡构建方法,其特征在于,所述微生物群落构建具体内容为:8. a kind of water ecosystem balance construction method according to claim 1, is characterized in that, described microbial community construction specific content is: 向水生态系统构建区域投放有益复合微生物,每亩中的所述有益复合微生物投放量相同。Add beneficial composite microorganisms to the water ecosystem construction area, and the dosage of the beneficial composite microorganisms in each mu is the same. 9.根据权利要求1所述的一种水生态系统平衡构建方法,其特征在于,所述后期管护的具体内容为:9. a kind of water ecosystem balance construction method according to claim 1, is characterized in that, the specific content of described late stage management and protection is: 对水质进行持续监测;Continuous monitoring of water quality; 根据水质实际情况定期进行底质改善;Regularly carry out bottom quality improvement according to the actual situation of water quality; 根据水质实际情况定期进行沉水植物栽植或者清理;Plant or clean submerged plants on a regular basis according to the actual water quality; 根据水质实际情况定期进行水生动物的投放及清理;According to the actual situation of water quality, release and clean up aquatic animals on a regular basis; 根据水质实际情况定期进行微生物群落的调整。Adjust the microbial community regularly according to the actual situation of water quality.
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