CN101671079A - Method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance - Google Patents

Method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance Download PDF

Info

Publication number
CN101671079A
CN101671079A CN200810200813A CN200810200813A CN101671079A CN 101671079 A CN101671079 A CN 101671079A CN 200810200813 A CN200810200813 A CN 200810200813A CN 200810200813 A CN200810200813 A CN 200810200813A CN 101671079 A CN101671079 A CN 101671079A
Authority
CN
China
Prior art keywords
water
fishes
fish
shellfishes
fresh
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN200810200813A
Other languages
Chinese (zh)
Other versions
CN101671079B (en
Inventor
张饮江
杜佳沐
张磊
罗坤
徐晶
何培民
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Shanghai Maritime University
Shanghai Ocean University
Original Assignee
Shanghai Maritime University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Shanghai Maritime University filed Critical Shanghai Maritime University
Priority to CN200810200813XA priority Critical patent/CN101671079B/en
Publication of CN101671079A publication Critical patent/CN101671079A/en
Application granted granted Critical
Publication of CN101671079B publication Critical patent/CN101671079B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Abstract

The invention discloses a method for constructing ntaxial system ecology for fishes, grasses and shellfishes in the fresh-water substance, which is characterized by effectively combining the ecological character of water with the ecological and physiological properties of aquatic organisms to build and repair the ecology of the water substance by the synergy of the symbiotic mode of various organisms such as sunken plants, emergent aquatic plants, floating plants, shellfishes, filter fishes, carnivorous fishes, predatory fishes, omnivorous fishes and herbivorous fishes, giving full play to theself-purification capacity of the ecological system of the water substance, controlling pollution to the water substance and protecting the environment of the waters. The method of the constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance of the invention can be suitably popularized in and applied to waters such as rivers, lakes, pools and streams.

Description

The method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance
Technical field:
The present invention relates to the method that a kind of fresh water water ecology makes up, particularly relate to a kind of method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance.
Background technology:
Along with society, expanding economy, the waters is built more and more, simultaneously, since human to the irrational development and use of natural resources, and industrial and agricultural production pollutes water surrounding, cause algae and water to be grown, the water quality rapid deterioration, in addition smelly, had a strong impact on hydrobiological normal development and breeding, destroyed the balance of aquatic ecosystem, the direct or indirect human existence that threatens.Therefore, water pollution control and improvement more and more are subjected to people's great attention, at present the pollution control and the improvement method of fresh water water body are arisen at the historic moment, and mainly contain physics method, chemical method, biological process.The physics method has methods such as mechanical filter, dredging bed mud, light adjusting, regulation of level, electrion, ultrasonic wave, and these technique effects are for the moment more obvious, but are difficult for popularizing, and the cost height is difficult to extensive enforcement.Chemical method effect in short-term is more obvious, but in the course of time, drug-fast algae can occur in the water, algae removal usefulness descends gradually, and shorten at the interval that causes offeing medicine, the amount that adds increases, the kind of algicide is frequently changed, and environment is easily caused secondary pollution, and chemical agent is unfavorable for the normal growth of waterplant, hydrocoles, influence the formation of aquatic ecosystem, can't reach the lively beautiful effect of water ecology view.Biological process is based on microorganism, an amount of microbial strains, can quicken the decomposition of water pollutant, play the effect that purifies water, the reproduction speed of microorganism is surprising, being how much levels increases, breeding meeting more or less each time produces some variation kinds, cause microbiological treatment water quality ability drop, microbial numbers is difficult to control usually, and its growth is subjected to environmental influence very big, for example temperature, air pressure or the like, the resolvent of microorganism can cause water quality to degenerate once more simultaneously, and requires also more and more higher to the microbiobacterial agent environmental safety assessment both at home and abroad.
Making up and the reparation water ecosystem, is that water pollution is controlled and administered and the vital link of protection water area ecological environment.Though and the purification of water quality mode of single cropping waterplant or single input hydrocoles produces effect in a short time, be unfavorable for the balance, stable of water ecosystem, be unfavorable for long-term recovery to water ecosystem.How making up and recovering water ecosystem has become water pollution control and has administered the key technical problem that need urgently solve.
Summary of the invention:
The objective of the invention is to provide a kind of method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance; it not only can be effectively combines the ecological characteristic of water body with hydrobiont ecological physiology characteristic; adopt multiclass species symbiosis mode to bring into play synergy; water ecology is set up and repaired; and; give full play to the self-purification capacity of water ecosystem, control water pollution, protection water environment.
The present invention is achieved in that the method for constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance of the present invention is as follows for operation in water body to achieve the above object:
(1) select kind of a planting submerged plant in advance, the fraction of coverage that described submerged plant accounts for whole water body bottom surface is 25%-35%;
(2) then treat to plant emergent after 26-30 days, density is 3-5 strain/m 2, plantation 4-6 days emergent initial stage water body is variable to be mixed, and after 9-11 days, water body begins limpid;
(3) then treat to plant floatingleaved plant and pleuston successively after 12-15 days, plantation floatingleaved plant density is 1-2 strain/m 2, it is 10%-15% that the plantation pleuston accounts for whole coverage of water;
(4) then treat to begin after 8-10 days to throw in shellfish to water body, throwing in to directly being invested in the bottom or keeping hanging on the water body middle part, throwing in density is 2-6/m 3
(5) then treat to throw in filter-feeding fish after 6-7 days, fish body specification is elected the juvenile fish of 10-15cm as, and throwing in density is 2-4 tail/m 3
(6) then treat 6-7 days after, throw in predacious fish, fish body specification is 12-18cm, throwing in density is 1-2 tail/m 3
(7) treat that then feeding habits, ominivore-fish are scraped in input on a small quantity after 6-7 days, fish body specification is elected 9-13cm as, and input density is 1 tail/m 3
(8) by observing, when the paludification phenomenon appears in water body, begin to throw in herbivorous fishes, fish body specification 15-25cm, input density is 1 tail/m 3
(9) through said process, water ecosystem makes up and finishes substantially;
(10) at ordinary times routine observation, safeguard water shield shellfish growth, survival condition.
The submerged plant group that described submerged plant is combined into by eel grass, water caltrop, hydrilla verticillata, potarnogeton lucens, waterweed, wherein the shared fraction of coverage of each species is that eel grass accounts for 35% respectively, water caltrop accounts for 25%, hydrilla verticillata accounts for 20%, potarnogeton lucens accounts for 15%, waterweed 5%.Described emergent is calamus, cattail, Spiked Loosestrife, Scirpus tabernaemontani, reed, and plants according to the size adjustment of every kind of plant.Described floatingleaved plant is a lotus, and described pleuston is a Gorgon fruit.Described shellfish is a hydriopsis cumingii.Described filter-feeding fish is silver carp, bighead.Described predacious fish is snakehead, mandarin fish.Describedly scrape feeding habits, ominivore-fish is silver xenocypris fish, bream.Described herbivorous fishes are grass carp, triangular bream.
The present invention has adopted following water shield shellfish syntaxial system and has stated each function:
Plant planting submerged plant and have the purifying water body function, increase the water body dissolved oxygen, can improve substrate, can reduce water nutrition salt in a large number, for hydrocoles provides the habitat, the horn of plenty species diversity provides favourable guarantee, improves water quality.
The plantation emergent occupies consequence in water body, emergent in can adsorbed water body suspended particle, increase the transparency of water body, it can also absorb the nutritive element of water body, prevents the generation of eutrophication, also the place that can provide hidden, perch for hydrocoles, seasonal difference, select different emergent kinds,, also have landscape effect according to its level setting.
Plantation floatingleaved plant and pleuston increase species diversity, can improve water quality, and improve landscape effect.
The input shellfish can filter suspended particle and the algae in the drinking water body, decomposes residue and organism in the bed mud, increases water transparency, suppresses algae and grows, and reduces water nutrition salt.
Throw in filter-feeding fish can ingest suspended particle and algae in the water body, increase water transparency, reduce the nutritive substance in the water body.
Throw in the herbivorous fishes waterplant that can ingest, the nutrition that waterplant is absorbed is converted into animal proteinum, prevents that waterplant from breeding in a large number.
Throw in predacious fish and can control quantity and the growth of other fish, improve the balance, stable of water ecosystem, promote substance flow, energy stream, information stream in the water body.
Throw in and scrape feeding habits, ominivore-fish on a small quantity, can remove residue and organic debris in the bottom, can decompose the organism in the water body, the suspended substance of ingesting is further kept the stable of water ecosystem, improves food chain.
The present invention has following outstanding advantage: 1, water shield shellfish syntaxial system can be brought into play synergy, more obvious than single cropping waterplant and single input hydrocoles to improving the water quality effect, improve water transparency, reduce nutritive salt, help the foundation and the recovery of water ecology; 2, promote substance flow in the aquatic ecosystem, energy stream, information stream, built good water body environment for the existence of other association of plants and animals with perching, effectively promote the aquatic organism growth conditions to form, the horn of plenty ecological diversity provides favourable guarantee; 3, the configuration structure, space-time structure and the trophic structure that help water biological species form the nature food chain, and management maintenance is convenient; 4, improve microorganism growth condition in water body and the bed mud, help improving its pollution degradation material efficient; 5, planting aquatic plants combines with putting hydrocoles in a suitable place to breed, pays attention to space-time layout and view coordination on every side, helps creating multi-form ecoscape, and global optimization embodies harmony between man and nature, beautifies the waters view; 6, pay attention to natural, ecological, the protection species diversity, effectively prevention and control alien species ecological invasion improves ecological security; 7, protection municipal water ecological safety can reduce and adopt chemical agent, mechanical filter, manually salvages, changes the process for purifying water that water etc. is wasted time and energy and cost is high, helps the water body environment ecological construction.
By the technology of the present invention, the water body of structure can promote the water ecology balance fast, for hydrobiont is created healthy, graceful living environment, and makes water quality reach good.This pattern side effect is little, easy to operate, and simple and convenient management has stronger applicability and development prospect.
The method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance of the present invention can be suitable for penetration and promotion application in river, lake, pond, waters, streams.
Embodiment:
The method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance of the present invention is described in further detail by following embodiment.
Enforcement of the present invention, addressing is carried out in river course, white lotus river rising in Ningxia and flowing into central Shaanxi, PVG, water surface area reaches 1200m 2, depth of water 2.0m.
Concrete implementation step is as follows:
1, selects kind of a planting submerged plant in advance, the submerged plant group that plantation is combined into by eel grass, water caltrop, hydrilla verticillata, potarnogeton lucens, waterweed, the fraction of coverage that the described submerged plant group that is combined into accounts for whole water body bottom surface is 28%, the fraction of coverage difference of each species, wherein eel grass accounts for 35%, water caltrop accounts for 25%, hydrilla verticillata 20%, potarnogeton lucens account for 15%, waterweed 5%;
2, secondly treat to plant emergent after 27 days, plantation calamus, cattail, Spiked Loosestrife, Scirpus tabernaemontani, reed, according to the size adjustment plantation of every kind of plant, planting density is 3-5 strain/m 2, observe water transparency variation, vegetation growth state and results of regular determination water quality, plantation 5 days emergent initial stages water body is variable to be mixed, and after 10 days, water body begins limpid, and water quality reaches the III class;
3, then treat to plant the floatingleaved plant lotus successively after 15 days, density is 1-2 strain/m 2, the pleuston Gorgon fruit accounts for whole coverage of water 12%;
4, then treating to begin after 8 days to throw in shellfish to water body is hydriopsis cumingii, throws in and divides dual mode, and a kind of is directly to be invested in the bottom, and another kind is to keep hanging on the water body middle part, and throwing in density is 4/m 3, through observation in 5 days and mensuration, hydriopsis cumingii does not have death;
5, treat that then throwing in filter-feeding fish after 6 days is silver carp, bighead, fish body specification is elected the juvenile fish of 10-15cm as, and input density is 3 tails/m 3, to measure through observation in 5 days, water quality does not have deterioration, no fish death;
6, then treat 6 days after, the input predacious fish is snakehead, mandarin fish, fish body specification is 12-18cm, input density is 1 tail/m 3, to measure through observation in 5 days, water quality does not have deterioration, no fish death;
7, treat that then feeding habits are scraped in input on a small quantity after 6 days, ominivore-fish is silver xenocypris fish, bream, fish body specification is elected 9-13cm as, and input density is 1 tail/m 3, to measure through observation in 5 days, water quality does not have deterioration, no fish death;
8, by observing, when the paludification phenomenon will appear in water body, beginning to throw in herbivorous fishes was grass carp, triangular bream, fish body specification 15-25cm, and input density is 1 tail/m 3, to measure through observation in 5 days, water quality does not have deterioration, no fish death;
9, through 95 days, water ecosystem makes up and finishes substantially, and detects water quality, and survival of water shield shellfish and upgrowth situation are observed and safeguarded in regular maintenance.
The method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance of the present invention was implemented in river course, white lotus river rising in Ningxia and flowing into central Shaanxi, PVG year June in April, 2007-2008, and water surface area reaches 1200m 2, depth of water 2.0m, water quality is the IV-V class before the ecological structure of water shield shellfish, water quality leading indicator total nitrogen TN average out to 3.42mg/L, total phosphorus TP average out to 0.25mg/L, ammonia nitrogen NH 4-N average out to 2.49mg/L, permanganate index COD MnAverage out to 10.38mg/L, dissolved oxygen DO average out to 5.48mg/L, transparency average out to 30cm.The ecological back that makes up of water shield shellfish produces ecological effect preferably to water body, and water quality reaches obvious improvement, and total nitrogen TN has reduced by 67.7%, total phosphorus TP has reduced by 75%, ammonia nitrogen NH 4-N has reduced by 75%, permanganate index COD MnReduced by 77%, dissolved oxygen DO raise 63%, transparency is up to 2.0m, water quality totally reaches national surface water II-III class standard, the restoration of the ecosystem effect is very remarkable.

Claims (9)

1, a kind of method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance is characterized in that this method is as follows for operation in water body:
(1) select kind of a planting submerged plant in advance, the fraction of coverage that described submerged plant accounts for whole water body bottom surface is 25%-35%;
(2) then treat to plant emergent after 26-30 days, density is 3-5 strain/m 2, the plantation emergent initial stage 4-6 sky and water are variable mixes, and after 9-11 days, water body begins limpid;
(3) then treat to plant floatingleaved plant and pleuston successively after 12-15 days, plantation floatingleaved plant density is 1-2 strain/m 2, it is 10%-15% that the plantation pleuston accounts for whole coverage of water;
(4) then treat to begin after 8-10 days to throw in shellfish to water body, throwing in to directly being invested in the bottom or keeping hanging on the water body middle part, throwing in density is 2-6/m 3
(5) then treat to throw in filter-feeding fish after 6-7 days, fish body specification is elected the juvenile fish of 10-15cm as, and throwing in density is 2-4 tail/m 3
(6) then treat 6-7 days after, throw in predacious fish, fish body specification is 12-18cm, throwing in density is 1-2 tail/m 3
(7) treat that then feeding habits, ominivore-fish are scraped in input on a small quantity after 6-7 days, fish body specification is elected 9-13cm as, and input density is 1 tail/m 3
(8) by observing, when the paludification phenomenon will appear in water body, begin to throw in herbivorous fishes, fish body specification 15-25cm, input density is 1 tail/m 3
(9) through said process, water ecosystem makes up and finishes substantially;
(10) at ordinary times routine observation, safeguard water shield shellfish growth, survival condition.
2, the method for constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance according to claim 1, it is characterized in that the submerged plant group that described submerged plant is combined into by eel grass, water caltrop, hydrilla verticillata, potarnogeton lucens, waterweed, wherein the shared fraction of coverage of each species is that eel grass accounts for 35% respectively, water caltrop accounts for 25%, hydrilla verticillata accounts for 20%, potarnogeton lucens accounts for 15%, waterweed 5%.
3, the method for constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance according to claim 1 is characterized in that described emergent is calamus, cattail, Spiked Loosestrife, Scirpus tabernaemontani, reed, and plants according to the size adjustment of every kind of plant.
4, the method for constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance according to claim 1 is characterized in that described floatingleaved plant is a lotus, and described pleuston is a Gorgon fruit.
5, the method for constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance according to claim 1 is characterized in that described shellfish is a hydriopsis cumingii.
6, the method for constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance according to claim 1 is characterized in that described filter-feeding fish is silver carp, bighead.
7, the method for constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance according to claim 1 is characterized in that described predacious fish is snakehead, mandarin fish.
8, the method for constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance according to claim 1 is characterized in that describedly scraping feeding habits, ominivore-fish is silver xenocypris fish, bream.
9, the method for constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance according to claim 1 is characterized in that described herbivorous fishes are grass carp, triangular bream.
CN200810200813XA 2008-10-07 2008-10-07 Method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance Expired - Fee Related CN101671079B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN200810200813XA CN101671079B (en) 2008-10-07 2008-10-07 Method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN200810200813XA CN101671079B (en) 2008-10-07 2008-10-07 Method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance

Publications (2)

Publication Number Publication Date
CN101671079A true CN101671079A (en) 2010-03-17
CN101671079B CN101671079B (en) 2011-05-11

Family

ID=42018538

Family Applications (1)

Application Number Title Priority Date Filing Date
CN200810200813XA Expired - Fee Related CN101671079B (en) 2008-10-07 2008-10-07 Method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance

Country Status (1)

Country Link
CN (1) CN101671079B (en)

Cited By (21)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102092857A (en) * 2010-12-16 2011-06-15 北京市水利科学研究所 Method for restoring river/lake water system by biological chain construction technology
CN102206005A (en) * 2011-03-24 2011-10-05 华东师范大学 River ecological reactor system and construction method thereof
CN102372366A (en) * 2011-06-20 2012-03-14 上海太和水环境科技发展有限公司 Method for restoring aquatic ecology by using snakeheads
CN102372363A (en) * 2011-06-20 2012-03-14 上海太和水环境科技发展有限公司 Method for restoring aquatic ecology by using fennelleaf pondweed herb
CN103858630A (en) * 2014-02-18 2014-06-18 深圳市益水生态科技有限公司 Construction method for sustainable ecological landscape water body
CN104230001A (en) * 2014-09-30 2014-12-24 浙江海洋学院 Freshwater lake ecological alga control method
CN105236579A (en) * 2015-09-28 2016-01-13 四川鑫淼环保科技有限责任公司 Method for controlling the nutritional salt balance between lake sediment and water interface
CN105254015A (en) * 2015-09-28 2016-01-20 四川鑫淼环保科技有限责任公司 Food chain reconstruction method for lake water ecological management
CN106561238A (en) * 2016-11-07 2017-04-19 南大(常熟)研究院有限公司 Method for constructing aquatic organism functional group
CN107223606A (en) * 2017-06-26 2017-10-03 铜仁市万山区生态渔业养殖有限公司 A kind of stereoscopic cultivation method of bighead
CN107804916A (en) * 2017-11-17 2018-03-16 博元生态修复(北京)有限公司 Ecosystem construction method in a kind of water body
CN107804914A (en) * 2017-11-13 2018-03-16 华北电力大学 A kind of method based on food web regulation and control lake alga eruption
CN108901789A (en) * 2018-06-11 2018-11-30 中国科学院南京地理与湖泊研究所 A kind of method of the culture of ornamental fish after landscape water body ecological system degradation
CN109179936A (en) * 2018-08-15 2019-01-11 上海水生环境工程有限公司 A kind of in-situ treatment method suitable for gently polluting cleaning pool restoration of the ecosystem
CN109516564A (en) * 2018-12-05 2019-03-26 广州市环境保护工程设计院有限公司 A kind of restorative procedure of black and odorous water ecological community
CN110078301A (en) * 2019-04-24 2019-08-02 中水北方勘测设计研究有限责任公司 A method of purifying small-sized landscape lake water quality
CN111547858A (en) * 2020-05-20 2020-08-18 北京林业大学 Method for treating water eutrophication by using various submerged plants and aquatic animals
CN111820155A (en) * 2020-05-28 2020-10-27 中国水产科学研究院南海水产研究所 Pond culture method of eleutheronema tetradactylum
CN112320959A (en) * 2020-10-16 2021-02-05 中国环境科学研究院 Comprehensive treatment method for urban water pollution ecological restoration
CN113170708A (en) * 2021-04-25 2021-07-27 北京市水科学技术研究院 Method for constructing underwater ecosystem of river and lake supplemented with reclaimed water
CN116831020A (en) * 2021-01-18 2023-10-03 何春远 Aquatic organism artificial ecological system construction method and application thereof

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DK0386578T3 (en) * 1989-03-08 1995-03-20 Decisions Investments Corp Closed ecological system
CN1162333C (en) * 2001-12-17 2004-08-18 中国科学院武汉植物研究所 Method of restoring nutrition enriched shallow lake aquatic vegetation
CN1562809A (en) * 2004-03-27 2005-01-12 中国科学院水生生物研究所 Method for controlling water bloom of blue algae
CN100418411C (en) * 2007-03-22 2008-09-17 中国水产科学研究院长江水产研究所 Pool culturing composite system with water-saving and safety function

Cited By (23)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102092857A (en) * 2010-12-16 2011-06-15 北京市水利科学研究所 Method for restoring river/lake water system by biological chain construction technology
CN102206005A (en) * 2011-03-24 2011-10-05 华东师范大学 River ecological reactor system and construction method thereof
CN102372366A (en) * 2011-06-20 2012-03-14 上海太和水环境科技发展有限公司 Method for restoring aquatic ecology by using snakeheads
CN102372363A (en) * 2011-06-20 2012-03-14 上海太和水环境科技发展有限公司 Method for restoring aquatic ecology by using fennelleaf pondweed herb
CN103858630A (en) * 2014-02-18 2014-06-18 深圳市益水生态科技有限公司 Construction method for sustainable ecological landscape water body
CN104230001A (en) * 2014-09-30 2014-12-24 浙江海洋学院 Freshwater lake ecological alga control method
CN105236579A (en) * 2015-09-28 2016-01-13 四川鑫淼环保科技有限责任公司 Method for controlling the nutritional salt balance between lake sediment and water interface
CN105254015A (en) * 2015-09-28 2016-01-20 四川鑫淼环保科技有限责任公司 Food chain reconstruction method for lake water ecological management
CN106561238A (en) * 2016-11-07 2017-04-19 南大(常熟)研究院有限公司 Method for constructing aquatic organism functional group
CN107223606A (en) * 2017-06-26 2017-10-03 铜仁市万山区生态渔业养殖有限公司 A kind of stereoscopic cultivation method of bighead
CN107804914A (en) * 2017-11-13 2018-03-16 华北电力大学 A kind of method based on food web regulation and control lake alga eruption
CN107804916A (en) * 2017-11-17 2018-03-16 博元生态修复(北京)有限公司 Ecosystem construction method in a kind of water body
CN108901789A (en) * 2018-06-11 2018-11-30 中国科学院南京地理与湖泊研究所 A kind of method of the culture of ornamental fish after landscape water body ecological system degradation
CN109179936A (en) * 2018-08-15 2019-01-11 上海水生环境工程有限公司 A kind of in-situ treatment method suitable for gently polluting cleaning pool restoration of the ecosystem
CN109179936B (en) * 2018-08-15 2021-05-25 上海水生环境工程有限公司 In-situ treatment method suitable for ecological restoration of light-pollution clean pond
CN109516564A (en) * 2018-12-05 2019-03-26 广州市环境保护工程设计院有限公司 A kind of restorative procedure of black and odorous water ecological community
CN110078301A (en) * 2019-04-24 2019-08-02 中水北方勘测设计研究有限责任公司 A method of purifying small-sized landscape lake water quality
CN111547858A (en) * 2020-05-20 2020-08-18 北京林业大学 Method for treating water eutrophication by using various submerged plants and aquatic animals
CN111820155A (en) * 2020-05-28 2020-10-27 中国水产科学研究院南海水产研究所 Pond culture method of eleutheronema tetradactylum
CN112320959A (en) * 2020-10-16 2021-02-05 中国环境科学研究院 Comprehensive treatment method for urban water pollution ecological restoration
CN112320959B (en) * 2020-10-16 2021-11-30 中国环境科学研究院 Comprehensive treatment method for urban water pollution ecological restoration
CN116831020A (en) * 2021-01-18 2023-10-03 何春远 Aquatic organism artificial ecological system construction method and application thereof
CN113170708A (en) * 2021-04-25 2021-07-27 北京市水科学技术研究院 Method for constructing underwater ecosystem of river and lake supplemented with reclaimed water

Also Published As

Publication number Publication date
CN101671079B (en) 2011-05-11

Similar Documents

Publication Publication Date Title
CN101671079B (en) Method of constructing ntaxial system ecology for fishes, grasses and shellfishes in fresh-water substance
Pillay Aquaculture and the Environment
CN103103960B (en) A kind of integral method administered for Water Environment In Lakes
CN103276696B (en) A kind of underwater slope protection based on ecology bag and Ecological water treatment method
CN101461337A (en) Pond culture method of grouper
Sosa-Villalobos et al. Diagnosis of the current state of aquaculture production systems with regard to the environment in Mexico
CN101885541A (en) Comprehensive treatment method of water eutrophication by anti-algae insects
CN108142329A (en) The raw mullet seedling desalination in sea is cultivated and high benefit, the ecological cultivation method of low blowdown
JP2003239240A (en) Method for cultivating coastal wetlands by using naturally decomposable plant material, and coastal wetlands
O'Sullivan Ecological effects of sewage discharge in the marine environment
Branch et al. Synopsis of the impact of artificially opening the mouth of the Bot River Estuary: implications for management
JP2011010645A (en) Marine water-circulatory natural-type fish-and-shellfish breeding system
CN101622973A (en) Soilless Nereid breeding method
CN102084842B (en) Method for controlling algae in freshwater pond by cultivating mullets
CN109678304A (en) A kind of systematization processing system of the exceeded shallow well water of iron content for Cultured Tenualosa Reevesii
Tagliarolo Acidification in aquatic systems
El-Sayed Intensive culture.
Szuster Shrimp farming in Thailand’s Chao Phraya river delta: Boom, bust and echo
Hargrave Impacts of man’s activities on aquatic systems
Ghosh et al. Eutrophication: Causative factors and remedial measures
Szuster Shrimp farming in Thailand’s Chao Phrya River Delta
KR20120138484A (en) Cultivating substrate for breeding shellfish
Golski et al. Habitat variability and fish species structure in the Kończak stream
Zieren et al. Significant coastal habitats, wildlife and water resources in Lampung
CN115745194A (en) Water ecology quick system restoration method for medium and large-sized freshwater lake

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20110511

Termination date: 20151007

EXPY Termination of patent right or utility model