CN112811607A - Method for constructing lake and reservoir water ecosystem - Google Patents
Method for constructing lake and reservoir water ecosystem Download PDFInfo
- Publication number
- CN112811607A CN112811607A CN202110272804.7A CN202110272804A CN112811607A CN 112811607 A CN112811607 A CN 112811607A CN 202110272804 A CN202110272804 A CN 202110272804A CN 112811607 A CN112811607 A CN 112811607A
- Authority
- CN
- China
- Prior art keywords
- water
- construction
- lake
- constructing
- aquatic
- 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.)
- Pending
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 123
- 238000000034 method Methods 0.000 title claims abstract description 19
- 238000010276 construction Methods 0.000 claims abstract description 46
- 244000005700 microbiome Species 0.000 claims abstract description 39
- 230000000694 effects Effects 0.000 claims abstract description 26
- 239000001301 oxygen Substances 0.000 claims abstract description 24
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 24
- 241001465754 Metazoa Species 0.000 claims abstract description 16
- 238000007667 floating Methods 0.000 claims abstract description 16
- 239000000463 material Substances 0.000 claims abstract description 16
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims abstract description 12
- 230000003197 catalytic effect Effects 0.000 claims abstract description 12
- 239000001257 hydrogen Substances 0.000 claims abstract description 12
- 229910052739 hydrogen Inorganic materials 0.000 claims abstract description 12
- 108090000790 Enzymes Proteins 0.000 claims abstract description 11
- 102000004190 Enzymes Human genes 0.000 claims abstract description 11
- 239000011232 storage material Substances 0.000 claims abstract description 10
- 230000006872 improvement Effects 0.000 claims abstract description 6
- -1 hydroxide ions Chemical class 0.000 claims abstract description 5
- 239000003344 environmental pollutant Substances 0.000 claims description 19
- 231100000719 pollutant Toxicity 0.000 claims description 19
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 14
- 230000000813 microbial effect Effects 0.000 claims description 12
- 238000011084 recovery Methods 0.000 claims description 7
- 238000005273 aeration Methods 0.000 claims description 6
- 238000003745 diagnosis Methods 0.000 claims description 4
- 235000013305 food Nutrition 0.000 claims description 4
- 239000000356 contaminant Substances 0.000 claims description 3
- 230000001965 increasing effect Effects 0.000 claims description 3
- 230000009467 reduction Effects 0.000 claims description 3
- 239000001963 growth medium Substances 0.000 claims description 2
- 238000012216 screening Methods 0.000 claims description 2
- 239000000126 substance Substances 0.000 abstract description 19
- 235000015097 nutrients Nutrition 0.000 abstract description 15
- 239000010802 sludge Substances 0.000 abstract description 12
- 238000006243 chemical reaction Methods 0.000 abstract description 9
- 150000003839 salts Chemical class 0.000 abstract description 7
- 230000015556 catabolic process Effects 0.000 abstract description 5
- 238000006731 degradation reaction Methods 0.000 abstract description 5
- 230000001737 promoting effect Effects 0.000 abstract 2
- 230000009286 beneficial effect Effects 0.000 abstract 1
- 241000196324 Embryophyta Species 0.000 description 29
- 241000195493 Cryptophyta Species 0.000 description 15
- 239000010410 layer Substances 0.000 description 14
- 241000251468 Actinopterygii Species 0.000 description 13
- 235000019688 fish Nutrition 0.000 description 13
- 229910052698 phosphorus Inorganic materials 0.000 description 12
- 239000011574 phosphorus Substances 0.000 description 9
- 238000000746 purification Methods 0.000 description 9
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 8
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 8
- 230000006870 function Effects 0.000 description 8
- 229910052757 nitrogen Inorganic materials 0.000 description 7
- 230000002829 reductive effect Effects 0.000 description 7
- 239000013049 sediment Substances 0.000 description 6
- 239000002245 particle Substances 0.000 description 5
- 230000004083 survival effect Effects 0.000 description 5
- 239000003795 chemical substances by application Substances 0.000 description 4
- 239000011162 core material Substances 0.000 description 4
- 238000000354 decomposition reaction Methods 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 230000029553 photosynthesis Effects 0.000 description 4
- 238000010672 photosynthesis Methods 0.000 description 4
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 4
- 238000001179 sorption measurement Methods 0.000 description 4
- 241000894007 species Species 0.000 description 4
- 241000252234 Hypophthalmichthys nobilis Species 0.000 description 3
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 3
- 229910052681 coesite Inorganic materials 0.000 description 3
- 230000001276 controlling effect Effects 0.000 description 3
- 229910052906 cristobalite Inorganic materials 0.000 description 3
- 230000012010 growth Effects 0.000 description 3
- 229910001385 heavy metal Inorganic materials 0.000 description 3
- 238000005342 ion exchange Methods 0.000 description 3
- 239000002957 persistent organic pollutant Substances 0.000 description 3
- 239000000377 silicon dioxide Substances 0.000 description 3
- 229910052682 stishovite Inorganic materials 0.000 description 3
- 229910052905 tridymite Inorganic materials 0.000 description 3
- 244000205574 Acorus calamus Species 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 2
- 235000011996 Calamus deerratus Nutrition 0.000 description 2
- 241000237858 Gastropoda Species 0.000 description 2
- 241000238631 Hexapoda Species 0.000 description 2
- 241000735470 Juncus Species 0.000 description 2
- 241000219991 Lythraceae Species 0.000 description 2
- 240000002853 Nelumbo nucifera Species 0.000 description 2
- 235000006508 Nelumbo nucifera Nutrition 0.000 description 2
- 235000006510 Nelumbo pentapetala Nutrition 0.000 description 2
- 235000014676 Phragmites communis Nutrition 0.000 description 2
- 241001647091 Saxifraga granulata Species 0.000 description 2
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 2
- 241000589886 Treponema Species 0.000 description 2
- 240000000260 Typha latifolia Species 0.000 description 2
- 230000009471 action Effects 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 230000004071 biological effect Effects 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 238000009395 breeding Methods 0.000 description 2
- 230000001488 breeding effect Effects 0.000 description 2
- 239000003054 catalyst Substances 0.000 description 2
- 238000006555 catalytic reaction Methods 0.000 description 2
- 210000005056 cell body Anatomy 0.000 description 2
- 210000000170 cell membrane Anatomy 0.000 description 2
- CETPSERCERDGAM-UHFFFAOYSA-N ceric oxide Chemical compound O=[Ce]=O CETPSERCERDGAM-UHFFFAOYSA-N 0.000 description 2
- 229910000422 cerium(IV) oxide Inorganic materials 0.000 description 2
- 230000008859 change Effects 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 230000002708 enhancing effect Effects 0.000 description 2
- 230000002550 fecal effect Effects 0.000 description 2
- 238000005189 flocculation Methods 0.000 description 2
- 230000016615 flocculation Effects 0.000 description 2
- 230000002401 inhibitory effect Effects 0.000 description 2
- MRELNEQAGSRDBK-UHFFFAOYSA-N lanthanum oxide Inorganic materials [O-2].[O-2].[O-2].[La+3].[La+3] MRELNEQAGSRDBK-UHFFFAOYSA-N 0.000 description 2
- 238000012423 maintenance Methods 0.000 description 2
- PLDDOISOJJCEMH-UHFFFAOYSA-N neodymium oxide Inorganic materials [O-2].[O-2].[O-2].[Nd+3].[Nd+3] PLDDOISOJJCEMH-UHFFFAOYSA-N 0.000 description 2
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 description 2
- KTUFCUMIWABKDW-UHFFFAOYSA-N oxo(oxolanthaniooxy)lanthanum Chemical compound O=[La]O[La]=O KTUFCUMIWABKDW-UHFFFAOYSA-N 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 230000000644 propagated effect Effects 0.000 description 2
- 229910052761 rare earth metal Inorganic materials 0.000 description 2
- 230000001105 regulatory effect Effects 0.000 description 2
- 230000009466 transformation Effects 0.000 description 2
- 244000257727 Allium fistulosum Species 0.000 description 1
- 235000008553 Allium fistulosum Nutrition 0.000 description 1
- 241000383620 Allium mongolicum Species 0.000 description 1
- 241000143060 Americamysis bahia Species 0.000 description 1
- 241000217381 Anodonta Species 0.000 description 1
- 239000002028 Biomass Substances 0.000 description 1
- 241001157813 Cercospora Species 0.000 description 1
- 241001597062 Channa argus Species 0.000 description 1
- 241000252203 Clupea harengus Species 0.000 description 1
- 241001113556 Elodea Species 0.000 description 1
- 244000268590 Euryale ferox Species 0.000 description 1
- 235000006487 Euryale ferox Nutrition 0.000 description 1
- 244000052355 Hydrilla verticillata Species 0.000 description 1
- 241000252232 Hypophthalmichthys Species 0.000 description 1
- 241000382840 Hyriopsis cumingii Species 0.000 description 1
- 240000008436 Ipomoea aquatica Species 0.000 description 1
- 235000019004 Ipomoea aquatica Nutrition 0.000 description 1
- 244000211187 Lepidium sativum Species 0.000 description 1
- 235000007849 Lepidium sativum Nutrition 0.000 description 1
- 241000237536 Mytilus edulis Species 0.000 description 1
- 241000209490 Nymphaea Species 0.000 description 1
- 235000016791 Nymphaea odorata subsp odorata Nutrition 0.000 description 1
- 241001311547 Patina Species 0.000 description 1
- 235000005205 Pinus Nutrition 0.000 description 1
- 241000218602 Pinus <genus> Species 0.000 description 1
- 241000791420 Plica Species 0.000 description 1
- 241000722195 Potamogeton Species 0.000 description 1
- 229910002637 Pr6O11 Inorganic materials 0.000 description 1
- 240000003705 Senecio vulgaris Species 0.000 description 1
- 244000113428 Sonchus oleraceus Species 0.000 description 1
- 235000006745 Sonchus oleraceus Nutrition 0.000 description 1
- 241000544047 Stuckenia pectinata Species 0.000 description 1
- 241000404975 Synchiropus splendidus Species 0.000 description 1
- 241000376029 Tachysurus fulvidraco Species 0.000 description 1
- 241000205578 Thalictrum Species 0.000 description 1
- 101710154918 Trigger factor Proteins 0.000 description 1
- 241001482311 Trionychidae Species 0.000 description 1
- 241001133085 Xenocypris davidi Species 0.000 description 1
- 244000085595 Zizania latifolia Species 0.000 description 1
- 235000004259 Zizania latifolia Nutrition 0.000 description 1
- 230000003213 activating effect Effects 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 230000005791 algae growth Effects 0.000 description 1
- 239000003619 algicide Substances 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- 210000004027 cell Anatomy 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 238000010516 chain-walking reaction Methods 0.000 description 1
- 229930002875 chlorophyll Natural products 0.000 description 1
- 235000019804 chlorophyll Nutrition 0.000 description 1
- ATNHDLDRLWWWCB-AENOIHSZSA-M chlorophyll a Chemical compound C1([C@@H](C(=O)OC)C(=O)C2=C3C)=C2N2C3=CC(C(CC)=C3C)=[N+]4C3=CC3=C(C=C)C(C)=C5N3[Mg-2]42[N+]2=C1[C@@H](CCC(=O)OC\C=C(/C)CCC[C@H](C)CCC[C@H](C)CCCC(C)C)[C@H](C)C2=C5 ATNHDLDRLWWWCB-AENOIHSZSA-M 0.000 description 1
- 238000010668 complexation reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 230000008094 contradictory effect Effects 0.000 description 1
- 229910052593 corundum Inorganic materials 0.000 description 1
- 238000012258 culturing Methods 0.000 description 1
- 210000000805 cytoplasm Anatomy 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 235000005911 diet Nutrition 0.000 description 1
- 230000037213 diet Effects 0.000 description 1
- 230000029087 digestion Effects 0.000 description 1
- 235000013399 edible fruits Nutrition 0.000 description 1
- 235000018927 edible plant Nutrition 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
- 230000002349 favourable effect Effects 0.000 description 1
- 238000011010 flushing procedure Methods 0.000 description 1
- 230000037406 food intake Effects 0.000 description 1
- 210000001035 gastrointestinal tract Anatomy 0.000 description 1
- 239000003102 growth factor Substances 0.000 description 1
- 235000019514 herring Nutrition 0.000 description 1
- 238000002513 implantation Methods 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 229920005610 lignin Polymers 0.000 description 1
- 230000000670 limiting effect Effects 0.000 description 1
- 230000005389 magnetism Effects 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 239000002609 medium Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 235000020638 mussel Nutrition 0.000 description 1
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 1
- 230000000050 nutritive effect Effects 0.000 description 1
- 210000000056 organ Anatomy 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 230000033116 oxidation-reduction process Effects 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 238000006213 oxygenation reaction Methods 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 244000062645 predators Species 0.000 description 1
- 244000038293 primary consumers Species 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 229910001404 rare earth metal oxide Inorganic materials 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 230000029058 respiratory gaseous exchange Effects 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 235000015170 shellfish Nutrition 0.000 description 1
- 239000000758 substrate Substances 0.000 description 1
- 239000002344 surface layer Substances 0.000 description 1
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 description 1
- 239000003440 toxic substance Substances 0.000 description 1
- 239000003053 toxin Substances 0.000 description 1
- 231100000765 toxin Toxicity 0.000 description 1
- 108700012359 toxins Proteins 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 230000007306 turnover Effects 0.000 description 1
- 235000013311 vegetables Nutrition 0.000 description 1
- 235000009360 water arrowhead Nutrition 0.000 description 1
- 244000209045 water arrowhead Species 0.000 description 1
- 239000003403 water pollutant Substances 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
- 229910001845 yogo sapphire Inorganic materials 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
- C02F3/327—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae characterised by animals and plants
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
Abstract
The invention relates to a method for constructing a lake and reservoir water ecosystem, which comprises the following steps: s1, firstly, carrying out water ecological basic condition construction and water quality improvement; in the construction of water ecological basic conditions, nano hydrogen storage-oxygen storage materials and catalytic materials are placed in a slow release box, and the slow release box is placed in a lake and reservoir bottom layer area and carries hydroxide ions in the natural environment to an underlying water body and a bottom layer; the water quality is improved, and a catalytic material is also filled in the slow release box to activate the enzyme activity and the microorganism activity in the water body; s2, constructing a water ecosystem; forming a vertical structure through aquatic plant construction, aquatic animal construction and microorganism construction to form an aquatic plant community, an aquatic animal community and a microorganism community; the aquatic plant construction comprises submerged plant construction, emergent aquatic plant construction and floating leaf plant construction. The invention achieves the following beneficial effects: promoting the degradation of the sludge, promoting the accelerated conversion of nutrient salt substances and naturally purifying.
Description
Technical Field
The utility model relates to the technical field of lake and reservoir ecology, in particular to a method for constructing a lake and reservoir water ecosystem.
Background
The lake is a unique resource closely related to human survival and development, and plays a great role in water supply, flood control, shipping, breeding, tourism and maintaining the ecological balance of the region. At present, due to the super-intensity development of a basin and the super-intensity utilization of lake resources, a series of problems of water environment deterioration, water resource shortage and frequent water disasters are caused.
The concrete change is as follows: the water quality improvement and treatment technology mainly focuses on research and application of single technologies such as dredging, water diversion and flow flushing, aeration and oxygenation, chemical flocculation, biological purification and the like. However, due to the characteristics of large areas of lakes and reservoirs, the current pollution situation and different climatic environments of lake and reservoir areas, the operability technology is few, the treatment cost is high, and the effect is poor.
Therefore, the construction method for the lake reservoir water ecosystem is formed by the company aiming at the lake environment. Aiming at the characteristics of water pollution at the present stage, natural elements with super-strong energy, high activity and strong power are taken as cores, and adsorption, flocculation, catalysis, degradation, complexation and ion exchange are integrated in the aspect of eliminating pollutant substances; in the aspect of microbial system construction, the microbial agent can activate a plurality of enzyme activities and promote the accelerated conversion and utilization of nutrient salt substances; in the aspect of biological recovery, the aim of enhancing the self-purification capacity of the water body is fulfilled by starting from the culture of indigenous microorganisms, plankton, microorganisms and aquatic organisms are cultured and propagated and expanded in the solution scheme of the whole system by removing pollutants and constructing a biological system, so that the dominant population of the microorganisms really forms strong power for eliminating pollutants, the water body naturally becomes alive, and the self-purification capacity of the water body is continuously enhanced.
Disclosure of Invention
The invention aims to overcome the defects of the prior art and provide a method for constructing a lake and reservoir water ecosystem, which can promote sludge degradation, promote the accelerated conversion of nutrient salt substances and can naturally purify the sludge.
The purpose of the invention is realized by the following technical scheme: a method for constructing a lake and reservoir water ecosystem comprises the following steps:
firstly, carrying out diagnosis and analysis;
the content of the diagnostic analysis includes: determining an ecological service function of the lake; analyzing a primary source of the contaminant; determining the time required for recovery according to the quantity of the pollutants; determining the amplitude and the quantity of pollutant emission reduction according to the water body environment capacity;
then, carrying out water ecological basic condition construction and water quality improvement;
during the construction of the water ecological basic condition, the nano hydrogen storage-oxygen storage material is placed in the slow release tank, the slow release tank is placed in the bottom layer area of the lake reservoir, and the slow release tank carries hydroxide ions in the natural environment to the underlying water body and the bottom layer, so that the activity of aerobic organisms is improved, the dissolved oxygen in the water body is increased, and meanwhile, the nano hydrogen storage-oxygen storage material also has a strong specific surface area and a super-strong catalytic function, so that the enzyme activity in the water body can be activated, and the activity of microorganisms can be excited;
when the water quality is lifted: adding a catalytic material into the lake to activate the enzyme activity and the microorganism activity in the water body; a nano oxygen-enriched aeration device is arranged in a region with large lake pollution. When the blue algae occurs, the blue algae removing agent is scattered into the lake.
Then, the construction of a specific water ecosystem is carried out: the vertical structure is formed by aquatic plant construction, aquatic animal construction and microorganism construction, so that an aquatic plant community, an aquatic animal community and a microorganism community are formed;
the aquatic plant is constructed, firstly, the aquatic plant is placed on the constructed floating carrier, then, soilless culture is carried out, and a biological floating island formed after the culture is thrown into a lake;
the microorganism construction comprises submerged plant construction, emergent aquatic plant construction and floating leaf plant construction; the method also comprises the construction of the biological floating island, namely, firstly placing aquatic plants on the constructed floating carrier, then carrying out soilless culture, and throwing the biological floating island formed after the culture into a lake.
Further, after the vertical structure is formed, water ecological restoration is required; and water ecological restoration, namely, artificially regulating and controlling aquatic plant communities, aquatic animal communities and microbial communities.
Further, the vertical structure is constructed to form a food chain to allow water to be ecologically balanced.
Furthermore, as the materials in the slow release box can continuously play a role for about 6 to 12 months, the materials are reasonably prepared and arranged according to the pollution degree and the water area; therefore, the hydrogen storage-oxygen storage material in the release tank is replaced by one batch every 6 to 12 months.
The invention has the following advantages:
(1) the novel natural element material capable of storing hydrogen and oxygen is placed in the slow release box and uniformly distributed on the bottom layer, and is implemented in the whole bottom layer treatment area, so that the environment of the bottom layer is mainly improved, the decomposition and transformation of substances in the bottom sludge are promoted, the residual quantity of pollutants in the bottom sludge is gradually reduced, and pollutants possibly reanalyzed in the bottom sludge are greatly reduced;
(2) in the aspect of microbial system construction, the microbial system can activate a plurality of enzyme activities, improve the biological activity and promote the accelerated conversion and utilization of nutrient salt substances;
(3) in the aspect of biological recovery, starting from culturing microorganisms, the purpose of enhancing the self-purification capacity of a water body is achieved, plankton, microorganisms and aquatic organisms are cultured, propagated and expanded in the solution scheme of the whole system through removing pollutants and constructing a biological system, so that the dominant population of the microorganisms really forms strong power for eliminating pollutants, the water body naturally becomes alive, and the purpose of natural purification is achieved.
Detailed Description
The present invention is further described below in conjunction with the following description, but the scope of the present invention is not limited to the following description.
A method for constructing a lake and reservoir water ecosystem comprises primary diagnosis and analysis, a specific construction method and subsequent recovery and maintenance.
In the diagnosis and analysis, determining the ecological service function of the lake; analyzing a primary source of the contaminant; determining the time required for recovery according to the quantity of the pollutants; and determining the magnitude and the quantity of pollutant emission reduction according to the water body environment capacity.
In the specific construction: the method comprises the steps of water ecological basic condition construction, water quality improvement and vertical structure construction;
in the construction of the water ecological basic condition, the bottom mud ecology is improved.
Because the bottom mud contains rich nitrogen and phosphorus nutritive salts, organic pollutants, heavy metal substances and the like, the vicious circle of the eutrophication problem of the water body is aggravated by consuming the dissolved oxygen of the water body and releasing various pollutants to influence the water quality of the overlying water. The material capable of storing hydrogen and oxygen in nanometer is placed in the slow release box and evenly distributed on the bottom layer, and is applied to the whole bottom layer treatment area, so that the environment of the bottom layer is mainly improved, conditions are provided for improving enzyme activity and biological activity, the decomposition and transformation of substances in the bottom sludge are promoted, the residual quantity of pollutants in the bottom sludge is gradually reduced, the pollutants which are possibly reanalyzed in the bottom sludge are greatly reduced, and favorable conditions are provided for the whole treatment.
The nano hydrogen storage-oxygen storage material in the slow release box plays a role in eliminating the bottom mud and also plays a role in fixing the bottom mud.
Eliminating: and (3) catalyzing and oxidizing to eliminate macromolecular organic matters in the sediment, for example, catalyzing and accelerating the degradation and conversion of the macromolecular nitrogenous organic matters in the sediment by ammoniation bacteria, so that the macromolecular nitrogenous organic matters are decomposed into ammonium nitrogen which can be used by plants and enter the overlying water. The catalysis promotes the microorganism to decompose the organic phosphorus in the sediment into inorganic phosphorus, and the insoluble phosphorus compound is converted into soluble phosphorus, enters into the upper water and is absorbed and utilized by the microorganism and plankton in a large amount under the aerobic condition, and the nutrient substances are removed from the water body through the biological chain.
Fixing: macromolecular organic matters in the sludge are degraded and converted to enable the sludge to be continuously desertified, then special materials are adopted to adsorb and deposit colloidal substances in a water body on a bottom layer, and the colloidal substances and the silt are fused and solidified to form a biological attachment film, so that conditions are provided for microbial implantation, nutrient substances generated by the bottom mud and the water body are continuously absorbed and utilized, and the self-cleaning capacity is comprehensively improved. Meanwhile, heavy metals are complexed and solidified in an ion exchange mode, so that toxic substances are subjected to harmless treatment.
In addition, according to the conditions of water turbidity, low transparency and reduced dissolved oxygen amount of water, a proper amount of water treatment material taking natural elements as cores is put into the water, so that the transparency is improved. The achieved effect is as follows:the (suspended) particles in the water body are adsorbed, the adsorption rate of the (suspended) particles on the suspended matters needs to reach 60% or more, the transparency of the water body is improved through sedimentation, and the photosynthesis is enhanced; increasing dissolved oxygen of water body by photosynthesis, and inhibiting H under aerobic state2S、CH4、NH3And (3) eliminating the peculiar smell of the water body when the anaerobic reaction occurs.
In water quality improvement, nutrient salt removal, algae removal, aeration, enzyme activation and microbial activity are required.
It is noted that the nano hydrogen-oxygen storage material and the catalytic material both comprise rare earth oxides, such as La2O3、CeO2、Nd2O3And also comprises TiO2、SiO2As a nano-based support. When the rare earth element accounts for a large amount, the rare earth element is a nano hydrogen storage-oxygen storage material; when TiO is present2、SiO2When the ratio is large, the catalyst is used as a catalytic material. Therefore, the mode of main function conversion can be realized by changing the formula, and the cost is saved. The main component is a La2O3 • b CeO2 • c Pr6O11 • d Nd2O3 •e SiO2 • f Al2O3 And small amounts of unavoidable impurities, wherein the coefficients a, b, c, d, e, f, g have the value ranges: a is more than or equal to 0.25, b is more than or equal to 0.30, c is more than or equal to 0.035, d is more than or equal to 0 and less than or equal to 0.015, e is more than or equal to 0.50, f is more than or equal to 0.09, and g is more than or equal to 0.014.
In removing nutrient salts: after the transparency of the water body is improved, substances such as nitrogen and phosphorus, substrate sludge, enzyme activity in the water body and microorganism activity need to be activated, and the water treatment catalytic material is usually adopted to achieve the purpose of improving physicochemical indexes. The effect that reaches is: (1) the new material realizes ion exchange, adsorption and effective oxidation reduction of interface reaction, and eliminates heavy metal harm; (2) the activity of microorganisms is catalytically activated, the ecological chain running of N, P, organic matters and the like is accelerated, the self-cleaning capacity of the water body is improved, and support is provided for ecological restoration; (3) p in the water body can generate phytoplankton with the dead weight of 500 times, N can generate phytoplankton with the dead weight of 71 times, C can generate phytoplankton with the dead weight of 12 times, N, P is a trigger factor for the growth of the phytoplankton, and the mass consumption ratio of C to N to P in the algae formation process is about 35 to 7 to 1.
In the algae removal, the blue algae removal agent is used for removing algae. The blue algae removing agent can change cell membrane potential after entering water body, and can be directly combined with algae protein or replace Mg2+So that the lamellar structure of the cell body is loosened or destroyed, the cell membrane is folded, the content is oozed out, the cell body is endangered to be disintegrated, the photosynthesis can not be normally carried out, and the chlorophyll content is gradually reduced. Excessive nitrogen and phosphorus in the water body are adsorbed in a large amount, so that the survival of the blue algae lacks growth factors, and algae cells gradually die due to loss of photosynthesis and nutrient substances and are deposited and accumulated to a bottom layer under the adsorption action. After the algae die and settle, under the catalytic action of the algaecide, the degradation of algal toxins is promoted, the decomposition of algal protoplasm into N, P and other nutrient substances is accelerated, the propagation and growth of microorganisms are accelerated, the nutrient substances in the water body and the bottom mud are gradually converted into other nutrient sources of plankton to be utilized, and then the nutrient sources are taken out of the water body by the utilization of fishes, so that the aim of bioremediation is fulfilled.
Because dissolved oxygen is essential for respiration of organisms in water and is also necessary for ensuring inorganic decomposition of organic matters in water, the nano oxygen-enriched aeration device is arranged in a region with large pollution in lakes and at a pollutant inlet, so that indigenous microorganisms in the original water area can recover activity. The ammonia nitrogen concentration is further reduced by a nano oxygen-enriched aeration technology.
The participation of nano hydrogen storage-oxygen storage materials is still needed when activating enzyme and microbial activity. The core material in the box body device has strong polarity and magnetism, has the functions of storing hydrogen and oxygen, can carry hydroxide ions in natural environment to the underlying water body and the bottom layer, and improves the activity of aerobic organisms and increases the dissolved oxygen in the water body; the catalyst has strong specific surface area and super-strong catalytic function, can activate a plurality of enzyme activities, and can excite the activity of microorganisms; can promote the conversion and utilization of nutrient substances and greatly reduce the residual quantity of ammonia nitrogen, phosphorus and other substances on the bottom layer.
When the vertical structure is constructed, the water body is recovered in a natural purification mode after construction.
The original microorganisms (namely indigenous microorganisms) in the lake are utilized to improve the water quality, and the essential difference of the water quality and the artificially-thrown exogenous biological bacteria is mutually contradictory.
As the depth of water in lakes and reservoirs, the degree of pollution and the like directly influence the survival and the propagation of various organisms in the water body, and some indigenous microorganisms are endangered to disappear, the removal of water pollutants and the self-purification capacity of the water body are greatly influenced. Therefore, the indigenous microorganisms are screened, domesticated and cultured to eliminate pollutants, absorb and utilize nutrients, improve the water body purification function and realize harmless transfer and resource utilization of the pollutants. Collecting the background muddy water in the lake and reservoir, screening and domesticating indigenous microorganisms from the muddy water, putting the muddy water into a microorganism culture medium, cultivating and breeding dominant microbial populations in a targeted manner, and putting the dominant microbial populations into the lake to restore the self-purification capacity of the water body.
When the aquatic plant community is constructed, submerged plants, emergent plants and floating-leaf plants are selected for matching according to different water depths and seasons, and necessary ecological floating islands are equipped on projects needing landscape effects or special water bodies.
In the scheme, the submerged plant is selected from one or more of common sowthistle herb, hydrilla verticillata, potamogeton pectinatus, potamogeton bambusoides, waterfish algae, waterweed and the like. The density is 60-150 strains/m according to different types2In the meantime.
In the scheme, the emergent aquatic plants comprise one or more of pinus, reed, cattail, loosestrife, allium fistulosum, thalictrum ramosissimum, lotus, calamus, saxifrage, juncus effuses, droughhaired groundsel herb and the like. The density is 1-30 plants/m according to different species2In the meantime.
In the scheme, the floating-leaf plants comprise water lily, vegetable, soft-shelled turtle, gorgon fruit and the like. The density is 1-5 strains/m according to different types2In the meantime.
The ecological floating island is characterized in that extra-light biological carriers are spliced, combined and built into a required area or geometric shape according to different design requirements, the ecological floating island is placed into a damaged water body, aquatic (terrestrial) plants which are screened and domesticated and have strong functions of absorbing organic pollutants in water are planted into a prefabricated floating carrier planting groove, the plants grow in an environment similar to soilless culture, plant root systems naturally extend and suspend in the water body, organic pollutants such as ammonia, nitrogen, phosphorus and the like in the water are absorbed and absorbed, living and attaching conditions are provided for fishes, shrimps, insects and microorganisms in the water body, and compounds for inhibiting algae growth are released. Under the combined action of plants, animals, insects and microorganisms, the environmental water quality is purified, and the purpose of restoring and rebuilding a water body ecological system is achieved.
In the scheme, the planted plants comprise edible plants such as cress, water spinach, water bamboo, arrowhead and the like and one or more ornamental plants such as carlsbergia, reed, cattail, loosestrife, allium mongolicum regel, relish flower, lotus flower, calamus, saxifrage, juncus effuses, drooping umbrellata and the like. The density is 1-30 plants/m according to different species2In the meantime.
In the construction of aquatic animal communities, food network chains are formed. And determining the type and the quantity of the thrown fishes according to the combination of the classic biological manipulation theory and the non-classic biological manipulation theory and the actual fish community structure in the water body to construct an aquatic ecosystem so as to obtain healthy water circulation.
The classical biological manipulation theory is that the fish community structure is adjusted to reduce the fishes which eat plankton, so as to strengthen the population of plankton, thereby controlling the excessive reproduction of algae, improving the transparency of water body and improving the water quality, namely, the carnivorous fish is put in a stocking or the plankton predatory fishes are killed, so as to strengthen the population of plankton, increase the feeding pressure to the plankton, and the plankton is taken as a direct predator of the plankton and acts on the downward effect of the plankton on the algae.
The non-classical biological manipulation theory is that the biomass of fierce fishes is controlled, planktonic predatory fishes are stocked, the cyanobacterial bloom species are directly herded by utilizing the special ingestion characteristics and the digestion mechanism of the zooplanktonic predatory fishes, and the core target positioning is to control the cyanobacterial bloom. In the application and practice of non-classical biological manipulation, silver carps and bighead carps are the most commonly used species due to the advantages of high survival rate of artificial propagation, long survival period, wider diet, incapability of natural propagation in lakes, easy population control, good biological manipulation stability and the like.
In the scheme, the fish comprises silver carp, bighead carp, snakehead fish,One or more of mandarin fish, weever, yellow catfish, xenocypris davidi bleeker, herring, etc. The stocking density is 1 tail/100 m21 tail/1000 m2。
In addition, a benthic organism community was constructed. For example, by feeding shellfish benthos, some bivalves ingest deposits from their habitat only in the area of the bed mud surface where the organisms fall, while some animals have specialized organs to obtain food from the water-mud interface and gastropods graze organic debris. The end result of this feeding pattern is the formation of a large number of fecal particles and their deposition on the surface of the sediment. Many animals prefer to digest these fecal particles, and each time they pass through the digestive tract of the benthic animals, a layer of microorganisms covering the surface is stripped off, and when it is again exposed to the environment, the microorganisms will reuse it, and thus be ingested, utilized and decomposed by primary consumers and decomposers. In this way some invertebrate indigestible plant matter such as cellulose and lignin break down rapidly. The large benthonic animals continuously dig holes and discharge excrement, so that the turnover rate of the surface layer of the water body sediment of a plurality of centimeters is very high. This process is called "biostirring" and it mixes organic matter into the sediment as finer particles that are ultimately used by small and medium sized benthonic animals. In addition, the large benthonic animals can also remove the periphyton covering layer on the surface of the submerged plant to promote the growth of the aquatic plant.
In the scheme, the benthos comprises one or more of pear-shaped treponema annulate, cercospora patina treponema, plica cristata, anodonta denticulata, hyriopsis cumingii and the like. The density of the snails is 2-10 g/m2The density of the mussels is 20-40 g/m2。
In the recovery maintenance, the water ecological system is reasonable and healthy in structure, plays a full role and operates stably and in a long-acting manner by optimally regulating and controlling the microbial population, the fish community, the higher aquatic plant community and the benthos community.
The above examples only represent preferred embodiments, and the description thereof is more specific and detailed, but not to be construed as limiting the scope of the invention. It should be noted that, for a person skilled in the art, several variations and modifications can be made without departing from the inventive concept, which falls within the scope of the present invention.
Claims (7)
1. A method for constructing a lake and reservoir water ecosystem is characterized by comprising the following steps: the method comprises the following steps:
s1, firstly, carrying out water ecological basic condition construction and water quality improvement;
in the construction of the water ecological basic condition, the nano hydrogen storage-oxygen storage material and the catalytic material are placed in the slow release box, and the slow release box is placed in the bottom layer area of the lake reservoir and carries hydroxide ions in the natural environment to the underlying water body and the bottom layer, so that the activity of aerobic organisms is improved, and the dissolved oxygen in the water body is increased;
the water quality is improved, the slow release box is also filled with a catalytic material to activate the enzyme activity and the microorganism activity in the water body, and meanwhile, a nano oxygen-enriched aeration device is arranged in a region with greater lake pollution;
s2, constructing a water ecosystem;
forming a vertical structure through aquatic plant construction, aquatic animal construction and microorganism construction to form an aquatic plant community, an aquatic animal community and a microorganism community;
the aquatic plant construction comprises submerged plant construction, emergent aquatic plant construction and floating leaf plant construction.
2. The method for constructing the lake and reservoir water ecosystem, according to claim 1, is characterized in that: the nano hydrogen storage-oxygen storage material and the catalytic material in the release box are replaced by one batch every 6 to 12 months.
3. The method for constructing the lake and reservoir water ecosystem, according to claim 2, wherein: the aquatic plant construction comprises submerged plant construction, emergent aquatic plant construction and floating leaf plant construction;
the microorganism construction comprises the steps of collecting muddy water at the bottom of a lake, screening out microorganisms, putting the microorganisms into a microorganism culture medium for mass culture, and finally putting the microorganisms into the lake.
4. A method for constructing a lake and reservoir water ecosystem, according to claim 3, wherein: the aquatic plant construction also comprises biological floating island construction, namely, the aquatic plant is placed on the constructed floating carrier, then soilless culture is carried out, and the biological floating island formed after the culture is thrown into a lake.
5. The method for constructing the lake and reservoir water ecosystem, according to claim 4, is characterized in that: when the vertical structure is constructed, a food chain is formed to balance water ecology.
6. The method for constructing the lake and reservoir water ecosystem, according to claim 5, wherein: before the water ecological basic condition is constructed, diagnosis and analysis are needed;
the content of the diagnostic analysis includes: determining an ecological service function of the lake; analyzing a primary source of the contaminant; determining the time required for recovery according to the quantity of the pollutants; and determining the magnitude and the quantity of pollutant emission reduction according to the water body environment capacity.
7. The method for constructing the lake and reservoir water ecosystem, according to claim 6, is characterized in that: after the vertical structure is formed, water ecological restoration is needed;
and the water ecological restoration is to artificially regulate and control an aquatic plant community, an aquatic animal community and a microbial community.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202110272804.7A CN112811607A (en) | 2021-03-12 | 2021-03-12 | Method for constructing lake and reservoir water ecosystem |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202110272804.7A CN112811607A (en) | 2021-03-12 | 2021-03-12 | Method for constructing lake and reservoir water ecosystem |
Publications (1)
Publication Number | Publication Date |
---|---|
CN112811607A true CN112811607A (en) | 2021-05-18 |
Family
ID=75863209
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202110272804.7A Pending CN112811607A (en) | 2021-03-12 | 2021-03-12 | Method for constructing lake and reservoir water ecosystem |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN112811607A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113371833A (en) * | 2021-07-02 | 2021-09-10 | 广西壮族自治区自然资源生态修复中心 | Composite ecological restoration method for lakeside zone of shallow lake |
Citations (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6350421B1 (en) * | 1998-08-24 | 2002-02-26 | Dmc2 Degussa Metals Catalysts Cerdec Ag | Nitrogen oxide storage material and nitrogen oxide storing catalyst prepared therefrom |
CN1647621A (en) * | 2005-02-05 | 2005-08-03 | 王德林 | Use of rare-earth additive as cultivating water nutrient material, aquatic product water nutrient material and its producing method |
CN101343090A (en) * | 2008-08-22 | 2009-01-14 | 王德林 | Lanthanide series water treatment agent and method of preparing the same |
CN102008937A (en) * | 2010-09-30 | 2011-04-13 | 西北师范大学 | Permanganate/montmorillonite nano composite material as well as preparation method and application thereof |
US20130274096A1 (en) * | 2010-12-22 | 2013-10-17 | Pacific Industrial Development Corporation | Catalyst support materials with oxygen storage capacity (osc) and method of making thereof |
CN105152346A (en) * | 2015-09-28 | 2015-12-16 | 四川鑫淼环保科技有限责任公司 | Large deep lake water ecosystem restoration method |
CN105152345A (en) * | 2015-09-28 | 2015-12-16 | 四川鑫淼环保科技有限责任公司 | Method for restoring existing lake water ecosystem |
US20170151551A1 (en) * | 2015-11-27 | 2017-06-01 | Toyota Jidosha Kabushiki Kaisha | Production method of oxygen storage material, and oxygen storage material |
CN107188311A (en) * | 2017-04-22 | 2017-09-22 | 江西怡杉环保股份有限公司 | The ecological restoring method of polluted river water |
CN109626766A (en) * | 2018-07-25 | 2019-04-16 | 长沙理工大学 | A kind of ecology of urban river is regulated and stored the construction method in lake |
CN110171914A (en) * | 2019-07-08 | 2019-08-27 | 武汉美佳源环境工程有限公司 | A kind of ecological treatment method of black and odorous water |
CN110902832A (en) * | 2019-11-07 | 2020-03-24 | 中交天航港湾建设工程有限公司 | Aquatic animal diversity regulation and control method |
CN112340932A (en) * | 2020-10-15 | 2021-02-09 | 长江水利委员会长江科学院 | Method for improving and treating water quality of rainwater collection type reservoir |
-
2021
- 2021-03-12 CN CN202110272804.7A patent/CN112811607A/en active Pending
Patent Citations (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6350421B1 (en) * | 1998-08-24 | 2002-02-26 | Dmc2 Degussa Metals Catalysts Cerdec Ag | Nitrogen oxide storage material and nitrogen oxide storing catalyst prepared therefrom |
CN1647621A (en) * | 2005-02-05 | 2005-08-03 | 王德林 | Use of rare-earth additive as cultivating water nutrient material, aquatic product water nutrient material and its producing method |
CN101343090A (en) * | 2008-08-22 | 2009-01-14 | 王德林 | Lanthanide series water treatment agent and method of preparing the same |
CN102008937A (en) * | 2010-09-30 | 2011-04-13 | 西北师范大学 | Permanganate/montmorillonite nano composite material as well as preparation method and application thereof |
US20130274096A1 (en) * | 2010-12-22 | 2013-10-17 | Pacific Industrial Development Corporation | Catalyst support materials with oxygen storage capacity (osc) and method of making thereof |
CN105152346A (en) * | 2015-09-28 | 2015-12-16 | 四川鑫淼环保科技有限责任公司 | Large deep lake water ecosystem restoration method |
CN105152345A (en) * | 2015-09-28 | 2015-12-16 | 四川鑫淼环保科技有限责任公司 | Method for restoring existing lake water ecosystem |
US20170151551A1 (en) * | 2015-11-27 | 2017-06-01 | Toyota Jidosha Kabushiki Kaisha | Production method of oxygen storage material, and oxygen storage material |
CN107188311A (en) * | 2017-04-22 | 2017-09-22 | 江西怡杉环保股份有限公司 | The ecological restoring method of polluted river water |
CN109626766A (en) * | 2018-07-25 | 2019-04-16 | 长沙理工大学 | A kind of ecology of urban river is regulated and stored the construction method in lake |
CN110171914A (en) * | 2019-07-08 | 2019-08-27 | 武汉美佳源环境工程有限公司 | A kind of ecological treatment method of black and odorous water |
CN110902832A (en) * | 2019-11-07 | 2020-03-24 | 中交天航港湾建设工程有限公司 | Aquatic animal diversity regulation and control method |
CN112340932A (en) * | 2020-10-15 | 2021-02-09 | 长江水利委员会长江科学院 | Method for improving and treating water quality of rainwater collection type reservoir |
Non-Patent Citations (1)
Title |
---|
韩长日等: "《电子及信息用化学品生产工艺与技术》", 31 March 2019, 科学技术文献出版社 * |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113371833A (en) * | 2021-07-02 | 2021-09-10 | 广西壮族自治区自然资源生态修复中心 | Composite ecological restoration method for lakeside zone of shallow lake |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN104803570B (en) | Ecological restoration and purification method for landscape water environment | |
Todd et al. | The design of living technologies for waste treatment | |
CN108298675A (en) | A kind of drop nitrogen subtracts the lake water ecological restoring method of phosphorus | |
CN106430526A (en) | River sewage treatment process | |
CN108147546A (en) | A kind of Two-way Cycle seawater Shrimp polyculture system | |
Nakphet et al. | Aquatic plants for bioremediation in red hybrid tilapia (Oreochromis niloticus× Oreochromis mossambicus) recirculating aquaculture | |
CN111422991A (en) | Biological combined purification pond for freshwater aquaculture tail water | |
CN108401970A (en) | A kind of fishes and shrimps algae Bao ginseng recirculated water ecology synthesis cultivating system | |
CN107399874A (en) | A kind of intensive culture tail water treatment system | |
CN110143667A (en) | A kind of ecological purification system for strengthening low C/N water bodies of rivers and lakes nitrate nitrogen removal | |
CN107673558B (en) | Black and odorous water body purification method | |
CN109052834A (en) | A kind of administering method of eutrophication water | |
JP6512467B1 (en) | Method of reforming aquaculture tank, and method of aquaculture | |
CN208273900U (en) | A kind of fishes and shrimps algae Bao ginseng recirculated water ecology synthesis cultivating system | |
CN106976992A (en) | Carry pond culture biological membrane water purifier and the process for purifying water of strain and culture medium | |
CN113371833A (en) | Composite ecological restoration method for lakeside zone of shallow lake | |
CN112811607A (en) | Method for constructing lake and reservoir water ecosystem | |
CN101955291A (en) | Biomanipulation theory based lake pollution treatment technology | |
CN113149331A (en) | Pond bypass circulation water body purification system | |
JP2539295B2 (en) | Circulation purification method and device for water for aquaculture | |
CN208279378U (en) | A kind of Two-way Cycle seawater Shrimp polyculture system | |
CN110577335A (en) | Method for promoting food chain operation and accelerating water environment treatment | |
Estim | Integrated multitrophic aquaculture | |
CN115490333A (en) | Construction method for ecological restoration and landscape improvement of eutrophic water body | |
CN103553185B (en) | A kind of micro-electrolysis treatment method that water body is carried out in-situ treatment |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20210518 |
|
RJ01 | Rejection of invention patent application after publication |