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Ecological Algae Control Method in Freshwater Lakes

A lake and ecological technology, applied in chemical instruments and methods, biological water/sewage treatment, water/sludge/sewage treatment, etc., can solve problems such as difficulty in guaranteeing effluent water quality, harm to humans and aquatic animals, and increased water treatment costs , to achieve the effects of long-term cycle operation, good recycling, and reducing the content of algae

Inactive Publication Date: 2016-04-20
ZHEJIANG OCEAN UNIV
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0002]With the increasing impact of human activities on water ecosystems, cyanobacterial blooms have become a sign of eutrophic water bodies around the world, resulting in deterioration of water quality and ecosystem damage. The structure and function are destroyed, and toxins are produced at the same time, especially the rapid proliferation of algae caused by eutrophication of the water body, which brings great trouble to drinking water, increases the cost of water treatment, and makes it difficult to guarantee the quality of effluent water. cause great harm to aquatic animals
[0003]Aiming at severe eutrophication of water bodies, various countries around the world have developed various algae removal methods, including chemical methods that use strong oxidants and algicides as algae removal methods. Adding medicaments achieves the purpose of algae removal, but in the process of algae removal, by-products harmful to the human body may be produced, especially the use of oxidants causes the algae to burst and lead to the release of intracellular toxins; the physical and chemical methods represented by air flotation, This method uses methods such as air flotation, membrane filtration, and ultrasonic algae removal. Although no by-products are produced, the operation is complicated and the operating cost is high; some biological methods are used to control algae and algae removal, usually by feeding silver carp, bighead carp and other fish and Using large shellfish to control the occurrence of cyanobacterial blooms is widely used at present, but there are certain problems: the commonly used silver carp and silver carp are mostly silver carp and silver carp, and silver carp and silver carp cannot control themselves in lakes. For breeding, silver carp and silver carp that are artificially propagated and cultivated in ponds need to be put into the lake every year. The operating cost is relatively high, which is not conducive to long-term circulation operation; large-scale shellfish have a strong drainage effect from the outlet holes and have a greater impact on the bottom of the water body. The large stirring effect makes the N and P deposited in the bottom silt disturbed and enters the water body, which is not conducive to the reduction of the N and P content in the water body, resulting in poor algae control effect

Method used

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Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0020] The area of ​​the fence is 1000 square meters. On March 27, 2013, the emergent water plant Nymphaeum was transplanted in the enclosure area. The transplanting density was 4 plants per square meter. The width of the enclosure area was 100cm, and the emergent plants were set In the enclosure area, to avoid the spread and overgrowth of the catfish, its roots are rooted in the bottom of the lake, which is convenient for absorbing N and P. On May 2, 2013, the yellow-tailed pomfret and the small-scaled pomfret with a body length of 6-8cm were released. The stocking amount of the yellow-tailed pomfret is 2,000, and that of the small-scaled pomfret is 4,000. The yellow-tailed pomfret and the small-scaled pomfret feed on detritus, diatoms, green algae, cyanobacteria, and aquatic insects, etc. Detritus, algae, etc. in the layer, after 50 days, put 3000 1-1.5-year-old flower bone fish bones. The flower bone fish is an omnivorous fish. The quantity is controlled to prevent excessiv...

Embodiment 2

[0024] The area of ​​the fence is 1500 square meters. On March 28, 2013, the water spring onion was transplanted into the enclosure area. The transplanting density was 6 plants per square meter. The width of the enclosure area was 150cm. In May 2013 On the 5th, the yellow-tailed pomfret and the small-scaled pomfret with a body length of 6-8cm were released. Among them, 3,750 yellow-tailed pomfrets and 7,500 small-scaled pomfrets were stocked. After 50 days, 1-1.5-year-old flower fish bones were released. 5625 tails. Seine management is the same as embodiment 1.

[0025] In embodiment 2, the water body in the fence area is turbid before the fence, the transparency of the water body is 1.75m, and the total phosphorus content is 53mg / m 3 , the total nitrogen content is 1100mg / m 3 , the content of chlorophyll a is 36.2mg / m 3 . Three months after the flower bone fish was stocked, the water quality was tested, and the test results were: the transparency of the water body was 2.6...

Embodiment 3

[0027] The area of ​​the fence is 2000 square meters. On March 29, 2013, the emergent plants Nymphaea, water onion and Alisma alisma were transplanted into the enclosure area. The transplanting density was 5 plants per square meter, and the width of the enclosure area was 200cm. , on May 8, 2013, the yellow-tailed pomfret and the small-scaled pomfret with a body length of 6-8cm were released, of which 6,000 yellow-tailed pomfrets were stocked and 12,000 small-scaled pomfrets were stocked. After 50 days, 1 - 9,000 1.5-year-old flower fish bones. Seine management is the same as embodiment 1.

[0028] In embodiment 3, the water body in the fence area is turbid before the fence, the transparency of the water body is 1.83m, and the total phosphorus content is 48mg / m 3 , the total nitrogen content is 1123mg / m 3 , the content of chlorophyll a is 33mg / m 3 . The water quality test was carried out three months after the flower bone fish was stocked, and the test results were: the tr...

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Abstract

The invention discloses a freshwater lake ecological alga control method which comprises the following steps: (1) setting up a net fencing region; (2) setting up an isolation region, wherein emergent aquatic plants are transplanted in the isolation region and the transplanting density is 4 to 6 plants per square meter; (3) putting in filter feeding fishes, wherein the ratio of the filter feeding fishes to omnivorous fishes is 2:1. The method disclosed by the invention is simple and easy to operate, has strong maneuverability, has no secondary pollution and prevents algal bloom by mixed culture of the filter feeding and omnivorous fishes; fragments, alga, zooplankter and the like in each layer of a water body are caught; alga content is reduced; the water body environment is more completely purified; the emergent aquatic plants are convenient to adsorb N and P and reduce the eutrophication degree of the water body; in addition, xenocypris davidi bleeker and plagiognathops microlepis are naturally bred without being put in every year, density control is implemented in a harvesting manner of catching big fishes and leaving small fishes in the later period, the operation cost is reduced, and caught fishes also can bring certain additional economic benefits.

Description

technical field [0001] The invention belongs to the technical field of environmental ecological engineering, and in particular relates to an ecological algae control method for freshwater lakes. Background technique [0002] With the increasing impact of human activities on water ecosystems, cyanobacterial blooms have become a sign of eutrophic water bodies around the world, resulting in deterioration of water quality, damage to the structure and function of ecosystems, and the production of toxins, especially in eutrophic water bodies. The rapid proliferation of algae caused by trophication has brought great troubles to drinking water, increased water treatment costs, made it difficult to guarantee the quality of effluent water, and brought great harm to humans and aquatic animals. [0003] In view of the severe eutrophication of water bodies, countries around the world have launched various algae removal methods. There are chemical methods that use strong oxidants and algi...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): C02F3/32
Inventor 方苏杭胡金保
Owner ZHEJIANG OCEAN UNIV
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