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A method for improving the transparency of eutrophic water body

A water body transparency and water body technology, applied in the field of environmental engineering, can solve problems such as difficult and continuous removal, insignificant effect, and reduced water body transparency, so as to reduce the concentration of suspended solids in water body, avoid the risk of chemical substances, and improve the effect of water body transparency

Active Publication Date: 2020-12-08
NANJING INST OF GEOGRAPHY & LIMNOLOGY
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0002] At present, the outbreak of cyanobacteria blooms in lakes and other water bodies in China is a common phenomenon. The consequences are reduced water transparency, water quality deterioration, and serious damage to ecosystems.
The control measures of cyanobacteria bloom are commonly used chemical, physical and biological methods. The chemical method is mainly to control the algae bloom by spreading chemical agents or flocculants. Secondary pollution
Physical methods mainly use manual salvage and mechanical algae removal, which is time-consuming and labor-intensive and difficult to remove continuously
Fish stocking mainly uses silver carp and bighead carp to directly control algae. Although the number of algae populations has decreased, the biomass of single-cell or small-scale algae often has not decreased. When the breeding density of silver carp and bighead carp is high, it will also cause negative effects such as an increase in the concentration of ammonia nitrogen in the water body. influences
Therefore, the algae control method of silver carp and bighead carp is effective in some water bodies with better water quality, such as Qiandao Lake, etc., but the effect is not significant in lakes with severe cyanobacteria outbreaks
Freshwater shellfish are also used to control algae. Although they can filter out single-cell or small-scale cyanobacteria, because cyanobacteria lack the essential nutrients for shellfish growth, they cannot meet the needs of shellfish growth and development. Long-term ingestion of cyanobacteria will cause shellfish Growth inhibition and even death (Park et al., 2002; Basenet al., 2011)
Moreover, the formation of cyanobacterial populations also has an impact on shellfish filter feeding, such as freshwater shellfish Anodonta anatina Reduced filter-feeding and increased pseudocone production when feeding on M. aeruginosa colonies (Bonteset al., 2007)
Submerged plants inhibit cyanobacteria from three aspects: nutrient competition, inhibition of sediment suspension and release of algastatin, but the recovery of aquatic plants requires many prerequisites, and submerged plants are not easy to survive when the conditions are immature

Method used

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Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0024] A eutrophic water body in Wuxi covers an area of ​​5,000 square meters, with a water depth of 3.5 meters. The water body is turbid and the transparency is less than 20cm. The cyanobacterial blooms occurred frequently in this water body, the chlorophyll concentration reached 100ug / L, and the cyanobacteria accounted for about 90% of the phytoplankton community. Construction started at the beginning of May 2013, and 30 g / m of silver carp and bighead fingerlings was put in first 3 , the specification is about 500 grams per tail. On July 20, the chlorophyll concentration was slightly reduced to 95ug / L, and the proportion of cyanobacteria was still more than 90%, but the proportion of cyanobacteria decreased significantly by only 10%, and the particle size was greater than 50μm The biomass of the cyanobacterial population is 30% of the total biomass of the cyanobacterial population. Immediately, alum stone powder was sprinkled on the water surface at a dosage of 1mg / L, once ...

Embodiment 2

[0026] The transparency of a certain eutrophic water body is less than 17cm. The cyanobacterial blooms occurred frequently in this water body, the chlorophyll concentration reached 120ug / L, and the cyanobacteria accounted for about 80% of the phytoplankton community. Construction began in early May of a certain year, and 10 g / m of silver carp and bighead fingerlings was put in first. 3 , the specification is about 50 grams per tail. At the end of July, the chlorophyll concentration was reduced to 87ug / L, the proportion of cyanobacteria was still more than 70%, and the biomass of cyanobacteria with a particle size larger than 50 μm was 10% of the total biomass of cyanobacteria. Immediately, alum stone powder was sprinkled on the water surface at a dosage of 1 mg / L, once every 3 days, 5 times in a row, and the pH of the water body was adjusted to about 7.5. At the end of August, the chlorophyll concentration was reduced to 34ug / L, and the proportion of cyanobacteria was about 10...

Embodiment 3

[0028] In 2017, 4 in-situ experimental enclosures were arranged in Taihu Lake in Wuxi, each enclosure area is 12 square meters, and there is basically no exchange between the enclosure water body and the lake water. Four groups of treatments were set up in the experiment, and one group was stocked with silver carp and bighead carp, 20 g / m2 3 , the specification is 250 grams per tail; one group is treated with alumite ore powder, the dosage is 1mg / L, once every 5 days, and used for 6 times continuously; 3 ; In the comprehensive treatment group, silver carp and bighead carp were stocked (the first month), alum stone powder was sprinkled (the second month), and river clams were stocked (the third month).

[0029] On June 5th, the transparency of the water body in the enclosure was 25cm, the chlorophyll concentration reached 60ug / L, and the cyanobacteria accounted for 80% of the phytoplankton community. The experiment was started according to the design, and the samples were take...

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Abstract

The invention provides a method for increasing transparency degree of a eutrophic water body. The method comprises the following steps of (1) selecting a target water body; (2) feeding filter-feedingaristichthysnobilis into the target water body; (3) when the biological amount of blue-green algae group with particle size greater than 50mum is smaller than 30% of total biological amount of blue-green algae, feeding minerals into the target water body, so as to convert the blue-green algae into green algae. The method has the characteristics that the problems of high outbreak degree of the blue-green algae in the eutrophic water body, low transparency degree of the water body and the like are solved, and the purposes of attenuating the blue-green algae group, converting the blue-green algaephase into the green algae phase, and obviously increasing the transparency degree of the water body are realized; the method is safe, the cost is low, and the like.

Description

technical field [0001] The invention belongs to the technical field of environmental engineering, and in particular relates to a method for improving the transparency of eutrophic water bodies. Background technique [0002] At present, the outbreak of cyanobacterial blooms in lakes and other water bodies in China is a common phenomenon. The control measures of cyanobacterial blooms are usually chemical, physical and biological methods. The chemical method is mainly to control algal blooms by spreading chemical agents or flocculants. Secondary pollution. The physical method is mainly through manual salvage and mechanical algae removal, which is time-consuming and labor-intensive and difficult to remove continuously. Fish feeding mainly uses silver carp and bighead fish to directly control algae. Although the number of algae populations has decreased, the algal biomass of single cells or small groups often does not decrease. When the silver carp and bighead carp breeding den...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): C02F9/14
CPCC02F1/5236C02F3/32C02F2103/007
Inventor 李宽意利翔燕肖羽堂黄晓峰
Owner NANJING INST OF GEOGRAPHY & LIMNOLOGY
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