CN103141370B - Method for restoring river submerged plant - Google Patents
Method for restoring river submerged plant Download PDFInfo
- Publication number
- CN103141370B CN103141370B CN201310090836.0A CN201310090836A CN103141370B CN 103141370 B CN103141370 B CN 103141370B CN 201310090836 A CN201310090836 A CN 201310090836A CN 103141370 B CN103141370 B CN 103141370B
- Authority
- CN
- China
- Prior art keywords
- river
- submerged plant
- water
- seedling
- plant
- 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.)
- Expired - Fee Related
Links
- 238000000034 method Methods 0.000 title claims abstract description 20
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 34
- 241000195493 Cryptophyta Species 0.000 claims description 19
- 238000011084 recovery Methods 0.000 claims description 10
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 4
- 239000004927 clay Substances 0.000 claims description 4
- 238000012364 cultivation method Methods 0.000 claims description 4
- 230000002706 hydrostatic effect Effects 0.000 claims description 4
- 238000005286 illumination Methods 0.000 claims description 4
- 230000008774 maternal effect Effects 0.000 claims description 4
- 229910052760 oxygen Inorganic materials 0.000 claims description 4
- 239000001301 oxygen Substances 0.000 claims description 4
- 239000013049 sediment Substances 0.000 claims description 4
- 239000000758 substrate Substances 0.000 claims description 4
- 230000004083 survival effect Effects 0.000 abstract description 8
- 238000005516 engineering process Methods 0.000 abstract description 3
- 230000008901 benefit Effects 0.000 abstract description 2
- 229910052799 carbon Inorganic materials 0.000 abstract description 2
- 230000007613 environmental effect Effects 0.000 abstract description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 abstract 1
- 238000012423 maintenance Methods 0.000 abstract 1
- 241000196324 Embryophyta Species 0.000 description 25
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 3
- 229910052698 phosphorus Inorganic materials 0.000 description 3
- 239000011574 phosphorus Substances 0.000 description 3
- 239000000356 contaminant Substances 0.000 description 2
- 230000000593 degrading effect Effects 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 108010022579 ATP dependent 26S protease Proteins 0.000 description 1
- 241000498251 Hydrilla Species 0.000 description 1
- 230000007850 degeneration Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 230000002401 inhibitory effect Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 230000000192 social effect Effects 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/40—Protecting water resources
- Y02A20/402—River restoration
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/80—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in fisheries management
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Cultivation Of Plants (AREA)
Abstract
The invention discloses a method for restoring a river submerged plant. The method is characterized in that the submerged plant is used as a pioneer species, appropriate submerged plant is cultivated in the river, different growth conditions of the submerged plant in the river are controlled, submerged vegetation is reconstructed in the degraded river through appropriate maintenance management technology, and the survival rate of the reconstructed submerged vegetation reaches 60 to 70 percent. The local environment of the river water ecological system is improved by restoring the water plants of the river, the structure and the function of the river ecological system can be restored, the cost is low, simplicity, feasibility, low carbon and environmental friendliness can be realized, the benefit is remarkable, the method is suitable for the restoration engineering of the water vegetation of the polluted river and for the ecological reconstruction engineering of the polluted river water plant diversity and water ecological system.
Description
Technical field:
The invention belongs to field of environment engineering technology, be specifically related to a kind of river and gush the recovering method of submerged plant.
Background technology:
The quality of Urban Water Environment is to weigh the important parameter of life of urban resident level.In China, along with improving constantly of the level of urbanization, Urban Water Environment is subject to the impact of urbanization process more and more remarkable.Due to economic fast development, increasing urban pollutant is discharged in city river, causes city river to pollute and increasingly sharpens, and has had a strong impact on Urban Water Environment quality and resident's healthy living.Particularly and economically developed area complicated in the coastal network of waterways, city river generally loses self-purification capacity.Gush in river how effectively to administer ecological functions degeneration, and restorative water ecological environment becomes the large problem of pendulum in face of government, environmental administration, enterprise, expert and scholar already.
At present, interior reconstruction submerged vegetation is gushed in river not yet report.The mode of gushing interior reconstruction submerged vegetation by river is explored river and gushes new way and the new method of improvement, not only has in theory important scientific value, and have great social effect in practice.
Summary of the invention:
The object of this invention is to provide a kind of river and gush the recovering method of submerged plant, utilize the method can promote river to gush the recovery of water ecosystem, the self-purification function of strengthening river water burst body, promotes degrading river water burst matter to take a turn for the better, and shortens river and gushes the improvement cycle.
The present invention is by applying submerged plant as pioneer, gush the suitable submerged plant of middle cultivation in river, and control the various growth conditionss of submerged plant in gush in river, again by suitable management technique, gush interior reconstruction submerged vegetation at degrading river, the submerged vegetation survival rate of rebuilding reaches 60%～70%, thereby has realized object of the present invention.
The recovering method of submerged plant is gushed in river of the present invention, comprises the following steps:
(1), determine place: selecting water transparency is that 0.5～1.2 meter, dissolved oxygen are 8.7～9.2mg/L, pH6～9, NH
3-N0.1～4.1mg/L, total nitrogen (TN) 1.2-5.9mg/L, total phosphorus (TP) 0.1～0.8mg/L, BOD5.3～59.8mg/L, COD
mn9.9～11.9mg/L, COD
crthe recovery of row submerged vegetation is poured in the river of 29.3～42.5mg/L;
(2), cultivating and growing: the healthy plant of selecting submerged plant, its seedling length is 10～15 centimetres, taking 3～5 strains as a Cong Zuowei plantation unit, seedling plantation density is 4～6 clumps every square metre, plantation period is 3～April, cultivation method is that seedling clay is fixed, and Planting pattern is that nature sinks;
(3), settle down and survive: when submerged plant recovery is gushed in river, water area is controlled at 500～5000 square metres, and the depth of water is controlled at 0.5～1.5 meter, current are controlled at 2.0～10.8 centimeters per seconds, water temperature is at 15～20 DEG C, water body illumination 2000～5000LX, and river is gushed substrate and is selected Mud Sediment.
Described submerged plant, is preferably black algae (Hydrilla verticillata).Because the weather hydrologic condition of black algae to region is adaptable, algae is gushed in river inhibitory action, and reproduction speed is fast, is the ideal material that improves river and gush water body environment.
Described black algae, its seedling preferably obtains by the following method: chooses black algae maternal plant in 2～March, is divided into 6～10 centimetres every section, cottage propagation seedling in hydrostatic, normal condition takes root for 5～10 days, and survival rate more than 95%, obtains black algae seedling in batches; The interior available same method of temperature canopy in winter can be bred black algae seedling, and survival rate is more than 95%.
Preferably, when submerged plant growing way in gush in river is vigorous, part salvaging be can carry out, self and the renewal of submerged plant are conducive to.
The present invention gushes by recovering river the local environment that aquatic vegetation is improved river and gushes water ecosystem, recover the 26S Proteasome Structure and Function of the natural ecosystem of rivers system, with low cost, simple and easy to do, low-carbon environment-friendly, benefit are obvious, be applicable to the recovery engineering of the aquatic vegetation of contaminant rivers, be applicable to contaminant rivers Aquatic Plant Diversity and aquatic ecosystem ecological restoration engineering.
Embodiment:
Following examples are to further illustrate of the present invention, instead of limitation of the present invention.
Embodiment 1:
(1), determine place: selecting water transparency is that 0.5～1.2 meter, dissolved oxygen are 8.7～9.2mg/L, pH6～9, NH
3-N0.1～4.1mg/L, total nitrogen (TN) 1.2-5.9mg/L, total phosphorus (TP) 0.1～0.8mg/L, BOD5.3～59.8mg/L, COD
mn9.9～11.9mg/L, COD
crthe recovery of row submerged vegetation is poured in the river of 29.3～42.5mg/L;
(2), cultivating and growing: choose black algae maternal plant in February, be divided into 6～10 centimetres every section, cottage propagation seedling in hydrostatic, takes root for 5～10 days, and survival rate more than 95%, obtains black algae seedling in batches; Select the healthy plant of black algae, its seedling length is 10～15 centimetres, and taking 3～5 strains as a Cong Zuowei plantation unit, seedling plantation density is 4～6 clumps every square metre, and plantation period is March, and cultivation method is that seedling clay is fixed, and Planting pattern is that nature sinks;
(3), settle down and survive: when submerged plant recovery is gushed in river, water area is controlled at 500 square metres, and the depth of water is controlled at 0.5～1.5 meter, current are controlled at 2.0～10.8 centimeters per seconds, water temperature is at 15～20 DEG C, water body illumination 2000～5000LX, and river is gushed substrate and is selected Mud Sediment.
When summer, the submerged plant growing way in gush in river was vigorous, carry out part salvaging.
Utilizing the black algae survival rate that recovering method that submerged plant is gushed in the river of this enforcement is planted is 60%.
Embodiment 2:
(1), determine place: selecting water transparency is that 0.5～1.2 meter, dissolved oxygen are 8.7～9.2mg/L, pH6～9, NH
3-N0.1～4.1mg/L, total nitrogen (TN) 1.2-5.9mg/L, total phosphorus (TP) 0.1～0.8mg/L, BOD5.3～59.8mg/L, COD
mn9.9～11.9mg/L, COD
crthe recovery of row submerged vegetation is poured in the river of 29.3～42.5mg/L;
(2), cultivating and growing: choose black algae maternal plant in March, be divided into 6～10 centimetres every section, cottage propagation seedling in hydrostatic, takes root for 5～10 days, and survival rate more than 95%, obtains black algae seedling in batches; Select the healthy plant of black algae, its seedling length is 10～15 centimetres, and taking 3～5 strains as a Cong Zuowei plantation unit, seedling plantation density is 4～6 clumps every square metre, and plantation period is April, and cultivation method is that seedling clay is fixed, and Planting pattern is that nature sinks;
(3), settle down and survive: when submerged plant recovery is gushed in river, water area is controlled at 5000 square metres, and the depth of water is controlled at 0.5～1.5 meter, current are controlled at 2.0～10.8 centimeters per seconds, water temperature is at 15～20 DEG C, water body illumination 2000～5000LX, and river is gushed substrate and is selected Mud Sediment.
When summer, the submerged plant growing way in gush in river was vigorous, carry out part salvaging.
Utilizing the black algae survival rate that recovering method that submerged plant is gushed in the river of this enforcement is planted is 70%.
Claims (3)
1. a recovering method for submerged plant is gushed in river, it is characterized in that, comprises the following steps:
(1), determine place: selecting water transparency is that 0.5～1.2 meter, dissolved oxygen are 8.7～9.2mg/L, pH6～9, NH
3-N0.1～4.1mg/L, TN1.2-5.9mg/L, TP0.1～0.8mg/L, BOD5.3～59.8mg/L, COD
mn9.9～11.9mg/L, COD
crthe recovery of row submerged vegetation is poured in the river of 29.3～42.5mg/L;
(2), cultivating and growing: the healthy plant of selecting submerged plant, its seedling length is 10～15 centimetres, taking 3～5 strains as a Cong Zuowei plantation unit, seedling plantation density is 4～6 clumps every square metre, plantation period is 3～April, cultivation method is that seedling clay is fixed, and Planting pattern is that nature sinks;
(3), settle down and survive: when submerged plant recovery is gushed in river, water area is controlled at 500～5000 square metres, and the depth of water is controlled at 0.5～1.5 meter, current are controlled at 2.0～10.8 centimeters per seconds, water temperature is at 15～20 DEG C, water body illumination 2000～5000LX, and river is gushed substrate and is selected Mud Sediment;
Described submerged plant is black algae.
2. the recovering method of submerged plant is gushed in river according to claim 1, it is characterized in that, described black algae, its seedling obtains by the following method: choose black algae maternal plant in 2～March, be divided into 6～10 centimetres every section, cottage propagation seedling in hydrostatic, takes root for 5～10 days, obtains black algae seedling in batches.
3. the recovering method of submerged plant is gushed in river according to claim 1, it is characterized in that, when submerged plant growing way in gush in river is vigorous, carries out part salvaging.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201310090836.0A CN103141370B (en) | 2013-03-20 | 2013-03-20 | Method for restoring river submerged plant |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201310090836.0A CN103141370B (en) | 2013-03-20 | 2013-03-20 | Method for restoring river submerged plant |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN103141370A CN103141370A (en) | 2013-06-12 |
| CN103141370B true CN103141370B (en) | 2014-10-29 |
Family
ID=48539932
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201310090836.0A Expired - Fee Related CN103141370B (en) | 2013-03-20 | 2013-03-20 | Method for restoring river submerged plant |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN103141370B (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105152347A (en) * | 2015-09-28 | 2015-12-16 | 四川鑫淼环保科技有限责任公司 | Building and management method for submerged vegetations in water of lakes |
| CN112544430A (en) * | 2020-12-10 | 2021-03-26 | 中国海洋大学 | Transplanting device and construction method for temperate zone rock reef matrix seaweed bed |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102491525A (en) * | 2011-12-07 | 2012-06-13 | 中国科学院武汉植物园 | Method for building river course ecological restoration vegetation |
| CN102550243A (en) * | 2011-12-20 | 2012-07-11 | 中国环境科学研究院 | Technical method for cultivating submerged plant in heavily polluted riverway |
| CN102730838A (en) * | 2012-07-16 | 2012-10-17 | 南京大学 | Method for reestablishing river submerged plant group |
-
2013
- 2013-03-20 CN CN201310090836.0A patent/CN103141370B/en not_active Expired - Fee Related
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102491525A (en) * | 2011-12-07 | 2012-06-13 | 中国科学院武汉植物园 | Method for building river course ecological restoration vegetation |
| CN102550243A (en) * | 2011-12-20 | 2012-07-11 | 中国环境科学研究院 | Technical method for cultivating submerged plant in heavily polluted riverway |
| CN102730838A (en) * | 2012-07-16 | 2012-10-17 | 南京大学 | Method for reestablishing river submerged plant group |
Non-Patent Citations (2)
| Title |
|---|
| 沉水植物生长影响因子研究进展;王华等;《生态学报》;20080831;第28卷(第8期);第3959-3961页 * |
| 王华等.沉水植物生长影响因子研究进展.《生态学报》.2008,第28卷(第8期), |
Also Published As
| Publication number | Publication date |
|---|---|
| CN103141370A (en) | 2013-06-12 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN102249416B (en) | Method for ecologically reconstructing lakeshore buffer zone | |
| CN101830565B (en) | Device for three-dimensional coupling and purification of water quality by lifting plant sinker and floater | |
| Pan et al. | A review of ecological restoration techniques in fluvial rivers | |
| CN103882828A (en) | Ecological restoration method for city watercourse | |
| CN102329000B (en) | Tandem type riverway water quality improvement and water resource storage adjustment method | |
| CN104032706B (en) | A kind of method that builds wetland type river course | |
| CN104030449A (en) | Closed or semi-closed landscape water body governance method | |
| CN201694895U (en) | Solid coupling water body purification device | |
| CN104310590A (en) | Method for constructing lake submerged plant communities | |
| Lenzi | Experiences for the management of Orbetello Lagoon: eutrophication and fishing | |
| CN105638015A (en) | Method for recovering intertidal zone salt marsh wetland | |
| Wang et al. | Ecological restoration of polluted plain rivers within the Haihe River Basin in China | |
| CN105417905A (en) | Method for treating in situ sludge of lake and river channel based on underwater lawn module system | |
| CN107996058A (en) | A kind of method for recovering the economic vegetation of protective embankments in lakeside areas ditch pool system ecology | |
| CN103141370B (en) | Method for restoring river submerged plant | |
| CN101595791A (en) | A kind of method of utilizing river bottom silt of contaminated river course to rebuild water ecology group | |
| CN102839632B (en) | Method of constructing ecological revetment for intensively intercepting and clearing non-point pollution based on organisms | |
| CN102461404A (en) | Reed floating planting method | |
| CN107651754B (en) | Composite ecological system construction method for restoring eutrophic water body and artificial reef | |
| CN205933403U (en) | Be suitable for revetment structure of river and lake shore hosepipe ecological remediation and quality of water purification | |
| CN103548529B (en) | A kind of spiral shell and water plants are rationally mixed takes the method building ecological revetment | |
| CN109588078A (en) | Bank band natural pond willow transplants restoration methods for river shore | |
| CN103609386A (en) | Muddy coastal zone plant groove or plant hole afforestation method | |
| CN207460932U (en) | A kind of submerged plant suspension culture apparatus of depth-adjustable | |
| CN104370370A (en) | Riverway sewage purification treatment method |
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: 20141029 |
|
| CF01 | Termination of patent right due to non-payment of annual fee |