CN110238179A - A kind of pterylosis rush as pionner Acid mine discardedly it is multiple it is green in application and method - Google Patents
A kind of pterylosis rush as pionner Acid mine discardedly it is multiple it is green in application and method Download PDFInfo
- Publication number
- CN110238179A CN110238179A CN201910634918.4A CN201910634918A CN110238179A CN 110238179 A CN110238179 A CN 110238179A CN 201910634918 A CN201910634918 A CN 201910634918A CN 110238179 A CN110238179 A CN 110238179A
- Authority
- CN
- China
- Prior art keywords
- pterylosis
- rush
- acid mine
- green
- discardedly
- 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
- 239000002253 acid Substances 0.000 title claims abstract description 54
- 238000000034 method Methods 0.000 title claims abstract description 22
- 239000002689 soil Substances 0.000 claims abstract description 35
- 239000011248 coating agent Substances 0.000 claims abstract description 24
- 238000000576 coating method Methods 0.000 claims abstract description 24
- 238000003306 harvesting Methods 0.000 claims abstract description 22
- 244000025254 Cannabis sativa Species 0.000 claims abstract description 13
- 238000011065 in-situ storage Methods 0.000 claims abstract description 11
- 230000005562 seed maturation Effects 0.000 claims abstract description 3
- 241000196324 Embryophyta Species 0.000 claims description 38
- 238000009331 sowing Methods 0.000 claims description 11
- 238000002513 implantation Methods 0.000 claims description 7
- 241000217776 Holocentridae Species 0.000 claims description 3
- 238000007605 air drying Methods 0.000 claims description 3
- 230000000694 effects Effects 0.000 abstract description 3
- 230000020477 pH reduction Effects 0.000 abstract description 3
- 238000004162 soil erosion Methods 0.000 abstract description 3
- 241000735470 Juncus Species 0.000 abstract description 2
- 230000035800 maturation Effects 0.000 description 8
- 230000004083 survival effect Effects 0.000 description 5
- 230000012010 growth Effects 0.000 description 3
- 230000008859 change Effects 0.000 description 2
- 230000018109 developmental process Effects 0.000 description 2
- 230000035558 fertility Effects 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 235000015097 nutrients Nutrition 0.000 description 2
- 238000005067 remediation Methods 0.000 description 2
- 230000008439 repair process Effects 0.000 description 2
- 239000002028 Biomass Substances 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- NYRAVIYBIHCEGB-UHFFFAOYSA-N [K].[Ca] Chemical compound [K].[Ca] NYRAVIYBIHCEGB-UHFFFAOYSA-N 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 238000005065 mining Methods 0.000 description 1
- 235000021232 nutrient availability Nutrition 0.000 description 1
- 235000018343 nutrient deficiency Nutrition 0.000 description 1
- 239000003895 organic fertilizer Substances 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 230000008635 plant growth Effects 0.000 description 1
- 239000002574 poison Substances 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000007670 refining Methods 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 241000894007 species Species 0.000 description 1
Classifications
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G22/00—Cultivation of specific crops or plants not otherwise provided for
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/10—Reclamation of contaminated soil microbiologically, biologically or by using enzymes
- B09C1/105—Reclamation of contaminated soil microbiologically, biologically or by using enzymes using fungi or plants
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Botany (AREA)
- Mycology (AREA)
- Biotechnology (AREA)
- Biomedical Technology (AREA)
- Health & Medical Sciences (AREA)
- General Health & Medical Sciences (AREA)
- Microbiology (AREA)
- Molecular Biology (AREA)
- Soil Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Environmental Sciences (AREA)
- Cultivation Of Plants (AREA)
- Pretreatment Of Seeds And Plants (AREA)
Abstract
The invention discloses a kind of pterylosis rush (Juncus ochraceus Buchen) as pionner Acid mine discardedly it is multiple it is green in application and method, the method includes 1) in the discarded plantation pterylosis rush on the ground of Acid mine；2) it to seed maturation, harvests grass seeds and gathers in aerial part, 1 ~ 5cm of toothing；3) the pterylosis rush aerial part of harvesting is uniformly paved in situ as coating；4) it is reseeded according to the growing state of coming year pterylosis rush, and circulation step (2) ~ (4).The invention uses pterylosis rush for discardedly multiple green in Acid mine as pionner, significant effect, the ecological environment on the discarded ground of Acid mine can not only be effectively improved, alleviate soil erosion, avoids mine soil acidification nearby, realization is replied immediately green fastly, and without carrying out early period pH adjusting, manpower is saved, it is multiple green fast, it is high-efficient.
Description
Technical field
The invention belongs to environment remediation technical fields, and in particular to a kind of pterylosis rush is as pionner in acid mine
Application and method in green are answered discardedly in mountain.
Background technique
Acid Mine Abandoned Land refers to being destroyed or pollute during mining, ore dressing and refining mine, non-difficult through improvement
With the soil used, acid Mine Abandoned Land soil has certain particularity, and physicochemical property and normal soil have larger difference
Not, extreme acid condition (pH < 3.0) is generally shown, the features such as content of beary metal is exceeded serious.
Soil acidification will lead to soil hardening, heavy in texture, soil texture is destroyed, aeration is deteriorated, and reduce soil
Middle nutrient availability, cation are lost, and make the nutrient deficiencies such as phosphorus, potassium calcium, magnesium, are caused under soil nutrient imbalance, fertility
Drop, moreover it is possible to the transportable property and bioavailability of heavy metal element be significantly increased, inhibit soil microbial activities etc.
A series of harm influence normal growth and the development of plant.Acid Mine Abandoned Land is also a potential threat, can be to periphery
An important factor for environment threatens, and is restriction China's agricultural sustainable development, while can also jeopardize human health.
In the prior art, to the main rationalization repairing method of the administering method of acid Mine Abandoned Land and biological restoration.Reason
Change repairing method mainly by into soil the alkaline materials such as liming improve soil acidification, but that there are project amounts is big, holds
Secondary pollution easily is caused to environment, and can not be tackled the problem at its root.Biological prosthetic includes that phytoremediation and microorganism are repaired
It is multiple, but microorganism remediation has certain limitation, repairs effectively to some organic polluted soils, and be poorly suitable for repairing
Acid Mine Abandoned Land.Phytoremediation be using plant acid resistance, be resistant to the characteristics of heavy metallic poison come to soil carry out
It repairs.But since the highly acid of acid Mine Abandoned Land, nutrient scarcity etc. usually hinder plant growth, biomass is low, plants
The short and small, slow growth of strain.
In the prior art, application No. is the Chinese patent application of 107347402 A of CN, to disclose a kind of highly acid tailing useless
Abandon the ecological restoring method on ground.This method is that the place covering after smooth neutralizes slag, toward coating on addition compound fertilizer, organic
Fertilizer and artificial soil screen resistance to suitable plant and carry out nursery, plant by stages to increase coating fertility, to carry out to acid soil
Improvement, but above method invests height, project amount is big, and complex process, is not easy to realize.Have no pterylosis rush in acid at present
Property mine solid waste answers the report of green upper application.
In view of the above problems, discardedly multiple green in Acid mine as pionner it is necessary to invent a kind of pterylosis rush
In application and method.
Summary of the invention
The first object of the present invention is to provide a kind of utilization pterylosis rush (Juncus ochraceus Buchen) work
Acid mine application that is multiple green and alleviating soil erosion discardedly is realized for pionner, and second is designed to provide the application
Method.
The first object of the present invention is achieved in that a kind of pterylosis rush is discarded in Acid mine as pionner
Answer the application in green in ground.
Preferably, the soil pH on the discarded ground of the Acid mine is 1 ~ 6.
Preferably, the Acid mine is discardedly the discarded ground of High aititude Acid mine, height above sea level 2500-4000m.
The second object of the present invention is achieved in that the pterylosis rush is useless in Acid mine as pionner
Answer the application method in green with abandoning, comprising the following steps:
1) in the discarded plantation pterylosis rush on the ground of Acid mine；
2) it to seed maturation, harvests grass seeds and gathers in aerial part, 1 ~ 5cm of toothing；
3) the pterylosis rush aerial part of harvesting is uniformly paved in situ as coating；
4) it is reseeded according to the growing state of coming year pterylosis rush, and circulation step (2) ~ (4).
Preferably, implantation time as described in step (1) be 3 ~ May, planting patterns be broadcast sowing pterylosis lampwick grass seed or
Pterylosis rush seedling is transplanted, the amount of scattering seeds is 1.0 ~ 1.5Kg/667m2, the transplanting plant spacing is 5 ~ 8cm, institute
The plant height for the transplanting pterylosis rush seedling stated is 10 ~ 15cm.
Preferably, paving thickness described in step (3) is 1 ~ 10cm.
Preferably, coating described in step (3) can carry out original place burning after natural air drying.
Preferably, described reseed to the spacing in the rows newly grown between plant can reach 5-8cm.
Compared with prior art, beneficial effects of the present invention:
1, the invention use pterylosis rush for as pionner Acid mine discardedly answer it is green, effect show
It writes, the ecological environment on the discarded ground of Acid mine can not only be effectively improved, alleviate soil erosion, avoid mine soil acid nearby
To change, realization is replied immediately green fastly, and without carrying out early period pH adjusting, saves manpower, and it is multiple green fast, it is high-efficient.
2, the Mine Abandoned Land that the present invention can be realized pH value down to 2 ~ 3 or so extreme environment is multiple green, easy to operate,
It is promoted convenient for extension.
3, the pionner pterylosis rush local species that the present invention uses, source of plant material facilitate breeding management to hold
Easily, can large-scale promotion application, Acid mine is discarded for ground, the present invention has that growth is fast, seed production is big, diffusion energy
The advantages of power is strong, has extremely indomitable vitality, and durability against pollution is good, good purification.
Specific embodiment
Below with reference to embodiment, the present invention is further illustrated, but the present invention is limited in any way,
Based on present invention teach that it is made it is any transform or replace, all belong to the scope of protection of the present invention.
Below with reference to 1 ~ embodiment of embodiment 8, the present invention will be further described.
Embodiment 1
1) interior formula of sowing seeds plants pterylosis rush, soil pH in the Acid mine discarded ground m cell of 5 m × 5 that height above sea level is 2500
Mean value is about 2, and soil pH most value difference is less than 1 in cell；The implantation time is March, and the amount of scattering seeds is
1.0Kg/667m2；
2) it to plant maturation, harvests grass seeds and gathers in aerial part, toothing 1cm；
3) the pterylosis rush aerial part of harvesting is uniformly paved in situ as coating, coating paving thickness is 1cm；
4) it is reseeded according to the growing state of coming year pterylosis rush, described reseeding is reachable to the spacing in the rows newly grown between plant
To 5cm, and circulation step (2) ~ (4).
Embodiment 2
1) interior formula of sowing seeds plants pterylosis rush, soil pH in the Acid mine discarded ground m cell of 5 m × 5 that height above sea level is 3000
Mean value is about 2.5, and soil pH most value difference is less than 1 in cell；The implantation time is April, and the amount of scattering seeds is
1.2Kg/667m2；
2) it to plant maturation, harvests grass seeds and gathers in aerial part, toothing 2cm；
3) the pterylosis rush aerial part of harvesting is uniformly paved in situ as coating, coating paving thickness is 2cm；
4) it is reseeded according to the growing state of coming year pterylosis rush, described reseeding is reachable to the spacing in the rows newly grown between plant
To 8cm, and circulation step (2) ~ (4).
Embodiment 3
1) interior formula of sowing seeds plants pterylosis rush, soil pH in the Acid mine discarded ground m cell of 5 m × 5 that height above sea level is 3500
Mean value is about 3, and soil pH most value difference is less than 1 in cell；The implantation time is May, and the amount of scattering seeds is
1.5Kg/667m2；
2) it to plant maturation, harvests grass seeds and gathers in aerial part, toothing 3cm；
3) the pterylosis rush aerial part of harvesting is uniformly paved in situ as coating, coating paving thickness is 5cm；
The coating can carry out original place burning after natural air drying；
4) it is reseeded according to the growing state of coming year pterylosis rush, and circulation step (2) ~ (4).
Embodiment 4
1) interior formula of sowing seeds plants pterylosis rush, soil pH in the Acid mine discarded ground m cell of 5 m × 5 that height above sea level is 4000
Mean value is about 3.5, and soil pH most value difference is less than 1 in cell；The amount of scattering seeds is 1.4Kg/667m2；
2) it to plant maturation, harvests grass seeds and gathers in aerial part, toothing 3cm；
3) the pterylosis rush aerial part of harvesting is uniformly paved in situ as coating, coating paving thickness is
10cm；
4) it is reseeded according to the growing state of coming year pterylosis rush, described reseeding is reachable to the spacing in the rows newly grown between plant
To 6cm, and circulation step (2) ~ (4).
Embodiment 5
1) pterylosis rush seedling, soil are planted in interior transplanting in the Acid mine discarded ground m cell of 5 m × 5 that height above sea level is 2800
PH mean value is about 2, and soil pH most value difference is less than 1 in cell；The implantation time is March, and the transplanting plant spacing is 5cm,
The plant height of the transplanting pterylosis rush seedling is 10cm；
2) it to plant maturation, harvests grass seeds and gathers in aerial part, toothing 4cm；
3) the pterylosis rush aerial part of harvesting is uniformly paved in situ as coating, coating paving thickness is 8cm；
4) it is reseeded according to the growing state of coming year pterylosis rush, described reseeding is reachable to the spacing in the rows newly grown between plant
To 5cm, and circulation step (2) ~ (4).
Embodiment 6
1) pterylosis rush seedling, soil are planted in interior transplanting in the Acid mine discarded ground m cell of 5 m × 5 that height above sea level is 3200
PH mean value is about 2.5, and soil pH most value difference is less than 1 in cell；The transplanting plant spacing is 8cm, the transplanting pterylosis lampwick
The plant height of careless seedling is 15cm；
2) it to plant maturation, harvests grass seeds and gathers in aerial part, toothing 5cm；
3) the pterylosis rush aerial part of harvesting is uniformly paved in situ as coating, coating paving thickness is 7cm；
4) it is reseeded according to the growing state of coming year pterylosis rush, described reseeding is reachable to the spacing in the rows newly grown between plant
To 5cm, and circulation step (2) ~ (4).
Embodiment 7
1) pterylosis rush seedling, soil are planted in interior transplanting in the Acid mine discarded ground m cell of 5 m × 5 that height above sea level is 3800
PH mean value is about 3, and soil pH most value difference is less than 1 in cell；The transplanting plant spacing is 7cm, the transplanting pterylosis rush
The plant height of seedling is 13cm；
2) it to plant maturation, harvests grass seeds and gathers in aerial part, toothing 2cm；
3) the pterylosis rush aerial part of harvesting is uniformly paved in situ as coating, coating paving thickness is 4cm；
4) it is reseeded according to the growing state of coming year pterylosis rush, and circulation step (2) ~ (4).
Embodiment 8
1) pterylosis rush seedling, soil are planted in interior transplanting in the Acid mine discarded ground m cell of 5 m × 5 that height above sea level is 4000
PH mean value is about 3.5, and soil pH most value difference is less than 1 in cell；The implantation time is April, and the transplanting plant spacing is
7cm, the plant height of the transplanting pterylosis rush seedling are 12cm；
2) it to plant maturation, harvests grass seeds and gathers in aerial part, toothing 2.5cm；
3) the pterylosis rush aerial part of harvesting is uniformly paved in situ as coating, coating paving thickness is 5cm；
4) it is reseeded according to the growing state of coming year pterylosis rush, and circulation step (2) ~ (4).
Following table is the determination data of embodiment 1 ~ 8:
Pterylosis rush survival rate when table 1 is not reseeded
| The mode time | First planting season survival rate | Second planting season survival rate |
| The formula of sowing seeds/pH=2 | 53% | 62% |
| The formula of sowing seeds/pH=2.5 | 61% | 69% |
| The formula of sowing seeds/pH=3 | 76% | 75% |
| The formula of sowing seeds/pH=3.5 | 85% | 87% |
| Transplanting type/pH=2 | 62% | 67% |
| Transplanting type/pH=2.5 | 66% | 69% |
| Transplanting type/pH=3 | 74% | 82% |
| Transplanting type/pH=3.5 | 88% | 91% |
As shown in table 1, the acidproof survival rate of pterylosis rush is higher, is a kind of acid resistance plant that expression effect is outstanding, transplanting
The planting patterns ratio of formula formula planting patterns survival rate of sowing seeds is relatively higher, but cost of labor is higher, and planting patterns can be according to reality
Border situation voluntarily selects.A kind of pterylosis rush as pionner Acid mine discardedly it is multiple it is green in application and its method
It can be carried out example verifying, popularizing planting can be carried out in acid tailing place.
Claims (8)
1. a kind of pterylosis rush answers the application in green as pionner in Acid mine discardedly.
2. pterylosis rush according to claim 1 answers the application in green as pionner discardedly in Acid mine,
It is characterized in that the soil pH on the discarded ground of the Acid mine is 1 ~ 6.
3. pterylosis rush according to claim 1 answers the application in green as pionner discardedly in Acid mine,
It is characterized in that the Acid mine is discardedly the discarded ground of High aititude Acid mine, height above sea level 2500-4000m.
4. a kind of pterylosis rush any according to claim 1 ~ 3 is discardedly multiple green in Acid mine as pionner
In application method, it is characterised in that the following steps are included:
1) in the discarded plantation pterylosis rush on the ground of Acid mine；
2) it to seed maturation, harvests grass seeds and gathers in aerial part, 1 ~ 5cm of toothing；
3) the pterylosis rush aerial part of harvesting is uniformly paved in situ as coating；
4) it is reseeded according to the growing state of coming year pterylosis rush, and circulation step (2) ~ (4).
5. pterylosis rush according to claim 4 answers the application side in green as pionner in Acid mine discardedly
Method, it is characterised in that implantation time as described in step (1) is 3 ~ May, and planting patterns is to broadcast sowing pterylosis lampwick grass seed or shifting
Pterylosis rush seedling is planted, the amount of scattering seeds is 1.0 ~ 1.5Kg/667m2, the transplanting plant spacing is 5 ~ 8cm, described
Transplanting pterylosis rush seedling plant height be 10 ~ 15cm.
6. pterylosis rush according to claim 4 answers the application side in green as pionner in Acid mine discardedly
Method, it is characterised in that paving thickness described in step (3) is 1 ~ 10cm.
7. pterylosis rush according to claim 4 answers the application side in green as pionner in Acid mine discardedly
Method, it is characterised in that coating described in step (3) can carry out original place burning after natural air drying.
8. pterylosis rush according to claim 4 answers the application side in green as pionner in Acid mine discardedly
Method, it is characterised in that described reseeding to the spacing in the rows newly grown between plant can reach 5-8cm.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201910634918.4A CN110238179A (en) | 2019-07-15 | 2019-07-15 | A kind of pterylosis rush as pionner Acid mine discardedly it is multiple it is green in application and method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201910634918.4A CN110238179A (en) | 2019-07-15 | 2019-07-15 | A kind of pterylosis rush as pionner Acid mine discardedly it is multiple it is green in application and method |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN110238179A true CN110238179A (en) | 2019-09-17 |
Family
ID=67892162
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201910634918.4A Pending CN110238179A (en) | 2019-07-15 | 2019-07-15 | A kind of pterylosis rush as pionner Acid mine discardedly it is multiple it is green in application and method |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN110238179A (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111226529A (en) * | 2020-01-18 | 2020-06-05 | 昆明理工大学 | Acid mine wasteland greening method using acid-resistant plants as pioneer plants |
| CN111264339A (en) * | 2020-01-18 | 2020-06-12 | 昆明理工大学 | Spray-seeding matrix for rush, spray-seeding method and application thereof |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103430727A (en) * | 2013-07-25 | 2013-12-11 | 王运海 | Method for planting medulla junci |
| CN108114977A (en) * | 2017-12-20 | 2018-06-05 | 北京东方复地环境科技有限公司 | It is a kind of to utilize super enriching plant and the method in the quick restoring cadmium polluted arable land of energy-source plant crop rotation plantation |
| CN109287182A (en) * | 2018-09-30 | 2019-02-01 | 中国林业科学研究院亚热带林业研究所 | A method of for Copper Mine Abandoned Place revegetation |
| CN109328523A (en) * | 2018-11-02 | 2019-02-15 | 浙江杭博生态环境建设有限公司 | A kind of abandoned mine ecological restoring method |
-
2019
- 2019-07-15 CN CN201910634918.4A patent/CN110238179A/en active Pending
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103430727A (en) * | 2013-07-25 | 2013-12-11 | 王运海 | Method for planting medulla junci |
| CN108114977A (en) * | 2017-12-20 | 2018-06-05 | 北京东方复地环境科技有限公司 | It is a kind of to utilize super enriching plant and the method in the quick restoring cadmium polluted arable land of energy-source plant crop rotation plantation |
| CN109287182A (en) * | 2018-09-30 | 2019-02-01 | 中国林业科学研究院亚热带林业研究所 | A method of for Copper Mine Abandoned Place revegetation |
| CN109328523A (en) * | 2018-11-02 | 2019-02-15 | 浙江杭博生态环境建设有限公司 | A kind of abandoned mine ecological restoring method |
Non-Patent Citations (2)
| Title |
|---|
| 卫智军等: "矿业废弃地的植被恢复与重建 ", 《水土保持学报》 * |
| 邓冬梅等: "南丹长坡尾矿坝五种植物富集重金属的生态调查 ", 《河池学院学报》 * |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111226529A (en) * | 2020-01-18 | 2020-06-05 | 昆明理工大学 | Acid mine wasteland greening method using acid-resistant plants as pioneer plants |
| CN111264339A (en) * | 2020-01-18 | 2020-06-12 | 昆明理工大学 | Spray-seeding matrix for rush, spray-seeding method and application thereof |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN102047808B (en) | Method for reducing heavy metal residues in tobacco by use of arbuscular mycorrhizal fungi | |
| CN103975811B (en) | A kind of Oryza sativa L. irrigation by infiltration cultural method | |
| CN108114977A (en) | It is a kind of to utilize super enriching plant and the method in the quick restoring cadmium polluted arable land of energy-source plant crop rotation plantation | |
| CN109565993A (en) | A kind of saline-alkali soil improvement method | |
| CN102318529B (en) | Aquatic and dry amphibious planting method for rice | |
| CN110627574A (en) | Biochar organic compound soil curing modifier and preparation method and application thereof | |
| CN101548621A (en) | A karst region rapid plant recovering method | |
| CN105290103A (en) | Method for utilizing cadmium-resisting fungus aspergillus aculeatus for promoting festuca arundinacea to remedy cadmium contaminated soil | |
| CN102513338A (en) | Method for restoring copper-polluted soil by plants | |
| CN102257915A (en) | Method for transversely growing yam and interplanting spring and autumn potato under coverage of straw | |
| CN106304991A (en) | Corn straw turnover corrosion-promotion soil moisture conservation cultivation method | |
| CN110238179A (en) | A kind of pterylosis rush as pionner Acid mine discardedly it is multiple it is green in application and method | |
| CN108738442B (en) | Tea-oil camellia forest soil curing system and manufacturing method thereof | |
| CN114097512A (en) | Coal mine area ecological restoration matrix and preparation method and application thereof | |
| CN106977244A (en) | A kind of vegetable seedling substrate | |
| CN106665104A (en) | Transplanting method for aquatic vegetable brasenia schreberi | |
| CN108636998A (en) | A method of utilizing No. five reparation manganese ore area heavy metal pollution meta-alkalescence soil of Festuca Arundinacea hunting dog | |
| CN107409900B (en) | Method for rapidly recovering vegetation in stony desertification red bare soil | |
| CN109365520A (en) | A kind of method of the remediating heavy metal cadmium pollution soil in production | |
| CN105684685A (en) | A pueraria cultivation method | |
| CN104641999A (en) | Method for manufacturing celery floating seedling culturing substrate based on mushroom residue | |
| CN109247178B (en) | Method for improving planting survival rate of mercerizing wood in saline-alkali soil | |
| CN104756839B (en) | Using tomato stalk as tomato seedling substrate of raw material and preparation method thereof | |
| CN107011032B (en) | Mushroom residue composite matrix for cultivating organic watermelon seedlings | |
| CN108738971B (en) | Method for cultivating dalbergia odorifera container seedlings by using waste mushroom residue-containing matrix |
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 | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20190917 |