CN105710122A - In-situ mechanical remediation method of urban landscaping planting soil - Google Patents

In-situ mechanical remediation method of urban landscaping planting soil Download PDF

Info

Publication number
CN105710122A
CN105710122A CN201610270861.0A CN201610270861A CN105710122A CN 105710122 A CN105710122 A CN 105710122A CN 201610270861 A CN201610270861 A CN 201610270861A CN 105710122 A CN105710122 A CN 105710122A
Authority
CN
China
Prior art keywords
soil
bacillus
nocard
lactic acid
acid bacteria
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
Application number
CN201610270861.0A
Other languages
Chinese (zh)
Inventor
杨永浩
宋有才
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
SHANGHAI DASONG BIOLOGICAL TECHNOLOGY Co Ltd
Original Assignee
SHANGHAI DASONG BIOLOGICAL TECHNOLOGY Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by SHANGHAI DASONG BIOLOGICAL TECHNOLOGY Co Ltd filed Critical SHANGHAI DASONG BIOLOGICAL TECHNOLOGY Co Ltd
Priority to CN201610270861.0A priority Critical patent/CN105710122A/en
Publication of CN105710122A publication Critical patent/CN105710122A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/10Reclamation of contaminated soil microbiologically, biologically or by using enzymes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C2101/00In situ

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Soil Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Biomedical Technology (AREA)
  • General Health & Medical Sciences (AREA)
  • Microbiology (AREA)
  • Molecular Biology (AREA)
  • Mycology (AREA)
  • Biotechnology (AREA)
  • Health & Medical Sciences (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

An in-situ mechanical remediation method of urban landscaping planting soil belongs to the field of soil remediation. The in-situ mechanical remediation method comprises the following remediation steps: grinding, oxygenating and sterilizing conventional landscaping planting soil and natural soil through mechanical single machine operation, and besides, sieving green bricks and impurities in soil; laminating to insulate heat and hold moisture after organic matrixes in microbial soil and the ground soil are mixed proportionally; activating function microorganisms in the organic matrixes in the microbial soil and indigenous microorganisms in soil to metabolize and be amplified, so that the activity of the soil after 15 days is improved; and removing the laminating to realize green planting. The in-situ mechanical remediation of the soil is realized by adopting a dedicated mechanical device through the single machine operation and the microbial organic matrixes rich in various probiotics, the hardened soil can be effectively ground, and the air permeability and the looseness of the soil are improved. The green bricks and the other impurities in the soil are removed, so that the crumb structure of the soil is improved, and the purity and the activity of the soil are restored and improved.

Description

A kind of original position mechanical prosthesis method of urban afforestation planting soil
Technical field
The invention belongs to soil remediation field, the original position mechanical prosthesis method of especially a kind of urban afforestation planting soil.
Background technology
The reform and opening-up of Jin20Nian Lai China and rapid development of economy, the particularly development of real estate in city big or middle, driven transformation and the development of urban landscaping.Meanwhile, development and the quality of urban afforestation in the lack of checks on power of afforestation planting soil.Substantial amounts of original soil outward transport in the real estate development process in city on the one hand, causes have a strong impact on environment, road traffic, personal safety;And with high costs, create huge waste;On the other hand, soil moved in improve the original is transported in process and also result in huge waste equally, and soil quality is difficult to be controlled, and causes the decline of the construction project quality such as urban green space, roadside greening.This is because the industry standard (CJT340-2011) of the afforestation planting soil of China is put into effect later, there is no to catch up with transformation and the development speed of urban afforestation, even to this day, there is soil compaction and the phenomenon of soil medium green brick and impurity content exceeding index in a large number in urban afforestation planting soil, declining occurs in greening quality, and Urban Greening is with high costs and waste is huge.
Summary of the invention
For above-mentioned background technology Problems existing, the purpose of the present invention aims to provide a kind of original position mechanical prosthesis method of urban afforestation planting soil.
For this, the present invention is by the following technical solutions: a kind of original position mechanical prosthesis method of urban afforestation planting soil, it is characterized in that, including following reparation step: through mechanization unit operation, pulverize for existing afforestation planting soil and original soil, oxygenation, sterilizing, screen out the green brick in soil and impurity simultaneously, soil after adopting microbe soil organic substrate and pulverizing carries out overlay film heat and moisture preserving after mixing in proportion, functional microorganism in activating microorganisms soil organic substrate produces metabolism and amplification with the indigenous microorganism in soil, after 15 days, the vigor of soil significantly improves, remove overlay film and can carry out planting technique.
As supplementing and perfect technique scheme, present invention additionally comprises techniques below feature.
Described microbe soil organic substrate includes microbial composite and absorption carrier.
Described microbial composite is one or more combinations in Nocard's bacillus, lactic acid bacteria, bacillus cereus.
Described microbial composite is whole combinations of Nocard's bacillus, lactic acid bacteria, bacillus cereus, described Nocard's bacillus: described lactic acid bacteria: the weight mass ratio of described bacillus cereus is: 0.75-5.5:0.75-1.25:0.75-2.5.
The weight ratio of described microbial composite and described absorption carrier is: 1:100-150, one or more combinations of the organic substrate that described absorption carrier obtains after greening garbage (leaves, branch etc.) and changing food waste carry out aerobic fermentation, utilize carbon source and the nitrogenous source of greening garbage and kitchen castoff, complete fermentation by rational carbon-nitrogen ratio.
Nocard's bacillus, lactic acid bacteria, bacillus cereus the preparation method of microbial composite that formed of combination: Nocard's bacillus, lactic acid bacteria, bacillus cereus are inoculated in first cell culture medium and carry out one-level cultivation by (1) respectively, it is thus achieved that first class inoculum;
(2) respectively by Nocard's bacillus, lactic acid bacteria, bacillus cereus first class inoculum be inoculated in secondary medium and carry out two grades of cultivations, it is thus achieved that zymocyte liquid;
(3) each zymocyte liquid is made microbial composite by the mixing of following part by weight: Nocard's bacillus: lactic acid bacteria: bacillus cereus=0.75-5.5:0.75-1.25:0.75-2.5;
(4) gained microbial composite and absorption carrier are mixed according to weight ratio 1:100-150.
Inoculum concentration 10% ~ 50% when Nocard's bacillus one-level is cultivated in step (1), cultivates pH6 ~ 8, cultivation temperature 27 ~ 32 DEG C, incubation time 5 ~ 7 days;Inoculum concentration 5% ~ 20% when lactic acid bacteria one-level is cultivated, cultivates pH6 ~ 8, cultivation temperature 28 ~ 34 DEG C, incubation time 2 ~ 5 days;Inoculum concentration 5% ~ 15% when bacillus cereus one-level is cultivated, cultivates pH6 ~ 8, cultivation temperature 28 ~ 34 DEG C, incubation time 2 ~ 3 days;In described step (2), Nocard's bacillus two grades is cultivated as aerobic culture, inoculum concentration 20% ~ 50%, cultivation pH6 ~ 8, cultivation temperature 27 ~ 32 DEG C, incubation time 5 ~ 7 days;Lactic acid bacteria two grades is cultivated and is cultivated for stuffiness, and inoculum concentration 5% ~ 20% cultivates pH6 ~ 8, cultivation temperature 28 ~ 34 DEG C, incubation time 2 ~ 5 days;Bacillus cereus two grades is cultivated as aerobic culture, inoculum concentration 5% ~ 15%, cultivation pH6 ~ 8, cultivation temperature 28 ~ 32 DEG C, incubation time 2 ~ 5 days;In described step (3), Nocard's bacillus fermentation culture is aerobic culture, second class inoculum is inoculated in 500mL seed tank, inoculum concentration 20% ~ 50%, cultivating pH6 ~ 8, cultivation temperature 27 ~ 32 DEG C, incubation time was inoculated in 2 village fermentation tanks after 5 ~ 7 days, inoculum concentration 20% ~ 50%, cultivate pH7 ~ 8, cultivation temperature 28 ~ 36 DEG C, incubation time 7 ~ 10 days;Lactic acid bacteria fermentation is cultivated and is cultivated for stuffiness, second class inoculum is inoculated in 200L seed tank, inoculum concentration 5% ~ 20%, cultivates pH6 ~ 8, cultivation temperature 28 ~ 32 DEG C, incubation time 2 ~ 3 days, it is inoculated in 2 village fermentation tanks, inoculum concentration 5% ~ 20% afterwards, cultivate pH7 ~ 8, cultivation temperature 28 ~ 36 DEG C, incubation time 2 ~ 3 days;Fermentation of bacillus is cultivated as aerobic culture, second class inoculum is inoculated in 200L seed tank, inoculum concentration 5% ~ 15%, cultivates pH6 ~ 8, cultivation temperature 28 ~ 32 DEG C, incubation time 2 ~ 3 days, it is inoculated in 2 tons of fermentation tanks, inoculum concentration 20% ~ 50% afterwards, cultivates pH7 ~ 8, cultivation temperature 28 ~ 36 DEG C, incubation time 2 ~ 3 days.
Use the present invention can reach following beneficial effect: the present invention adopts special plant equipment and the organic substrate rich in multiple soil probiotics, by on-the-spot original position mechanical prosthesis, it is possible to the green brick effectively pulverize the soil hardened, removing in soil and other impurity;The organic substrate rich in multiple soil probiotics is utilized to activate the indigenous microorganism in original soil, perfect the biotic population of soil, gradually reduce the pH value of soil, improve breathability and the sedimentation of soil, reduce heavy metal analysis value, recovery and raising soil vitality, after making reparation, the indices of original soil is improved, and meets the relevant criterion of urban landscaping planting soil.
Detailed description of the invention
Embodiment: test plot is divided into 8 regions, including 2 clear areas and 6 trial zones, every 2 of 6 trial zones be a component are 3 groups, often organize respectively according to every mu of 1000kg(DS1000), 2000kg(DS2000), 3000kg(DS3000) use described microbe soil organic substrate, adopt Shen Di gardens Nutrition Soil as comparison.Method particularly includes: Nocard's bacillus, bacillus acidophilus and bacillus subtilis are weighed as microbe soil organic substrate, add in the organic substrate obtained after greening garbage (leaves, branch etc.) carries out aerobic fermentation with changing food waste in proportion, uniformly puddle in the soil of test plot by machinery operation, and be suitably humidified as required, plant after 15 days;Wherein work machine is giant caterpillar formula engineering machinery, is transported to trial zone with flat car, and additionally domestic digging machine does to coordinate and completes original soil reparation in position, and the day hack ability of machine is: 250-350 cube of soil, soil grinding particle size is: 5-25mm.After crop growth period terminates, taking pedotheque and detect, the overall test cycle is about 5 months.
Result of the test:
The equal multi-point sampling of regional, pH value, have matrix content, total nutrient content by compose Buddhist nun test, content of beary metal entrust Shanghai City academy of agricultural sciences detect.
1.pH value is tested
Blank group: 8.72
DS1000:8.43
DS2000:8.56
DS3000:8.71
Matched group: 8.56
Each test group is after less than the process of 5 months, and compared with blank group, soil pH all shows downward trend.
2. there is matrix content detection (weight percent hundred)
Blank group: 0.806%
DS1000:1.81%
DS2000:1.52%
DS3000:1.09%
Each test group there is matrix content all to rise to some extent, and the most obvious with DS1000 group.
3. total nutrient content detection (mg/kg, by N, P, K summation meter)
Blank group: 0.278
DS1000:0.309
DS2000:0.362
DS3000:0.339
In each test group, total nutrient content all rises to some extent, and the most obvious with DS2000 group.
4. shown in the following form of content of beary metal detection (mg/kg)
5. the soil texture and geobiont are observed
The original soil of pilot region is before reparation, biological variety and quantity are very low, substantial amounts of various geobiont is occurred in that in the repairing test stage, including substantial amounts of Aranea, Big Formica fusca, locust, Bufo siccus, Aeschna melanictera and part Lumbricus etc., soil occurs in that the mycelium not having in original soil, although only having repair time 10 months, but the sedimentation of soil is significantly improved.
The present invention adds microbe soil remediation microbial inoculum by plant equipment in proportion in original soil and yellow ground is uniformly puddled; microbe soil repair materials contains substantial amounts of soil probiotics; the indigenous microorganism in soil can be activated; by metabolism and amplification; probiotics content in soil is greatly increased and occupies advantage; can effectively suppress the harmful levels of pathogens in soil; the pH value (being particularly conducive to the growth of the happiness acid trees such as oriental cherry, Semen Ginkgo, red maple) of original soil, the overall vigor improving soil can be reduced.On the other hand, soil, by mechanical activation comminution, has been carried out oxygenation and ultraviolet disinfection by the present invention, improves the oxygen content of soil, and ultraviolet has killed substantial amounts of harmful bacteria in soil effectively simultaneously;It is effectively increased the soil property of original soil after process, is conducive to the root of hair of trees and flowers and plants, is conducive to the sprouting of shoot, young leaves.
Practical situation for the low and existing planting technique soil poor quality of original soil utilization rate, mechanization original soil and existing urban afforestation planting soil is carried out in-situ immobilization, can effectively pulverize the soil hardened, remove the green brick in a large amount of soil and impurity, soil is smashed, oxygenation and ultraviolet disinfection, improve crumb structure and the purity of soil, by mixed microorganism organic substrate in soil in proportion, function probiotics contained in microbe organic matrix is made to produce metabolism and amplification with indigenous microorganism, improve breathability and the sedimentation of soil, green brick in removing soil and other impurity, improve the crumb structure of soil, the purity of recovery and raising soil and vigor are simultaneously, can also effectively reduce the acid-base value of soil and relevant heavy metal analysis value, after making reparation, the indices of original soil reaches the industry standard (CJT340-2011) with compound afforestation planting soil.Therefore, this technology, while solving the existing quality problems of urban afforestation planting soil, also solves the practical problems such as environmental protection and huge waste that in real estate development of the city process, the outward transport of a large amount of original soils causes.
The ultimate principle of the present invention and principal character and advantages of the present invention have more than been shown and described.Skilled person will appreciate that of the industry; the present invention is not restricted to the described embodiments; described in above-described embodiment and description is that principles of the invention is described; without departing from the spirit and scope of the present invention; the present invention also has various changes and modifications, and these changes and improvements both fall within the claimed scope of the invention.Claimed scope is defined by appending claims and equivalent thereof.

Claims (6)

1. the original position mechanical prosthesis method of a urban afforestation planting soil, it is characterized in that: include following reparation step: by mechanization unit operation, soil is smashed, oxygenation and ultraviolet disinfection, mix in proportion with microbe soil organic substrate, after completing, overlay film makes it keep uniform temperature and humidity, the soil after repairing can be carried out greening and utilize plantation after 15 days.
2. the original position mechanical prosthesis method of a kind of urban afforestation planting soil according to claim 1, it is characterised in that: described microbe soil organic substrate includes microbial composite and absorption carrier.
3. the original position mechanical prosthesis method of a kind of urban afforestation planting soil according to claim 3, it is characterised in that: described microbial composite is one or more combinations in Nocard's bacillus, lactic acid bacteria, bacillus cereus.
4. the original position mechanical prosthesis method of a kind of urban afforestation planting soil according to claim 3, it is characterized in that: described microbial composite is whole combinations of Nocard's bacillus, lactic acid bacteria, bacillus cereus, described Nocard's bacillus: described lactic acid bacteria: the weight mass ratio of described bacillus cereus is: 0.75-5.5:0.75-1.25:0.75-2.5.
5. the original position mechanical prosthesis method of a kind of urban afforestation planting soil according to claim 2, it is characterized in that: the weight ratio of described microbial composite and described absorption carrier is: 1:100-150, one or more of the organic substrate that described absorption carrier obtains after greening garbage and changing food waste carry out aerobic fermentation combine.
6. the original position mechanical prosthesis method of a kind of urban afforestation planting soil according to claim 4, it is characterised in that: described Nocard's bacillus, lactic acid bacteria, the preparation method of microbial composite that the combination of bacillus cereus is formed be:
(1) respectively Nocard's bacillus, lactic acid bacteria, bacillus cereus are inoculated in first cell culture medium and carry out one-level cultivation, it is thus achieved that first class inoculum;
(2) respectively by Nocard's bacillus, lactic acid bacteria, bacillus cereus first class inoculum be inoculated in secondary medium and carry out two grades of cultivations, it is thus achieved that zymocyte liquid;
(3) each zymocyte liquid is made microbial composite by the mixing of following part by weight: Nocard's bacillus: lactic acid bacteria: bacillus cereus=0.75-5.5:0.75-1.25:0.75-2.5;
(4) gained microbial composite and absorption carrier are mixed according to weight ratio 1:100-150.
CN201610270861.0A 2016-04-27 2016-04-27 In-situ mechanical remediation method of urban landscaping planting soil Pending CN105710122A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610270861.0A CN105710122A (en) 2016-04-27 2016-04-27 In-situ mechanical remediation method of urban landscaping planting soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610270861.0A CN105710122A (en) 2016-04-27 2016-04-27 In-situ mechanical remediation method of urban landscaping planting soil

Publications (1)

Publication Number Publication Date
CN105710122A true CN105710122A (en) 2016-06-29

Family

ID=56162504

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610270861.0A Pending CN105710122A (en) 2016-04-27 2016-04-27 In-situ mechanical remediation method of urban landscaping planting soil

Country Status (1)

Country Link
CN (1) CN105710122A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108034650A (en) * 2017-12-27 2018-05-15 北京嘉博文生物科技有限公司 A kind of microbial bacteria agent carrier and preparation method and application
CN114651547A (en) * 2022-03-04 2022-06-24 上海园林绿化建设有限公司 Landscaping soil remediation treatment method

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1173835A (en) * 1995-09-25 1998-02-18 曾尼卡有限公司 Anaerobic/aerobic decontamination of DDT contaminated soil by repeated anaerobic/aerobic treatments
KR20080112753A (en) * 2007-06-22 2008-12-26 강원대학교산학협력단 Composition comprising zerovalent iron for remediation of rice paddy soils contaminated with heavy metals and a method using the same
CN103736725A (en) * 2014-01-17 2014-04-23 上海大颂生物技术有限公司 Soil remediation method and biological agent for same, and preparation method and application of biological agent
CN203817043U (en) * 2013-12-05 2014-09-10 沈阳环境科学研究院 Circulation type ozone oxidation treatment system of contaminated soil
CN104338741A (en) * 2013-07-23 2015-02-11 上海环垦生态科技有限公司 Heavy metal polluted soil repairing agent with high content of biocarbon and humus and application method thereof
CN104583389A (en) * 2012-05-31 2015-04-29 华沙大学 Composition of bacterial strains, bioremediation mixture and use of this composition for the removal of contaminants from the soil and a method for purifying of the soil contaminants
CN104607460A (en) * 2015-03-02 2015-05-13 南京科盛环保技术有限公司 Bioremediation method of organic matter contaminated soil

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1173835A (en) * 1995-09-25 1998-02-18 曾尼卡有限公司 Anaerobic/aerobic decontamination of DDT contaminated soil by repeated anaerobic/aerobic treatments
KR20080112753A (en) * 2007-06-22 2008-12-26 강원대학교산학협력단 Composition comprising zerovalent iron for remediation of rice paddy soils contaminated with heavy metals and a method using the same
CN104583389A (en) * 2012-05-31 2015-04-29 华沙大学 Composition of bacterial strains, bioremediation mixture and use of this composition for the removal of contaminants from the soil and a method for purifying of the soil contaminants
CN104338741A (en) * 2013-07-23 2015-02-11 上海环垦生态科技有限公司 Heavy metal polluted soil repairing agent with high content of biocarbon and humus and application method thereof
CN203817043U (en) * 2013-12-05 2014-09-10 沈阳环境科学研究院 Circulation type ozone oxidation treatment system of contaminated soil
CN103736725A (en) * 2014-01-17 2014-04-23 上海大颂生物技术有限公司 Soil remediation method and biological agent for same, and preparation method and application of biological agent
CN104607460A (en) * 2015-03-02 2015-05-13 南京科盛环保技术有限公司 Bioremediation method of organic matter contaminated soil

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
黄海涛: "《循环城市:北京环境危机与城市新陈代谢系统构建》", 31 January 2015 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108034650A (en) * 2017-12-27 2018-05-15 北京嘉博文生物科技有限公司 A kind of microbial bacteria agent carrier and preparation method and application
CN114651547A (en) * 2022-03-04 2022-06-24 上海园林绿化建设有限公司 Landscaping soil remediation treatment method

Similar Documents

Publication Publication Date Title
CN105838644B (en) Complex micro organism fungicide and bacterial manure and preparation method thereof and the application in reparation salt affected soil
CN101507409B (en) Disease-resistant, wireworm-resistant seedling raising matrix and production method thereof
CN105695354B (en) The technique and application of superhigh temperature aerobic composting fermentation processing municipal sludge
CN101717315B (en) Special peanut organic and inorganic compound fertilizer for biologically preventing and treating root knot nematode disease and preparation method thereof
CN105198639A (en) Special micro-balance ecological fertilizer for organic tea garden and preparation method thereof
CN106947725A (en) Microbial bacterial agent and its application in alkaline land soil improvement
CN102876576A (en) Acidic soil conditioner, and preparation method and application thereof
CN105255794A (en) Pseudomonas frederiksbergensis sp. NT-2 and application thereof
CN106734188A (en) A kind of nitrate nitrogen contamination method of heavy metals in farmland pollution
CN109504622A (en) A kind of lysine bacillus and the composite bacteria agent of bacillus subtilis and preparation method thereof
CN104056858A (en) Soil restoration method
CN106544302A (en) A kind of complex micro organism fungicide for soil improvement and preparation method thereof
CN107012105A (en) Composite bacteria agent, animals died of illness harmless treatment fermenting agent, composite microbe fertilizer, solid medium and fluid nutrient medium
CN108821908A (en) A kind of microbial inoculum comprising Batavia bacillus HJ-1 and its application
CN105684849A (en) Organic substrate containing arbuscular mycorrhiza fungi and preparing method and application thereof
CN105061004A (en) Preparation method for biological organic fertilizer
CN105505843B (en) One plant of Photosynthetic bacterium strain, the Liquid Fertilizer containing the bacterial strain and preparation method, application
Zhai et al. Long-term ditch-buried straw return alters soil carbon sequestration, nitrogen availability and grain production in a rice–wheat rotation system
CN106673736A (en) Microbial decomposing agent and humus prepared thereby
CN102039305A (en) Method for improving repair efficiency of plant on low As and Hg combined contamination soil
CN106701094A (en) Soil improving type microbial agent and application thereof
CN106399157A (en) Microbial agent with facility agricultural soil remediation function, and preparation and application of microbial agent
CN104273176A (en) Plant organic matter-bacillus subtils mixed inoculum and its preparation method and use
CN105710122A (en) In-situ mechanical remediation method of urban landscaping planting soil
CN105950480B (en) A kind of method of herbage degradation volume reduction

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
CB03 Change of inventor or designer information

Inventor after: Yang Yonghao

Inventor after: Song Zhicai

Inventor before: Yang Yonghao

Inventor before: Song Youcai

CB03 Change of inventor or designer information
RJ01 Rejection of invention patent application after publication

Application publication date: 20160629

RJ01 Rejection of invention patent application after publication