CN109626583A - A kind of intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source - Google Patents

A kind of intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source Download PDF

Info

Publication number
CN109626583A
CN109626583A CN201811601662.9A CN201811601662A CN109626583A CN 109626583 A CN109626583 A CN 109626583A CN 201811601662 A CN201811601662 A CN 201811601662A CN 109626583 A CN109626583 A CN 109626583A
Authority
CN
China
Prior art keywords
rice field
water
field ditch
cement tub
honeycomb
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
CN201811601662.9A
Other languages
Chinese (zh)
Inventor
娄翼来
张庆忠
杜章留
宋吉青
王俊
韩硕
袁梦
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.)
Institute of Environment and Sustainable Development in Agriculturem of CAAS
Original Assignee
Institute of Environment and Sustainable Development in Agriculturem of CAAS
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 Institute of Environment and Sustainable Development in Agriculturem of CAAS filed Critical Institute of Environment and Sustainable Development in Agriculturem of CAAS
Priority to CN201811601662.9A priority Critical patent/CN109626583A/en
Publication of CN109626583A publication Critical patent/CN109626583A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/105Phosphorus compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen

Abstract

The invention discloses a kind of intensified ecological intercepting systems of rice field ditch nitrogen phosphorus pollution of area source, for existing rice field nitrogen phosphorus pollution of area source problem, now propose following scheme, it includes rice field ditch, water-break runoff and honeycomb cement tub, flowing has water-break runoff in the rice field ditch, and the identical honeycomb cement tub of multiple structures is provided in rice field ditch, the rice field ditch includes water inlet, water outlet, furrow bank and bottom of trench, and honeycomb cement tub is located at the top of bottom of trench, the inside of the honeycomb cement tub is filled with the mixture of host material and functional microorganism, and the top of honeycomb cement tub is provided with opening, cultivation has water plant in the honeycomb cement tub, and the root of water plant extends to the inside of host material Yu functional microorganism mixture.The present invention can achieve the effect that highly enriched interception to rice field ditch nitrogen phosphorus pollution of area source.

Description

A kind of intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source
Technical field
The present invention relates to agricultural non-point source pollution control technology field more particularly to a kind of rice field ditch nitrogen phosphorus pollution of area source Intensified ecological intercepting system.
Background technique
During China's Rice Production, due to blindly a large amount of application chemical fertilizer, water and fertilizer management Technical comparing backwardness etc., Cause chemical fertilizer utilization ratio generally low, the nitrogen phosphorus major part that chemical fertilizer loses is finally flowed by irrigating water-break and rainfall runoff Environment water causes water eutrophication, threatens water ecological setting safety, restricts rice field agricultural sustainable development.Therefore, it solves Certainly rice field nitrogen phosphorus pollution of area source problem is for improving water body environment quality, promoting agricultural cleaning watershed construction with highly important Meaning.
The existing technical measures for solving rice field nitrogen phosphorus pollution of area source mainly include source abatement technology, process Interception Technology With end circulating technology, wherein abatement technology in source is the most key, relates generally to liquid manure optimum management technology, such as side slat is applied deeply Fertile rice transplanting integrated technique, slow-release or control-release fertilizer technology, organic fertilizer substitute technology, warehouse of vibrating water-saving technology etc., these technologies It promotes and applies and different degrees of on source has cut down nitrogen and phosphorus loading;Process Interception Technology mainly includes ecological canal, people The engineering ecologies class recovery technique such as work wetland, wherein ecological canal technology is since it focuses on Ecological Restoration and has both landscape effect Benefit is concerned at present.It is built by ecological canal, the self-cleaning for restoring raising system intercepts function, can effectively reduce ditch water in a canal Body nitrogen and phosphorus loading, removal efficiency of nitrogen and phosphorus is up to 30% level above;In order to further strengthen the purification function of irrigation canals and ditches, people are also The reinforcing for developing irrigation canals and ditches nitrogen and phosphorus pollution intercepts slot technology, intercepts slot and is placed in irrigation canals and ditches the removal effect for strengthening nitrogen phosphorus, still Existing this reinforcing Interception Technology is that it is net not combine integrated microorganism based on material absorption retention and plant absorption effect Change technology, so strengthening, interception effect is limited, and irrigation canals and ditches nitrogen, tp removal rate are promoted to 40% level above, and remaining nitrogen phosphorus is still Still there is certain optimization room for promotion in terms of constituting certain threat, technological synthesis and reinforcing interception effect to water body environment.This Outside, as the extensive construction of ecological canal is applied, the requirement to work in maintenance management for plant harvesting and irrigation canals and ditches dredging is cured Come higher, environmental pressure brought by the straw and bed mud waste generated therewith is increasingly severe.
So in view of the above-mentioned problems, we have proposed a kind of intensified ecologicals of rice field ditch nitrogen phosphorus pollution of area source to intercept system System.
Summary of the invention
A kind of intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source proposed by the present invention, solves existing rice Field nitrogen phosphorus pollution of area source problem.
To achieve the goals above, present invention employs following technical solutions:
A kind of intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source, including rice field ditch, water-break runoff and Honeycomb cement tub, the rice field ditch include water inlet, water outlet, furrow bank and bottom of trench, there is flowing in the rice field ditch Water-break runoff, and the identical honeycomb cement tub of multiple structures is provided in rice field ditch, and each honeycomb cement tub It being respectively positioned on bottom of trench inner wall, the inside of the honeycomb cement tub is filled with the mixture of host material and functional microorganism, and The top of honeycomb cement tub is provided with opening, and cultivation has water plant, and the root of water plant in the honeycomb cement tub Portion extends to the inside of host material Yu functional microorganism mixture.
Preferably, the honeycomb cement tub is hollow rectangular-shape, and groove body surrounding is in that honeycomb socket bore structure is set It sets, the width of the honeycomb cement tub is the 1/3~2/3 of bottom of trench width, and length is 1~1.5 times of width, is highly higher than rice The field water-break phase irrigation canals and ditches highest water surface.
Preferably, the host material be using after harvesting rice straw, harvesting plant residue is raw material in irrigation canals and ditches, preparation Made of partial size < 1mm charcoal, then again by the bed mud substance of irrigation canals and ditches dredging after natural drying with the charcoal according to 20 What~30:1 mass ratio was prepared after mixing well, the packing volume of the host material accounts for the honeycomb cement tub inner body Long-pending 2/3 or more.
Preferably, the functional microorganism is microbial bacterial agent, including roost rose of Sharon pseudomonad strain, bacillus cereus Strain, the functional microorganism microbial inoculum are mixed with the host material according to the mass ratio of 1:20~30.
Preferably, the water plant is one or more combinations of very water, heavy water class water plant.
The invention has the benefit that 1, intensified ecological Interception Technology of the invention combines material absorption retention, plant It absorbs, the pollutant catabolic gene action principle of the multipath of microorganism conversion, more canals is carried out to nitrogen, the phosphorus substance of rice field ditch water body The combined purifying in road intercepts, and then height reduces the nitrogen and phosphorus loading of rice field ditch water body;2, the host material of the technology It is entirely derived from the resource utilization of internal system waste, efficiently solves the problem of environmental pollution of ecological canal waste, And it is cost-saved compared with exogenous material;3, the charcoal of the technology-bed mud compound matrix material is that water plant, function are micro- Biology provides good habitat, especially bed mud material as system endogenous substance, effectively provides centainly for plant, microorganism Carbon source, nutrient, avoid the nutrition pollution of exogenous material aggravation system, promote plant growth and microbial survival and its performance Biological and ecological intercept function.
Detailed description of the invention
Fig. 1 is the structural diagram of the present invention;
Fig. 2 is water-break phase structural schematic diagram in rice field of the invention;
Fig. 3 is the structural schematic diagram of honeycomb cement tub of the invention;
Fig. 4 is nitrogen phosphorus ligands effect picture of the invention.
Figure label: 1 furrow bank, 2 bottoms of trench, 3 water-break runoffs, 4 honeycomb cement tubs, 5 host materials, 6 functional microorganisms, 7 Water plant.
Specific embodiment
Following will be combined with the drawings in the embodiments of the present invention, and technical solution in the embodiment of the present invention carries out clear, complete Site preparation description, it is clear that described embodiments are only a part of the embodiments of the present invention, instead of all the embodiments.
Roost rose of Sharon pseudomonad strain and bacillus cereus strain used are in microorganism fungus kind in following embodiments The existing strain that preservation administrative center is commercially available, is not related to the exploitation of novel bacterial, pertains only to its application.Also, in embodiment Roost rose of Sharon pseudomonad used is specially that China typical culture collection center deposit number is CCTCC NO.M2014244 Bacterial strain;Bacillus cereus is specially that China Committee for Culture Collection of Microorganisms's common micro-organisms center's deposit number is The bacterial strain of CGMCC No.8614;
Roost rose of Sharon pseudomonad zymocyte liquid and Bacillus cereus fermentation bacterium solution are using conventional method in embodiment What culture obtained;Experimental facilities and experimental method described in following each embodiments, unless otherwise specified, be conventional equipment and often Rule method;The material unless otherwise specified, can be commercially available on the market.
Referring to Fig.1-3, a kind of intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source, including rice field ditch, move back Water runoff 3 and honeycomb cement tub 4, the interior flowing of rice field ditch has water-break runoff 3, and multiple structures are provided in rice field ditch Identical honeycomb cement tub 4, the rice field ditch include water inlet, water outlet, furrow bank 1 and bottom of trench 2, and honeycomb cement Slot 4 is located on the inner wall of bottom of trench 2, and the inside of honeycomb cement tub 4 is filled with the mixture of host material 5 and functional microorganism 6, And the top of honeycomb cement tub 4 is provided with opening, cultivating in honeycomb cement tub 4 has water plant 7, and water plant 7 Root extends to the inside of host material 5 Yu 6 mixture of functional microorganism, and honeycomb cement tub 4 is arranged in hollow rectangular-shape, And honeycomb socket bore structure setting is presented in groove body surrounding, the width of honeycomb cement tub 4 is the 1/3~2/3 of 2 width of bottom of trench, Length is 1~1.5 times of width, and height is slightly above the rice field water-break phase irrigation canals and ditches highest water surface, and host material 5 is with the water after harvest It is raw material, the partial size < 1mm charcoal being prepared, then again by irrigation canals and ditches dredging that plant residue is gathered in rice straw, irrigation canals and ditches What bed mud substance was prepared after mixing well after natural drying with the charcoal according to 20~30:1 mass ratio, host material 5 packing volume accounts for 2/3 or more of 4 inner volume of honeycomb cement tub, and functional microorganism 6 is microbial bacterial agent, including is dwelt Rose of Sharon pseudomonad strain, bacillus cereus strain, 6 microbial inoculum of functional microorganism is with host material 5 according to the matter of 1:20~30 Amount than mixing, water plant 7 be very water, sink water class water plant one or more combinations, including reed, cattail, Lythrum salicaria, Rib water shield.
In the description of the present invention, it is to be understood that, term " center ", " longitudinal direction ", " transverse direction ", " length ", " width ", " thickness ", "upper", "lower", "front", "rear", "left", "right", "vertical", "horizontal", "top", "bottom", "inner", "outside", " up time The orientation or positional relationship of the instructions such as needle ", " counterclockwise " is to be based on the orientation or positional relationship shown in the drawings, and is merely for convenience of The description present invention and simplified description, rather than the equipment of indication or suggestion meaning or element must have a particular orientation, with spy Fixed orientation construction and operation, therefore be not considered as limiting the invention.
In addition, term " first ", " second " are used for descriptive purposes only and cannot be understood as indicating or suggesting relative importance Or implicitly indicate the quantity of indicated technical characteristic.Define " first " as a result, the feature of " second " can be expressed or Implicitly include one or more of the features.In the description of the present invention, the meaning of " plurality " is two or more, Unless otherwise specifically defined.
Embodiment: having carried out plant harvesting and dredging operation to ecological canal before test, selects representative strong neighbouring Two almost the same ecological canals of specification are studied, will be on 10 in an ecological canal as embodiment research Open honeycomb cement tub 4 is held, it is parallel to be staggeredly equidistantly placed in the heavier canal section of water pollution load, another irrigation canals and ditches conduct Comparative example.Cement tub is rectangular parallelepiped structure, and length 0.6m, width 0.4m are highly 0.6m, and spacing 1.2m, water flow can Pass freely through groove body.
Host material 5 is prepared, the resource utilization of source waste in the rice field ditch system of proving ground is entirely derived from: will The plant residue of rice straw, irrigation canals and ditches harvesting after the harvest of rice field is prepared into charcoal under the conditions of high temperature anaerobic, crushed 1mm Sieve, the bed mud substance of irrigation canals and ditches dredging is mixed well with charcoal 25:1 in mass ratio after natural drying, forms host material 5. It is packed into cement tub after host material 5 and denitrogenation dephosphorizing microbial inoculum are mixed well according to the mass ratio of 25:1, loading accounts for cement Water plant reed is cultivated in the 2/3 of slot space later, respectively the setting sampling section at the water inlet of irrigation canals and ditches and discharge outlet, In rice field water-break phase sample detection water body nitrogen, phosphorus concentration three times, nitrogen, the tp removal rate of ecological canal are analyzed, it can from Fig. 4 Out, there is no the irrigation canals and ditches for implementing intensified ecological Interception Technology to the removal rate of total nitrogen, total phosphorus in 30% level above in comparative example, and The irrigation canals and ditches for implementing intensified ecological Interception Technology in embodiment are more preferable to total nitrogen, the removal effect of total phosphorus in the water-break of rice field, total nitrogen, total The removal rate of phosphorus is up to 50% or more, and removal effect is also apparently higher than existing ecological canal and strengthens what Interception Technology was reported 40% level above;It can be seen that Interception Technology of the invention reaches highly enriched interception to rice field ditch nitrogen phosphorus pollution of area source Effect.
The foregoing is only a preferred embodiment of the present invention, but scope of protection of the present invention is not limited thereto, Anyone skilled in the art in the technical scope disclosed by the present invention, according to the technique and scheme of the present invention and its Inventive concept is subject to equivalent substitution or change, should be covered by the protection scope of the present invention.

Claims (5)

1. a kind of intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source, including rice field ditch, water-break runoff (3) and Honeycomb cement tub (4), which is characterized in that the rice field ditch includes furrow bank (1) and bottom of trench (2), in the rice field ditch Flowing has water-break runoff (3), and the identical honeycomb cement tub (4) of multiple structures is provided in rice field ditch, and each described Honeycomb cement tub (4) is respectively positioned on bottom of trench (2) inner wall, and the inside of the honeycomb cement tub (4) is filled with host material (5) The top of the mixture of functional microorganism (6), and honeycomb cement tub (4) is provided with opening, the honeycomb cement tub (4) Interior cultivation has water plant (7), and the root of water plant (7) extends to host material (5) and functional microorganism (6) mixture Inside.
2. the intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source according to claim 1, which is characterized in that institute Honeycomb cement tub (4) are stated in hollow rectangular-shape, and groove body surrounding is in honeycomb socket bore structure setting, the honeycomb water The width of mud groove (4) is the 1/3~2/3 of bottom of trench (2) width, and length is 1~1.5 times of width, is highly higher than the rice field water-break phase The irrigation canals and ditches highest water surface.
3. the intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source according to claim 1, which is characterized in that institute State host material (5) be using after harvesting rice straw, harvesting plant residue is raw material in irrigation canals and ditches, partial size < 1mm for being prepared Charcoal, then the bed mud substance of irrigation canals and ditches dredging is filled with the charcoal according to 20~30:1 mass ratio after natural drying again It is prepared after point mixing, the packing volume of the host material (5) accounts for the 2/3 of honeycomb cement tub (4) inner volume More than.
4. the intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source according to claim 1, which is characterized in that institute Stating functional microorganism (6) is microbial bacterial agent, including roost rose of Sharon pseudomonad strain, bacillus cereus strain, the function Microorganism (6) microbial inoculum is mixed with the host material (5) according to the mass ratio of 1:20~30.
5. the intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source according to claim 1, which is characterized in that institute State one or more combinations that water plant (7) is very water, heavy water class water plant.
CN201811601662.9A 2018-12-26 2018-12-26 A kind of intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source Pending CN109626583A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811601662.9A CN109626583A (en) 2018-12-26 2018-12-26 A kind of intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811601662.9A CN109626583A (en) 2018-12-26 2018-12-26 A kind of intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source

Publications (1)

Publication Number Publication Date
CN109626583A true CN109626583A (en) 2019-04-16

Family

ID=66077966

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811601662.9A Pending CN109626583A (en) 2018-12-26 2018-12-26 A kind of intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source

Country Status (1)

Country Link
CN (1) CN109626583A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110204050A (en) * 2019-05-29 2019-09-06 农业农村部环境保护科研监测所 The agricultural ecological intercepting system and method for preventing area source pollutants from spreading
CN114230105A (en) * 2021-12-27 2022-03-25 南京大学 Method for reducing farmland non-point source pollution by utilizing reinforced natural irrigation and drainage ditches
CN115583730A (en) * 2022-09-28 2023-01-10 西南科技大学 Method for purifying rice field water discharge by planting hydroponic vegetables in rice field drainage ditch
WO2023115781A1 (en) * 2021-12-21 2023-06-29 浙江大学 Farmland drainage water treatment system and method based on ecological interception and cyclic purification

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102966083A (en) * 2012-11-30 2013-03-13 中国科学院东北地理与农业生态研究所 Ecological ditch constructing method for controlling nitrogen and phosphorus in farmland drainage
CN206799267U (en) * 2017-04-28 2017-12-26 南京万德斯环保科技股份有限公司 A kind of cities and towns irrigation canals and ditches ecological purification system

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102966083A (en) * 2012-11-30 2013-03-13 中国科学院东北地理与农业生态研究所 Ecological ditch constructing method for controlling nitrogen and phosphorus in farmland drainage
CN206799267U (en) * 2017-04-28 2017-12-26 南京万德斯环保科技股份有限公司 A kind of cities and towns irrigation canals and ditches ecological purification system

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110204050A (en) * 2019-05-29 2019-09-06 农业农村部环境保护科研监测所 The agricultural ecological intercepting system and method for preventing area source pollutants from spreading
WO2023115781A1 (en) * 2021-12-21 2023-06-29 浙江大学 Farmland drainage water treatment system and method based on ecological interception and cyclic purification
CN114230105A (en) * 2021-12-27 2022-03-25 南京大学 Method for reducing farmland non-point source pollution by utilizing reinforced natural irrigation and drainage ditches
CN115583730A (en) * 2022-09-28 2023-01-10 西南科技大学 Method for purifying rice field water discharge by planting hydroponic vegetables in rice field drainage ditch

Similar Documents

Publication Publication Date Title
CN109626583A (en) A kind of intensified ecological intercepting system of rice field ditch nitrogen phosphorus pollution of area source
CN104609995B (en) Plant growth promoting bio-organic fertilizer for saline-alkali land
CN103086513B (en) Ecological ditch for increasing utilization rates of N and P in farmland by controlling agricultural non-point source pollution
CN107285918A (en) A kind of biological mixing bacterial manure and its preparation method and application
CN1301310C (en) Saline-alkali land improving and fertilizing agent and its preparation method
CN105175180A (en) Method for improving saline alkali land by combination of biochar with organic fertilizer
CN108034620B (en) One plant of bacillus megaterium bacterial strain, peanut drop cadmium agent and its application
CN101993182A (en) Livestock and poultry farm dung dirt biological fermentation treatment method and device
CN102874985B (en) Method for treating waste pollutants in pig farm
CN106433661A (en) Composite microbial organosilicon liquid soil repairing agent for degrading pesticide and heavy metal residues, and preparation method thereof
CN109644609A (en) A kind of method of Degraded Alpine ecological restoration of grassland
CN108476955A (en) The facility and method of summer strawberry are planted using White mushroom slag in salt-soda soil
CN106212094B (en) Dedicated recycling improvement matrix in a kind of salt-soda soil and preparation method thereof
CN105766201B (en) A kind of clover imposes Water soluble fertilizer equipment
CN109716955A (en) It is a kind of to cultivate and plant ecological recycle system
CN109380088A (en) A kind of Low hilly red soil small watershed ecological harnessing system
CN104099282A (en) Environment-friendly straw degradation agent
CN105723845A (en) Ecological water draining ditch
CN110122201A (en) A kind of high and cold upland meadow guard method can adapt to climate change
CN108163987B (en) Constructed wetland construction method for comprehensive treatment of agricultural production non-point source pollution
CN106478263B (en) Saline-alkali soil corn planting method
CN107354105A (en) A kind of complex microbial inoculum and preparation method thereof and the system for administering sewage
CN103271093B (en) Method for preventing soil-borne diseases of crops by using ammonium-reinforced biogas slurry
CN106718754A (en) A kind of classification loop Application way of soilless culture cultivation residue
CN106399167A (en) Biocontrol agent for lily continuous cropping obstacles and preparation method

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

Application publication date: 20190416

RJ01 Rejection of invention patent application after publication