CN108432385A - A kind of Reclaimed Land green fertilizer application method - Google Patents

A kind of Reclaimed Land green fertilizer application method Download PDF

Info

Publication number
CN108432385A
CN108432385A CN201810263197.6A CN201810263197A CN108432385A CN 108432385 A CN108432385 A CN 108432385A CN 201810263197 A CN201810263197 A CN 201810263197A CN 108432385 A CN108432385 A CN 108432385A
Authority
CN
China
Prior art keywords
bacteria residue
soil
application
spring
crop
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.)
Granted
Application number
CN201810263197.6A
Other languages
Chinese (zh)
Other versions
CN108432385B (en
Inventor
周伟
邓良基
张世熔
凌静
邓欧平
谢沂希
胡玉福
高雪松
谢尚春
熊雷
徐博寒
唐祺超
张腾
刘子骁
陈露丹
邹光基
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.)
Chengdu Metropolitan Modern Agricultural Industry Technology Research Institute Co ltd
Sichuan Huadikang Ecological Agriculture Technology Co ltd
Sichuan Zhongnong Runze Biological Technology Co ltd
Original Assignee
Sichuan Agricultural University
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 Sichuan Agricultural University filed Critical Sichuan Agricultural University
Priority to CN201810263197.6A priority Critical patent/CN108432385B/en
Publication of CN108432385A publication Critical patent/CN108432385A/en
Application granted granted Critical
Publication of CN108432385B publication Critical patent/CN108432385B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01BSOIL WORKING IN AGRICULTURE OR FORESTRY; PARTS, DETAILS, OR ACCESSORIES OF AGRICULTURAL MACHINES OR IMPLEMENTS, IN GENERAL
    • A01B79/00Methods for working soil
    • A01B79/02Methods for working soil combined with other agricultural processing, e.g. fertilising, planting

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • Soil Sciences (AREA)
  • Environmental Sciences (AREA)
  • Fertilizers (AREA)

Abstract

The present invention relates to soil improvement fermenting fertilizer field, more particularly to a kind of Reclaimed Land green fertilizer application method.The Reclaimed Land green fertilizer application method includes:Rubble after house site is reclaimed in the soil in soil screens out;Bacteria residue is crushed, using after crushing bacteria residue and urea the soil after reclaiming is improved:Vernal crop diversity and crop sown in spring are sowed first 5~7 days, and bacteria residue is mixed with topsoil;Vernal crop diversity and crop sown in spring are sowed first 1~2 day, apply urea, bacteria residue is covered on soil;In the gap phase in spring to late autumn, bacteria residue is mixed with topsoil.0~20cm Reclaimed Land soil organism highests can be promoted to promote 12.9% every year on average using Reclaimed Land green fertilizer application method of the present invention, N, P, K is promoted to promote 6.2%~10.4%, unit weight reduces by 3.6%~6.9%, field capacity increase about 2.8%~3.8%.The crop yields such as wheat jade every year on average promote 3.6%~5.5%.

Description

A kind of Reclaimed Land green fertilizer application method
Technical field
The present invention relates to soil improvement fermenting fertilizer field, more particularly to a kind of Reclaimed Land green fertilizer application method.
Background technology
The per capita area of cultivated farmland of China is had a large population and a few land, soil pressure is very huge less than four one-tenth of world average level.I Government of state has carried out house site and has reclaimed project, to rural area configure it is improper, utilize the unreasonable house site disperse, leave unused, discarded Implement to arrange and reclaim, becomes arable land resource.However house site Reclaimed Soil is because brick stone is more, soil nutrient status It is poor, cause soil original function and characteristic to be lost, causes crop yield and quality low.However after current house site is reclaimed Fermenting fertilizer applies excessive organic materials and inorganic fertilizer more, and amount of application seriously exceeds soil bearing capacity, exists and cause soil And the risk of environmental pollution;Excessively there is also heavy metals for application or even portion of techniques addition flyash, mine tailings etc. for feces of livestock and poultry The substance that equal potential pollutions threaten;Using the measures such as the miscellaneous smoked soil for waiting weeds and leaf of dry beans are burned, soil is only carried out merely and is supported Point fertilizing, and do not consider soil nutrient growth, safety of soil environment, operating cost and crop short-term yield etc. and ask Topic.
Meanwhile China is the first big country of global Edible Fungi, annual generated culture medium of edible fungus waste material (bacteria residue) Reach 8.0 × 107T becomes the third-largest agricultural wastes in addition to stalk, feces of livestock and poultry.Current annual bacteria residue efficiently uses The 50% of lazy weight total amount, most of bacteria residues are incinerated, abandon or heap is abandoned, and not only cause a large amount of organic resources and land resource Waste, returns surrounding enviroment and brings certain ecological pollution risk.Some researches show that bacteria residues to contain a certain amount of N P and K etc. Nutrient can increase soil fertility after, improve water flowing situation of breathing freely, and promote crop yield.Meanwhile bacteria residue is remained Content of beary metal it is lower than organic materials such as animal feces of livestock and poultry, caused by risk of environmental pollution it is small.However it is current, it is based on bacteria residue Still lack using house site Reclaimed Land green fermenting fertilizer.
Invention content
In view of this, the present invention provides a kind of Reclaimed Land green fertilizer application methods.The Reclaimed Land green fertilizer application method The utilization rate of bacteria residue can be improved, the promotion of the soil organism can be remarkably promoted, crop yield can be improved, reduce fertilizing cost, drop The risk of low heavy metal pollution.
In order to achieve the above-mentioned object of the invention, the present invention provides following technical scheme:
The present invention provides a kind of Reclaimed Land green fertilizer application methods, include the following steps:
Rubble after house site is reclaimed in the soil in soil screens out;Bacteria residue is crushed, using the bacteria residue and urine after crushing Element improves the soil after reclaiming, and the improved, process is as follows:
Vernal crop diversity is sowed first 5~7 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 3000~3500kg/ hm2
Vernal crop diversity is sowed preceding 1~2 day, applies urea, bacteria residue is covered on soil, bacteria residue amount of application for 1000~ 1500kg/hm2
Crop sown in spring is sowed first 5~7 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 3500~4000kg/ hm2
Crop sown in spring is sowed preceding 1~2 day, applies urea, bacteria residue is covered on soil, bacteria residue amount of application for 1500~ 2000kg/hm2
In the gap phase in spring to late autumn, bacteria residue is mixed with topsoil, bacteria residue amount of application is 5500~6500kg/hm2
In the present invention, bacteria residue is the culture medium waste planted after agaricus bisporus.Culture medium prescription is chicken manure, stalk, oil The materials such as the agricultural wastes such as the dregs of rice and lime, urea, phosphate fertilizer.
In the present invention, late autumn refers to that the crops such as wheat sow the plantation period harvested to second year early summer in First Year. Generally October to second year April.
In the present invention, spring refers to the plantation period of seeding corn and other crops spring and summer.Generally May is to September part.
In the present invention, vernal crop diversity is wheat.
In the present invention, crop sown in spring is corn.
Preferably, rubble is the rubble that diameter is more than 40mm.
Preferably, the diameter of the bacteria residue after crushing is no more than 30mm.
Preferably, the soil that it is 0~25cm that topsoil, which is depth,.
Preferably, the amount of application of urea is:It is 160~180kg/hm that vernal crop diversity, which sows preceding 1~2 day amount of application,2, It is 180~200kg/hm that crop sown in spring, which sows preceding 1~2 day amount of application,2
Preferably, the amount of application of urea is:It is 160~180kg/hm that vernal crop diversity, which sows preceding 1~2 day amount of application,2, greatly It is 190~200kg/hm that spring sown crop, which sows preceding 1~2 day amount of application,2
In a specific embodiment provided by the invention, the amount of application of urea is:Vernal crop diversity sows preceding 1 day amount of application For 160kg/hm2, it is 190kg/hm that crop sown in spring, which sows preceding 1~2 day amount of application,2
In another specific embodiment provided by the invention, the amount of application of urea is:Vernal crop diversity sows preceding application in 1 day Amount is 180kg/hm2, it is 200kg/hm that crop sown in spring, which sows preceding 1~2 day amount of application,2
Preferably, improved, process is as follows:
Vernal crop diversity is sowed first 6 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 3000~3500kg/hm2
Vernal crop diversity is sowed preceding 1 day, applies urea, bacteria residue is covered on soil, bacteria residue amount of application for 1000~ 1500kg/hm2
Crop sown in spring is sowed first 6 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 3500~4000kg/hm2
Crop sown in spring is sowed preceding 1 day, applies urea, bacteria residue is covered on soil, bacteria residue amount of application for 1500~ 2000kg/hm2
In the gap phase in spring to late autumn, bacteria residue is mixed with topsoil, bacteria residue amount of application is 6000~6500kg/hm2
Preferably, improved, process is as follows:
Vernal crop diversity is sowed first 6 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 3500kg/hm2
Vernal crop diversity is sowed first 1 day, applies urea, bacteria residue is covered on soil, and bacteria residue amount of application is 1500kg/ hm2
Crop sown in spring is sowed first 6 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 4000kg/hm2
Crop sown in spring is sowed first 1 day, applies urea, bacteria residue is covered on soil, and bacteria residue amount of application is 2000kg/ hm2
In the gap phase in spring to late autumn, bacteria residue is mixed with topsoil, bacteria residue amount of application is 6500kg/hm2
In another specific embodiment provided by the invention, improved, process is as follows:
Vernal crop diversity is sowed first 6 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 3000kg/hm2
Vernal crop diversity is sowed first 1 day, applies urea, bacteria residue is covered on soil, and bacteria residue amount of application is 1000kg/ hm2
Crop sown in spring is sowed first 6 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 3500kg/hm2
Crop sown in spring is sowed first 1 day, applies urea, bacteria residue is covered on soil, and bacteria residue amount of application is 1500kg/ hm2
In the gap phase in spring to late autumn, bacteria residue is mixed with topsoil, bacteria residue amount of application is 6000kg/hm2
Preferably, the gap phase in spring to late autumn is annual 9~October.
Preferably, the gap phase in spring to late autumn is annual mid-September~late September.
It is highly preferred that gap phase in spring to late autumn, 7 days, i.e. mid-September after spring harvests.
The present invention provides a kind of Reclaimed Land green fertilizer application methods.The Reclaimed Land green fertilizer application method includes following step Suddenly:Rubble after house site is reclaimed in the soil in soil screens out;Bacteria residue is crushed, using after crushing bacteria residue and urea to multiple Soil after cultivating is improved, and the improved, process is as follows:Vernal crop diversity is sowed first 5~7 days, and bacteria residue is mixed with topsoil, Bacteria residue amount of application is 3000~3500kg/hm2;Vernal crop diversity sow preceding 1~2 day, application urea, by bacteria residue be covered in soil it On, bacteria residue amount of application is 1000~1500kg/hm2;Crop sown in spring is sowed first 5~7 days, bacteria residue is mixed with topsoil, bacterium Slag amount of application is 3500~4000kg/hm2;Crop sown in spring sow preceding 1~2 day, application urea, by bacteria residue be covered in soil it On, bacteria residue amount of application is 1500~2000kg/hm2;In the gap phase in spring to late autumn, bacteria residue is mixed with topsoil, bacteria residue Amount of application is 5500~6500kg/hm2.The technique effect that the present invention has is:
It can promote 0~20cm Reclaimed Land soil every year on average by using Reclaimed Land green fertilizer application method of the present invention Organic matter highest promotes 12.9%, promotes N, P, K to promote 6.2%~10.4%, unit weight reduces by 3.6%~6.9%, field water holding Amount increases about 2.8%~3.8%.The crop yields such as wheat jade every year on average promote 3.6%~5.5%, while than existing animal dung Just about 1500~1800Yuan/hm is increased income with the annual abridged edition of chemical fertilizer fermenting fertilizer2, cost-effective compared with organic commercial fertilizer fermenting fertilizer About 60%~70%.Heavy metal-polluted soil Hazard ratio feces of livestock and poultry is promoted to reduce by 38% or more with chemical fertilizer fermenting fertilizer.The present invention is A set of house site Reclaimed Land for considering soil nutrient growth, safety of soil environment, operating cost and crop short-term yield Green fermenting fertilizer.
Compared with existing bacteria residue compost returning to the field technology, the present invention has following advantage:
1. than existing bacteria residue compost returning to the field technology, reduce time and the nutrient loss of compost;
2. in size spring, the environmental pressure and pollution risk that are brought to soil environment reduce nearly 30%;
3. after measured in crop kernel heavy metal Cu, Cd, Pb and Zn the content year existing bacteria residue compost returning to the field of value added ratio Technology low nearly 15% shows that the technology is low closer to the heavy metal pollution risk of crop kernel than existing bacteria residue compost returning to the field technology 15%;
4. soil organism year value added increases highest nearly 50% than existing bacteria residue compost returning to the field technology, can more promote multiple Cultivate soil physico-chemical property improvement;
5. wheat and corn crop yield year value added are higher by nearly 30% than existing bacteria residue compost returning to the field technology, can more promote Increase into crop yield.
6. the technology reduces the chemical fertilizer applications such as urea, phosphate fertilizer, potash fertilizer than existing bacteria residue compost returning to the field technology, annual per hectare About 900 kilograms, year net income increase reaches as high as 2700 yuans.
Specific implementation mode
The invention discloses a kind of Reclaimed Land green fertilizer application method, those skilled in the art can use for reference present disclosure, It is suitably modified technological parameter realization.In particular, it should be pointed out that all similar substitutions and modifications carry out those skilled in the art Say it is it will be apparent that they are considered as being included in the present invention.The method of the present invention and application have passed through preferred embodiment It is described, related personnel can obviously not depart from the content of present invention, in spirit and scope to method described herein and answer With being modified or suitably changing and combine, to realize and apply the technology of the present invention.
Seed used, fertilizer are available on the market in Reclaimed Land green fertilizer application method provided by the invention.Following reality Bacteria residue used in example is applied purchased from Dayi County ring town mushroom crop cultivation speciality cooperative society.
With reference to embodiment, the present invention is further explained:
Embodiment 1
(1) experiment and promoting region:The Chengdu towns Qi Quan;
(2) time:In April, 2017 in April, 2014-;
(3) long-term cropping:Wheat jade crop rotation (wheat, Corn Rotation System);
(4) fertilizing scheme:
Totally 3 processing schemes, each processing are set for blank control, common fertilizer, feces of livestock and poultry and chemical fertilizer fertilizing and embodiment 1 3 parallel, totally 12 random alignment cells.Plot area is 30m2, Tu Gou, ditch depth 20cm are built between cell.
1. the rubble that is relatively large in diameter in the soil in soil after manual screening removal is reclaimed, the stone sizes in Reclaimed Land are not More than 40mm;
2. bacteria residue, which is crushed to particle length, using pulverizer is no more than 30mm;
3. before big spring and small spring are sowed first 6 days, by bacteria residue (big spring 3500kg/hm2, small spring 3000kg/ hm2) it is flat be spread on soil, mixed with 0-25cm soil with rotary cultivator;
4. being sowed first 1 day in big spring and small spring, inorganic fertilizer (big spring urea 190kg/hm is applied2, small spring 160kg/hm2), by bacteria residue (big spring 1500kg/hm2, small spring 1000kg/hm2) be covered on soil;
5. in big spring and the gap phase (mid-September) in small spring, by 6000kg/hm2Bacteria residue application is uniformly spread on soil Surface is mixed bacteria residue with 0-25cm soil using rotary cultivator.
(5) sample collection is measured and is analyzed
The acquisition time of soil is 2014 to 2017 annual April.Each cell soil is acquired using multiple spot mixing method Cut open and depth be 0-20cm soil sample, with aseptic PET resin pocket encapsulation take back laboratory.It is measured after room-dry.Soil Organic matter, full nitrogen, full phosphorus, full potassium measurement are all made of conventional method.
Data processing is for statistical analysis using 19.0 softwares of SPSS.
(6) effect:
1 soil nutrient content list (g/kg) of table
2 heavy metal content in soil list (mg/kg) of table
3 Heavy Metals Quantity of Crop in Wastewater list (mg/kg) of table
4 yield of table and annual income pay list
Note:Year expenditure=seed+machinery+fertilizer+artificial+pesticide+depreciation, annual income=stalk sells+and seed sells, year Net income=annual income-year pays
Conclusion:
1. 0-20cm Reclaimed Land soil organism highests are promoted up to 10.5% every year on average, N, P, K is promoted to be promoted 6.3% -10.2%, unit weight reduces by 3.6% -6.2%, field capacity increase about 2.8% -3.2%.
2. the crop yields such as wheat jade every year on average promote 3.6% -5.3%, than feces of livestock and poultry and chemical fertilizer fermenting fertilizer abridged edition Increase income about 1800 yuan/hm2
3. than feces of livestock and poultry and chemical fertilizer fermenting fertilizer, the heavy metals increase in 3 years such as 0-20cm soil Cu, Cd, Pb and Zn Amount reduces 52.8% -65.8%.
Embodiment 2
(1) experiment and promoting region:Chengdu Dayi County;
(2) time:In November, 2014-in September, 2017;
(3) long-term cropping:Wheat jade crop rotation (wheat, Corn Rotation System);
(4) fertilizing scheme:
Each processing sets 3 parallel, totally 15 random alignment cells.Plot area is 21m2, Tu Gou is built between cell, Ditch depth 20cm.
1. the rubble that is relatively large in diameter in the soil in soil after manual screening removal is reclaimed, the stone sizes in Reclaimed Land are not More than 40mm;
2. bacteria residue, which is crushed to particle length, using pulverizer is no more than 30mm;
3. before big spring and small spring are sowed first 6 days, by bacteria residue (big spring 3500kg/hm2, small spring 3000kg/ hm2) it is flat be spread on soil, mixed with 0-25cm soil with rotary cultivator;
4. being sowed first 1 day in big spring and small spring, inorganic fertilizer (big spring urea 200kg/hm is applied2, small spring 180kg/hm2), by bacteria residue (big spring 2000kg/hm2, small spring 1500kg/hm2) be covered on soil;
5. in big spring and the gap phase (mid-September) in small spring, by 6500kg/hm2Bacteria residue application is uniformly spread on soil Surface is mixed bacteria residue with 0-25cm soil using rotary cultivator.
(5) sample collection is measured and is analyzed
The acquisition time of soil is 1 day after 2014 to 2017 annual September part crop sown in spring harvests.It is mixed using multiple spot Method acquire each cell soil cut open and depth be 0-20cm soil sample, with aseptic PET resin pocket encapsulation take back laboratory.Room-dry After be measured.The soil organism, full nitrogen, full phosphorus, full potassium measurement be all made of conventional method.
Data processing is for statistical analysis using 19.0 softwares of SPSS.
(6) effect:
5 soil nutrient content list (g/kg) of table
6 heavy metal content in soil list (mg/kg) of table
7 Heavy Metals Quantity of Crop in Wastewater list (mg/kg) of table
8 yield of table and annual income pay list
Note:Year expenditure=seed+machinery+fertilizer+artificial+pesticide+depreciation, annual income=stalk sells+and seed sells, year Net income=annual income-year pays
Conclusion:
1. 0-20cm Reclaimed Land soil organism highests are promoted up to 12.9% every year on average, N, P, K is promoted to be promoted 6.2% -10.4%, unit weight reduces by 4.7% -6.9%, field capacity increase about 3.3% -3.8%.
2. the crop yields such as wheat jade every year on average promote 4.2% -5.5%, than feces of livestock and poultry and chemical fertilizer fermenting fertilizer abridged edition Increase income about 1500 yuan/hm2
3. poultry manure and chemical fertilizer fermenting fertilizer, the content of beary metal low 38.3%-such as 0-20cm soil Cu, Cd, Pb and Zn 61.4%.
Comparative example 1
(1) experiment and promoting region:The Chengdu towns Qi Quan;
(2) time:In May, 2017 in April, 2016-;
(3) long-term cropping:Wheat jade crop rotation (wheat, Corn Rotation System);
(4) fertilizing scheme:
It was delivered in 2016 with reference to Yan Rui《Influence of 3 kinds of organic materials to house site Reclaimed Soil mutability organic carbon》In Disclosed bacteria residue compost returning to the field is with technology to fertilize.
(5) sample collection is measured and is analyzed
With embodiment 1.
(6) effect
9 chemical composition of soil year of table value added list
10 crop kernel heavy metal year value added list (mg/kg) of table
11 yield of table and statement of the income and expenditure
Note:Year expenditure=seed+machinery+fertilizer+artificial+pesticide+depreciation, annual income=stalk sells+and seed sells, year Net income=annual income-year pays
Conclusion:
For embodiment 1,2 than existing bacteria residue compost returning to the field technology, the environmental pressure and pollution risk brought to soil environment is low Nearly 30%;The content year value added low nearly 15% of heavy metal Cu, Cd, Pb and Zn in crop kernel;The soil organism year value added Reach as high as 48.05%;Wheat and corn crop yield year value added increase nearly 30%, annual per hectare reduce urea, phosphate fertilizer, About 900 kilograms of the chemical fertilizer applications such as potash fertilizer, year net income increase reaches as high as 2700 yuans.
Comparative example 2
Compared with Example 2, the dosage of bacteria residue and inorganic fertilizer improves this comparative example.
(1) experiment and promoting region:Chengdu Dayi County;
(2) time:In May, 2017 in April, 2015-;
(3) long-term cropping:Wheat jade crop rotation (wheat, Corn Rotation System);
(4) fertilizing scheme:
Each processing sets 3 parallel, totally 9 random alignment cells.Plot area is 30m2, Tu Gou is built between cell, Ditch depth 20cm.
1. the rubble that is relatively large in diameter in the soil in soil after manual screening removal is reclaimed, the stone sizes in Reclaimed Land are not More than 40mm;
2. bacteria residue, which is crushed to particle length, using pulverizer is no more than 30mm;
3. before big spring and small spring are sowed first 6 days, by bacteria residue (big spring 4000kg/hm2, small spring 3500kg/ hm2) it is flat be spread on soil, mixed with 0-25cm soil with rotary cultivator;
4. being sowed first 1 day in big spring and small spring, inorganic fertilizer (big spring urea 220kg/hm is applied2, small spring 200kg/hm2), by bacteria residue (big spring 2500kg/hm2, small spring 2000kg/hm2) be covered on soil;
5. in big spring and the gap phase (mid-September) in small spring, by 7000kg/hm2Bacteria residue application is uniformly spread on soil Surface is mixed bacteria residue with 0-25cm soil using rotary cultivator.
(5) sample collection is measured and is analyzed
With embodiment 1.
(6) effect
12 chemical composition of soil year of table value added list
13 crop kernel heavy metal year value added list (mg/kg) of table
14 yield of table and statement of the income and expenditure
Note:Year expenditure=seed+machinery+fertilizer+artificial+pesticide+depreciation, annual income=stalk sells+and seed sells, year Net income=annual income-year pays
Conclusion:
The results show that comparing embodiment 1,2, this comparative example improves the amount of application of bacteria residue and inorganic fertilizer, but effect of reclaiming Fruit is not so good as embodiment 1,2 instead.Although 2 organic matter of comparative example and full potassium year value added are higher than embodiment 1,2, soil weight Metal and seed content of beary metal are above embodiment 1,2, and yield is reduced compared with embodiment 1,2, and year, net income was than embodiment 1,2 It is more than 2400 yuan-more than 3800 yuan low.
Comparative example 3
For this comparative example compared with embodiment 1,2, the administration time of bacteria residue and inorganic fertilizer has adjustment.
(1) experiment and promoting region:Chengdu Dayi County;
(2) time:In May, 2017 in April, 2015-;
(3) long-term cropping:Wheat jade crop rotation (wheat, Corn Rotation System);
(4) fertilizing scheme:
Each processing sets 3 parallel, totally 9 random alignment cells.Plot area is 30m2, Tu Gou is built between cell, Ditch depth 20cm.
1. the rubble that is relatively large in diameter in the soil in soil after manual screening removal is reclaimed, the stone sizes in Reclaimed Land are not More than 40mm;
2. bacteria residue, which is crushed to particle length, using pulverizer is no more than 30mm;
3. before big spring and small spring are sowed first 15 days, by bacteria residue (big spring 3500kg/hm2, small spring 3000kg/hm2) it is flat be spread on soil, mixed with 0-25cm soil with rotary cultivator;
4. being sowed first 7 days in big spring and small spring, inorganic fertilizer (big spring urea 200kg/hm is applied2, small spring 180kg/hm2), by bacteria residue (big spring 2000kg/hm2, small spring 1500kg/hm2) be covered on soil;
5. in big spring and the gap phase (late October) in small spring, by 6500kg/hm2Bacteria residue application is uniformly spread on soil Surface is mixed bacteria residue with 0-25cm soil using rotary cultivator.
(5) sample collection is measured and is analyzed
With embodiment 1.
(6) effect
15 chemical composition of soil year of table value added list
16 crop kernel heavy metal year value added list (mg/kg) of table
17 yield of table and statement of the income and expenditure
Note:Year expenditure=seed+machinery+fertilizer+artificial+pesticide+depreciation, annual income=stalk sells+and seed sells, year Net income=annual income-year pays
Conclusion:
Test result is shown, compared with embodiment 1,2, the test period of bacteria residue and inorganic fertilizer has adjustment, in amount of application In the case of identical, the soil organism, full nitrogen, full phosphorus under this comparative example, full potassium value added are superior to embodiment 1, with implementation 2 no significant difference of example.3 heavy metal-polluted soil of comparative example and seed heavy metal value added and embodiment 2 are above reality without significant difference Example 1 is applied, shows that comparative example 3 is high for soil and crop heavy metal Hazard ratio embodiment 1.But 3 wheat of comparative example and corn production Amount is below embodiment 1,2, year net income it is nearly 1400 yuan -2800 yuan lower than embodiment 1,2.It can be seen that comparative example 3 exists Effect is far away from embodiment 1,2 in actual production.
The above is only a preferred embodiment of the present invention, it is noted that for the ordinary skill people of the art For member, various improvements and modifications may be made without departing from the principle of the present invention, these improvements and modifications are also answered It is considered as protection scope of the present invention.

Claims (9)

1. a kind of Reclaimed Land green fertilizer application method, which is characterized in that include the following steps:
Rubble after house site is reclaimed in the soil in soil screens out;Bacteria residue is crushed, using the bacteria residue and urea pair after crushing Soil after reclaiming is improved, and the improved, process is as follows:
Vernal crop diversity is sowed first 5~7 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 3000~3500kg/hm2
Vernal crop diversity is sowed preceding 1~2 day, applies urea, bacteria residue is covered on soil, bacteria residue amount of application for 1000~ 1500kg/hm2
Crop sown in spring is sowed first 5~7 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 3500~4000kg/hm2
Crop sown in spring is sowed preceding 1~2 day, applies urea, bacteria residue is covered on soil, bacteria residue amount of application for 1500~ 2000kg/hm2
In the gap phase in spring to late autumn, bacteria residue is mixed with topsoil, bacteria residue amount of application is 5500~6500kg/hm2
2. Reclaimed Land green fertilizer application method according to claim 1, which is characterized in that the rubble is more than for diameter The rubble of 40mm.
3. Reclaimed Land green fertilizer application method according to claim 1, which is characterized in that bacteria residue after the crushing it is straight Diameter is no more than 30mm.
4. Reclaimed Land green fertilizer application method according to claim 1, which is characterized in that the topsoil is that depth is The soil of 0~25cm.
5. Reclaimed Land green fertilizer application method according to claim 5, which is characterized in that the amount of application of the urea is: It is 160~180kg/hm that vernal crop diversity, which sows preceding 1~2 day amount of application,2, crop sown in spring sows preceding 1~2 day amount of application and is 180~200kg/hm2
6. Reclaimed Land green fertilizer application method according to claim 1, which is characterized in that the improved, process is as follows:
Vernal crop diversity is sowed first 6 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 3000~3500kg/hm2
Vernal crop diversity is sowed first 1 day, applies urea, bacteria residue is covered on soil, and bacteria residue amount of application is 1000~1500kg/ hm2
Crop sown in spring is sowed first 6 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 3500~4000kg/hm2
Crop sown in spring is sowed first 1 day, applies urea, bacteria residue is covered on soil, and bacteria residue amount of application is 1500~2000kg/ hm2
In the gap phase in spring to late autumn, bacteria residue is mixed with topsoil, bacteria residue amount of application is 6000~6500kg/hm2
7. Reclaimed Land green fertilizer application method according to claim 1, which is characterized in that the improved, process is as follows:
Vernal crop diversity is sowed first 6 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 3500kg/hm2
Vernal crop diversity is sowed first 1 day, applies urea, bacteria residue is covered on soil, and bacteria residue amount of application is 1500kg/hm2
Crop sown in spring is sowed first 6 days, and bacteria residue is mixed with topsoil, and bacteria residue amount of application is 4000kg/hm2
Crop sown in spring is sowed first 1 day, applies urea, bacteria residue is covered on soil, and bacteria residue amount of application is 2000kg/hm2
In the gap phase in spring to late autumn, bacteria residue is mixed with topsoil, bacteria residue amount of application is 6500kg/hm2
8. Reclaimed Land green fertilizer application method according to claim 1, which is characterized in that the gap phase in the spring to late autumn For annual 9~October.
9. Reclaimed Land green fertilizer application method according to any one of claim 1 to 9, which is characterized in that the spring It it is annual mid-September~late September to the gap phase in late autumn.
CN201810263197.6A 2018-03-28 2018-03-28 A kind of Reclaimed Land green fertilizer application method Active CN108432385B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810263197.6A CN108432385B (en) 2018-03-28 2018-03-28 A kind of Reclaimed Land green fertilizer application method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810263197.6A CN108432385B (en) 2018-03-28 2018-03-28 A kind of Reclaimed Land green fertilizer application method

Publications (2)

Publication Number Publication Date
CN108432385A true CN108432385A (en) 2018-08-24
CN108432385B CN108432385B (en) 2019-10-22

Family

ID=63197604

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810263197.6A Active CN108432385B (en) 2018-03-28 2018-03-28 A kind of Reclaimed Land green fertilizer application method

Country Status (1)

Country Link
CN (1) CN108432385B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110839384A (en) * 2019-11-28 2020-02-28 重庆市农业科学院 Rapid fertilization method for soil of new remediation land
CN111264283A (en) * 2020-04-03 2020-06-12 四川农业大学 Green fertilizing method for pretty girl planting soil

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103224433A (en) * 2013-05-16 2013-07-31 山东省农业科学院农业资源与环境研究所 Soil fertility improver produced by utilizing waste bacterial residues
CN104285532A (en) * 2014-10-15 2015-01-21 重庆市农业科学院 Reclamated slope purple soil rapid fertilizing method
CN105075444A (en) * 2014-05-19 2015-11-25 上海崇明低碳农业科技有限公司 Soil improving method
CN105622265A (en) * 2015-12-28 2016-06-01 常州思宇环保材料科技有限公司 Method for preparing biological soil conditioner by utilizing edible mushroom dregs

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103224433A (en) * 2013-05-16 2013-07-31 山东省农业科学院农业资源与环境研究所 Soil fertility improver produced by utilizing waste bacterial residues
CN105075444A (en) * 2014-05-19 2015-11-25 上海崇明低碳农业科技有限公司 Soil improving method
CN104285532A (en) * 2014-10-15 2015-01-21 重庆市农业科学院 Reclamated slope purple soil rapid fertilizing method
CN105622265A (en) * 2015-12-28 2016-06-01 常州思宇环保材料科技有限公司 Method for preparing biological soil conditioner by utilizing edible mushroom dregs

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
闫锐等: "3种有机物料对宅基地复垦土壤易变有机碳的影响", 《水土保持学报》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110839384A (en) * 2019-11-28 2020-02-28 重庆市农业科学院 Rapid fertilization method for soil of new remediation land
CN111264283A (en) * 2020-04-03 2020-06-12 四川农业大学 Green fertilizing method for pretty girl planting soil

Also Published As

Publication number Publication date
CN108432385B (en) 2019-10-22

Similar Documents

Publication Publication Date Title
Lal et al. The potential of world cropland soils to sequester C and mitigate the greenhouse effect
CN102876576B (en) Acidic soil conditioner, and preparation method and application thereof
Das et al. Conservation tillage and residue management improves soil properties under a upland rice–rapeseed system in the subtropical eastern Himalayas
CN104761379A (en) Novel multifunctional compound microbial fertilizer and preparation method thereof
CN104813885A (en) Production method for cadmium-polluted rice land governing and rice cadmium reduction
CN106077056A (en) A kind of Bioremediation method for heavy-metal contaminated soil of mining area
CN105695354A (en) Process and application for treating municipal sewage sludge by means of ultrahigh-temperature aerobic composting fermentation
CN106010546A (en) Passivant for treating heavy metal cadmium in acidic farmland soil as well as preparation and use methods of passivant
CN106825026A (en) A kind of method that modified biomass charcoal and its resistance control heavy metal are accumulated in vegetables body
CN105565959A (en) Soil ecological system restoring organic fertilizer
CN108456105A (en) A kind of pine charcoal base microbe soil conditioner and preparation method thereof
CN108059569A (en) A kind of ecology organic type soil conditioner and preparation method thereof
CN105950174B (en) A kind of microbial soil conditioner for salt-soda soil
CN105481505A (en) Special organic fertilizer for wheat plantation and preparation method and application thereof
CN111408618B (en) Method for restoring cadmium-polluted soil by utilizing black nightshade and corn intercropping plants
CN109679665A (en) A kind of soil conditioner, preparation method and applications
CN108432385B (en) A kind of Reclaimed Land green fertilizer application method
CN108690629A (en) A kind of farmland soil modifying agent and preparation method thereof
Busari et al. Influence of mulch and poultry manure application on soil temperature, evapotranspiration and water use efficiency of dry season cultivated okra
CN103834409A (en) Passivating agent for mercury-polluted soil remediation
CN108323264B (en) A kind of Reclaimed Land ecology fertilizer application method
CN107413830A (en) A kind of agricultural land soil processing method for reducing Cd concentration of brown rice
CN110692460A (en) Method for planting energy sorghum in cadmium-polluted rice field
Ciesielczuk et al. Homemade slow-action fertilizers, as an economic solution for organic food production
CN109608282A (en) A kind of biomass carbon base organic fertilizer compost and its preparation method and application

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
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right

Effective date of registration: 20200720

Address after: 611130 No. 203, 204 and 205, No. 355 Kejin Road, Wenjiang District, Chengdu City, Sichuan Province

Co-patentee after: SICHUAN ZHONGNONG RUNZE BIOLOGICAL TECHNOLOGY Co.,Ltd.

Patentee after: Sichuan huadikang Ecological Agriculture Co.,Ltd.

Co-patentee after: Chengdu Metropolitan Modern Agricultural Industry Technology Research Institute Co.,Ltd.

Address before: Ya'an City, Sichuan Province, 625014 new Yucheng Kang Road No. 46

Patentee before: SICHUAN AGRICULTURAL University

TR01 Transfer of patent right
CP01 Change in the name or title of a patent holder

Address after: 611130 No. 203, 204 and 205, No. 355 Kejin Road, Wenjiang District, Chengdu City, Sichuan Province

Patentee after: Sichuan Huadikang Ecological Agriculture Technology Co.,Ltd.

Patentee after: SICHUAN ZHONGNONG RUNZE BIOLOGICAL TECHNOLOGY Co.,Ltd.

Patentee after: Chengdu Metropolitan Modern Agricultural Industry Technology Research Institute Co.,Ltd.

Address before: 611130 No. 203, 204 and 205, No. 355 Kejin Road, Wenjiang District, Chengdu City, Sichuan Province

Patentee before: Sichuan huadikang Ecological Agriculture Co.,Ltd.

Patentee before: SICHUAN ZHONGNONG RUNZE BIOLOGICAL TECHNOLOGY Co.,Ltd.

Patentee before: Chengdu Metropolitan Modern Agricultural Industry Technology Research Institute Co.,Ltd.

CP01 Change in the name or title of a patent holder