CN107827657A - A kind of red soil conditioner of wormcast compounding boron fertilizer - Google Patents
A kind of red soil conditioner of wormcast compounding boron fertilizer Download PDFInfo
- Publication number
- CN107827657A CN107827657A CN201711214831.9A CN201711214831A CN107827657A CN 107827657 A CN107827657 A CN 107827657A CN 201711214831 A CN201711214831 A CN 201711214831A CN 107827657 A CN107827657 A CN 107827657A
- Authority
- CN
- China
- Prior art keywords
- soil
- boron
- parts
- conditioner
- red soil
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 229910052796 boron Inorganic materials 0.000 title claims abstract description 118
- ZOXJGFHDIHLPTG-UHFFFAOYSA-N Boron Chemical compound [B] ZOXJGFHDIHLPTG-UHFFFAOYSA-N 0.000 title claims abstract description 116
- 239000003516 soil conditioner Substances 0.000 title claims abstract description 31
- 239000003337 fertilizer Substances 0.000 title abstract description 10
- 238000013329 compounding Methods 0.000 title abstract description 5
- 239000002689 soil Substances 0.000 claims abstract description 154
- 240000006794 Volvariella volvacea Species 0.000 claims abstract description 20
- 239000002893 slag Substances 0.000 claims abstract description 19
- 240000008042 Zea mays Species 0.000 claims abstract description 12
- 235000016383 Zea mays subsp huehuetenangensis Nutrition 0.000 claims abstract description 12
- 235000002017 Zea mays subsp mays Nutrition 0.000 claims abstract description 12
- 235000009973 maize Nutrition 0.000 claims abstract description 12
- 239000010902 straw Substances 0.000 claims abstract description 12
- 229910052902 vermiculite Inorganic materials 0.000 claims abstract description 12
- 239000010455 vermiculite Substances 0.000 claims abstract description 12
- 235000019354 vermiculite Nutrition 0.000 claims abstract description 12
- 210000003608 fece Anatomy 0.000 claims description 19
- 239000010871 livestock manure Substances 0.000 claims description 13
- 241000361919 Metaphire sieboldi Species 0.000 claims description 9
- 238000000034 method Methods 0.000 claims description 8
- 239000004327 boric acid Substances 0.000 claims description 7
- 230000001580 bacterial effect Effects 0.000 claims description 3
- WUUHFRRPHJEEKV-UHFFFAOYSA-N tripotassium borate Chemical compound [K+].[K+].[K+].[O-]B([O-])[O-] WUUHFRRPHJEEKV-UHFFFAOYSA-N 0.000 claims description 3
- 125000005619 boric acid group Chemical group 0.000 claims description 2
- 241000545744 Hirudinea Species 0.000 claims 1
- 239000004575 stone Substances 0.000 claims 1
- 241000196324 Embryophyta Species 0.000 abstract description 25
- 230000007812 deficiency Effects 0.000 abstract description 10
- 230000007613 environmental effect Effects 0.000 abstract description 2
- 230000036541 health Effects 0.000 abstract description 2
- 238000002360 preparation method Methods 0.000 abstract description 2
- 239000005416 organic matter Substances 0.000 description 28
- 239000002028 Biomass Substances 0.000 description 23
- 230000000813 microbial effect Effects 0.000 description 21
- 229910052799 carbon Inorganic materials 0.000 description 19
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 18
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 16
- 241000894006 Bacteria Species 0.000 description 13
- 244000005700 microbiome Species 0.000 description 13
- 235000015097 nutrients Nutrition 0.000 description 12
- 229910052757 nitrogen Inorganic materials 0.000 description 10
- KGBXLFKZBHKPEV-UHFFFAOYSA-N boric acid Chemical compound OB(O)O KGBXLFKZBHKPEV-UHFFFAOYSA-N 0.000 description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 8
- 230000000694 effects Effects 0.000 description 7
- 230000012010 growth Effects 0.000 description 6
- JVTAAEKCZFNVCJ-UHFFFAOYSA-N lactic acid Chemical compound CC(O)C(O)=O JVTAAEKCZFNVCJ-UHFFFAOYSA-N 0.000 description 6
- 244000061458 Solanum melongena Species 0.000 description 5
- 235000002597 Solanum melongena Nutrition 0.000 description 5
- 238000002474 experimental method Methods 0.000 description 5
- 239000000463 material Substances 0.000 description 5
- 229910052698 phosphorus Inorganic materials 0.000 description 5
- -1 boron ion Chemical class 0.000 description 4
- 238000005341 cation exchange Methods 0.000 description 4
- 230000008859 change Effects 0.000 description 4
- 238000006243 chemical reaction Methods 0.000 description 4
- 238000010586 diagram Methods 0.000 description 4
- 230000035558 fertility Effects 0.000 description 4
- 230000001965 increasing effect Effects 0.000 description 4
- 230000004060 metabolic process Effects 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- 235000001674 Agaricus brunnescens Nutrition 0.000 description 3
- 241000193830 Bacillus <bacterium> Species 0.000 description 3
- 229920002488 Hemicellulose Polymers 0.000 description 3
- 241000108664 Nitrobacteria Species 0.000 description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 3
- 241000235342 Saccharomycetes Species 0.000 description 3
- 238000010521 absorption reaction Methods 0.000 description 3
- 238000005273 aeration Methods 0.000 description 3
- 239000002585 base Substances 0.000 description 3
- 230000009286 beneficial effect Effects 0.000 description 3
- 238000009395 breeding Methods 0.000 description 3
- 230000001488 breeding effect Effects 0.000 description 3
- 239000001913 cellulose Substances 0.000 description 3
- 229920002678 cellulose Polymers 0.000 description 3
- 239000003795 chemical substances by application Substances 0.000 description 3
- 150000001875 compounds Chemical class 0.000 description 3
- 238000000354 decomposition reaction Methods 0.000 description 3
- 230000007423 decrease Effects 0.000 description 3
- 235000013399 edible fruits Nutrition 0.000 description 3
- 239000004310 lactic acid Substances 0.000 description 3
- 235000014655 lactic acid Nutrition 0.000 description 3
- 238000002386 leaching Methods 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 239000011574 phosphorus Substances 0.000 description 3
- 230000000243 photosynthetic effect Effects 0.000 description 3
- 230000008635 plant growth Effects 0.000 description 3
- 230000000630 rising effect Effects 0.000 description 3
- 238000005070 sampling Methods 0.000 description 3
- 238000001179 sorption measurement Methods 0.000 description 3
- 244000025254 Cannabis sativa Species 0.000 description 2
- 102000004190 Enzymes Human genes 0.000 description 2
- 108090000790 Enzymes Proteins 0.000 description 2
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 2
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 230000004913 activation Effects 0.000 description 2
- 239000012615 aggregate Substances 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- 230000015556 catabolic process Effects 0.000 description 2
- 150000001768 cations Chemical class 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 239000002361 compost Substances 0.000 description 2
- VFLDPWHFBUODDF-FCXRPNKRSA-N curcumin Chemical compound C1=C(O)C(OC)=CC(\C=C\C(=O)CC(=O)\C=C\C=2C=C(OC)C(O)=CC=2)=C1 VFLDPWHFBUODDF-FCXRPNKRSA-N 0.000 description 2
- 230000006378 damage Effects 0.000 description 2
- 238000006731 degradation reaction Methods 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 230000018109 developmental process Effects 0.000 description 2
- 238000009826 distribution Methods 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 230000002255 enzymatic effect Effects 0.000 description 2
- 239000011521 glass Substances 0.000 description 2
- 238000003306 harvesting Methods 0.000 description 2
- 229910001385 heavy metal Inorganic materials 0.000 description 2
- 239000003864 humus Substances 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 230000007774 longterm Effects 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 231100000252 nontoxic Toxicity 0.000 description 2
- 230000003000 nontoxic effect Effects 0.000 description 2
- 239000012071 phase Substances 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 229940072033 potash Drugs 0.000 description 2
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Substances [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 description 2
- 235000015320 potassium carbonate Nutrition 0.000 description 2
- 230000005855 radiation Effects 0.000 description 2
- 239000004016 soil organic matter Substances 0.000 description 2
- 208000024891 symptom Diseases 0.000 description 2
- 238000012360 testing method Methods 0.000 description 2
- 230000009466 transformation Effects 0.000 description 2
- 230000032258 transport Effects 0.000 description 2
- 241000186046 Actinomyces Species 0.000 description 1
- 229930192334 Auxin Natural products 0.000 description 1
- BTBUEUYNUDRHOZ-UHFFFAOYSA-N Borate Chemical compound [O-]B([O-])[O-] BTBUEUYNUDRHOZ-UHFFFAOYSA-N 0.000 description 1
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 1
- 102000016938 Catalase Human genes 0.000 description 1
- 108010053835 Catalase Proteins 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 241000233866 Fungi Species 0.000 description 1
- 241000726221 Gemma Species 0.000 description 1
- 241000219098 Parthenocissus Species 0.000 description 1
- 108091005804 Peptidases Proteins 0.000 description 1
- 235000008331 Pinus X rigitaeda Nutrition 0.000 description 1
- 235000011613 Pinus brutia Nutrition 0.000 description 1
- 241000018646 Pinus brutia Species 0.000 description 1
- 239000004365 Protease Substances 0.000 description 1
- 102100037486 Reverse transcriptase/ribonuclease H Human genes 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- KPSZQYZCNSCYGG-UHFFFAOYSA-N [B].[B] Chemical compound [B].[B] KPSZQYZCNSCYGG-UHFFFAOYSA-N 0.000 description 1
- CKUAXEQHGKSLHN-UHFFFAOYSA-N [C].[N] Chemical compound [C].[N] CKUAXEQHGKSLHN-UHFFFAOYSA-N 0.000 description 1
- 238000003916 acid precipitation Methods 0.000 description 1
- 239000011149 active material Substances 0.000 description 1
- 230000006978 adaptation Effects 0.000 description 1
- 238000012271 agricultural production Methods 0.000 description 1
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 1
- 150000001413 amino acids Chemical class 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 238000003556 assay Methods 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000002363 auxin Substances 0.000 description 1
- 230000006399 behavior Effects 0.000 description 1
- 230000003851 biochemical process Effects 0.000 description 1
- 238000004173 biogeochemical cycle Methods 0.000 description 1
- 230000031018 biological processes and functions Effects 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 229910001424 calcium ion Inorganic materials 0.000 description 1
- 235000013339 cereals Nutrition 0.000 description 1
- 238000004737 colorimetric analysis Methods 0.000 description 1
- 239000011365 complex material Substances 0.000 description 1
- 239000002131 composite material Substances 0.000 description 1
- 230000003750 conditioning effect Effects 0.000 description 1
- 229940109262 curcumin Drugs 0.000 description 1
- 235000012754 curcumin Nutrition 0.000 description 1
- 239000004148 curcumin Substances 0.000 description 1
- 238000005520 cutting process Methods 0.000 description 1
- 230000001351 cycling effect Effects 0.000 description 1
- 230000001086 cytosolic effect Effects 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 239000012954 diazonium Substances 0.000 description 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-O diazynium Chemical compound [NH+]#N IJGRMHOSHXDMSA-UHFFFAOYSA-O 0.000 description 1
- VFLDPWHFBUODDF-UHFFFAOYSA-N diferuloylmethane Natural products C1=C(O)C(OC)=CC(C=CC(=O)CC(=O)C=CC=2C=C(OC)C(O)=CC=2)=C1 VFLDPWHFBUODDF-UHFFFAOYSA-N 0.000 description 1
- 230000004069 differentiation Effects 0.000 description 1
- 230000001079 digestive effect Effects 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000002708 enhancing effect Effects 0.000 description 1
- 210000003238 esophagus Anatomy 0.000 description 1
- 238000000855 fermentation Methods 0.000 description 1
- 230000004151 fermentation Effects 0.000 description 1
- 230000004720 fertilization Effects 0.000 description 1
- 239000012847 fine chemical Substances 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- SEOVTRFCIGRIMH-UHFFFAOYSA-N indole-3-acetic acid Chemical compound C1=CC=C2C(CC(=O)O)=CNC2=C1 SEOVTRFCIGRIMH-UHFFFAOYSA-N 0.000 description 1
- 230000008595 infiltration Effects 0.000 description 1
- 238000001764 infiltration Methods 0.000 description 1
- 238000011081 inoculation Methods 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 238000003780 insertion Methods 0.000 description 1
- 230000037431 insertion Effects 0.000 description 1
- 229910001710 laterite Inorganic materials 0.000 description 1
- 239000011504 laterite Substances 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 230000003050 macronutrient Effects 0.000 description 1
- 235000021073 macronutrients Nutrition 0.000 description 1
- 239000002905 metal composite material Substances 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 235000010755 mineral Nutrition 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 230000000050 nutritive effect Effects 0.000 description 1
- 210000000056 organ Anatomy 0.000 description 1
- 239000003895 organic fertilizer Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 230000035699 permeability Effects 0.000 description 1
- 150000004965 peroxy acids Chemical class 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 230000035790 physiological processes and functions Effects 0.000 description 1
- 230000007198 pollen germination Effects 0.000 description 1
- 230000010152 pollination Effects 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 229910052939 potassium sulfate Inorganic materials 0.000 description 1
- 238000003825 pressing Methods 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000005067 remediation Methods 0.000 description 1
- 230000001850 reproductive effect Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 230000000241 respiratory effect Effects 0.000 description 1
- 230000002786 root growth Effects 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 230000003248 secreting effect Effects 0.000 description 1
- 150000003384 small molecules Chemical class 0.000 description 1
- 239000002681 soil colloid Substances 0.000 description 1
- 239000002881 soil fertilizer Substances 0.000 description 1
- 239000007790 solid phase Substances 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 230000001629 suppression Effects 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 238000010998 test method Methods 0.000 description 1
- 230000008719 thickening Effects 0.000 description 1
- 239000011573 trace mineral Substances 0.000 description 1
- 235000013619 trace mineral Nutrition 0.000 description 1
- 230000007306 turnover Effects 0.000 description 1
- 235000013343 vitamin Nutrition 0.000 description 1
- 239000011782 vitamin Substances 0.000 description 1
- 229940088594 vitamin Drugs 0.000 description 1
- 229930003231 vitamin Natural products 0.000 description 1
- 150000003722 vitamin derivatives Chemical class 0.000 description 1
- 238000010792 warming Methods 0.000 description 1
- 238000005303 weighing Methods 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D9/00—Other inorganic fertilisers
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05G—MIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
- C05G3/00—Mixtures of one or more fertilisers with additives not having a specially fertilising activity
- C05G3/80—Soil conditioners
Landscapes
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Organic Chemistry (AREA)
- Soil Sciences (AREA)
- Pest Control & Pesticides (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Soil Conditioners And Soil-Stabilizing Materials (AREA)
- Fertilizers (AREA)
Abstract
The invention discloses a kind of red soil conditioner of wormcast compounding boron fertilizer.In parts by mass, its host component is：40~60 parts of wormcast, 25~35 parts of straw mushroom slag, 8~12 parts of vermiculite, 8~12 parts of maize straw, often added in kg host components containing the boron source that boron element is 1.50~3.00g.The conditioner can effectively improve soil 10cm depth temperature, increase soil microbe quantity, improve the content and the Boron contents of plant and the yield of crops of Effective Boron of Soil, reparation suitable for Degraded Red Soil is nursed one's health, be particularly suitable for use in boron deficiency red soil, and the preparation method of the conditioner is simple and easy, cost is cheap, safety and environmental protection.
Description
Technical field
The present invention relates to soil remediation field, more particularly to a kind of red soil conditioner of wormcast compounding boron fertilizer.
Background technology
According to statistics, the Red Soils in Southern China area gross area reaches 217.96 ten thousand square kilometres, including 15 provinces (area), accounts for complete
The 1/5 of state's land area；Population 4.8 hundred million, account for the whole nation 40%；Plough 28,000,000 hectares, account for the 30% of the whole nation.In the whole nation 1/3
The agriculture value of national half, the grain of half and the population for having born nearly half are provided on arable land.But due to for a long time to soil
The irrational utilization of ground resource, for whole distract ecology with environment by heavy damage, soil degradation problem is extremely serious, including
Several aspects：
1st, the soil moisture declines：
The soil moisture is important soil physical properties, not only influences the chemistry and biology mistake of the materials such as SOIL CARBON AND NITROGEN
Journey, soil quality is had an effect on, so as to influence growing, breed and being distributed for geobiont, itself and agricultural production and ecological ring
Border is closely related.
All biological processes and various chemical reactions in soil, such as：The activity of microorganism, the decomposition of organic matter, ore deposit
The differentiation of material and the conversion of nutrient etc. are all with the release and absorption of heat.Generally, in certain soil moisture model
In enclosing, transporting to organic matter of the rise of the soil moisture, cytoplasmic flowing, the absorption of nutrient, the transport of nutriment, soil
Respiratory intensity, soil microbe quantity and enzymatic activity etc. have facilitation.Due to long-term " the light phosphorus potash fertilizer of diazonium ", " weight chemical fertilizer is light
Organic fertilizer ", or even the cultivation pattern of formula is robbed, soil moisture decline is result in, so as to influence the implementation of soil environment, also therefore
Influence root system of plant growth, in fact, the content of organic matter number and micro organism quantity number, largely determine
The height of the soil moisture.Therefore, the decline of the soil moisture, the basis of stable structure red soil environment can be influenceed.
2nd, microbial biomass declines：
Soil microbial biomass number and its change be one of important evidence of soil fertility height.Soil microbial biomass is
The soil organism and the power of soil nutrient (C, N, P, S etc.) conversion and circulation, and participate in the decomposition of organic matter, the shape of humus
Into regulation and control each biochemical process such as soil energy and Nutrient Cycling, is important nutrient warehouse, to Nutrient Transformation, organic matter
Metabolism and the degraded of pollutant have a very important role.But soil microbial biomass by soil types, human activity, apply
The environment of fertile mode, Land-Use, different temperatures and humidity etc. has a great influence, and warming with global climate, ring
Border pollution increasingly sharpens, and various pollutants caused by industrial activity enter soil, acid, nitrogen with unprecedented scope and speed
The influence settled to soil microbial biomass is increasing.
Research shows：Under Simulated Acid Rain, in the red soil and yellow-red soil of different composite level of pollution microbial biomass carbon by
It is further exacerbated by different degrees of suppression, and with the increase of heavy metal amount, heavy-metal composite pollution causes micro- in soil
Biomass C and enzymatic activity are substantially reduced, and serious harm is caused to microbial biomass.It is another it is reported that：In the gloomy of long-term nitrogen
In woods soil, in pine forest and broad-leaf forest the increase of nitrogen cause the reduction of microbial biomass C.And microbial biomass is soil pair
One of most sensitive index of environment, therefore, soil microbial biomass decline are the important behaviours of soil degradation.
3rd, micro- particularly boron deficiency is serious：
Guangdong Province's boron (B) average content is 41.38mg/kg, less than Chinese soil average content 64mg/kg and Chinese soil
Background value 44.6mg/kg, and it is higher than world soil intermediate value 20mg/kg, but content distribution is uneven, the Boron contents of most of samples
All very low, the laterite Boron contents only developed on aleuritic texture sandstone are very high.
Being shown according to soil survey information, 68% is middle-and-low-yielding fields in current farmland, and arable land generally lacks organic matter and nitrogen,
Whole nonirrigated farmlands and 60% paddy field lack phosphorus, 80% boron deficiency in arable land.Boron in soil can simply be divided into full dose boron and effective boron, have
Imitating boron includes the water-soluble boron in the soil liquid and the boron of organic matter absorption, and the existence form of both boron can be converted mutually,
But limited by certain condition, mainly effective boron that plant can absorb and utilize, and effective boron in red soil accounts for full boron and contained
Amount is less than 1%.The factor for influenceing Effective Boron of Soil has a lot, and usually, the water miscible Boron contents of soil of peracid are higher but hold
It is easy to run off, it is soluble because it mainly exists in the form of boric acid, it is not easy by adsorption by soil；The soil of alkali is crossed, such as：Using big
Amount lime can reduce the utilizability of boron to handle soil, and excessive calcium ion can inactivate boron ion；Clayey soil, boron are not easy
By leaching loss, but boron is readily absorbed by fixing, therefore relatively low using boron；And sand loam soil, generally infiltration is good and rainfall compared with
Greatly, the boron of soil application easily leaching loss；Under conditions of rainy in south, the physical arrangement boron of its powdery is easy to rainwater stream
Lose；And the soil validity boron more than organic matter is more.So the shortage of trace element particularly boron element, is that soil nutrient is not complete
One of the important embodiment in face.
The content of the invention
For above-mentioned soil issues, it is an object of the invention to provide a kind of red soil conditioner of wormcast compounding boron fertilizer.
The conditioner can effectively improve soil 10cm depths temperature, increase soil microbe quantity, improve Effective Boron of Soil content and plant
Boron content and the yield of crops.
The technical solution used in the present invention is：
A kind of red soil conditioner, in parts by mass, its host component is：40~60 parts of wormcast, 25~35 parts of straw mushroom slag,
8~12 parts of vermiculite, 8~12 parts of maize straw, often added in kg host components containing the boron source that boron element is 1.50~3.00g.
Preferably, a kind of red soil conditioner, in parts by mass, its host component is：45~55 parts of wormcast, grass
28~33 parts of mushroom slag, 9~11 parts of vermiculite, 9~11 parts of maize straw, per kg host components in addition containing boron element be 2.00~
2.50g boron source.
As further preferred scheme, a kind of red soil conditioner, in parts by mass, its host component is：50 parts of wormcast,
30 parts of straw mushroom slag, 10 parts of vermiculite, 10 parts of maize straw, often added in kg host components containing the boron source that boron element is 2.33g.
Preferably, boron source is selected from least one of boric acid, Boratex, potassium borate.
Preferably, appropriate bio-bacterial manure leavening is also added with above-mentioned conditioner.
A kind of red soil method of adjustment, it is included in red soil and applies above-mentioned red soil conditioner.
Preferably, the dosage of red soil conditioner is：800~1200kg/ mus.
Preferably, the dosage of red soil conditioner is：1000kg/ mus.
The beneficial effects of the invention are as follows：
1) conditioner prepared by the present invention can effectively improve soil 10cm depth temperature, increase soil microbe quantity, improve
The yield of the boron content and crops of Effective Boron of Soil content and plant, using the soil microbe quantity after conditioner, effectively
Boron contents, plant boron content, crop yield are 1.47 times, 1.89 times, 1.17 times and 2.90 times of control group respectively.
2) the conditioner preparation method is simple and easy, and cost is cheap, and using organic matter as base stock, non-toxic and safe ring
Protect, secondary pollution will not be caused to environment.
3) conditioner is applied to the reparation conditioning of Degraded Red Soil, and be particularly suitable for use in boron deficiency red soil.
Brief description of the drawings
Fig. 1 is the curve map that conditioner of the present invention influences on the 10cm depths soil moisture；
Fig. 2 is influence block diagram of the conditioner of the present invention to microbial biomass C content；
Fig. 3 is influence block diagram of the conditioner of the present invention to Effective Boron of Soil content；
Fig. 4 is influence block diagram of the conditioner of the present invention to boron content in plant body；
Fig. 5 is influence block diagram of the conditioner of the present invention to plant yield.
Embodiment
A kind of red soil conditioner, in parts by mass, its host component is：40~60 parts of wormcast, 25~35 parts of straw mushroom slag,
8~12 parts of vermiculite, 8~12 parts of maize straw, often added in kg host components containing the boron source that boron element is 1.50~3.00g.
Preferably, a kind of red soil conditioner, in parts by mass, its host component is：45~55 parts of wormcast, grass
28~33 parts of mushroom slag, 9~11 parts of vermiculite, 9~11 parts of maize straw, per kg host components in addition containing boron element be 2.00~
2.50g boron source.
As further preferred scheme, a kind of red soil conditioner, in parts by mass, its host component is：50 parts of wormcast,
30 parts of straw mushroom slag, 10 parts of vermiculite, 10 parts of maize straw, often added in kg host components containing the boron source that boron element is 2.33g.
Preferably, boron source is selected from least one of boric acid, Boratex, potassium borate.
Preferably, appropriate bio-bacterial manure leavening is also added with above-mentioned conditioner.
A kind of red soil method of adjustment, it is included in red soil and applies above-mentioned red soil conditioner.
Preferably, the dosage of red soil conditioner is：800~1200kg/ mus.
Preferably, the dosage of red soil conditioner is：1000kg/ mus.
Wormcast is that earthworm eats after cow dung by the postdigestive excreta of earthworm enteron aisle, rich in nutrients such as N, P, K and
All kinds of active materials, organic matter is abundant and particle is tiny, and aggregate structure is good, and surface area is big, contains substantial amounts of microorganism and reunion
Body, water-stable aggregate content is high, has stronger resiliency, aeration is good, and pore structure is good, and pH value is 7.0-7.2 (Guangdong
Save beneficially agricultural science and technology Co., Ltd to provide, organic carbon content 288g/kg, 7.66 hundred million/g of living bacteria count).
Vermiculite is a kind of natural, inorganic, nontoxic mineral matter, has cation exchange and adsorptivity, pH value 7.0-
8.0 (Guangzhou Fang Cun flowers and plants market is bought, and it is 32.1 (cmol (+)/kg) to measure its CEC, and CEC is cation exchange capacity (CEC)).
Straw mushroom slag is then the straw mushroom slag formed after producing straw mushroom as raw material using Chinese medicine slag, and main component is organic carbon, is micro-
The place of biological concentration (Guangzhou town dragon Yongming mushroom field provides, organic carbon 620g/kg).
Effective viable bacteria is rich in bio-bacterial manure leavening, quantity is 51,600,000,000/g (Zhengzhou agriculture Citroen zx bio tech ltd
Production).
Embodiment is enumerated further below to describe the present invention in detail.It will similarly be understood that following examples are served only for this
Invention is further described, it is impossible to is interpreted as limiting the scope of the invention, those skilled in the art are according to the present invention
Some nonessential modifications and adaptations that the principle of elaboration is made belong to protection scope of the present invention.Following specific works of example
Skill parameter etc. is also only an example in OK range, i.e. those skilled in the art can do suitable model by this paper explanation
Interior selection is enclosed, and does not really want to be defined in the specific data of hereafter example.
The activation of bio-bacterial manure leavening：
1) add and 5kg water and boiled in 1kg brown sugar, after add 10kg water；
2) 100g bio-bacterial manure leavening is added in above-mentioned brown sugar water and stirred, 4 days as biologies are placed in sealing
Bacterial manure zymotic fluid；Bio-bacterial manure leavening after activation is diluted with water 10 times, you can for spraying.
Testing program：
This experiment selection Guangzhou Guangdong Huangpu District Kowloon Zhen Yang Tian Cun field experiment, (north latitude 23o19'15 ", east longitude
113o34'56”).Practice ground is divided into 15 fritters, per fritter 8m × 7.5m, i.e. every piece of area is 6m2。
Experiment is arranged to 3 groups altogether；
1st, QY-T1, using conditioner 500kg/ mus (i.e. 750g/m2)；
2nd, QY-T3, using conditioner 1000kg/ mus (i.e. 1500g/m2)；
3rd, QY-CK, conditioner (control group) is not applied.
3 repetitions of every group of setting are tested, and the arrangement of completely random district's groups, each plot area is 6m2。
Wherein, this experiment conditioner is：50 parts of wormcast, 30 parts of straw mushroom slag, 10 parts of vermiculite, 10 parts of maize straw, biology
Bacterial manure leavening is appropriate, boric acid 13.3g/kg.
By above-mentioned different conditioner dosages, uniformly apply to after smooth experimental field in, after with creeper turn over whole mix thoroughly to about
20cm soil thickness.
This conditioner covers the film of black after being added as base manure, from continuous 17 days the 13-29 days measure soil after overlay film
Earth temperature, and the 20th day after overlay film samples, sampling depth 0-20cm, the method for sampling is using 5 point sampling methods and is well mixed, and surveys
Determine microbial biomass carbon, effective boron；And in the boron of the 76th day measure eggplant, record yield.
(1) method of testing：
The soil moisture：Determine within continuous 17 days the 13-29 days after transplanting, using angle-style glass-stem thermometer (Hebei China
Rich weighing apparatus instrument and meter factory production), insertion subterranean depth is respectively 5cm, 10cm, 15cm, respectively at 9：00、14：00 reading；
Microbial biomass C：Using imitative stifling-potassium sulfate extraction-potassium bichromate Measuring The Volume Density measure；
Effective Boron of Soil：- ginger-colored colorimetric method NY/T 1121.8-2006 measure is extracted using boiling water；
Boron content in plant body：Using Curcumin Colorimetric.
All results are in terms of the average value in 3 plot.
(2) instrument and reagent：
Ultraviolet-uisible spectrophotometer：The general analysis TU-1810 in Beijing；
Assay balance：Double outstanding board centesimal balance and the Precisa balances very much in the U.S.；
Boric acid (H3BO3)：Tianjin is that north joins the wholesale Co., Ltd of fine chemicals, GR；
Remaining agents useful for same derives from Guangzhou Chemical Reagent Factory, and glass apparatus derives from northern glass.
The soil moisture：
It will be seen from figure 1 that overlay film the 13-27 days, daily 14：The 10cm deep soil moistures are measured when 00：QY-CK soil
For earth temperature (soil temperature) in addition to the 13rd day and QY-T3 maintains an equal level, remaining below applies the QY-T1 and QY-T3 of conditioner daily,
Such as：23rd day, QY-CK soil temperature was 30.6 DEG C, and QY-T1, QY-T3 soil temperature are respectively 32.5 DEG C, 33.6 DEG C, are compared respectively
1.90 DEG C, 3.00 DEG C have been higher by according to group；25th day, QY-CK soil temperatures were 30.0 DEG C, and QY-T1, QY-T3 soil temperature are respectively
32.2 DEG C, 32.0 DEG C, 2.20 DEG C, 2.00 DEG C have been higher by it than control group respectively；This trend is continued until whole soil test
Phase (the 13-27 days i.e. after overlay film), this is primarily due to the change of the soil moisture not only by solar radiation, atmospheric air circulation, drop
The influence of the factors such as water Land use systems, is also significantly influenceed by soil organic matter and edaphon, i.e.,：Using energy after conditioner
Effectively improve the soil moisture.
The organic carbon content of wormcast is 288g/kg in soil conditioner, and the organic carbon content of straw mushroom slag is 620g/kg,
Plus maize straw it is decomposed after very big composition be all organic carbon；In addition, wormcast is cow dung by being squeezed after earthworm esophagus through enteron aisle
The graininess excreta for pressing and secreting a variety of digestive ferments and being formed, living bacteria count reach 7.66 hundred million/g, and straw mushroom slag is straw mushroom receipts
The flora compound based on cellulose and hemicellulose left after cutting, and contain substantial amounts of gemma in bio-bacterial manure leavening
A variety of organic floras such as bacillus, nitrobacteria, photosynthetic bacteria, lactic acid bacteria, saccharomycete, therefore, when conditioner is applied in soil
When can significantly improve soil organic carbon and the quantity of edaphon.Edaphon is decomposing organic matter, can produce big
The heat of amount, and caused heat is directly proportional to the content of organic matter and the quantity of microorganism, i.e.,：The content of organic matter is higher, micro-
Biomass is bigger, and soil moisture rising is also bigger, otherwise just smaller, is similar to the fermentation heating principle of compost, although, conditioner
The quantity of organic matter and microorganism in being manured into soil, much less is wanted than the amount in compost, but ratio is still influenceed on the soil moisture
It is larger.
In addition, away from topsoil 10cm depths, influenceed by solar radiation, air, rainfall etc. fewer than topsoil
Much, so air, water flow are slow, metastable space is formed, and the microorganism in soil is saprophytic aerobic mostly
Bacterium, required oxygen is not required to too many but can not had, and this condition is fully met at 10cm depth soil, so 10cm or so
Depths should be the ideal place that edaphon decomposes organic matter.
Microbial biomass C content：
Edaphon plays important in the biogeochemical cycle process such as Zinc fractions, metabolism and Nutrient Transformation
Effect.Although Soil Microbial Biomass Carbon only accounts for the 1%-5% of soil organic matter, but the important driving of the soil organism and nutrient
Person, while be also the important indicator of overall merit soil carbon dynamics, soil quality and soil fertility, or soil biochemistry
The important component of matter, soil microbial biomass number and its change be soil fertility height change important evidence it
One.Usually, microbial biomass carbon is index very sensitive in soil, is influenceed substantially by soil regime.
Figure it is seen that with the increase of conditioner amount of application, microbial biomass carbon is in rising trend, is adjusted using soil
The microbial biomass carbon content for managing the QY-T1 and QY-T3 of agent is respectively 252mg/kg, 286mg/kg, is that QY-CK microbial biomass carbons contain
1.30 times and 1.47 times of (194mg/kg) are measured, this explanation, which applies conditioner, can effectively improve the content of microbial biomass C.
After soil conditioner based on wormcast is manured into soil, due to that containing abundant organic matter, can not only improve
Soil physical and chemical property can also provide good environmental condition for the growth of microorganism, i.e.,：Organic matter is that edaphon growth carries
Abundant carbon source and nitrogen source have been supplied, greatly have stimulated the activity of microorganism, has promoted the breeding of microorganism, edaphon profit
While quickly breeding with nutrients such as the carbon of organic matter, nitrogen, humus is formd, macro-nutrients are decomposed and are mineralized into plant
The small-molecule substance that thing can be absorbed directly, while substantial amounts of organized enzyme is also secreted, such as catalase, urase, phosphoric acid
Enzyme, protease etc., further promote the conversion of soil nutritive element, in fact, 80%-90% soil total metabolism is by micro-
The effect of biology is completed.
Furthermore the wormcast of this soil conditioner reaches 7.66 hundred million/g containing living bacteria count, bio-bacterial manure leavening is effective
Viable count reaches 51,600,000,000/g, has containing substantial amounts of bacillus, nitrobacteria, photosynthetic bacteria, lactic acid bacteria, saccharomycete etc. are a variety of
Machine flora, straw mushroom slag are the flora compounds based on cellulose and hemicellulose left after straw mushroom is gathered in.
Therefore, after this soil conditioner is manured into soil, on the one hand equivalent to the multiple beneficial microorganism to soil inoculation, separately
The organic matter of one side high content promotes the breeding of microorganism, thus the quantity of Soil Microorganism is significantly increased, so as to
Improve edaphon carbon content.
Effective Boron of Soil content：
Shown according to soil survey information, there is 80% soil lacking boron in China, and especially in acid soil, boron is mainly with boric acid
Form exist, it is soluble, be not easy by adsorption by soil, thus elute more serious.Boron leaching will lack Effective Boron of Soil, lead
Plant boron deficiency is caused, so as to seriously affect the growth of plant and production.When Effective Boron of Soil lacks, growth and development of plants is not
Good, setting percentage is remarkably decreased.In fact, boron canopy in soil is relatively broad in distributed in nature, all contain in most of soils
Boron, boron is in king's earth except a small amount of boric acid molecule (H3BO3) and ion (HBO4-) soil liquid China and foreign countries be present, it is most of with nothing
Machine or organic form are present in solid phase of soil, and the boron in soil can divide into water-soluble boron, acid-soluble boron and slightly solubility boron.
The full Boron contents of soil should not typically be used for judging that soil supplies boron ability to plant, but with the content of effective boron
Boron ability is supplied to evaluate soil.The content of Available Boron In Soils is not only relevant with soil parent material, also directly by soil acidity or alkalinity,
The influence of cropping system, cultivation management, weather and ecological condition.The trend of Effective Boron of Soil content distribution and Soil total boron amount phase
Together, different types of Effective Boron of Soil content difference is larger.
From figure 3, it can be seen that with the increase of conditioner addition, effective boron is in rising trend, using the QY- of conditioner
T1 and QY-T3 effective boron content be respectively 0.24mg/kg and 0.36mg/kg be 1.26 times of QY-CK (0.19mg/kg) and
1.89 again.This explanation, which applies conditioner, can increase the content of Effective Boron of Soil.
For this soil conditioner in addition to directly adding the content of boric acid increase boron, the increase of organic matter also play important work
With：It is generally acknowledged that pH value is in 5-7, the content highest of effective boron and crosses alkali and can all influence the content of effective boron peracid, and this examination
The pH value of soil can be properly increased by testing the conditioner enriched in the soil of acidity using organic matter, so as to increase in soil effectively
The content of boron；On the other hand, effective boron content is also higher when soil with organic matter content is more because boron and organic matter combine or
The amount fixed by organic matter is also higher, can be discharged after organic matter decomposition and be made for thing and absorb, effective boron and organic
Matter content is proportionate, therefore the content of Available Boron In Soils can be significantly improved after administration conditioner, and with the increasing of amount of application
Add and increase.
The content of plant boron：
One of nutrient necessary to boron is plant, boron element important physiological function be to sugar transport, metabolism, synthesis with
Transhipment plays an important role；The supply of each organ organic substance of plant can be improved simultaneously, promote Fruit, dry increases；
Boron can also promote root growth, promote the elongation of pollen germination and pollen tube, be advantageous to Pollination Fertilization.
Following symptom occurs in boron deficiency plant：Shoot tip meristem growth is suppressed, is withered when serious until dead；Old leaf blade
Thickening to become fragile, deformity, branch internode is short, suberification phenomenon occurs；Growing for root is obvious impacted, root is short and thick have concurrently it is brown
Color；Reproductive development is obstructed, and setting percentage is low, and fruit is small, and deformity, boron deficiency causes seed and the fruit underproduction, can had no harvest when serious.
And nitrogen, phosphorus, potash fertilizer are applied in boron deficiency, boron deficiency symptom can be aggravated on the contrary.
From fig. 4, it can be seen that the boron content in eggplant body increases with the increase of conditioner amount of application, nursed one's health applying
The boron content of the eggplant grown in the QY-T1 and QY-T3 of agent is 1.12 times and 1.17 times of QY-CK (12.41mg/kg) respectively,
Therefore boron content in plant can be significantly improved using boracic conditioner.Because boron is to be inhaled in the form of borate by plant
Receive, the boron in plant is most of to be existed in the form of insoluble, and soluble part is seldom, so boron recycles to newborn position
It is few, thus plant need to absorb boron for needed for itself during whole grow from the external world.Therefore, this soil conditioner contains
The boron fertilizer of higher concentration, it is the conditioner of preferable red soil boron deficiency soil.
Crop yield：
From fig. 5, it can be seen that 6m2Experimental field exemplified by cultivating eggplant, it is not using the QY-CK of conditioner eggplant yield
5.535kg, and the yield for applying the QY-T1 and QY-T3 of conditioner is respectively 7.15kg and 16.05kg, is 1.29 times of QY-CK
With 2.90 times, it follows that the yield of crop can be effectively improved using conditioner, and increase with the increase of conditioner amount of application
Add.
Wormcast in soil conditioner is that earthworm has eaten excreta of the cow dung after earthworm, and the content of organic matter is enriched
(288mg/kg), while there is good crumb structure, good permeability, aeration and drainage and high water-holding capacity, and pH
It is worth for neutrality, rich in bacterium, actinomyces and fungi, these microorganisms not only make complex material mineralising have for what plant was easy to absorb
Material is imitated, also synthesizes a series of materials for having bioactivity, such as：Sugar, amino acid, vitamin and auxin etc., every gram
Wormcast contains the beneficial microbe colony of more than 7.66 hundred million, and along with weakly alkaline straw mushroom slag, the content of organic matter reaches
620mg/kg；Bio-bacterial manure leavening living bacteria count reaches 51,600,000,000/g, contains substantial amounts of bacillus, nitrobacteria, photosynthetic
A variety of organic floras such as bacterium, lactic acid bacteria, saccharomycete, straw mushroom slag be leave after straw mushroom harvesting using cellulose and hemicellulose as
Main flora compound；And vermiculite, there is larger adsorptivity and ion exchangeable, its cation exchange capacity (CEC) reaches 32.1mg/
Kg, Cation Exchange Capacity in Soils (CEC) refer to that soil colloid can adsorb the total amount of various cations, and it directly reflects soil
Fertilizer conservation, the size of nutrient-supply capacity and buffer capacity, the increase of soil CEC contents, show the adsorption capacity to cation of soil
Enhancing, and then improve the fertilizer-preserving ability of soil.
Thus, compared using conditioner with the soil for not applying conditioner：With more preferable aeration, water-retaining property, getting fat
Property, higher soil fertility while edaphon content also raises, carbon-nitrogen ratio is more suitable for root system of plant and absorbed, and adds
Convenient acid-base value.Good soil environment is provided for plant growth, in addition, this experiment is no to apply top dressing, so
Fertilizer efficiency wretched insufficiency in the later stage QY-CK of plant strain growth, leads to not meet needed for plant strain growth, so using conditioner
QY-T1 and QY-T3 is more much higher than QY-CK yield.
Claims (8)
1. a kind of red soil conditioner, in parts by mass, its host component is：40~60 parts of wormcast, 25~35 parts of straw mushroom slag, leech
8~12 parts of stone, 8~12 parts of maize straw, often added in kg host components containing the boron source that boron element is 1.50~3.00g.
A kind of 2. red soil conditioner according to claim 1, it is characterised in that：In parts by mass, its host component is：Earthworm
45~55 parts of earthworm excrement, 28~33 parts of straw mushroom slag, 9~11 parts of vermiculite, 9~11 parts of maize straw, often add and contain in kg host components
Boron element is 2.00~2.50g boron source.
A kind of 3. red soil conditioner according to claim 1, it is characterised in that：In parts by mass, its host component is：Earthworm
50 parts of earthworm excrement, 30 parts of straw mushroom slag, 10 parts of vermiculite, 10 parts of maize straw, it is 2.33g's often to be added in kg host components containing boron element
Boron source.
A kind of 4. red soil conditioner according to claim 1, it is characterised in that：Boron source is selected from boric acid, Boratex, potassium borate
At least one of.
A kind of 5. red soil conditioner according to any one of Claims 1 to 4, it is characterised in that：Also added with appropriate biology
Bacterial manure leavening.
A kind of 6. red soil method of adjustment, it is characterised in that：It is included in red soil using red described in any one of Claims 1 to 5
Earth conditioner.
A kind of 7. red soil method of adjustment according to claim 5, it is characterised in that：The dosage of red soil conditioner is：800~
1200kg/ mus.
A kind of 8. red soil method of adjustment according to claim 7, it is characterised in that：The dosage of red soil conditioner is：
1000kg/ mus.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711214831.9A CN107827657A (en) | 2017-11-28 | 2017-11-28 | A kind of red soil conditioner of wormcast compounding boron fertilizer |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711214831.9A CN107827657A (en) | 2017-11-28 | 2017-11-28 | A kind of red soil conditioner of wormcast compounding boron fertilizer |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN107827657A true CN107827657A (en) | 2018-03-23 |
Family
ID=61646235
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201711214831.9A Pending CN107827657A (en) | 2017-11-28 | 2017-11-28 | A kind of red soil conditioner of wormcast compounding boron fertilizer |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN107827657A (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110698286A (en) * | 2019-10-23 | 2020-01-17 | 中国科学院南京土壤研究所 | Acidic soil conditioner and application thereof |
| CN112646586A (en) * | 2020-12-11 | 2021-04-13 | 广东省科学院生态环境与土壤研究所 | Method for enhancing stability of organic carbon in soil |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106544037A (en) * | 2016-10-21 | 2017-03-29 | 吴迪 | A kind of preparation method of biological soil conditioner |
-
2017
- 2017-11-28 CN CN201711214831.9A patent/CN107827657A/en active Pending
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106544037A (en) * | 2016-10-21 | 2017-03-29 | 吴迪 | A kind of preparation method of biological soil conditioner |
Non-Patent Citations (3)
| Title |
|---|
| 何电源等: "华南红壤中硼钼含量及硼钼肥对豆科作物的肥效", 《土壤》 * |
| 陈小锦: "基于蚯蚓消解牛粪后的蚯蚓粪改良红壤的效果研究", 《万方学位论文》 * |
| 龚建军: "《农业化学应用》", 30 April 2015, 西北工业大学出版社 * |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110698286A (en) * | 2019-10-23 | 2020-01-17 | 中国科学院南京土壤研究所 | Acidic soil conditioner and application thereof |
| CN112646586A (en) * | 2020-12-11 | 2021-04-13 | 广东省科学院生态环境与土壤研究所 | Method for enhancing stability of organic carbon in soil |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Rodrigues et al. | Azotobacter-enriched organic manures to increase nitrogen fixation and crop productivity | |
| CN105838644B (en) | Complex micro organism fungicide and bacterial manure and preparation method thereof and the application in reparation salt affected soil | |
| Mazid et al. | Future of bio-fertilizers in Indian agriculture: an overview | |
| Zancan et al. | Soil algae composition under different agro-ecosystems in North-Eastern Italy | |
| Jian-She et al. | Emissions of N2O and NH3, and nitrogen leaching from direct seeded rice under different tillage practices in central China | |
| Alizadeh et al. | Potential N mineralization and availability to irrigated maize in a calcareous soil amended with organic manures and urea under field conditions | |
| Jami et al. | Investigating the use of different levels of Mycorrhiza and Vermicompost on quantitative and qualitative yield of saffron (Crocus sativus L.) | |
| CN102816005B (en) | Peanut special microbial fertilizer and production method thereof | |
| CN106810370A (en) | A kind of microbial manure containing chelated microelements and preparation method thereof | |
| CN102167631B (en) | Plug seedling matrix and application thereof | |
| CN106171098A (en) | The method of the improvement of a kind of soil and improvement soil | |
| CN106590671A (en) | Soil conditioner and preparation method and applications thereof | |
| CN107324945A (en) | A kind of method that utilization animal dung produces particular biological organic fertilizer | |
| Zheng et al. | Tree-scale spatial responses of extracellular enzyme activities and stoichiometry to different types of fertilization and cover crop in an apple orchard | |
| NS et al. | Effects of palm kernel biochar and food waste compost on the growth of palm lily (Cordyline fruticosa), coleus (Coleus sp.), and boat lily (Rhoeo discolor). | |
| Islam et al. | The effect of zinc fertilization and cow dung on sterility and quantitative traits of rice | |
| CN109874443A (en) | A kind of method of cadmium pollution dryland soil long-term cropping | |
| CN107827657A (en) | A kind of red soil conditioner of wormcast compounding boron fertilizer | |
| CN104560788A (en) | Peanut root growth-promoting bacterium HS9 and application thereof | |
| CN107827658A (en) | A kind of red soil conditioner of Heisui River gadfly sand compounding chelating boron | |
| CN110218117A (en) | A kind of micro-nano carbon long-acting environment friendly compound magnetic fertilizer and its preparation method and application | |
| Bondoc | Nutrient restoration capacity of Eichhornia crassipes compost on a nutrient-depleted soil | |
| CN108675894A (en) | A kind of microbial organic fertilizer containing bacillus cereus | |
| CN106982641A (en) | A kind of method for improveing herbage strain plex structure under photovoltaic frame | |
| Ahsan et al. | Biofertiliser a highly potent alternative to chemical fertilisers: Uses and future prospects |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| RJ01 | Rejection of invention patent application after publication | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20180323 |