CN104355903A - Method for preparing biochar based slow release fertilizers by utilizing Chinese torreya shells - Google Patents
Method for preparing biochar based slow release fertilizers by utilizing Chinese torreya shells Download PDFInfo
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- CN104355903A CN104355903A CN201410680492.3A CN201410680492A CN104355903A CN 104355903 A CN104355903 A CN 104355903A CN 201410680492 A CN201410680492 A CN 201410680492A CN 104355903 A CN104355903 A CN 104355903A
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- biochar
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- torreya
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- 239000003337 fertilizer Substances 0.000 title claims abstract description 78
- 238000000034 method Methods 0.000 title claims abstract description 9
- 240000000147 Torreya grandis Species 0.000 title claims 2
- 235000016410 Torreya grandis Nutrition 0.000 title claims 2
- 239000000126 substance Substances 0.000 claims abstract description 24
- 239000010903 husk Substances 0.000 claims abstract description 21
- 238000000197 pyrolysis Methods 0.000 claims abstract description 21
- 241000488908 Torreya Species 0.000 claims abstract description 19
- 229910052799 carbon Inorganic materials 0.000 claims abstract description 11
- 210000003608 fece Anatomy 0.000 claims abstract description 11
- 239000003112 inhibitor Substances 0.000 claims abstract description 10
- 235000015097 nutrients Nutrition 0.000 claims abstract description 9
- 239000002601 urease inhibitor Substances 0.000 claims abstract description 9
- 238000006243 chemical reaction Methods 0.000 claims description 41
- 239000000203 mixture Substances 0.000 claims description 29
- 238000002360 preparation method Methods 0.000 claims description 22
- NLSCHDZTHVNDCP-UHFFFAOYSA-N caesium nitrate Chemical compound [Cs+].[O-][N+]([O-])=O NLSCHDZTHVNDCP-UHFFFAOYSA-N 0.000 claims description 18
- 239000000243 solution Substances 0.000 claims description 18
- 239000002028 Biomass Substances 0.000 claims description 14
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 claims description 12
- 235000011114 ammonium hydroxide Nutrition 0.000 claims description 12
- 238000001179 sorption measurement Methods 0.000 claims description 12
- 239000011259 mixed solution Substances 0.000 claims description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 10
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 9
- NWAHZABTSDUXMJ-UHFFFAOYSA-N platinum(2+);dinitrate Chemical compound [Pt+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O NWAHZABTSDUXMJ-UHFFFAOYSA-N 0.000 claims description 9
- 229940090496 Urease inhibitor Drugs 0.000 claims description 8
- 238000001816 cooling Methods 0.000 claims description 8
- 238000005056 compaction Methods 0.000 claims description 7
- 239000012153 distilled water Substances 0.000 claims description 7
- 238000010438 heat treatment Methods 0.000 claims description 7
- 229910052573 porcelain Inorganic materials 0.000 claims description 7
- 238000003756 stirring Methods 0.000 claims description 7
- 239000011230 binding agent Substances 0.000 claims description 4
- 239000005416 organic matter Substances 0.000 claims description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 3
- -1 biochar≧30 % Substances 0.000 claims 1
- 239000002994 raw material Substances 0.000 abstract description 11
- 239000002689 soil Substances 0.000 abstract description 11
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 abstract description 7
- 239000011591 potassium Substances 0.000 abstract description 7
- 229910052700 potassium Inorganic materials 0.000 abstract description 7
- 238000004519 manufacturing process Methods 0.000 abstract description 6
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract description 4
- 230000008901 benefit Effects 0.000 abstract description 3
- 238000011161 development Methods 0.000 abstract description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 abstract description 2
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 2
- 229910052698 phosphorus Inorganic materials 0.000 abstract description 2
- 239000011574 phosphorus Substances 0.000 abstract description 2
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Natural products NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 13
- 239000008187 granular material Substances 0.000 description 12
- QIGBRXMKCJKVMJ-UHFFFAOYSA-N 1,4-Benzenediol Natural products OC1=CC=C(O)C=C1 QIGBRXMKCJKVMJ-UHFFFAOYSA-N 0.000 description 11
- 238000012360 testing method Methods 0.000 description 10
- 239000000440 bentonite Substances 0.000 description 6
- 229910000278 bentonite Inorganic materials 0.000 description 6
- SVPXDRXYRYOSEX-UHFFFAOYSA-N bentoquatam Chemical group O.O=[Si]=O.O=[Al]O[Al]=O SVPXDRXYRYOSEX-UHFFFAOYSA-N 0.000 description 6
- YYRMJZQKEFZXMX-UHFFFAOYSA-N calcium;phosphoric acid Chemical compound [Ca+2].OP(O)(O)=O.OP(O)(O)=O YYRMJZQKEFZXMX-UHFFFAOYSA-N 0.000 description 6
- 239000004202 carbamide Substances 0.000 description 6
- 239000002686 phosphate fertilizer Substances 0.000 description 6
- 239000002426 superphosphate Substances 0.000 description 6
- 238000001035 drying Methods 0.000 description 5
- 229910052739 hydrogen Inorganic materials 0.000 description 5
- 239000004615 ingredient Substances 0.000 description 5
- OTYBMLCTZGSZBG-UHFFFAOYSA-L potassium sulfate Chemical compound [K+].[K+].[O-]S([O-])(=O)=O OTYBMLCTZGSZBG-UHFFFAOYSA-L 0.000 description 5
- 229910052939 potassium sulfate Inorganic materials 0.000 description 5
- 235000011151 potassium sulphates Nutrition 0.000 description 5
- 241000196324 Embryophyta Species 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 239000000618 nitrogen fertilizer Substances 0.000 description 4
- 239000007787 solid Substances 0.000 description 4
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 3
- 238000011282 treatment Methods 0.000 description 3
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonia chloride Chemical compound [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 description 2
- WCUXLLCKKVVCTQ-UHFFFAOYSA-M Potassium chloride Chemical group [Cl-].[K+] WCUXLLCKKVVCTQ-UHFFFAOYSA-M 0.000 description 2
- JUJWROOIHBZHMG-UHFFFAOYSA-N Pyridine Chemical compound C1=CC=NC=C1 JUJWROOIHBZHMG-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 239000003905 agrochemical Substances 0.000 description 2
- YCIMNLLNPGFGHC-UHFFFAOYSA-N catechol Chemical compound OC1=CC=CC=C1O YCIMNLLNPGFGHC-UHFFFAOYSA-N 0.000 description 2
- 235000013339 cereals Nutrition 0.000 description 2
- 238000013270 controlled release Methods 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- QGBSISYHAICWAH-UHFFFAOYSA-N dicyandiamide Chemical compound NC(N)=NC#N QGBSISYHAICWAH-UHFFFAOYSA-N 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 239000002893 slag Substances 0.000 description 2
- JNMRHUJNCSQMMB-UHFFFAOYSA-N sulfathiazole Chemical compound C1=CC(N)=CC=C1S(=O)(=O)NC1=NC=CS1 JNMRHUJNCSQMMB-UHFFFAOYSA-N 0.000 description 2
- UMGDCJDMYOKAJW-UHFFFAOYSA-N thiourea Chemical compound NC(N)=S UMGDCJDMYOKAJW-UHFFFAOYSA-N 0.000 description 2
- XEMRAKSQROQPBR-UHFFFAOYSA-N (trichloromethyl)benzene Chemical compound ClC(Cl)(Cl)C1=CC=CC=C1 XEMRAKSQROQPBR-UHFFFAOYSA-N 0.000 description 1
- PAWQVTBBRAZDMG-UHFFFAOYSA-N 2-(3-bromo-2-fluorophenyl)acetic acid Chemical compound OC(=O)CC1=CC=CC(Br)=C1F PAWQVTBBRAZDMG-UHFFFAOYSA-N 0.000 description 1
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 description 1
- 235000019739 Dicalciumphosphate Nutrition 0.000 description 1
- OAKJQQAXSVQMHS-UHFFFAOYSA-N Hydrazine Chemical compound NN OAKJQQAXSVQMHS-UHFFFAOYSA-N 0.000 description 1
- 240000007594 Oryza sativa Species 0.000 description 1
- 235000007164 Oryza sativa Nutrition 0.000 description 1
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 108010046334 Urease Proteins 0.000 description 1
- 239000000853 adhesive Substances 0.000 description 1
- 230000001070 adhesive effect Effects 0.000 description 1
- 238000012271 agricultural production Methods 0.000 description 1
- 125000003277 amino group Chemical group 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 239000001099 ammonium carbonate Substances 0.000 description 1
- 235000012501 ammonium carbonate Nutrition 0.000 description 1
- 235000019270 ammonium chloride Nutrition 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- YYRMJZQKEFZXMX-UHFFFAOYSA-L calcium bis(dihydrogenphosphate) Chemical compound [Ca+2].OP(O)([O-])=O.OP(O)([O-])=O YYRMJZQKEFZXMX-UHFFFAOYSA-L 0.000 description 1
- 239000001506 calcium phosphate Substances 0.000 description 1
- 229910000389 calcium phosphate Inorganic materials 0.000 description 1
- KMQAPZBMEMMKSS-UHFFFAOYSA-K calcium;magnesium;phosphate Chemical compound [Mg+2].[Ca+2].[O-]P([O-])([O-])=O KMQAPZBMEMMKSS-UHFFFAOYSA-K 0.000 description 1
- 238000003763 carbonization Methods 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 229910000365 copper sulfate Inorganic materials 0.000 description 1
- ARUVKPQLZAKDPS-UHFFFAOYSA-L copper(II) sulfate Chemical compound [Cu+2].[O-][S+2]([O-])([O-])[O-] ARUVKPQLZAKDPS-UHFFFAOYSA-L 0.000 description 1
- JLYVRXJEQTZZBE-UHFFFAOYSA-N ctk1c6083 Chemical compound NP(N)(N)=S JLYVRXJEQTZZBE-UHFFFAOYSA-N 0.000 description 1
- 230000002950 deficient Effects 0.000 description 1
- 230000003111 delayed effect Effects 0.000 description 1
- OKGXJRGLYVRVNE-UHFFFAOYSA-N diaminomethylidenethiourea Chemical compound NC(N)=NC(N)=S OKGXJRGLYVRVNE-UHFFFAOYSA-N 0.000 description 1
- NEFBYIFKOOEVPA-UHFFFAOYSA-K dicalcium phosphate Chemical compound [Ca+2].[Ca+2].[O-]P([O-])([O-])=O NEFBYIFKOOEVPA-UHFFFAOYSA-K 0.000 description 1
- 229910000390 dicalcium phosphate Inorganic materials 0.000 description 1
- 229940038472 dicalcium phosphate Drugs 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
- 238000002474 experimental method Methods 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
- 125000000524 functional group Chemical group 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 238000003306 harvesting Methods 0.000 description 1
- 125000000687 hydroquinonyl group Chemical group C1(O)=C(C=C(O)C=C1)* 0.000 description 1
- 230000002401 inhibitory effect Effects 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- SWHAQEYMVUEVNF-UHFFFAOYSA-N magnesium potassium Chemical compound [Mg].[K] SWHAQEYMVUEVNF-UHFFFAOYSA-N 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000006011 modification reaction Methods 0.000 description 1
- 235000019691 monocalcium phosphate Nutrition 0.000 description 1
- 229910000402 monopotassium phosphate Inorganic materials 0.000 description 1
- 235000019796 monopotassium phosphate Nutrition 0.000 description 1
- 238000006396 nitration reaction Methods 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
- 239000002367 phosphate rock Substances 0.000 description 1
- 150000003013 phosphoric acid derivatives Chemical class 0.000 description 1
- PJNZPQUBCPKICU-UHFFFAOYSA-N phosphoric acid;potassium Chemical compound [K].OP(O)(O)=O PJNZPQUBCPKICU-UHFFFAOYSA-N 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 239000001103 potassium chloride Substances 0.000 description 1
- 235000011164 potassium chloride Nutrition 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- UMJSCPRVCHMLSP-UHFFFAOYSA-N pyridine Natural products COC1=CC=CN=C1 UMJSCPRVCHMLSP-UHFFFAOYSA-N 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 235000009566 rice Nutrition 0.000 description 1
- 235000002639 sodium chloride Nutrition 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 239000003802 soil pollutant Substances 0.000 description 1
- 239000002195 soluble material Substances 0.000 description 1
- 238000009331 sowing Methods 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
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- 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
- C05G3/90—Mixtures of one or more fertilisers with additives not having a specially fertilising activity for affecting the nitrification of ammonium compounds or urea in the soil
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05B—PHOSPHATIC FERTILISERS
- C05B17/00—Other phosphatic fertilisers, e.g. soft rock phosphates, bone meal
-
- 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
-
- 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
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/22—Improving land use; Improving water use or availability; Controlling erosion
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P60/00—Technologies relating to agriculture, livestock or agroalimentary industries
- Y02P60/20—Reduction of greenhouse gas [GHG] emissions in agriculture, e.g. CO2
- Y02P60/21—Dinitrogen oxide [N2O], e.g. using aquaponics, hydroponics or efficiency measures
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Pest Control & Pesticides (AREA)
- Soil Sciences (AREA)
- Fertilizers (AREA)
Abstract
一种利用香榧果壳制备生物碳基缓释肥料的方法,它是以香榧果壳为原料,经厌氧热解制备改性生物碳,再与牛粪沼渣、化肥、脲酶抑制剂和硝化抑制剂等混合制备高效缓释肥料。本发明制备的缓释肥料,生产工艺简单,原料易得,生产成本低,不但能够有效提高氮磷钾的利用率,减少养分流失,同时可以改善土壤质量,提高农产品品质,并利于农业生态系统的良性发展。A method for preparing bio-carbon-based slow-release fertilizers using Torreya husks, which uses Torreya husks as raw materials, prepares modified biochar through anaerobic pyrolysis, and then mixes cow dung biogas residues, chemical fertilizers, urease inhibitors and nitrification Inhibitors, etc. are mixed to prepare high-efficiency slow-release fertilizers. The slow-release fertilizer prepared by the invention has simple production process, easy-to-obtain raw materials, and low production cost. It can not only effectively improve the utilization rate of nitrogen, phosphorus, and potassium, reduce nutrient loss, but also improve soil quality, improve the quality of agricultural products, and benefit the agricultural ecosystem. benign development.
Description
技术领域 technical field
本发明涉及生物碳基肥料制备技术领域,特别涉及一种用香榧果壳制备生物炭基缓释肥料的方法。 The invention relates to the technical field of preparation of biochar-based fertilizers, in particular to a method for preparing biochar-based slow-release fertilizers from Torreya husks.
背景技术 Background technique
据统计,我国化肥年使用量已达到4214万吨,平均368 kg/hm2,并且化肥在施用过程中还存在结构不合理的现象,化肥利用率极低。据资料显示,目前我国氮肥平均利用率只有30%~40%、磷肥只有10%~20%、钾肥只有35%~50%。化肥的流失,不仅增加生产成本,还造成湖泊、水库、江河等水体富营养化,土壤性质改变,生产力下降,农产品品质下降等诸多问题。因此,减轻农业化肥面源污染,发展生态农业,改善生态环境是当前农业生产的重要任务。为此,国内外进行了大量研究工作,研发各型缓释肥料,极大降低了化肥面源污染。 According to statistics, the annual use of chemical fertilizers in China has reached 42.14 million tons, with an average of 368 kg/hm 2 , and the structure of chemical fertilizers is still unreasonable in the process of application, and the utilization rate of chemical fertilizers is extremely low. According to data, the average utilization rate of nitrogen fertilizer in my country is only 30% to 40%, phosphate fertilizer is only 10% to 20%, and potassium fertilizer is only 35% to 50%. The loss of chemical fertilizers not only increases production costs, but also causes eutrophication of lakes, reservoirs, rivers and other water bodies, changes in soil properties, decline in productivity, and decline in the quality of agricultural products. Therefore, reducing non-point source pollution from agricultural chemical fertilizers, developing ecological agriculture, and improving the ecological environment are important tasks in current agricultural production. For this reason, a lot of research work has been carried out at home and abroad, and various types of slow-release fertilizers have been developed, which have greatly reduced the non-point source pollution of chemical fertilizers.
缓释肥料又称长效肥料或控释肥料,指由于化学成分改变或表面包涂半透水性或不透水性物质,而使其中有效养分慢慢释放,保持肥效的长效性。缓释氮肥的最重要特性是可以控制其释放速度,在施入土壤以后逐渐分解,逐渐为作物吸收利用,使肥料中养分能满足作物整个生长期中各个生长阶段的不同需要,一次施用后,肥效可维持数月至一年以上。施用缓释/控释肥料,既可以降低生产成本,又可以减少农业化肥面源污染,利用农业的持续发展。 Slow-release fertilizers, also known as long-acting fertilizers or controlled-release fertilizers, refer to the slow release of effective nutrients due to changes in chemical composition or coating of semi-permeable or impermeable substances on the surface to maintain long-term fertilizer effects. The most important feature of slow-release nitrogen fertilizer is that it can control its release rate, and gradually decompose after being applied to the soil, and gradually be absorbed and utilized by crops, so that the nutrients in the fertilizer can meet the different needs of crops in each growth stage throughout the growth period. After one application, The fertilizer effect can be maintained for several months to more than a year. The application of slow-release/controlled-release fertilizers can not only reduce production costs, but also reduce non-point source pollution from agricultural chemical fertilizers, and take advantage of the sustainable development of agriculture.
生物炭是生物质材料在缺氧或限氧条件下热解,去除生物质中的油和气后剩下的固体物质。生物碳具有优异的吸附性能,能直接吸附废水中的污染物质;施用土壤后还可以改善土壤理化性质、减少养分流失、促进作物生长、吸附固定土壤污染物质,并能起到土壤碳库增汇减排的作用。因此,生物炭已成为近年来环境和农业科学领域的研究热点之一。 Biochar is a solid substance left after biomass material is pyrolyzed under anoxic or oxygen-limited conditions to remove oil and gas from the biomass. Biochar has excellent adsorption properties and can directly adsorb pollutants in wastewater; after soil application, it can also improve soil physical and chemical properties, reduce nutrient loss, promote crop growth, adsorb and fix soil pollutants, and increase soil carbon pools The role of emission reduction. Therefore, biochar has become one of the research hotspots in the field of environmental and agricultural sciences in recent years.
发明内容 Contents of the invention
本发明的另一目的在于提供上述生物碳基缓释肥料的制备方法和施用方法。 Another object of the present invention is to provide the preparation method and application method of the biochar-based slow-release fertilizer.
为了实现本发明的目的,本发明提供一种生物碳基缓释肥料的制备方法,主要包括生物炭、有机质和化肥,所述的生物炭由香榧果壳低温碳化改性制得。 In order to achieve the purpose of the present invention, the present invention provides a preparation method of biochar-based slow-release fertilizer, which mainly includes biochar, organic matter and chemical fertilizer, and the biochar is prepared by low-temperature carbonization modification of Torreya husk.
本发明提供的生物碳基缓释肥料,其原料包括如下质量比例的成分: The biological carbon-based slow-release fertilizer provided by the invention, its raw material comprises the composition of following mass ratio:
改性后的生物碳产物:25~40 Modified biochar product: 25-40
牛粪沼渣:25~35 Cow dung biogas residue: 25~35
化肥:30~40 Fertilizer: 30~40
脲酶抑制剂和硝化抑制剂的混合溶液:2~5 Mixed solution of urease inhibitor and nitrification inhibitor: 2 to 5
粘合剂:5-10 Adhesive: 5-10
所述生物炭与沼渣、化肥、脲酶抑制剂和硝化抑制剂的混合溶液、粘合剂的质量比为(25~40):(25~35):(30~40):(2~5):(5~10),优选为32:27:33:3:5。 The mass ratio of the biochar to biogas residue, fertilizer, urease inhibitor and nitrification inhibitor mixed solution and binder is (25-40): (25-35): (30-40): (2-5 ): (5-10), preferably 32:27:33:3:5.
所述的生物碳基缓释肥,其总养分(N+P2O5+K2O)≧20%,生物炭≧30%,有机质≧30%。 The biochar-based slow-release fertilizer has total nutrients (N+P 2 O 5 +K 2 O)≧20%, biochar≧30%, and organic matter≧30%.
此外,本发明首先提供一种上述生物碳基缓释肥料的制备方法,包括以下具体步骤: In addition, the present invention firstly provides a method for preparing the above-mentioned biochar-based slow-release fertilizer, comprising the following specific steps:
(1)将收集的香榧果壳粉碎过筛。 (1) Crush and sieve the collected torreya husks.
(2)在上述粉碎后的香榧果壳加入稀盐酸搅拌混匀,密封静置24h,再加入硝酸铯溶液混匀密封静置12h,自然风干。 (2) Add dilute hydrochloric acid to the crushed torreya husk, stir and mix well, seal and let stand for 24 hours, then add cesium nitrate solution, mix and seal and let stand for 12 hours, then air dry naturally.
(3)将上述处理过的生物质置于瓷坩埚中压实,盖上盖子进行厌氧热解;热解反应结束后,待坩埚冷却至室温后取出。 (3) Put the above-mentioned treated biomass in a porcelain crucible for compaction, cover the lid for anaerobic pyrolysis; after the pyrolysis reaction is completed, take out the crucible after cooling to room temperature.
(4)将上述制备的生物碳与一定浓度的H2O2混匀,在振荡器中震荡24h取出,用蒸馏水洗净后烘干,即获得高吸附性能生物碳。 (4) Mix the biochar prepared above with a certain concentration of H 2 O 2 , shake it in a shaker for 24 hours, take it out, wash it with distilled water and dry it to obtain biochar with high adsorption performance.
(5)将上述制备的生物炭置入密闭容器中,加入一定量的浓氨水、硝酸铂溶液后加热反应,待反应3-10小时后取出。反应期间调节反应容器压力,使其维持在5-15个标准大气压。 (5) Put the above-prepared biochar into an airtight container, add a certain amount of concentrated ammonia water and platinum nitrate solution, heat it for reaction, and take it out after 3-10 hours of reaction. During the reaction, the pressure of the reaction vessel was adjusted so as to maintain it at 5-15 standard atmospheres.
(6)以上述反应后的改性生物炭为主体,加入一定量的沼渣、化肥(氮肥、磷肥、钾肥)、脲酶抑制剂/硝化抑制剂混合液、粘合剂等,在有机无机肥料造粒机中造粒,造粒后的物料进入烘干机中烘干,经冷却即获得生物碳基缓释肥料。 (6) With the above-mentioned modified biochar as the main body, add a certain amount of biogas residue, chemical fertilizers (nitrogen fertilizer, phosphate fertilizer, potassium fertilizer), urease inhibitor/nitration inhibitor mixture, binder, etc., in organic and inorganic fertilizers The granulated material is granulated in the granulator, and the granulated material is dried in the dryer, and the bio-carbon-based slow-release fertilizer is obtained after cooling.
为确保热解时的缺氧环境以及热解效果,所述步骤1中生物质原料粉碎粒径为20~100目。 In order to ensure an oxygen-deficient environment and pyrolysis effect during pyrolysis, the particle size of the biomass raw material crushed in the step 1 is 20-100 mesh.
所述步骤2中稀盐酸浓度为0.5-2.5mol/L,硝酸铯溶液浓度为0.05-1.5mol/L。 In the step 2, the concentration of dilute hydrochloric acid is 0.5-2.5mol/L, and the concentration of cesium nitrate solution is 0.05-1.5mol/L.
所述步骤3中生物质热解温度400~700℃,热解时间60-300min,升温速度为5-15℃/min。 In the step 3, the biomass pyrolysis temperature is 400-700°C, the pyrolysis time is 60-300min, and the heating rate is 5-15°C/min.
所述步骤4中H2O2浓度为1~10%。 The concentration of H 2 O 2 in step 4 is 1-10%.
为提高生物炭与氨水间的反应效果,增加改性生物炭官能团中结合的氨含量,所述步骤5中浓氨水浓度为5%-28%,硝酸铂溶液浓度为 0.02-1.0mol/L,反应期间反应容器压力维持在5-15个标准大气压。 In order to improve the reaction effect between biochar and ammonia water, increase the combined ammonia content in the modified biochar functional group, the concentration of concentrated ammonia water in the step 5 is 5%-28%, and the concentration of platinum nitrate solution is 0.02-1.0mol/L, During the reaction, the pressure of the reaction vessel was maintained at 5-15 standard atmospheres.
为提高步骤5中氨水利用率,在调节步骤5所述反应容器压力时,可将减压阀出口置于水中,并将吸收氨气后的水溶液用于制备肥料。 In order to improve the utilization rate of ammonia water in step 5, when adjusting the pressure of the reaction vessel described in step 5, the outlet of the pressure reducing valve can be placed in water, and the aqueous solution after absorbing ammonia gas can be used to prepare fertilizer.
所述步骤6中脲酶抑制剂为氢醌、硫酸铜、邻-苯基磷酰二胺(PPD)、儿茶酚、硫代磷酰三胺(NBPT)、硫脲或其他常温下以固态存在的具有脲酶抑制作用的可溶于水的材料;硝化抑制剂为2-氯-6-(三氯甲苯)吡啶(又称西吡)、脒基硫脲(ASU)、双氰胺(DCD)、2-甲基-4,6-双(三氯甲苯)均三嗪(MDCT)、2-磺胺噻唑(ST)等或其他常温下以固态存在的具有硝化抑制剂作用的可溶于水的材料。所述步骤6中的脲酶抑制剂、硝化抑制剂混合液为脲酶抑制剂、硝化抑制剂按质量比1:1的混合液。 In the step 6, the urease inhibitor is hydroquinone, copper sulfate, o-phenylphosphoric diamide (PPD), catechol, thiophosphoric triamide (NBPT), thiourea or other solid state at normal temperature Water-soluble materials with urease inhibitory effect; nitrification inhibitors are 2-chloro-6-(trichlorotoluene)pyridine (also known as xipyridine), amidinothiourea (ASU), dicyandiamide (DCD) , 2-methyl-4,6-bis(trichlorotoluene)-s-triazine (MDCT), 2-sulfathiazole (ST), etc. or other water-soluble nitrification inhibitors that exist in solid state at room temperature Material. The mixed solution of urease inhibitor and nitrification inhibitor in the step 6 is a mixed solution of urease inhibitor and nitrification inhibitor in a mass ratio of 1:1.
所述步骤6中沼渣为经过沼气发酵处理后残留的牛粪固体(使用前先自然风干粉碎至20-50目),氮肥为尿素、碳酸铵、硝酸铵、氯化铵中的一种或几种,磷肥为过磷酸钙、重过磷酸钙、磷酸二钙、钙镁磷肥、脱氟磷肥、磷矿粉肥、炉渣磷肥、钢渣磷肥中的一种或几种,钾肥为氯化钾、硫酸钾、磷酸二氢钾、钾石盐、钾镁盐中的一种或几种,粘合剂为膨润土。 The biogas residue in step 6 is the cow dung solid left after biogas fermentation treatment (naturally air-dried and crushed to 20-50 mesh before use), and the nitrogen fertilizer is one or more of urea, ammonium carbonate, ammonium nitrate, and ammonium chloride. The phosphate fertilizer is one or more of calcium superphosphate, heavy superphosphate, dicalcium phosphate, calcium magnesium phosphate fertilizer, defluorinated phosphate fertilizer, phosphate rock powder fertilizer, slag phosphate fertilizer, and steel slag phosphate fertilizer. The potassium fertilizer is potassium chloride, sulfuric acid One or more of potassium, potassium dihydrogen phosphate, potassium rock salt, potassium magnesium salt, and the binder is bentonite.
本发明具有如下的有益效果:The present invention has following beneficial effect:
本发明利用香榧果壳制备的改性生物碳和牛粪沼渣为原料制备缓释肥料,其生产工艺简单,原料易得,生产成本低。 The invention uses modified biochar prepared from Torreya husk and cow dung biogas residue as raw materials to prepare the slow-release fertilizer, the production process is simple, the raw materials are easy to obtain, and the production cost is low.
生物碳具有极强的吸附能力,可延缓养分的释放速度;经过改性的生物碳吸附能力进一步得到加强,且在改性反应过程中增加了大量氨基,进一步增强了肥料的缓释特性;同时,肥料中的牛粪沼渣也具有较强的吸附能力,也可延缓养分的释放。 Biochar has a strong adsorption capacity, which can delay the release rate of nutrients; the adsorption capacity of modified biochar is further enhanced, and a large amount of amino groups are added in the modification reaction process, which further enhances the slow-release characteristics of fertilizers; at the same time , The cow dung biogas residue in the fertilizer also has a strong adsorption capacity and can also delay the release of nutrients.
生物碳基缓释肥料不但能够有效提高氮磷钾的利用率,减少养分流失,同时可以改善土壤质量,提高农产品品质,并利于农业生态系统的良性发展。 Biochar-based slow-release fertilizers can not only effectively increase the utilization rate of nitrogen, phosphorus and potassium, reduce nutrient loss, but also improve soil quality, improve the quality of agricultural products, and benefit the healthy development of agricultural ecosystems.
具体实施方式 Detailed ways
下面通过实施例对本发明进行具体的描述,有必要在此指出的是以下实施例只用于对本发明进行进一步说明,不能理解为对本发明保护范围的限制,该领域的技术人员可以根据上述发明内容对本发明作出一些非本质的改进和调整。 The present invention is specifically described by the following examples. It is necessary to point out that the following examples are only used to further illustrate the present invention, and cannot be interpreted as limiting the protection scope of the present invention. Those skilled in the art can according to the above-mentioned content Some non-essential improvements and adjustments are made to the present invention.
实施例1Example 1
1、生物碳基缓释肥料制备 1. Preparation of biochar-based slow-release fertilizer
生物碳基缓释肥料的原料包括以下质量比例的成分: The raw materials of the biochar-based slow-release fertilizer include the following components by mass ratio:
改性后的生物碳30,牛粪沼渣(30目)30、化肥31、氢醌与西吡质量比1:1的混合溶液3、膨润土6。 Modified biochar 30, cow dung biogas residue (30 mesh) 30, chemical fertilizer 31, a mixed solution of hydroquinone and cepiryl in a mass ratio of 1:1 3, bentonite 6.
其中化肥是将尿素、过磷酸钙、硫酸钾按质量比1:2:2混合。 Among them, the chemical fertilizer is to mix urea, superphosphate and potassium sulfate in a mass ratio of 1:2:2.
制备方法:将各成分按上述比例混合,在模具中通过挤压造粒,造粒后的物料筛分后放入烘箱中烘干,经冷却即获得生物碳基缓释肥料。 The preparation method: mix the ingredients according to the above ratio, extrude and granulate in a mold, sieve the granulated material, put it in an oven for drying, and obtain the bio-carbon-based slow-release fertilizer after cooling.
2、改性生物碳制备方法: 2. Preparation method of modified biochar:
(1)将收集的香榧果壳粉碎过80目筛。 (1) Crush the collected torreya husks through an 80-mesh sieve.
(2)取100g上述粉碎后的香榧果壳加入1.0mol/L的稀盐酸25ml搅拌混匀,密封静置24h,再加入0.1mol/L硝酸铯溶液2ml混匀密封静置12h,自然风干。 (2) Take 100g of the above pulverized Torreya husk, add 25ml of 1.0mol/L dilute hydrochloric acid, stir and mix, seal and let stand for 24h, then add 2ml of 0.1mol/L cesium nitrate solution, mix evenly, seal and let stand for 12h, and air dry naturally.
(3)将上述处理过得生物质置于瓷坩埚中压实,盖上盖子在600℃环境下厌氧热解3小时,升温速度为10℃/min;热解反应结束后,待坩埚冷却至室温后取出。 (3) Put the above treated biomass in a porcelain crucible for compaction, put the lid on and perform anaerobic pyrolysis at 600°C for 3 hours, with a heating rate of 10°C/min; after the pyrolysis reaction is completed, cool the crucible Remove from room temperature.
(4)将上述制备生物碳与100ml浓度为8%的H2O2混匀,在振荡器中震荡24h取出,用蒸馏水洗净后烘干,即获得高吸附性能生物碳。 (4) Mix the above prepared biochar with 100ml of 8% H 2 O 2 , shake it in a shaker for 24 hours, take it out, wash it with distilled water and dry it to obtain biochar with high adsorption performance.
(5)将上述制备的生物炭置入密闭容器中,加入25ml浓度为25%的氨水、0.5mol/L硝酸铂溶液1ml后加热反应,反应2小时后取出。反应期间调节反应容器压力,使其维持在8个标准大气压。 (5) Put the above-prepared biochar into an airtight container, add 25ml of 25% ammonia water and 1ml of 0.5mol/L platinum nitrate solution, heat for reaction, and take it out after 2 hours of reaction. During the reaction, the pressure of the reaction vessel was adjusted to maintain 8 standard atmospheres.
实施例2Example 2
1、生物碳基缓释肥料制备 1. Preparation of biochar-based slow-release fertilizer
生物碳基缓释肥料的原料包括以下质量比例的成分: The raw materials of the biochar-based slow-release fertilizer include the following components by mass ratio:
改性后的生物碳32,牛粪沼渣(30目)30、化肥33、氢醌与西吡质量比1:1的混合溶液3、膨润土6。 Modified biochar 32, cow dung biogas residue (30 mesh) 30, chemical fertilizer 33, a mixed solution of hydroquinone and cepiryl in a mass ratio of 1:1 3, bentonite 6.
其中化肥是将尿素、过磷酸钙、硫酸钾按质量比1:2:2混合。 Among them, the chemical fertilizer is to mix urea, superphosphate and potassium sulfate in a mass ratio of 1:2:2.
制备方法:将各成分按上述比例混合,在模具中通过挤压造粒,造粒后的物料筛分后放入烘箱中烘干,经冷却即获得生物碳基缓释肥料。 The preparation method: mix the ingredients according to the above ratio, extrude and granulate in a mold, sieve the granulated material, put it in an oven for drying, and obtain the bio-carbon-based slow-release fertilizer after cooling.
2、改性生物碳制备方法: 2. Preparation method of modified biochar:
(1)将收集的香榧果壳粉碎过80目筛。 (1) Crush the collected torreya husks through an 80-mesh sieve.
(2)取100g上述粉碎后的香榧果壳加入1.0mol/L的稀盐酸25ml搅拌混匀,密封静置24h,再加入0.1mol/L硝酸铯溶液2ml混匀密封静置12h,自然风干。 (2) Take 100g of the above pulverized Torreya husk, add 25ml of 1.0mol/L dilute hydrochloric acid, stir and mix, seal and let stand for 24h, then add 2ml of 0.1mol/L cesium nitrate solution, mix evenly, seal and let stand for 12h, and air dry naturally.
(3)将上述处理过得生物质置于瓷坩埚中压实,盖上盖子在600℃环境下厌氧热解3小时,升温速度为10℃/min;热解反应结束后,待坩埚冷却至室温后取出。 (3) Put the above treated biomass in a porcelain crucible for compaction, put the lid on and perform anaerobic pyrolysis at 600°C for 3 hours, with a heating rate of 10°C/min; after the pyrolysis reaction is completed, cool the crucible Remove from room temperature.
(4)将上述制备生物碳与100ml浓度为8%的H2O2混匀,在振荡器中震荡24h取出,用蒸馏水洗净后烘干,即获得高吸附性能生物碳。 (4) Mix the above prepared biochar with 100ml of 8% H 2 O 2 , shake it in a shaker for 24 hours, take it out, wash it with distilled water and dry it to obtain biochar with high adsorption performance.
(5)将上述制备的生物炭置入密闭容器中,加入25ml浓度为25%的氨水、0.5mol/L硝酸铂溶液1ml后加热反应,反应2小时后取出。反应期间调节反应容器压力,使其维持在8个标准大气压。 (5) Put the above-prepared biochar into an airtight container, add 25ml of 25% ammonia water and 1ml of 0.5mol/L platinum nitrate solution, heat for reaction, and take it out after 2 hours of reaction. During the reaction, the pressure of the reaction vessel was adjusted to maintain 8 standard atmospheres.
实施例3Example 3
1、生物碳基缓释肥料制备 1. Preparation of biochar-based slow-release fertilizer
生物碳基缓释肥料的原料包括以下质量比例的成分: The raw materials of the biochar-based slow-release fertilizer include the following components by mass ratio:
改性后的生物碳32,牛粪沼渣(30目)27、化肥33、氢醌与西吡质量比1:1的混合溶液3、膨润土5。 Modified biochar 32, cow dung biogas residue (30 mesh) 27, chemical fertilizer 33, a mixed solution of hydroquinone and cepiryl in a mass ratio of 1:1, 3, bentonite 5.
其中化肥是将尿素、过磷酸钙、硫酸钾按质量比1:2:2混合。 Among them, the chemical fertilizer is to mix urea, superphosphate and potassium sulfate in a mass ratio of 1:2:2.
制备方法:将各成分按上述比例混合,在模具中通过挤压造粒,造粒后的物料筛分后放入烘箱中烘干,经冷却即获得生物碳基缓释肥料。 The preparation method: mix the ingredients according to the above ratio, extrude and granulate in a mold, sieve the granulated material, put it in an oven for drying, and obtain the bio-carbon-based slow-release fertilizer after cooling.
2、改性生物碳制备方法: 2. Preparation method of modified biochar:
(1)将收集的香榧果壳粉碎过80目筛。 (1) Crush the collected torreya husks through an 80-mesh sieve.
(2)取100g上述粉碎后的香榧果壳加入1.0mol/L的稀盐酸25ml搅拌混匀,密封静置24h,再加入0.1mol/L硝酸铯溶液2ml混匀密封静置12h,自然风干。 (2) Take 100g of the above pulverized Torreya husk, add 25ml of 1.0mol/L dilute hydrochloric acid, stir and mix, seal and let stand for 24h, then add 2ml of 0.1mol/L cesium nitrate solution, mix evenly, seal and let stand for 12h, and air dry naturally.
(3)将上述处理过得生物质置于瓷坩埚中压实,盖上盖子在600℃环境下厌氧热解3小时,升温速度为10℃/min;热解反应结束后,待坩埚冷却至室温后取出。 (3) Put the above treated biomass in a porcelain crucible for compaction, put the lid on and perform anaerobic pyrolysis at 600°C for 3 hours, with a heating rate of 10°C/min; after the pyrolysis reaction is completed, cool the crucible Remove from room temperature.
(4)将上述制备生物碳与100ml浓度为8%的H2O2混匀,在振荡器中震荡24h取出,用蒸馏水洗净后烘干,即获得高吸附性能生物碳。 (4) Mix the above prepared biochar with 100ml of 8% H 2 O 2 , shake it in a shaker for 24 hours, take it out, wash it with distilled water and dry it to obtain biochar with high adsorption performance.
(5)将上述制备的生物炭置入密闭容器中,加入25ml浓度为25%的氨水、0.5mol/L硝酸铂溶液1ml后加热反应,反应2小时后取出。反应期间调节反应容器压力,使其维持在8个标准大气压。 (5) Put the above-prepared biochar into an airtight container, add 25ml of 25% ammonia water and 1ml of 0.5mol/L platinum nitrate solution, heat for reaction, and take it out after 2 hours of reaction. During the reaction, the pressure of the reaction vessel was adjusted to maintain 8 standard atmospheres.
实施例4Example 4
1、生物碳基缓释肥料制备 1. Preparation of biochar-based slow-release fertilizer
生物碳基缓释肥料的原料包括以下质量比例的成分: The raw materials of the biochar-based slow-release fertilizer include the following components by mass ratio:
改性后的生物碳30,牛粪沼渣(30目)27、化肥30、氢醌与西吡质量比1:1的混合溶液3、膨润土5。 Modified biochar 30, cow dung biogas residue (30 mesh) 27, chemical fertilizer 30, a mixed solution of hydroquinone and cepiryl at a mass ratio of 1:1 3, bentonite 5.
其中化肥是将尿素、过磷酸钙、硫酸钾按质量比1:2:2混合。 Among them, the chemical fertilizer is to mix urea, superphosphate and potassium sulfate in a mass ratio of 1:2:2.
制备方法:将各成分按上述比例混合,在模具中通过挤压造粒,造粒后的物料筛分后放入烘箱中烘干,经冷却即获得生物碳基缓释肥料。 The preparation method: mix the ingredients according to the above ratio, extrude and granulate in a mold, sieve the granulated material, put it in an oven for drying, and obtain the bio-carbon-based slow-release fertilizer after cooling.
2、改性生物碳制备方法: 2. Preparation method of modified biochar:
(1)将收集的香榧果壳粉碎过80目筛。 (1) Crush the collected torreya husks through an 80-mesh sieve.
(2)取100g上述粉碎后的香榧果壳加入1.0mol/L的稀盐酸25ml搅拌混匀,密封静置24h,再加入0.1mol/L硝酸铯溶液2ml混匀密封静置12h,自然风干。 (2) Take 100g of the above pulverized Torreya husk, add 25ml of 1.0mol/L dilute hydrochloric acid, stir and mix, seal and let stand for 24h, then add 2ml of 0.1mol/L cesium nitrate solution, mix evenly, seal and let stand for 12h, and air dry naturally.
(3)将上述处理过得生物质置于瓷坩埚中压实,盖上盖子在600℃环境下厌氧热解3小时,升温速度为10℃/min;热解反应结束后,待坩埚冷却至室温后取出。 (3) Put the above treated biomass in a porcelain crucible for compaction, put the lid on and perform anaerobic pyrolysis at 600°C for 3 hours, with a heating rate of 10°C/min; after the pyrolysis reaction is completed, cool the crucible Remove from room temperature.
(4)将上述制备生物碳与100ml浓度为8%的H2O2混匀,在振荡器中震荡24h取出,用蒸馏水洗净后烘干,即获得高吸附性能生物碳。 (4) Mix the above prepared biochar with 100ml of 8% H 2 O 2 , shake it in a shaker for 24 hours, take it out, wash it with distilled water and dry it to obtain biochar with high adsorption performance.
(5)将上述制备的生物炭置入密闭容器中,加入25ml浓度为25%的氨水、0.5mol/L硝酸铂溶液1ml后加热反应,反应2小时后取出。反应期间调节反应容器压力,使其维持在8个标准大气压。 (5) Put the above-prepared biochar into an airtight container, add 25ml of 25% ammonia water and 1ml of 0.5mol/L platinum nitrate solution, heat for reaction, and take it out after 2 hours of reaction. During the reaction, the pressure of the reaction vessel was adjusted to maintain 8 standard atmospheres.
实施例5Example 5
1、生物碳基缓释肥料制备 1. Preparation of biochar-based slow-release fertilizer
生物碳基缓释肥料的原料包括以下质量比例的成分: The raw materials of the biochar-based slow-release fertilizer include the following components by mass ratio:
改性后的生物碳30,牛粪沼渣(30目)27、化肥32、氢醌与西吡质量比1:1的混合溶液3、膨润土5。 Modified biochar 30, cow dung biogas residue (30 mesh) 27, chemical fertilizer 32, a mixed solution of hydroquinone and cepiryl in a mass ratio of 1:1 3, bentonite 5.
其中化肥是将尿素、过磷酸钙、硫酸钾按质量比1:2:2混合。 Among them, the chemical fertilizer is to mix urea, superphosphate and potassium sulfate in a mass ratio of 1:2:2.
制备方法:将各成分按上述比例混合,在模具中通过挤压造粒,造粒后的物料筛分后放入烘箱中烘干,经冷却即获得生物碳基缓释肥料。 The preparation method: mix the ingredients according to the above ratio, extrude and granulate in a mold, sieve the granulated material, put it in an oven for drying, and obtain the bio-carbon-based slow-release fertilizer after cooling.
2、改性生物碳制备方法: 2. Preparation method of modified biochar:
(1)将收集的香榧果壳粉碎过80目筛。 (1) Crush the collected torreya husks through an 80-mesh sieve.
(2)取100g上述粉碎后的香榧果壳加入1.0mol/L的稀盐酸25ml搅拌混匀,密封静置24h,再加入0.1mol/L硝酸铯溶液2ml混匀密封静置12h,自然风干。 (2) Take 100g of the above pulverized Torreya husk, add 25ml of 1.0mol/L dilute hydrochloric acid, stir and mix, seal and let stand for 24h, then add 2ml of 0.1mol/L cesium nitrate solution, mix evenly, seal and let stand for 12h, then air dry naturally.
(3)将上述处理过得生物质置于瓷坩埚中压实,盖上盖子在600℃环境下厌氧热解3小时,升温速度为10℃/min;热解反应结束后,待坩埚冷却至室温后取出。 (3) Put the above treated biomass in a porcelain crucible for compaction, put the lid on and perform anaerobic pyrolysis at 600°C for 3 hours, with a heating rate of 10°C/min; after the pyrolysis reaction is completed, cool the crucible Remove from room temperature.
(4)将上述制备生物碳与100ml浓度为8%的H2O2混匀,在振荡器中震荡24h取出,用蒸馏水洗净后烘干,即获得高吸附性能生物碳。 (4) Mix the above prepared biochar with 100ml of 8% H 2 O 2 , shake it in a shaker for 24 hours, take it out, wash it with distilled water and dry it to obtain biochar with high adsorption performance.
(5)将上述制备的生物炭置入密闭容器中,加入25ml浓度为25%的氨水、0.5mol/L硝酸铂溶液1ml后加热反应,反应2小时后取出。反应期间调节反应容器压力,使其维持在8个标准大气压。 (5) Put the above-prepared biochar into an airtight container, add 25ml of 25% ammonia water and 1ml of 0.5mol/L platinum nitrate solution, heat for reaction, and take it out after 2 hours of reaction. During the reaction, the pressure of the reaction vessel was adjusted to maintain 8 standard atmospheres.
实施例6Example 6
生物碳基缓释肥料施用试验例: Biochar-based slow-release fertilizer application test example:
盆栽试验: Pot test:
1、本试验共设两个处理,即对照组和试验组。试验釆用盆栽种植,盆钵口径30cm、底径20cm、高30cm,每盆装土8kg。以普通施肥(施普通复混肥5g为基肥)为对照,施用5g自制缓释肥料为试验组,以水稻为供试作物,移栽后全生育期保持2-3cm水层。4月播种,5月移栽,每盆1穴,每穴1苗。每一处理均重复三次。 1. There are two treatments in this experiment, namely the control group and the test group. The test adopts potted planting, the diameter of the pot is 30cm, the bottom diameter is 20cm, the height is 30cm, and the soil in each pot is 8kg. Common fertilization (5g of common compound fertilizer as base fertilizer) was used as the control, 5g of self-made slow-release fertilizer was used as the test group, rice was used as the test crop, and a 2-3cm water layer was maintained throughout the growth period after transplanting. Sowing in April, transplanting in May, 1 hole per pot, 1 seedling per hole. Each treatment was repeated three times.
2、试验结果:试验结果显示,对照组植株于9月2日收割,植株生物量238g,谷粒102g;对照组植株根系发达,植株生长健壮,抽穗期较对照组推迟5-10天,成熟期较对照组推迟10-15天。收获后植株生物量较对照组高5%-15%,谷粒产量高2%-10%。将植株收获后的土壤风干,分析测试发现试验组土壤TN、TP、TK有机质较对照土壤高25%-30%、15%-23%、16%-24%、23%-29%。 2. Test results: The test results showed that the plants in the control group were harvested on September 2, with a plant biomass of 238g and grains of 102g; The period was delayed by 10-15 days compared with the control group. After harvest, the plant biomass was 5%-15% higher than that of the control group, and the grain yield was 2%-10% higher. After the plants were harvested, the soil was air-dried, and the analysis and testing found that the organic matter of the soil TN, TP, and TK in the test group was 25%-30%, 15%-23%, 16%-24%, and 23%-29% higher than that of the control soil.
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| US11124461B2 (en) | 2019-07-04 | 2021-09-21 | Incitec Pivot Limited | Fertilizer |
| US11691929B2 (en) | 2019-07-04 | 2023-07-04 | Incitec Fertilizers Pty Limited | Fertiliser |
| CN115735716A (en) * | 2022-11-23 | 2023-03-07 | 浙江省农业科学院 | Culture medium and preparation method thereof |
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