CN106187451A - A kind of method preparing selenium-rich crops cultivation matrix with marc biomass carbon - Google Patents
A kind of method preparing selenium-rich crops cultivation matrix with marc biomass carbon Download PDFInfo
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- CN106187451A CN106187451A CN201610522461.4A CN201610522461A CN106187451A CN 106187451 A CN106187451 A CN 106187451A CN 201610522461 A CN201610522461 A CN 201610522461A CN 106187451 A CN106187451 A CN 106187451A
- Authority
- CN
- China
- Prior art keywords
- selenium
- biochar
- enriched
- marc
- biomass carbon
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- Pending
Links
- 239000011669 selenium Substances 0.000 title claims abstract description 284
- 229910052711 selenium Inorganic materials 0.000 title claims abstract description 272
- BUGBHKTXTAQXES-UHFFFAOYSA-N Selenium Chemical compound [Se] BUGBHKTXTAQXES-UHFFFAOYSA-N 0.000 title claims abstract description 271
- 238000000034 method Methods 0.000 title claims abstract description 35
- 239000011159 matrix material Substances 0.000 title claims description 24
- 239000002028 Biomass Substances 0.000 title claims description 22
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 title claims description 17
- 229910052799 carbon Inorganic materials 0.000 title claims description 17
- 239000000758 substrate Substances 0.000 claims abstract description 53
- 235000015097 nutrients Nutrition 0.000 claims abstract description 38
- 239000008187 granular material Substances 0.000 claims abstract description 26
- 238000003756 stirring Methods 0.000 claims abstract description 17
- 238000002156 mixing Methods 0.000 claims abstract description 7
- 229920000881 Modified starch Polymers 0.000 claims abstract description 6
- 239000004368 Modified starch Substances 0.000 claims abstract description 6
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- 239000000243 solution Substances 0.000 claims description 42
- 239000003610 charcoal Substances 0.000 claims description 22
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 22
- 229920002472 Starch Polymers 0.000 claims description 19
- 235000019698 starch Nutrition 0.000 claims description 19
- 239000008107 starch Substances 0.000 claims description 19
- 238000000197 pyrolysis Methods 0.000 claims description 16
- 239000011734 sodium Substances 0.000 claims description 16
- 239000000463 material Substances 0.000 claims description 14
- 238000010438 heat treatment Methods 0.000 claims description 13
- 239000000203 mixture Substances 0.000 claims description 13
- 239000003415 peat Substances 0.000 claims description 13
- 239000002893 slag Substances 0.000 claims description 13
- 239000010902 straw Substances 0.000 claims description 13
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 12
- 239000012266 salt solution Substances 0.000 claims description 12
- 150000003342 selenium Chemical class 0.000 claims description 11
- 238000005507 spraying Methods 0.000 claims description 10
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- 235000019362 perlite Nutrition 0.000 claims description 8
- 239000010451 perlite Substances 0.000 claims description 8
- 239000011781 sodium selenite Substances 0.000 claims description 8
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- 239000012286 potassium permanganate Substances 0.000 claims description 6
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- 239000002253 acid Substances 0.000 claims description 4
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- 239000004328 sodium tetraborate Substances 0.000 claims description 4
- 235000010339 sodium tetraborate Nutrition 0.000 claims description 4
- 235000013162 Cocos nucifera Nutrition 0.000 claims description 3
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- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 3
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- 229910003424 Na2SeO3 Inorganic materials 0.000 claims 1
- 241000220324 Pyrus Species 0.000 claims 1
- 238000007171 acid catalysis Methods 0.000 claims 1
- 239000007788 liquid Substances 0.000 claims 1
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- 239000001117 sulphuric acid Substances 0.000 claims 1
- 235000011149 sulphuric acid Nutrition 0.000 claims 1
- 239000002023 wood Substances 0.000 claims 1
- 239000011230 binding agent Substances 0.000 abstract description 17
- 238000010521 absorption reaction Methods 0.000 abstract description 13
- 239000000945 filler Substances 0.000 abstract description 11
- 230000012010 growth Effects 0.000 abstract description 8
- 238000002360 preparation method Methods 0.000 abstract description 7
- 238000005469 granulation Methods 0.000 abstract description 5
- 230000003179 granulation Effects 0.000 abstract description 5
- 230000009466 transformation Effects 0.000 abstract description 4
- 229940091258 selenium supplement Drugs 0.000 description 242
- 235000013311 vegetables Nutrition 0.000 description 27
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- 238000005516 engineering process Methods 0.000 description 10
- 238000006243 chemical reaction Methods 0.000 description 7
- BVTBRVFYZUCAKH-UHFFFAOYSA-L disodium selenite Chemical compound [Na+].[Na+].[O-][Se]([O-])=O BVTBRVFYZUCAKH-UHFFFAOYSA-L 0.000 description 7
- 229960001471 sodium selenite Drugs 0.000 description 7
- 235000015921 sodium selenite Nutrition 0.000 description 7
- 240000008067 Cucumis sativus Species 0.000 description 6
- 235000010799 Cucumis sativus var sativus Nutrition 0.000 description 6
- 235000002597 Solanum melongena Nutrition 0.000 description 6
- 244000061458 Solanum melongena Species 0.000 description 6
- 240000009088 Fragaria x ananassa Species 0.000 description 5
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- 238000004519 manufacturing process Methods 0.000 description 5
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- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 4
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- 241000282412 Homo Species 0.000 description 4
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- 229910052698 phosphorus Inorganic materials 0.000 description 4
- 239000004576 sand Substances 0.000 description 4
- JPJALAQPGMAKDF-UHFFFAOYSA-N selenium dioxide Chemical compound O=[Se]=O JPJALAQPGMAKDF-UHFFFAOYSA-N 0.000 description 4
- 238000001179 sorption measurement Methods 0.000 description 4
- 239000007921 spray Substances 0.000 description 4
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- 235000003228 Lactuca sativa Nutrition 0.000 description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 3
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 3
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- 238000002474 experimental method Methods 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- 229910052757 nitrogen Inorganic materials 0.000 description 3
- 239000011574 phosphorus Substances 0.000 description 3
- 229910052700 potassium Inorganic materials 0.000 description 3
- 239000011591 potassium Substances 0.000 description 3
- 239000011573 trace mineral Substances 0.000 description 3
- 235000013619 trace mineral Nutrition 0.000 description 3
- 239000010455 vermiculite Substances 0.000 description 3
- 235000019354 vermiculite Nutrition 0.000 description 3
- 229910052902 vermiculite Inorganic materials 0.000 description 3
- PMYDPQQPEAYXKD-UHFFFAOYSA-N 3-hydroxy-n-naphthalen-2-ylnaphthalene-2-carboxamide Chemical compound C1=CC=CC2=CC(NC(=O)C3=CC4=CC=CC=C4C=C3O)=CC=C21 PMYDPQQPEAYXKD-UHFFFAOYSA-N 0.000 description 2
- 244000298697 Actinidia deliciosa Species 0.000 description 2
- 235000009436 Actinidia deliciosa Nutrition 0.000 description 2
- 244000144730 Amygdalus persica Species 0.000 description 2
- 244000099147 Ananas comosus Species 0.000 description 2
- 235000007119 Ananas comosus Nutrition 0.000 description 2
- CIWBSHSKHKDKBQ-JLAZNSOCSA-N Ascorbic acid Chemical compound OC[C@H](O)[C@H]1OC(=O)C(O)=C1O CIWBSHSKHKDKBQ-JLAZNSOCSA-N 0.000 description 2
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 2
- 244000241235 Citrullus lanatus Species 0.000 description 2
- 235000012828 Citrullus lanatus var citroides Nutrition 0.000 description 2
- 235000007688 Lycopersicon esculentum Nutrition 0.000 description 2
- 240000005561 Musa balbisiana Species 0.000 description 2
- 235000018290 Musa x paradisiaca Nutrition 0.000 description 2
- 240000007594 Oryza sativa Species 0.000 description 2
- 235000007164 Oryza sativa Nutrition 0.000 description 2
- 235000006040 Prunus persica var persica Nutrition 0.000 description 2
- 235000014443 Pyrus communis Nutrition 0.000 description 2
- 240000003768 Solanum lycopersicum Species 0.000 description 2
- 235000009754 Vitis X bourquina Nutrition 0.000 description 2
- 235000012333 Vitis X labruscana Nutrition 0.000 description 2
- 240000006365 Vitis vinifera Species 0.000 description 2
- 235000014787 Vitis vinifera Nutrition 0.000 description 2
- 239000003463 adsorbent Substances 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 235000013339 cereals Nutrition 0.000 description 2
- 239000011651 chromium Substances 0.000 description 2
- 229910052804 chromium Inorganic materials 0.000 description 2
- 238000012272 crop production Methods 0.000 description 2
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- 238000003306 harvesting Methods 0.000 description 2
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- 239000002609 medium Substances 0.000 description 2
- 230000000813 microbial effect Effects 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 230000008635 plant growth Effects 0.000 description 2
- 235000009566 rice Nutrition 0.000 description 2
- 125000003748 selenium group Chemical group *[Se]* 0.000 description 2
- 229910052708 sodium Inorganic materials 0.000 description 2
- 229960001881 sodium selenate Drugs 0.000 description 2
- 239000011655 sodium selenate Substances 0.000 description 2
- 235000018716 sodium selenate Nutrition 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000013589 supplement Substances 0.000 description 2
- 235000009434 Actinidia chinensis Nutrition 0.000 description 1
- 244000247812 Amorphophallus rivieri Species 0.000 description 1
- 235000001206 Amorphophallus rivieri Nutrition 0.000 description 1
- 244000003416 Asparagus officinalis Species 0.000 description 1
- 235000005340 Asparagus officinalis Nutrition 0.000 description 1
- 235000017166 Bambusa arundinacea Nutrition 0.000 description 1
- 235000017491 Bambusa tulda Nutrition 0.000 description 1
- 240000007124 Brassica oleracea Species 0.000 description 1
- 235000003899 Brassica oleracea var acephala Nutrition 0.000 description 1
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- 235000001169 Brassica oleracea var oleracea Nutrition 0.000 description 1
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- 235000000536 Brassica rapa subsp pekinensis Nutrition 0.000 description 1
- 241000499436 Brassica rapa subsp. pekinensis Species 0.000 description 1
- 235000008534 Capsicum annuum var annuum Nutrition 0.000 description 1
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- 244000234623 Coprinus comatus Species 0.000 description 1
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- 241001264174 Cordyceps militaris Species 0.000 description 1
- 235000019750 Crude protein Nutrition 0.000 description 1
- ZZZCUOFIHGPKAK-UHFFFAOYSA-N D-erythro-ascorbic acid Natural products OCC1OC(=O)C(O)=C1O ZZZCUOFIHGPKAK-UHFFFAOYSA-N 0.000 description 1
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 1
- 235000016640 Flammulina velutipes Nutrition 0.000 description 1
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- 235000015334 Phyllostachys viridis Nutrition 0.000 description 1
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- 229920000297 Rayon Polymers 0.000 description 1
- 206010039921 Selenium deficiency Diseases 0.000 description 1
- 102000008114 Selenoproteins Human genes 0.000 description 1
- 108010074686 Selenoproteins Proteins 0.000 description 1
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- 238000009825 accumulation Methods 0.000 description 1
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- 238000013461 design Methods 0.000 description 1
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- 238000011065 in-situ storage Methods 0.000 description 1
- 235000010485 konjac Nutrition 0.000 description 1
- 239000000252 konjac Substances 0.000 description 1
- 235000021190 leftovers Nutrition 0.000 description 1
- 239000003446 ligand Substances 0.000 description 1
- 231100000053 low toxicity Toxicity 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 239000000618 nitrogen fertilizer Substances 0.000 description 1
- 239000013110 organic ligand Substances 0.000 description 1
- 231100000572 poisoning Toxicity 0.000 description 1
- 230000000607 poisoning effect Effects 0.000 description 1
- 229920001282 polysaccharide Polymers 0.000 description 1
- 239000005017 polysaccharide Substances 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000004321 preservation Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 239000006041 probiotic Substances 0.000 description 1
- 235000018291 probiotics Nutrition 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000013138 pruning Methods 0.000 description 1
- 238000010298 pulverizing process Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 230000005070 ripening Effects 0.000 description 1
- 229940082569 selenite Drugs 0.000 description 1
- MCAHWIHFGHIESP-UHFFFAOYSA-L selenite(2-) Chemical compound [O-][Se]([O-])=O MCAHWIHFGHIESP-UHFFFAOYSA-L 0.000 description 1
- -1 selenium polysaccharides Chemical class 0.000 description 1
- 230000009919 sequestration Effects 0.000 description 1
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Classifications
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
-
- 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
-
- 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
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Organic Chemistry (AREA)
- Environmental Sciences (AREA)
- Pest Control & Pesticides (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Cultivation Of Plants (AREA)
Abstract
一种用果渣生物质炭制备富硒作物栽培基质的方法,其特征在于:依次包括下列步骤:第一步,制备果渣生物质炭;第二步,制备硒营养液;第三步,制备富硒生物炭:(1)制得加温态富硒生物炭;(2)制得常温态富硒生物炭;(3)将加温态富硒生物炭与常温态富硒生物炭混合制成富硒生物炭;第四步,制备改性淀粉粘结剂;第五步,制备硒生物炭颗粒剂;第六步,取富硒生物炭与硒生物炭颗粒剂,将二者混合送入造粒机造粒中;第七步,将第六步制得的颗粒与作物无土栽培基质填充料搅拌均匀,得富硒作物栽培基质。使用本发明的方法制备出的富硒栽培基质能够提高作物对硒元素的吸收转化率,并且硒元素能够在作物整个生长周期内缓慢、均匀释放。
A method for preparing a selenium-enriched crop cultivation substrate with pomace biochar, characterized in that: the following steps are sequentially included: the first step, preparing pomace biochar; the second step, preparing selenium nutrient solution; the third step, Preparation of selenium-enriched biochar: (1) preparation of heated selenium-enriched biochar; (2) preparation of normal temperature selenium-enriched biochar; (3) mixing of heated selenium-enriched biochar with normal temperature selenium-enriched biochar Make selenium-enriched biochar; the fourth step, prepare modified starch binder; the fifth step, prepare selenium biochar granules; the sixth step, take selenium-enriched biochar and selenium biochar granules, and mix the two Sending it into a granulator for granulation; in the seventh step, stirring evenly the granules prepared in the sixth step with the crop soilless cultivation substrate filler to obtain a selenium-enriched crop cultivation substrate. The selenium-enriched cultivation substrate prepared by the method of the invention can improve the absorption and transformation rate of selenium element by crops, and the selenium element can be released slowly and uniformly in the whole growth cycle of crops.
Description
技术领域technical field
本发明涉及一种无土栽培基质及其制备方法,尤其涉及一种用果渣生物质炭制备富硒作物栽培基质的方法。The invention relates to a soilless cultivation substrate and a preparation method thereof, in particular to a method for preparing a selenium-enriched crop cultivation substrate by using pomace biochar.
背景技术Background technique
硒是一种人体必需微量元素,是谷胱甘肽过氧化物酶(GSH-Px) 的活性中心,适量补硒有增强机体免疫力,延缓衰老,防癌抗癌的效果。然而,我国是一个贫硒的国家,富硒农产品是人体补充硒元素有效途径。蔬菜中的硒分为无机硒和有机硒两大类,前者包括硒酸盐、亚硒酸盐等,无机硒对于人和动物来说吸收效果差,毒性风险大,使用不当极易造成硒中毒;后者主要包括硒代氨基酸、硒代蛋白、硒多糖等形态,对人和动物来说吸收效果好,毒性小,更适合补硒的要求。因此通过作物施硒,使无机硒转化为有机硒,提高人或动物体内硒含量是公认的一条安全、有效的补硒途径,对防治人体硒缺乏具有重要的现实意义。目前作物施硒主要有以下几种方式:Selenium is an essential trace element for the human body, and it is the active center of glutathione peroxidase (GSH-Px). Supplementing selenium in an appropriate amount can enhance the body's immunity, delay aging, and prevent and fight cancer. However, my country is a selenium-deficient country, and selenium-enriched agricultural products are an effective way for the human body to supplement selenium. Selenium in vegetables is divided into two categories: inorganic selenium and organic selenium. The former includes selenate, selenite, etc. Inorganic selenium is poorly absorbed by humans and animals, and has a high risk of toxicity. Improper use can easily cause selenium poisoning The latter mainly includes selenoamino acids, selenoproteins, selenium polysaccharides and other forms, which have good absorption effect and low toxicity for humans and animals, and are more suitable for the requirements of selenium supplementation. Therefore, applying selenium to crops to convert inorganic selenium into organic selenium and increasing the selenium content in humans or animals is a recognized safe and effective way to supplement selenium, which has important practical significance for the prevention and treatment of selenium deficiency in humans. At present, there are mainly the following ways to apply selenium to crops:
一是在天然富硒地区种植富集能力较强的农作物,此方法对硒含量定量控制困难,且存在地域局限性,不利于大规模的标准化生产,尤其是我国绝大部分地区属贫硒地区,无条件做到。One is to plant crops with strong enrichment ability in natural selenium-rich areas. This method is difficult to quantitatively control selenium content, and there are geographical limitations, which is not conducive to large-scale standardized production, especially in most areas of my country that are selenium-deficient areas , do it unconditionally.
二是在农作物收获前喷施无机硒溶液,使农作物可以迅速吸收无机硒从而达到富硒水平。如中国专利CN1594234A、CN101182246A 等。该方法中富硒营养剂实施方式较为复杂,需喷施5~6次,而且最终农作物中无机硒残留量很大,由于无机硒吸收前必须先与肠道中的有机配体结合才能被机体吸收利用,而肠道中存在着多种元素与硒竞争有限配体,不利于人体吸收利用,而且无机硒对机体有明显的毒害作用。The second is to spray the inorganic selenium solution before the crops are harvested, so that the crops can quickly absorb the inorganic selenium to reach the selenium-enriched level. Such as Chinese patents CN1594234A, CN101182246A and so on. In this method, the implementation of the selenium-enriched nutrient is relatively complicated, and it needs to be sprayed 5 to 6 times, and the residual amount of inorganic selenium in the final crops is large. Before the absorption of inorganic selenium, it must be combined with the organic ligand in the intestinal tract before it can be absorbed by the body. However, there are a variety of elements in the intestinal tract that compete with selenium for limited ligands, which is not conducive to the absorption and utilization of the human body, and inorganic selenium has obvious toxic effects on the body.
三是追施富硒肥料,如中国专利CN101734971A。此方法可以保证农作物达到富硒标准,无无机硒残留,提高蔬菜有机硒含量。但因为农作物大田施肥,硒肥利用率低,大量的硒容易随着灌溉水和雨水淋入深层土壤或河流中,而且流失的硒容易增加土壤和水体环境中硒的负担,长期使用易导致硒污染。The 3rd, topdressing selenium-enriched fertilizer, as Chinese patent CN101734971A. The method can ensure that the crops can reach the selenium-rich standard without inorganic selenium residues, and can increase the organic selenium content of vegetables. However, due to the fertilization of crops in large fields, the utilization rate of selenium fertilizer is low, and a large amount of selenium is easy to drip into the deep soil or rivers with irrigation water and rainwater, and the lost selenium is easy to increase the burden of selenium in the soil and water environment, and long-term use is easy to cause selenium. pollute.
据相关统计,化肥投入约占农民进行种植业生产总投入的50%左右,发展中国家粮食增产中50%来自于化肥的作用。但目前我国当季氮肥利用率仅为20%~35%, 磷肥的利用率为10%~20%,钾肥的利用率为30%~60%,远低于世界发达国家利用水平。硒作为一种微量元素,其利用率的提高也是我国农业科技工作者亟待需要解决的问题。According to relevant statistics, the input of chemical fertilizers accounts for about 50% of the total input of farmers in planting production, and 50% of the increase in grain production in developing countries comes from the role of chemical fertilizers. But at present, the utilization rate of nitrogen fertilizer in the current season in my country is only 20%-35%, the utilization rate of phosphorus fertilizer is 10%-20%, and the utilization rate of potassium fertilizer is 30%-60%, which is far lower than the utilization level of developed countries in the world. Selenium is a trace element, and the improvement of its utilization rate is also an urgent problem to be solved by agricultural science and technology workers in our country.
生物炭是一类由生物质在300℃~700℃低温条件下热解炭化形成的高度芳香化难熔性固态物质,具有较高的比表面积、孔隙结构、一定的机械强度和较小的堆积密度,这使生物炭具有较高的吸附性能。生物炭具有增加土壤碳库储量,改良土壤,提高土壤肥力,促进作物增产和维系土壤生态系统平衡的作用。不仅如此,高度稳定性、经济性、固碳减排和对N、P等养分的专性吸附与持留特性,使其成为一种理想的肥料吸附剂。另一方面,我国农作物秸秆生物质资源丰富,但主要采用露天简易焚烧方式进行处理处置,资源浪费和环境污染极其严重。如能将价廉易得的农作物秸秆生物质原料经适当加工制备成适用于硒元素的吸附剂,再将含硒生物炭融入基质原料从而制备环境友好型富含硒的蔬菜栽培基质,不仅可以有效解决农作物秸秆处置难题,使农作物秸秆废弃物资源得到高效利用,而且可以对促进蔬菜对硒元素的高效转化与富集。Biochar is a kind of highly aromatized refractory solid material formed by pyrolysis and carbonization of biomass at a low temperature of 300 ° C to 700 ° C. It has a high specific surface area, pore structure, certain mechanical strength and small accumulation. Density, which gives biochar a high adsorption performance. Biochar can increase soil carbon storage, improve soil, improve soil fertility, promote crop production and maintain the balance of soil ecosystem. Not only that, high stability, economy, carbon sequestration and emission reduction, and the specific adsorption and retention characteristics of N, P and other nutrients make it an ideal fertilizer adsorbent. On the other hand, my country is rich in crop straw biomass resources, but it is mainly treated and disposed of by open-air simple incineration, which leads to extremely serious waste of resources and environmental pollution. If the cheap and easy-to-get crop straw biomass raw material can be properly processed into an adsorbent suitable for selenium, and then selenium-containing biochar can be incorporated into the substrate material to prepare an environmentally friendly selenium-rich vegetable cultivation substrate, not only can Effectively solve the problem of crop straw disposal, make efficient use of crop straw waste resources, and can promote the efficient transformation and enrichment of selenium in vegetables.
期刊论文“硒肥对马铃薯硒素吸收、转化及产量、品质的影响”(殷金岩,耿增超,李致颖等2015,35(3):823—829)报道一种生物炭基硒肥及其使用效果,在适宜施硒量(0.379kg/hm2)时马铃薯产量提高了4.87%~5.44%,粗蛋白含量增加了12.18%~20.03%,还原糖提高了6.45%~12.90%,维生素C含量提高了-0.54%~3.1l%,有机硒转化率增加13.00%~15.10%,淀粉含量增加了-0.73%~1.12%。生物炭基硒肥是由硒酸钠与生物炭在实验室通过吸附反应制备而成,生物炭与硒的配比为176:1。其中,生物炭由间歇式热裂解中试设备生产并过1mm筛孔。硒源为分析纯Na2Se04·10H20。文中报道的生物炭基硒肥从本质上看,是一种施用于土壤之中的肥料,需经科学试验后确定应用于各种蔬菜作物的施用量及施用技术后,方能使用,增加了施用难度。The journal paper "Effects of Selenium Fertilizer on Potato Selenium Absorption, Transformation, Yield and Quality" (Yin Jinyan, Geng Zengchao, Li Zhiying et al. 2015, 35(3): 823-829) reported a biochar-based selenium fertilizer and its application effect, When the appropriate amount of selenium (0.379kg/hm 2 ) was applied, the potato yield increased by 4.87%-5.44%, the crude protein content increased by 12.18%-20.03%, the reducing sugar increased by 6.45%-12.90%, and the vitamin C content increased- 0.54%~3.1l%, the conversion rate of organic selenium increased by 13.00%~15.10%, and the starch content increased by -0.73%~1.12%. Biochar-based selenium fertilizer is prepared by adsorption reaction of sodium selenate and biochar in the laboratory. The ratio of biochar to selenium is 176:1. Among them, biochar is produced by batch pyrolysis pilot equipment and passed through a 1mm sieve. The selenium source is analytically pure Na 2 Se0 4 ·10H 2 0. The biochar-based selenium fertilizer reported in this article is essentially a fertilizer applied to the soil. It can only be used after scientific experiments to determine the application amount and application technology applied to various vegetable crops. Difficulty of application.
中国专利“一组远红外线功能富硒富铬微生物菌肥及其制备方法”(公开号104692903A),提供一种以人工培育的富硒富铬蛹虫草的栽培基质(即下脚料)和生物碳(竹炭、木炭及桔杆等废弃物烧制的炭)为主要原料配伍的微生物菌肥。The Chinese patent "A group of far-infrared functional selenium-rich chromium-rich microbial fertilizers and its preparation method" (publication number 104692903A) provides a cultivation substrate (i.e. leftovers) and biochar of artificially cultivated selenium-rich chromium-rich Cordyceps militaris (Charcoal fired from waste such as bamboo charcoal, charcoal, and orange stalks) is a microbial fertilizer that is compatible with the main raw materials.
中国专利CN104177194A 公开了一种炭基硒肥的制备方法,将培养好的微生物通过过滤的方式使微生物从培养基中附着到生物炭表面,之后将富含硒元素的营养液浸没生物炭,使农作物益生菌和生物炭能充分接触吸收营养液中硒元素及其他农作物所需元素,并原位还原硒元素为单质硒,最终产出富含硒元素的炭基硒肥。Chinese patent CN104177194A discloses a method for preparing a carbon-based selenium fertilizer. The cultured microorganisms are filtered from the culture medium to attach the microorganisms to the surface of the biochar, and then the nutrient solution rich in selenium is immersed in the biochar to make the Crop probiotics and biochar can fully contact and absorb selenium in nutrient solution and other elements needed by crops, and in situ reduce selenium to elemental selenium, and finally produce carbon-based selenium fertilizer rich in selenium.
上述3例均采用有效成分硒制得一种用于土壤施用的硒肥。但是,硒肥的最大问题是施用技术难以掌握,通常需要在对各种作物进行专门试验后,提出施用量、施用方法等,再推荐给使用者。其次,即使农民掌握了施用技术,由于蔬菜大田施肥,硒肥利用率低,大量的硒容易随着灌溉水和雨水淋入深层土壤或河流中,而且流失的硒容易增加土壤和水体环境中硒的负担,长期使用易导致硒污染。再次,由于耕作层的深度不同,施用硒肥难以做到精确定量,容易造成肥料浪费。Above-mentioned 3 examples all adopt active ingredient selenium to make a kind of selenium fertilizer for soil application. However, the biggest problem with selenium fertilizer is that it is difficult to master the application technology. It is usually necessary to propose the application amount, application method, etc. after conducting special experiments on various crops, and then recommend them to users. Secondly, even if farmers have mastered the application technology, due to fertilization of vegetables in large fields, the utilization rate of selenium fertilizer is low, and a large amount of selenium is easy to drip into the deep soil or rivers with irrigation water and rainwater, and the lost selenium is easy to increase the amount of selenium in the soil and water environment. The burden of long-term use can easily lead to selenium pollution. Thirdly, due to the different depths of the cultivated layers, it is difficult to apply selenium fertilizer accurately and quantitatively, and it is easy to cause waste of fertilizer.
中国专利CN104585001A 公开了一种提高茄子有机硒含量的无土栽培方法,该方法操作步骤为首先制备含纳米硒的无土栽培基质,然后选取健壮的茄子苗,对茄子苗进行根部消毒后移植到温室大棚内的定制槽内,填入含纳米硒的无土栽培基质,以常规方法对茄子进行整枝、病害防治和促花保果等管理,果实成熟后采摘,得到有机硒含量高的茄子。Chinese patent CN104585001A discloses a soilless cultivation method for increasing the organic selenium content of eggplant. The operation steps of the method are firstly preparing a soilless cultivation substrate containing nano-selenium, and then selecting robust eggplant seedlings, disinfecting the roots of the eggplant seedlings and transplanting them to The custom-made tanks in the greenhouse are filled with soilless cultivation substrates containing nano-selenium, and the eggplants are managed by conventional methods such as pruning, disease control, flower promotion and fruit preservation, and the fruits are picked after ripening to obtain eggplants with high organic selenium content.
中国专利CN104591866A 公开了一种含纳米硒的无土栽培基质及其制备方法。该发明公开内容为,一种含纳米硒的无土栽培基质包括动物尿液、农作物秸秆、工农业副产物、二氧化硒和机制砂等原料,通过将动物尿液、农作物秸秆、工农业废弃物、二氧化硒混合进行发酵,得到含纳米硒的腐熟有机质,将腐熟有机质与机制砂混合制成含纳米硒的无土栽培基质。Chinese patent CN104591866A discloses a soilless cultivation substrate containing nano-selenium and a preparation method thereof. The disclosed content of the invention is that a soilless cultivation substrate containing nano-selenium includes raw materials such as animal urine, crop straw, industrial and agricultural by-products, selenium dioxide, and machine-made sand. The fermented material and selenium dioxide are mixed to obtain decomposed organic matter containing nano-selenium, and the decomposed organic matter is mixed with machine-made sand to make a soilless culture substrate containing nano-selenium.
以上技术的共性是采用纳米硒植物营养剂,再配合其他基质材料复合而成,其效果一般。The commonality of the above technologies is that the nano-selenium plant nutrient is combined with other matrix materials, and the effect is average.
期刊论文“基质施硒对生菜富硒效果及品质的影响”(山西农业科学2013,41(1):57—59)报道了一种在蔬菜栽培基质中添加硒的方法。供试硒为分析纯亚硒酸钠(Na2SeO3)试剂。先将草炭和珍珠岩按体积比2:1的比例配制成混合基质。共设5个梯度的亚硒酸钠处理,基质施硒量分别为0、0.3、0.6、1.2、2.5mg/kg,将亚硒酸钠配制成溶液后,用小型喷雾器喷入基质中,并与基质充分混匀。采用这种技术制备的基质,工艺较简单,基质对硒元素的缓释能力有限,硒元素易于短时间内快速释放,与作物吸收机制不协调,故效果一般,硒转化率较低。The journal paper "Effect of Substrate Selenium Application on Selenium Enrichment Effect and Quality of Lettuce" (Shanxi Agricultural Sciences 2013, 41(1):57-59) reported a method of adding selenium to vegetable cultivation substrate. The tested selenium is analytically pure sodium selenite (Na 2 SeO 3 ) reagent. First, peat and perlite are prepared into a mixed matrix at a volume ratio of 2:1. There are 5 gradients of sodium selenite treatment, the amount of selenium applied to the substrate is 0, 0.3, 0.6, 1.2, 2.5 mg/kg respectively, after sodium selenite is formulated into a solution, it is sprayed into the substrate with a small sprayer, and Mix well with base. The matrix prepared by this technology has a relatively simple process, and the matrix has limited slow-release ability of selenium. Selenium is easy to be released quickly in a short period of time, which is not coordinated with the absorption mechanism of crops. Therefore, the effect is general and the conversion rate of selenium is low.
为此,如何提供一种采用农作物秸秆生物质炭制备高吸收率、高转化率并且硒元素在作物的整个生长周期内缓慢释放的富硒蔬菜栽培基质的方法成为本发明的研究课题。Therefore, how to provide a method for preparing a selenium-enriched vegetable cultivation substrate with high absorption rate and high conversion rate and slow release of selenium element throughout the whole growth cycle of crops by using crop straw biochar has become the research topic of the present invention.
发明内容Contents of the invention
本发明提供一种用果渣生物质炭制备富硒作物栽培基质的方法,其目的在于解决现有的蔬菜栽培基质对于硒元素吸收转化率低的问题。The invention provides a method for preparing a selenium-enriched crop cultivation substrate by using pomace biomass charcoal, and aims to solve the problem that the existing vegetable cultivation substrate has a low absorption conversion rate of selenium element.
为达到上述目的,本发明采用的技术方案是:一种用果渣生物质炭制备富硒作物栽培基质的方法,所述方法依次包括下列步骤:In order to achieve the above object, the technical solution adopted in the present invention is: a method for preparing selenium-enriched crop cultivation substrate with pomace biochar, said method comprising the following steps in turn:
第一步,制备果渣生物质炭,The first step is to prepare pomace biochar,
将果渣在晒干后加入热解炉中,通入氩气,以排除热解炉中的氧气,将热解炉内温度在5分钟之内快速升温至95℃~105℃,然后再以1℃/分钟的升温速率加热至550℃~600℃,并保持25~35分钟,自然冷却至室温后,收集生物质,粉碎,过60目筛子,制得果渣生物质炭;After drying the pomace, put it into the pyrolysis furnace, pass in argon gas to get rid of the oxygen in the pyrolysis furnace, quickly raise the temperature in the pyrolysis furnace to 95°C~105°C within 5 minutes, and then Heating at a heating rate of 1°C/min to 550°C~600°C, and keeping it for 25~35 minutes, after natural cooling to room temperature, collect the biomass, crush it, and pass it through a 60-mesh sieve to obtain pomace biochar;
第二步,制备硒营养液,The second step is to prepare selenium nutrient solution,
将Na2Se04·10H2O或Na2SeO3与水按重量比1:20~1:40溶解制成硒盐溶液,再向硒盐溶液加入酸剂以调节硒盐溶液的pH到4.5~5.5,制得硒营养液;Dissolve Na 2 Se0 4 ·10H 2 O or Na 2 SeO 3 and water at a weight ratio of 1:20~1:40 to make a selenium salt solution, and then add an acid agent to the selenium salt solution to adjust the pH of the selenium salt solution to 4.5 ~5.5, the selenium nutrient solution was prepared;
第三步,制备富硒生物炭:The third step is to prepare selenium-enriched biochar:
(1)将一部分所述第一步制得的果渣生物质炭加热到70℃~100℃,立即将所述硒营养液均匀喷洒在果渣生物质炭上,硒营养液与果渣生物质炭的体积为1:15~1:30,边喷洒边搅拌,制得加温态富硒生物炭;(1) Heating a part of the pomace biochar prepared in the first step to 70°C to 100°C, immediately spraying the selenium nutrient solution evenly on the pomace biochar, the selenium nutrient solution and the pomace biochar The volume of material charcoal is 1:15~1:30, while spraying and stirring, the heated selenium-enriched biochar is obtained;
(2)取另一部分所述第一步制得的果渣生物质炭,在10℃~40℃下将硒营养液均匀喷洒在该果渣生物质炭上,硒营养液与果渣生物质炭的体积为1:15~1:30,边喷洒边搅拌,制得常温态富硒生物炭;(2) Take the pomace biochar prepared in the first step described in the other part, and evenly spray the selenium nutrient solution on the pomace biochar at 10°C~40°C, the selenium nutrient solution and the pomace biomass The volume of charcoal is 1:15~1:30, and it is stirred while spraying to obtain selenium-enriched biochar at normal temperature;
(3)将所述加温态富硒生物炭与所述常温态富硒生物炭混合制成富硒生物炭,其中,加温态富硒生物炭与常温态富硒生物炭的体积比为7:3~6:4;(3) Mixing the heated selenium-enriched biochar and the normal temperature selenium-enriched biochar to make selenium-enriched biochar, wherein the volume ratio of the heated selenium-enriched biochar to the normal temperature selenium-enriched biochar is 7:3~6:4;
第四步,制备改性淀粉粘结剂,The fourth step is to prepare modified starch binder,
首先将50重量份的玉米或木薯淀粉溶解于90~100重量份的水中,不断搅拌下加入2~3重量份的浓硫酸催化,然后加入5重量份高猛酸钾溶液氧化1~1.5小时并不断搅拌,再加入4重量份的氢氧化钠糊化20~30分钟,加入1重量份硼砂交联15~20分钟,最后补加入水充分搅拌后冷却得到质量浓度为0.2~0.5%的淀粉粘结剂;First, 50 parts by weight of corn or tapioca starch are dissolved in 90 to 100 parts by weight of water, 2 to 3 parts by weight of concentrated sulfuric acid are added under constant stirring for catalysis, and then 5 parts by weight of potassium permanganate solution is added to oxidize for 1 to 1.5 hours and Stir continuously, then add 4 parts by weight of sodium hydroxide for gelatinization for 20-30 minutes, add 1 part by weight of borax for cross-linking for 15-20 minutes, and finally add water to fully stir and cool to obtain a starch viscose with a mass concentration of 0.2-0.5%. Binder;
第五步,制备硒生物炭颗粒剂,The fifth step is to prepare selenium biochar granules,
将所述第三步制得的富硒生物炭送入上方具有喷头的搅拌机中,搅拌物料的同时均匀喷洒质量浓度为0.2~0.5%的淀粉粘结剂,所述富硒生物炭与淀粉粘结剂的体积比为95~90:5~10,制得硒生物炭颗粒剂;The selenium-enriched biochar prepared in the third step is sent into a mixer with a nozzle above, and the starch binder with a mass concentration of 0.2 to 0.5% is evenly sprayed while stirring the material, and the selenium-enriched biochar is bonded to the starch. The volume ratio of the binder is 95-90:5-10 to prepare selenium biochar granules;
第六步,取所述第三步制得的富硒生物炭与所述第五步制得的硒生物炭颗粒剂,将二者混合均匀得湿物料,富硒生物炭与硒生物炭颗粒剂的体积比为2~4:8~6,再将所述湿物料送入具有热风机的造粒机中造粒,设定转速为250~300r/min,温度为70~120℃,造粒30~40分钟后,过30目筛;The sixth step is to take the selenium-enriched biochar prepared in the third step and the selenium biochar granules prepared in the fifth step, and mix the two evenly to obtain a wet material, selenium-enriched biochar and selenium biochar granules The volume ratio of the agent is 2~4:8~6, and then the wet material is sent to a granulator with a hot air blower for granulation, the set speed is 250~300r/min, and the temperature is 70~120°C. After granulation for 30~40 minutes, pass through a 30-mesh sieve;
第七步,将所述第六步制得的颗粒与作物无土栽培基质填充料按重量比1:100~1:200搅拌均匀,即制得所述富硒作物栽培基质。In the seventh step, the granules prepared in the sixth step and the crop soilless cultivation substrate filler are evenly stirred at a weight ratio of 1:100 to 1:200 to obtain the selenium-enriched crop cultivation substrate.
上述技术方案中的有关内容解释如下:The relevant content in the above-mentioned technical scheme is explained as follows:
1、上述方案中,所述果渣选自苹果渣、梨渣、桃渣、草莓渣、猕猴桃渣、葡萄渣、西瓜渣、香蕉渣以及菠萝渣中的至少一种;在投入至热解炉之前,将所述果渣晾晒到含水量小于40%,粉碎到颗粒的平均直径不大于10cm。1. In the above scheme, the pomace is selected from at least one of apple pomace, pear pomace, peach pomace, strawberry pomace, kiwi pomace, grape pomace, watermelon pomace, banana pomace and pineapple pomace; Before, the pomace is air-dried until the water content is less than 40%, and crushed until the average diameter of the particles is not greater than 10 cm.
2、上述方案中,所述第二步中加入的酸剂为醋酸或稀盐酸。2. In the above scheme, the acid agent added in the second step is acetic acid or dilute hydrochloric acid.
3、上述方案中,所述第四步中的“重量份”是指以任意重量为1份来表示的含量单位。3. In the above scheme, "parts by weight" in the fourth step refers to a content unit expressed by taking any weight as 1 part.
4、上述方案中,所述作物无土栽培基质填充料的原料为草炭、珍珠岩、椰子壳、沙石、蛭石、锯木屑、炉渣以及玉米秸秆中的至少两种的混合物。无土栽培基质填充料的选取为现有技术,可外购或自制,也可采用其他废弃物制成,并适合植物生长。无土栽培基质填充料的配方举例如下:4. In the above solution, the raw material of the crop soilless culture matrix filler is a mixture of at least two of peat, perlite, coconut shell, sandstone, vermiculite, sawdust, slag and corn stalk. The selection of soilless culture matrix filler is an existing technology, which can be purchased or self-made, and can also be made from other wastes, and is suitable for plant growth. The formula of soilless culture matrix filler is as follows:
(1)7份草炭、3份珍珠岩;(2)1份椰子壳、1份沙;(3)1份草炭、1份蛭石、1份锯木屑;(4)1份草炭、1份锯木屑;(5)1份草炭、1份珍珠岩、1份沙;(6)2份草炭、2份蛭石、5份炉渣、1份珍珠岩;(7)1份草炭、1份炉渣;(8)1份草炭、1份树皮;(9)3份玉米秸杆、2份炉渣;(10)1份玉米秸杆、1份草炭、3份炉渣。(1) 7 parts peat, 3 parts perlite; (2) 1 part coconut shell, 1 part sand; (3) 1 part peat, 1 part vermiculite, 1 part sawdust; (4) 1 part peat, 1 part Sawdust; (5) 1 part peat, 1 part perlite, 1 part sand; (6) 2 parts peat, 2 parts vermiculite, 5 parts slag, 1 part perlite; (7) 1 part peat, 1 part slag ; (8) 1 part of peat, 1 part of bark; (9) 3 parts of corn stalk, 2 parts of slag; (10) 1 part of corn stalk, 1 part of peat, 3 parts of slag.
本发明设计原理是:本发明提出一种富含硒元素的作物无土栽培基质,其特点是采用硒元素缓释技术使得栽培作物在整个生长周期内对硒元素都具有较高的吸收利用率,并且用户无需再施用硒肥料,只需按常规管理施用氮磷钾等大量元素或栽培营养液,因而更易于掌握施用方法,又使蔬菜含硒量控制在安全范围内,生产出安全、优质、洁净的绿色富硒蔬菜,而且对环境也不会造成污染。The design principle of the present invention is: the present invention proposes a crop soilless culture substrate rich in selenium element, which is characterized in that the selenium element slow-release technology is used to make the cultivated crops have a higher absorption and utilization rate of selenium element throughout the growth cycle , and the user does not need to apply selenium fertilizers, but only needs to apply a large number of elements such as nitrogen, phosphorus, potassium or cultivation nutrient solution according to routine management, so it is easier to master the application method, and the selenium content of vegetables is controlled within a safe range to produce safe, high-quality vegetables. , clean green selenium-rich vegetables, and will not cause pollution to the environment.
在本发明的方法的第二步中,将硒营养液调整到酸性的目的是,农作物秸秆生物质炭的pH约为8~10,在后续将硒营养液喷洒到农作物秸秆生物炭上后,有利于将农作物秸秆生物炭的pH从8~10调整到中性7.0左右,从而有利于植物生长。In the second step of the method of the present invention, the purpose of adjusting the selenium nutrient solution to acidity is that the pH of the crop straw biochar is about 8-10, and after the subsequent spraying of the selenium nutrient solution on the crop straw biochar, It is beneficial to adjust the pH of crop straw biochar from 8 to 10 to a neutral value of about 7.0, which is beneficial to plant growth.
在所述第三步中,分别制备加温态富硒生物炭与常温态富硒生物炭,目的在于在70℃~100℃加热条件下增加了生物炭的孔隙度,硒元素更多的被保留在生物炭的微孔中,在加热条件下制得的加温态富硒生物炭在栽培基质中的硒元素的释放时间比常温态富硒生物炭的硒元素释放时间更持久,因此,将加温态富硒生物炭与常温态富硒生物炭二者混合,能够保证硒元素释放期延长以及硒元素在作物的不同生长时期内均匀释放。In the third step, the heated selenium-enriched biochar and the normal-temperature selenium-enriched biochar are prepared respectively, with the purpose of increasing the porosity of the biochar under the heating condition of 70°C to 100°C, and more selenium is absorbed. Retained in the micropores of the biochar, the release time of selenium in the cultivation medium of the heated selenium-enriched biochar prepared under heating conditions is longer than that of the selenium-enriched biochar at normal temperature. Therefore, Mixing the heated selenium-enriched biochar with the normal-temperature selenium-enriched biochar can ensure that the selenium release period is extended and the selenium is evenly released in different growth periods of the crops.
在所述第六步中,由于第三步的富硒生物炭没有经过淀粉粘结剂粘结,而第五步的硒生物炭颗粒剂经过了淀粉粘结剂的包裹,那么二者在无土栽培基质中的硒元素释放速度不同,第五步的硒生物炭颗粒剂硒元素释放速度更慢,第三步的富硒生物炭的硒元素释放速度相对较快,将二者混合均匀造粒可有效控制硒元素在无土栽培基质中的释放速度,保证了在硒元素在作物的不同生长时期内都能有所均匀释放以供作物吸收利用,保证了硒元素释放期的延长;In the sixth step, since the selenium-enriched biochar in the third step is not bonded by a starch binder, and the selenium biochar granules in the fifth step are wrapped by a starch binder, the two are separated in the absence of a starch binder. The release rate of selenium in the soil cultivation substrate is different. The selenium release rate of the selenium biochar granule in the fifth step is slower, and the selenium release rate of the selenium-enriched biochar in the third step is relatively fast. Mix the two evenly to make The grains can effectively control the release rate of selenium in the soilless culture substrate, ensuring that the selenium can be released evenly in different growth periods of the crops for absorption and utilization of the crops, and ensure the extension of the selenium release period;
由于上述技术方案运用,本发明与现有技术相比具有下列优点和效果:Due to the use of the above-mentioned technical solutions, the present invention has the following advantages and effects compared with the prior art:
1、本发明综合运用生物炭的吸附原理及改性淀粉粘结剂的粘结性能,提高了硒元素的吸持及缓释能力,能够保证在3~7个月较长的蔬菜生长周期内的硒元素供应,从而保证了硒元素在作物体内的高转化率,因为生物质炭的具有多孔性、巨大的比表面积、表面负电荷和电荷密度等特性使其能够吸附和固持肥料中的养分,实现其缓释效果,显著削减硒元素流失量,提高土壤肥力,促进作物增产和维持土壤生态系统平衡的作用。1. The present invention comprehensively uses the adsorption principle of biochar and the bonding performance of the modified starch binder to improve the absorption and slow release ability of selenium element, which can ensure that the selenium element can be maintained within a long vegetable growth cycle of 3 to 7 months. Selenium supply, thus ensuring a high conversion rate of selenium in crops, because the characteristics of biochar, such as porosity, huge specific surface area, surface negative charge and charge density, can absorb and hold nutrients in fertilizers , to achieve its slow-release effect, significantly reduce the loss of selenium, improve soil fertility, promote crop production and maintain the balance of the soil ecosystem.
2、本发明运用的硒元素有效载体是Na2SeO4•10H2O或亚硒酸钠(Na2SeO3),Na2SeO4•10H2O或亚硒酸钠(Na2SeO3)是作物更易吸收、更环保的有效载体。2. The effective carrier of selenium used in the present invention is Na 2 SeO 4 •10H 2 O or sodium selenite (Na 2 SeO 3 ), Na 2 SeO 4 •10H 2 O or sodium selenite (Na 2 SeO 3 ) It is an effective carrier that is more easily absorbed by crops and more environmentally friendly.
3、采用本方法制备的基质,根据不同蔬菜作物一生的硒元素需求量做到精确定制,本发明提供的栽培基质无需人工再次添加硒元素,可以直接放入栽培容器内种植各种蔬菜,并且种植后只需按常规管理,施用氮磷钾等大量元素或栽培营养液,因而更易于掌握施用方法,又使蔬菜的含硒量控制在安全范围内,生产出安全、优质、洁净的绿色富硒蔬菜,而且对环境也不会造成污染。3. The substrate prepared by this method can be precisely customized according to the lifetime selenium demand of different vegetable crops. The cultivation substrate provided by the present invention does not need to add selenium again manually, and can be directly put into the cultivation container to plant various vegetables, and After planting, it only needs to be managed according to the routine, and a large number of elements such as nitrogen, phosphorus, and potassium or cultivation nutrient solution are applied, so it is easier to master the application method, and the selenium content of vegetables is controlled within a safe range to produce safe, high-quality, clean green rich Selenium vegetables, and will not cause pollution to the environment.
4、采用本方法制备的作物栽培基质是可直接应用的作物栽培载体,而期刊论文“硒肥对马铃薯硒素吸收、转化及产量、品质的影响”(殷金岩,耿增超,李致颖等2015,35(3):823—829)报道的一种生物炭基硒肥,是一种微量元素肥料,需经进行科学试验后确定应用于各种蔬菜作物的施用量及施用技术后,方能使用,增加了施用难度。4. The crop cultivation substrate prepared by this method is a directly applicable crop cultivation carrier, and the journal article "Selenium Fertilizer Effects on Potato Selenium Absorption, Transformation, Yield, and Quality" (Yin Jinyan, Geng Zengchao, Li Zhiying, etc. 2015, 35( 3): 823-829) reported a biochar-based selenium fertilizer, which is a kind of trace element fertilizer. It can only be used after scientific experiments are carried out to determine the application amount and application technology for various vegetable crops. Increase application difficulty.
5、本发明富硒基质中的硒元素不易流失,利用率明显提高,更适合于设施栽培。5. The selenium element in the selenium-enriched matrix of the present invention is not easy to lose, and the utilization rate is obviously improved, which is more suitable for facility cultivation.
6、应用本发明所述方法后,栽培基质中硒含量为2~10mg/kg时,收获番茄中有机硒含量为5~200μg/kg,且有机硒占总硒比例≥85%。6. After applying the method of the present invention, when the selenium content in the cultivation medium is 2-10 mg/kg, the organic selenium content in the harvested tomato is 5-200 μg/kg, and the organic selenium accounts for ≥85% of the total selenium.
总之,使用本发明的方法制备出的富硒作物栽培基质能够提高作物对硒元素的吸收转化率,并且富硒作物栽培基质中的硒元素能够在蔬菜作物的整个生长周期内缓慢、均匀释放,使得蔬菜作物在各个生长时期内都能够有效吸收硒元素,因而,栽培出的蔬菜作物中的有机硒含量较高,大大提高了商品的附加值。In a word, the selenium-enriched crop cultivation substrate prepared by the method of the present invention can improve the absorption and conversion rate of selenium element by crops, and the selenium element in the selenium-enriched crop cultivation substrate can be released slowly and evenly during the whole growth cycle of vegetable crops, The vegetable crops can effectively absorb the selenium element in each growth period, therefore, the organic selenium content in the cultivated vegetable crops is relatively high, which greatly improves the added value of the commodity.
附图说明Description of drawings
附图1为本发明方法的技术路线图;Accompanying drawing 1 is the technical road map of the inventive method;
附图2为实施例一的富硒黄瓜栽培基质与普通无土栽培基质中硒元素溶出率动态变化图;Accompanying drawing 2 is the dynamic variation diagram of selenium element dissolution rate in the selenium-enriched cucumber cultivation substrate of embodiment one and common soilless cultivation substrate;
附图3为实施例一的富硒黄瓜栽培基质与普通无土栽培基质在收获黄瓜后黄瓜内有机硒含量对比图。Accompanying drawing 3 is the comparison diagram of the content of organic selenium in the cucumber after the cucumber is harvested between the selenium-enriched cucumber cultivation substrate of Example 1 and the common soilless cultivation substrate.
具体实施方式detailed description
下面结合实施例对本发明作进一步描述:The present invention will be further described below in conjunction with embodiment:
实施例一:一种用果渣生物质炭制备富硒作物栽培基质的方法Embodiment 1: A kind of method of preparing selenium-enriched crop cultivation substrate with pomace biochar
所述方法依次包括下列步骤:The method comprises the following steps in turn:
第一步,制备果渣生物质炭,The first step is to prepare pomace biochar,
将果渣在晒干后加入热解炉中,通入氩气,以排除热解炉中的氧气,将热解炉内温度在5分钟之内快速升温至100℃,然后再以1℃/分钟的升温速率加热至550℃℃,并保持30分钟,自然冷却至室温后,收集生物质,粉碎,过60目筛子,制得果渣生物质炭;所述果渣选自苹果渣、梨渣、桃渣、草莓渣、猕猴桃渣、葡萄渣、西瓜渣、香蕉渣以及菠萝渣中的至少一种;在投入至热解炉之前,将所述果渣晾晒到含水量小于40%,粉碎到颗粒的平均直径不大于10cm;Put the fruit pomace into the pyrolysis furnace after drying, pass in argon gas to get rid of the oxygen in the pyrolysis furnace, rapidly raise the temperature in the pyrolysis furnace to 100°C within 5 minutes, and then increase the temperature at 1°C/ Heating at a heating rate of 1 minute to 550°C and maintaining it for 30 minutes, after naturally cooling to room temperature, collecting the biomass, pulverizing, and passing through a 60-mesh sieve to obtain pomace biochar; the pomace is selected from apple pomace, pear pomace at least one of pomace, peach pomace, strawberry pomace, kiwi fruit pomace, grape pomace, watermelon pomace, banana pomace and pineapple pomace; before being put into the pyrolysis furnace, the pomace is air-dried until the water content is less than 40%, and crushed The average diameter of the particles is not more than 10cm;
第二步,制备硒营养液,The second step is to prepare selenium nutrient solution,
将Na2Se04·10H2O或Na2SeO3与水按重量比1:20溶解制成硒盐溶液,再向硒盐溶液加入醋酸以调节硒盐溶液的pH到4.5~5.5,制得硒营养液;Dissolving Na 2 Se0 4 ·10H 2 O or Na 2 SeO 3 with water at a weight ratio of 1:20 to make a selenium salt solution, and then adding acetic acid to the selenium salt solution to adjust the pH of the selenium salt solution to 4.5~5.5 to obtain Selenium nutrient solution;
第三步,制备富硒生物炭:The third step is to prepare selenium-enriched biochar:
(1)将一部分所述第一步制得的果渣生物质炭加热到70℃,立即将所述硒营养液均匀喷洒在果渣生物质炭上,硒营养液与果渣生物质炭的体积为1:20,边喷洒边搅拌,制得加温态富硒生物炭;(1) Heating a part of the pomace biochar prepared in the first step to 70°C, and immediately spraying the selenium nutrient solution evenly on the pomace biochar, the difference between the selenium nutrient solution and the pomace biochar The volume is 1:20, while spraying and stirring, the heated selenium-enriched biochar is obtained;
(2)取另一部分所述第一步制得的果渣生物质炭,在常温(也即室温下,约为10℃~40℃)下将硒营养液均匀喷洒在该果渣生物质炭上,硒营养液与果渣生物质炭的体积为1:20,边喷洒边搅拌,制得常温态富硒生物炭;(2) Take the pomace biochar prepared in the first step described in the other part, and evenly spray the selenium nutrient solution on the pomace biochar at room temperature (that is, at room temperature, about 10°C~40°C). Above, the volume of selenium nutrient solution and pomace biochar is 1:20, and they are sprayed and stirred to prepare selenium-enriched biochar at normal temperature;
(3)将所述加温态富硒生物炭与所述常温态富硒生物炭混合制成富硒生物炭,其中,加温态富硒生物炭与常温态富硒生物炭的体积比为7:3;(3) Mixing the heated selenium-enriched biochar and the normal temperature selenium-enriched biochar to make selenium-enriched biochar, wherein the volume ratio of the heated selenium-enriched biochar to the normal temperature selenium-enriched biochar is 7:3;
第四步,制备改性淀粉粘结剂,The fourth step is to prepare modified starch binder,
首先将50重量份的玉米或木薯淀粉溶解于100重量份的水中,不断搅拌下加入2重量份的浓硫酸催化,然后加入5重量份高猛酸钾溶液氧化1小时并不断搅拌,再加入4重量份的氢氧化钠糊化20分钟,加入1重量份硼砂交联15分钟,最后补加入水充分搅拌后冷却得到质量浓度为0.3%的淀粉粘结剂;First, 50 parts by weight of corn or tapioca starch are dissolved in 100 parts by weight of water, 2 parts by weight of concentrated sulfuric acid is added under constant stirring for catalysis, then 5 parts by weight of potassium permanganate solution is added to oxidize for 1 hour and continuously stirred, then 4 parts by weight of potassium permanganate are added. The sodium hydroxide gelatinization of weight part is 20 minutes, add 1 weight part of borax cross-linking 15 minutes, add the starch binder that the mass concentration is 0.3% after adding water fully to stir finally;
第五步,制备硒生物炭颗粒剂The fifth step, preparing selenium biochar granules
将所述第三步制得的富硒生物炭送入上方具有喷头的搅拌机中,搅拌物料的同时均匀喷洒质量浓度为0.3%的淀粉粘结剂,所述富硒生物炭与淀粉粘结剂的体积比为90:10,制得硒生物炭颗粒剂;The selenium-enriched biochar prepared in the third step is sent into the mixer with a nozzle above, and the starch binder with a mass concentration of 0.3% is uniformly sprayed while stirring the material, and the selenium-enriched biochar and the starch binder The volume ratio is 90:10 to prepare selenium biochar granules;
第六步,取所述第三步制得的富硒生物炭与所述第五步制得的硒生物炭颗粒剂,将二者混合均匀得湿物料,富硒生物炭与硒生物炭颗粒剂的体积比为3:7,再将所述湿物料送入具有热风机的滚筒造粒机中,设定转速为300r/min,温度为70℃,造粒30~40分钟后,过30目筛;The sixth step is to take the selenium-enriched biochar prepared in the third step and the selenium biochar granules prepared in the fifth step, and mix the two evenly to obtain a wet material, selenium-enriched biochar and selenium biochar granules The volume ratio of the agent is 3:7, and then the wet material is sent into a drum granulator with a hot air blower, the set speed is 300r/min, the temperature is 70°C, after 30-40 minutes of granulation, after 30 Mesh sieve;
第七步,将所述第六步制得的颗粒与蔬菜无土栽培基质填充料按重量比1:100搅拌均匀,其中,无土栽培基质填充料是由草炭与珍珠岩按体积比3:1均匀混合制得的,最后,制得所述富硒蔬菜栽培基质。The seventh step is to mix the granules prepared in the sixth step with the vegetable soilless culture matrix filler in a weight ratio of 1:100, wherein the soilless culture matrix filler is made of peat and perlite in a volume ratio of 3: 1 prepared by uniform mixing, and finally, the selenium-enriched vegetable cultivation substrate is prepared.
第八步,将富硒蔬菜栽培基质装入8L的栽培袋中,另设在普通无土栽培基质(草炭与珍珠岩按体积比3:1均匀)中施入相同量Na2Se04·10H2O的基质作为对照,二种基质中硒元素含量相同,硒含量均为5.2mg/kg。每袋种植一株黄瓜,定期浇灌常规氮磷钾营养液(霍格兰营养液)及水。成熟期收获黄瓜后测定表明,参见附图2和3所示,生物炭富硒基质处理的有机硒含量为5.9μg/kg,有机硒占总硒量的86.4%,而硒酸钠(Na2Se04·10H2O)直接加入商品基质(对照)含量为3.3μg/kg,有机硒占总硒量的65.1%。说明生物炭富硒基质的硒缓释效果较明显,而且得到了作物的充分吸收利用。In the eighth step, put the selenium-enriched vegetable cultivation substrate into an 8L cultivation bag, and add the same amount of Na 2 Se0 4 ·10H to the common soilless cultivation substrate (peat and perlite in a volume ratio of 3:1) The matrix of 2 O was used as a control, and the content of selenium in the two kinds of matrix was the same, and the content of selenium was 5.2mg/kg. Plant one cucumber per bag, and regularly water with conventional NPK nutrient solution (Hoagland nutrient solution) and water. Determination after harvesting the cucumber at the mature stage shows that, referring to the accompanying drawings 2 and 3, the organic selenium content of the biochar selenium-enriched matrix treatment is 5.9 μ g/kg, and the organic selenium accounts for 86.4% of the total selenium content, while sodium selenate (Na 2 Se0 4 ·10H 2 O) was directly added to the commercial matrix (control) with a content of 3.3 μg/kg, and organic selenium accounted for 65.1% of the total selenium. It shows that the slow-release effect of selenium in biochar selenium-enriched matrix is obvious, and it has been fully absorbed and utilized by crops.
实施例二:一种用果渣生物质炭制备富硒草莓栽培基质的方法Embodiment 2: A kind of method of preparing selenium-enriched strawberry cultivation substrate with pomace biochar
所述方法依次包括下列步骤:The method comprises the following steps in turn:
第一步,制备果渣生物质炭,The first step is to prepare pomace biochar,
将果渣在晒干后加入热解炉中,通入氩气,以排除热解炉中的氧气,将热解炉内温度在5分钟之内快速升温至105℃,然后再以1℃/分钟的升温速率加热至600℃,并保持25分钟,自然冷却至室温后,收集生物质,粉碎,过60目筛子,制得果渣生物质炭;Put the fruit pomace into the pyrolysis furnace after drying, feed argon gas to get rid of the oxygen in the pyrolysis furnace, rapidly raise the temperature in the pyrolysis furnace to 105°C within 5 minutes, and then increase the temperature at 1°C/ Heat up to 600°C at a heating rate of 1 minute, and keep it for 25 minutes. After naturally cooling to room temperature, collect the biomass, pulverize it, and pass it through a 60-mesh sieve to obtain pomace biochar;
第二步,制备硒营养液,The second step is to prepare selenium nutrient solution,
将分析纯Na2SeO3与水按重量比1:30溶解制成硒盐溶液,再向硒盐溶液加入稀盐酸以调节硒盐溶液的pH到4.5~5.5,制得硒营养液;Dissolve analytically pure Na 2 SeO 3 and water at a weight ratio of 1:30 to make a selenium salt solution, and then add dilute hydrochloric acid to the selenium salt solution to adjust the pH of the selenium salt solution to 4.5-5.5 to obtain a selenium nutrient solution;
第三步,制备富硒生物炭:The third step is to prepare selenium-enriched biochar:
(1)将一部分所述第一步制得的果渣生物质炭加热到100℃,立即将所述硒营养液均匀喷洒在果渣生物质炭上,硒营养液与果渣生物质炭的体积为1:30,边喷洒边搅拌,制得加温态富硒生物炭;(1) Heating a part of the pomace biochar prepared in the first step to 100°C, and immediately spraying the selenium nutrient solution evenly on the pomace biochar, the difference between the selenium nutrient solution and the pomace biochar The volume is 1:30, while spraying and stirring, the heated selenium-enriched biochar is obtained;
(2)取另一部分所述第一步制得的果渣生物质炭,在常温(约10℃~40℃)下将硒营养液均匀喷洒在该果渣生物质炭上,硒营养液与果渣生物质炭的体积为1:20,边喷洒边搅拌,制得常温态富硒生物炭;(2) Take the pomace biochar prepared in the first step described in the other part, and evenly spray the selenium nutrient solution on the pomace biochar at room temperature (about 10°C~40°C), the selenium nutrient solution and The volume of pomace biochar is 1:20, and it is stirred while spraying to prepare selenium-enriched biochar at normal temperature;
(3)将所述加温态富硒生物炭与所述常温态富硒生物炭混合制成富硒生物炭,其中,加温态富硒生物炭与常温态富硒生物炭的体积比为6:4;(3) Mixing the heated selenium-enriched biochar and the normal temperature selenium-enriched biochar to make selenium-enriched biochar, wherein the volume ratio of the heated selenium-enriched biochar to the normal temperature selenium-enriched biochar is 6:4;
第四步,制备改性淀粉粘结剂,The fourth step is to prepare modified starch binder,
首先将50重量份的玉米或木薯淀粉溶解于100重量份的水中,不断搅拌下加入3重量份的浓硫酸催化,然后加入5重量份高猛酸钾溶液氧化1.5小时并不断搅拌,再加入4重量份的氢氧化钠糊化20分钟,加入1重量份硼砂交联15分钟,最后补加入水充分搅拌后冷却得到质量浓度为0.2%的淀粉粘结剂;First, 50 parts by weight of corn or tapioca starch are dissolved in 100 parts by weight of water, 3 parts by weight of concentrated sulfuric acid is added under constant stirring for catalysis, then 5 parts by weight of potassium permanganate solution is added to oxidize for 1.5 hours and continuously stirred, and then 4 parts by weight of potassium permanganate are added. The sodium hydroxide gelatinization of weight part is 20 minutes, add 1 weight part borax cross-linking 15 minutes, add water and fully stir at last and cool down to obtain the starch binder that mass concentration is 0.2%;
第五步,制备硒生物炭颗粒剂The fifth step, preparing selenium biochar granules
将所述第三步制得的富硒生物炭送入上方具有喷头的搅拌机中,搅拌物料的同时均匀喷洒质量浓度为0.2%的淀粉粘结剂,所述富硒生物炭与淀粉粘结剂的体积比为95:5,制得硒生物炭颗粒剂;The selenium-enriched biochar prepared in the third step is sent into the mixer with a nozzle above, and the starch binder with a mass concentration of 0.2% is evenly sprayed while stirring the material, and the selenium-enriched biochar and the starch binder The volume ratio is 95:5 to prepare selenium biochar granules;
第六步,取所述第三步制得的富硒生物炭与所述第五步制得的硒生物炭颗粒剂,将二者混合均匀得湿物料,富硒生物炭与硒生物炭颗粒剂的体积比为2:8,再将所述湿物料送入具有热风机的滚筒造粒机中,设定转速为250r/min,温度为70℃,造粒40分钟后,过30目筛;The sixth step is to take the selenium-enriched biochar prepared in the third step and the selenium biochar granules prepared in the fifth step, and mix the two evenly to obtain a wet material, selenium-enriched biochar and selenium biochar granules The volume ratio of the agent is 2:8, and then the wet material is sent into a drum granulator with a hot air blower, the set speed is 250r/min, the temperature is 70°C, and after 40 minutes of granulation, pass through a 30-mesh sieve ;
第七步,将所述第六步制得的颗粒与蔬菜无土栽培基质填充料按重量比1:150搅拌均匀,即制得所述富硒蔬菜栽培基质。In the seventh step, the granules prepared in the sixth step and the soilless vegetable cultivation substrate filling material are evenly stirred at a weight ratio of 1:150 to obtain the selenium-enriched vegetable cultivation substrate.
其中,无土栽培基质填充料的制备:Wherein, the preparation of soilless culture substrate filler:
(1)采用饲料粉碎机或秸杆揉搓机将水稻秸杆粉碎成5~10cm长;(1) Use a feed grinder or a straw rubbing machine to crush the rice straw into 5-10cm long;
(2)食用菌菌渣为食用菌生产后的废弃培养基质,如鸡腿菇、金针菇渣,粉碎到2~5mm;(2) Edible fungus residue is the discarded culture substrate after the production of edible fungi, such as Coprinus comatus and Flammulina velutipes residue, crushed to 2~5mm;
(3)木薯渣为酒精厂制酒后的发酵废弃物,直径1~3mm;(3) The cassava residue is the fermentation waste after making wine in the alcohol factory, with a diameter of 1~3mm;
将上述水稻秸杆、食用菌菌渣、木薯渣按体积比4:1:5混合均匀,得到混合物;Mix the above-mentioned rice straw, edible fungus residue, and cassava residue in a volume ratio of 4:1:5 to obtain a mixture;
将上述混合物堆成条垛形状进行好氧堆腐发酵,条垛堆体高1~3米,宽2~8米,长度30~100米;堆体含水量范围控制在50%~65%,堆制时通风供氧;控制堆体温度在65℃~45℃范围,超出该温度范围时及时对堆体进行翻拌,当混合物的温度等于环境温度时堆腐发酵完成(一般30天左右),将所得到的腐熟物晾晒到含水率30-40%即为所述基质填充料。The above mixture is stacked into strips for aerobic compost fermentation. The stacks are 1-3 meters high, 2-8 meters wide, and 30-100 meters long; the water content of the stacks is controlled at 50%-65%. Ventilation and oxygen supply during production; control the temperature of the pile in the range of 65°C to 45°C, turn over the pile in time when the temperature exceeds this range, and complete the fermentation of the pile when the temperature of the mixture is equal to the ambient temperature (generally about 30 days). The obtained decomposed matter is air-dried until the water content is 30-40%, which is the matrix filler.
第八步,将富硒栽培基质装入8L的栽培袋中,另设普通无土栽培基质填充料中施入相同量亚硒酸钠(Na2SeO3)的基质作为对照,二种基质中硒元素含量相同,硒含量均为6.1mg/kg。每袋种植一株草莓,定期浇灌常规氮磷钾营养液(霍格兰营养液)及水,成熟期收获草莓后测定表明,生物炭富硒基质处理的有机硒含量为4.1μg/kg,有机硒占总硒量的67.3%,而亚硒酸钠(Na2SeO3)直接加入基质填充料(对照)处理的含量为1.8μg/kg,有机硒占总硒量的45.2%。说明生物炭富硒基质的硒缓释效果较明显,而且得到了作物的充分吸收利用。In the eighth step, put the selenium-enriched cultivation substrate into an 8L cultivation bag, and set a substrate in which the same amount of sodium selenite (Na 2 SeO 3 ) was applied to the ordinary soilless cultivation substrate filler as a control, and the two substrates The selenium content is the same, and the selenium content is 6.1mg/kg. Plant one strawberry in each bag, and regularly irrigate the conventional NPK nutrient solution (Hoagland nutrient solution) and water. After harvesting the strawberries at the mature stage, the measurement shows that the organic selenium content of the biochar selenium-enriched substrate is 4.1 μg/kg, organic Selenium accounted for 67.3% of the total selenium content, while the content of sodium selenite (Na 2 SeO 3 ) directly added to the matrix filler (control) was 1.8 μg/kg, and organic selenium accounted for 45.2% of the total selenium content. It shows that the slow-release effect of selenium in biochar selenium-enriched matrix is obvious, and it has been fully absorbed and utilized by crops.
上述实施例只为说明本发明的技术构思及特点,其目的在于让熟悉此项技术的人士能够了解本发明的内容并据以实施,并不能以此限制本发明的保护范围,采用本发明的方法制备出的富硒作物栽培基质可以用于种植各种农作物,包括蔬菜和水果,如小白菜、茄子、番茄、生菜、魔芋、大白菜、西兰花、芦笋、莴苣、萝卜、菠菜、青椒等。凡根据本发明精神实质所作的等效变化或修饰,都应涵盖在本发明的保护范围之内。The above-mentioned embodiments are only to illustrate the technical concept and characteristics of the present invention, and its purpose is to allow those familiar with this technology to understand the content of the present invention and implement it accordingly, and cannot limit the protection scope of the present invention with this. The selenium-enriched crop cultivation substrate prepared by the method can be used to grow various crops, including vegetables and fruits, such as cabbage, eggplant, tomato, lettuce, konjac, Chinese cabbage, broccoli, asparagus, lettuce, radish, spinach, green pepper, etc. . All equivalent changes or modifications made according to the spirit of the present invention shall fall within the protection scope of the present invention.
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