CN103159529B - Technical method for biological fermentation of liquid dung and biogas slurry - Google Patents
Technical method for biological fermentation of liquid dung and biogas slurry Download PDFInfo
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- CN103159529B CN103159529B CN201310107613.0A CN201310107613A CN103159529B CN 103159529 B CN103159529 B CN 103159529B CN 201310107613 A CN201310107613 A CN 201310107613A CN 103159529 B CN103159529 B CN 103159529B
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- 239000002002 slurry Substances 0.000 title claims abstract description 46
- 210000003608 fece Anatomy 0.000 title claims abstract description 45
- 238000000034 method Methods 0.000 title claims abstract description 23
- 238000000855 fermentation Methods 0.000 title claims abstract description 20
- 230000004151 fermentation Effects 0.000 title claims abstract description 16
- 239000007788 liquid Substances 0.000 title claims abstract description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 39
- 241000894006 Bacteria Species 0.000 claims abstract description 22
- 239000010871 livestock manure Substances 0.000 claims abstract description 11
- 239000002994 raw material Substances 0.000 claims abstract description 10
- 239000003337 fertilizer Substances 0.000 claims abstract description 6
- 238000004332 deodorization Methods 0.000 claims abstract description 4
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 38
- ZOKXTWBITQBERF-UHFFFAOYSA-N Molybdenum Chemical compound [Mo] ZOKXTWBITQBERF-UHFFFAOYSA-N 0.000 claims description 20
- ZOXJGFHDIHLPTG-UHFFFAOYSA-N Boron Chemical compound [B] ZOXJGFHDIHLPTG-UHFFFAOYSA-N 0.000 claims description 19
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 19
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 claims description 19
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims description 19
- 229910052796 boron Inorganic materials 0.000 claims description 19
- 229910052802 copper Inorganic materials 0.000 claims description 19
- 239000010949 copper Substances 0.000 claims description 19
- 229910052742 iron Inorganic materials 0.000 claims description 19
- 229910052750 molybdenum Inorganic materials 0.000 claims description 19
- 239000011733 molybdenum Substances 0.000 claims description 19
- 229910052698 phosphorus Inorganic materials 0.000 claims description 19
- 239000011574 phosphorus Substances 0.000 claims description 19
- 239000011701 zinc Substances 0.000 claims description 19
- 229910052725 zinc Inorganic materials 0.000 claims description 19
- 239000000203 mixture Substances 0.000 claims description 18
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 claims description 16
- 238000003756 stirring Methods 0.000 claims description 12
- 239000003795 chemical substances by application Substances 0.000 claims description 11
- 150000001875 compounds Chemical class 0.000 claims description 8
- 238000005516 engineering process Methods 0.000 claims description 6
- 230000001580 bacterial effect Effects 0.000 claims description 5
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 claims description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 3
- 239000002781 deodorant agent Substances 0.000 claims description 3
- 230000001877 deodorizing effect Effects 0.000 claims description 3
- 229910052748 manganese Inorganic materials 0.000 claims description 3
- 239000011572 manganese Substances 0.000 claims description 3
- 238000005457 optimization Methods 0.000 claims description 3
- 229910052760 oxygen Inorganic materials 0.000 claims description 3
- 239000001301 oxygen Substances 0.000 claims description 3
- 230000008439 repair process Effects 0.000 claims description 3
- 239000007858 starting material Substances 0.000 claims description 3
- 230000009286 beneficial effect Effects 0.000 abstract description 7
- 241000167880 Hirundinidae Species 0.000 abstract description 2
- JVTAAEKCZFNVCJ-UHFFFAOYSA-N lactic acid Chemical compound CC(O)C(O)=O JVTAAEKCZFNVCJ-UHFFFAOYSA-N 0.000 description 4
- 239000010865 sewage Substances 0.000 description 4
- 239000002689 soil Substances 0.000 description 4
- 210000002700 urine Anatomy 0.000 description 3
- 240000004808 Saccharomyces cerevisiae Species 0.000 description 2
- 238000003912 environmental pollution Methods 0.000 description 2
- 230000002550 fecal effect Effects 0.000 description 2
- 235000014655 lactic acid Nutrition 0.000 description 2
- 239000004310 lactic acid Substances 0.000 description 2
- 230000000813 microbial effect Effects 0.000 description 2
- 230000035699 permeability Effects 0.000 description 2
- 230000000243 photosynthetic effect Effects 0.000 description 2
- 206010057249 Phagocytosis Diseases 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 230000003203 everyday effect Effects 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 230000008782 phagocytosis Effects 0.000 description 1
- 239000002574 poison Substances 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 244000144977 poultry Species 0.000 description 1
- 238000003900 soil pollution Methods 0.000 description 1
Classifications
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- 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
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
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- Fertilizers (AREA)
Abstract
本发明涉及一种粪水、沼液生物发酵技术方法，该方法包括以下步骤：第一步，准备粪水、沼液生物发酵的原料和工具：第二步，有氧除臭发酵：第三步，厌氧发酵优化处理。本发明的有益效果在于：本发明粪水、沼液生物发酵技术方法，通过对粪水、沼液进行二次发酵，彻底分解、吞噬有害病菌，将粪水、沼液变为有益的生物液肥，彻底解决了粪水、沼液带来的污染。The invention relates to a technical method of biofermentation of dung water and biogas slurry. The method comprises the following steps: first step, preparing raw materials and tools for biofermentation of dung water and biogas slurry; second step, aerobic deodorization fermentation; third step The first step is to optimize the anaerobic fermentation treatment. The beneficial effects of the present invention are: the technical method of biofermentation of manure water and biogas slurry in the present invention, through secondary fermentation of manure water and biogas slurry, thoroughly decomposes and swallows harmful bacteria, and turns manure water and biogas slurry into beneficial biological liquid fertilizer , Completely solve the pollution caused by dung water and biogas slurry.
Description
技术领域 technical field
本发明涉及一种粪水、沼液生物发酵技术方法。 The invention relates to a biological fermentation technology method of dung water and biogas slurry.
背景技术 Background technique
目前，我区畜禽养殖业迅速向集约化和高效化的方向发展，可是，由于集约化养殖场每天产生的大量的粪污水所带来的环境污染问题又成为其发展的制约因素。现阶段粪尿污水的处理方法工艺复杂，投资大，耗水多，特别是粪水的处理、利用困难，且无法消除有害病菌，易造成环境污染，病害流行；其次是未经处理的粪尿污水施入农田会造成土壤污染，使土壤透气、透水性下降及板结，严重影响土壤质量，会使作物徒长、倒伏，造成减产，甚至毒害作物。沼液中也存在大量有害病菌，不能直接利用,粪水、沼液是一种污染源头，如何彻底解决粪尿污水的污染成为当务之急。 At present, the livestock and poultry breeding industry in our district is rapidly developing in the direction of intensification and high efficiency. However, the environmental pollution caused by the large amount of manure and sewage produced by intensive farms every day has become a restrictive factor for its development. At present, the treatment method of feces and urine sewage is complex in process, large in investment, and high in water consumption. In particular, the treatment and utilization of feces are difficult, and harmful bacteria cannot be eliminated, which is easy to cause environmental pollution and epidemic diseases; followed by untreated feces and urine The application of sewage into the farmland will cause soil pollution, reduce the air permeability and water permeability of the soil and compact it, seriously affect the soil quality, cause the crops to grow excessively, lodging, reduce production, and even poison the crops. There are also a large number of harmful bacteria in the biogas slurry, which cannot be used directly. Fecal water and biogas slurry are a source of pollution. How to completely solve the pollution of fecal and urine sewage has become a top priority.
发明内容 Contents of the invention
本发明所要解决的技术问题是提供一种粪水、沼液生物发酵技术方法，以克服现有粪水、沼液带来的污染，通过对粪水、沼液进行二次发酵，彻底分解、吞噬有害病菌，将粪水、沼液变为有益的生物液肥。 The technical problem to be solved by the present invention is to provide a technical method of biological fermentation of dung water and biogas slurry to overcome the pollution caused by existing dung water and biogas slurry, and to completely decompose and Phagocytosis of harmful bacteria, turning manure and biogas slurry into beneficial biological liquid fertilizer.
本发明解决技术问题的技术方案如下：一种粪水、沼液生物发酵技术方法，该方法包括以下步骤： The technical solution of the present invention to solve the technical problem is as follows: a biological fermentation technology method of dung water and biogas slurry, the method comprises the following steps:
1. 一种粪水、沼液生物发酵技术方法，该方法包括以下步骤： 1. A biofermentation technology method for dung water and biogas slurry, the method comprising the following steps:
第一步，准备粪水、沼液生物发酵的原料和工具： The first step is to prepare raw materials and tools for biological fermentation of manure and biogas slurry:
（1）原材料：粪水或沼液或粪水与沼液混合物10吨； (1) Raw materials: 10 tons of dung water or biogas slurry or mixture of dung water and biogas slurry;
（2）除臭发酵剂1-1.2千克； (2) 1-1.2 kg of deodorant starter;
（3）复合型EM菌剂0.1-0.12千克，复合型EM菌剂含有光合菌群、乳酸菌群、酵母菌群、革兰氏菌群等五大类80余种对土壤、农作物有益的微生物菌群； (3) Compound EM bacterial agent 0.1-0.12 kg, the compound EM bacterial agent contains more than 80 kinds of microbial flora beneficial to soil and crops in five categories, including photosynthetic bacteria, lactic acid bacteria, yeast bacteria, and Gram bacteria ;
（4）红糖0.1-0.12千克； (4) Brown sugar 0.1-0.12 kg;
（5）硼铁锰锌磷铜钼元素，其中硼铁锰锌磷铜钼元素的总质量为原材料重量的0.005%,硼占该元素质量的10%至14%，铁占该元素质量的12%至16%，锰占该元素质量的15%至18%，锌占该元素质量的8%至12%，磷占该元素质量的20%至24%，铜占该元素质量的15%至18%，钼占该元素质量的12%至16%。 (5) Boron, iron, manganese, zinc, phosphorus, copper, and molybdenum elements, wherein the total mass of boron, iron, manganese, zinc, phosphorus, copper, and molybdenum elements is 0.005% of the weight of the raw materials, boron accounts for 10% to 14% of the mass of the element, and iron accounts for 12% of the mass of the element % to 16%, manganese accounts for 15% to 18% of the element's mass, zinc accounts for 8% to 12% of the element's mass, phosphorus accounts for 20% to 24% of the element's mass, copper accounts for 15% to 15% of the element's mass 18%, and molybdenum accounts for 12% to 16% of the mass of the element.
第二步，有氧除臭发酵： The second step, aerobic deodorization fermentation:
（1）将第一步中的除臭发酵剂配入粪水或沼液或粪水与沼液的混合物中，搅动均匀，此过程中进行除臭，抗有害病菌，降低COD；同时启动好氧生物系统快速修复、抑制、除灭有害病菌； (1) Mix the deodorizing fermentation agent in the first step into the dung water or biogas slurry or the mixture of dung water and biogas slurry, and stir evenly. During this process, deodorize, resist harmful bacteria, and reduce COD; at the same time, start up The oxygen biological system quickly repairs, inhibits and eliminates harmful bacteria;
（2）每24小时搅动一次，72小时完毕。 (2) Stir once every 24 hours and finish in 72 hours.
第三步，厌氧发酵优化处理； The third step is anaerobic fermentation optimization treatment;
（1）在第二步有氧处理完毕后池子中配入第一步中的复合型EM菌剂和红糖，搅动均匀，并进行封闭； (1) After the second step of aerobic treatment is completed, mix the compound EM bacteria agent and brown sugar in the first step into the pool, stir evenly, and seal it;
（2）每24小时搅动一次，72小时完毕； (2) Stir once every 24 hours and finish in 72 hours;
（3）发酵好的粪水或沼液或粪水与沼液混合物配入硼铁锰锌磷铜钼元素，硼铁锰锌磷铜钼元素总量按照1方粪水或沼液或粪水与沼液混合物配入0.35公斤，制成高效有机液肥，即可装桶或装袋使用。 (3) The fermented dung water or biogas slurry or the mixture of dung water and biogas slurry is mixed with boron, iron, manganese, zinc, phosphorus, copper, and molybdenum elements. Mix 0.35 kg with biogas slurry to make high-efficiency organic liquid fertilizer, which can be used in barrels or bags.
本发明的有益效果在于：本发明粪水、沼液生物发酵技术方法，通过对粪水、沼液进行二次发酵，彻底分解、吞噬有害病菌，将粪水、沼液变为有益的生物液肥，彻底解决了粪水、沼液带来的污染。 The beneficial effects of the present invention are: the technical method of biofermentation of manure water and biogas slurry in the present invention, through secondary fermentation of manure water and biogas slurry, thoroughly decomposes and swallows harmful bacteria, and turns manure water and biogas slurry into beneficial biological liquid fertilizer , Completely solve the pollution caused by dung water and biogas slurry.
具体实施方式 Detailed ways
粪水、沼液生物发酵技术方法，该方法包括以下步骤： A biofermentation technology method for dung water and biogas slurry, the method comprising the following steps:
1. 一种粪水、沼液生物发酵技术方法，该方法包括以下步骤： 1. A biofermentation technology method for dung water and biogas slurry, the method comprising the following steps:
第一步，准备粪水、沼液生物发酵的原料和工具： The first step is to prepare raw materials and tools for biological fermentation of manure and biogas slurry:
（1）原材料：粪水或沼液或粪水与沼液混合物10吨； (1) Raw materials: 10 tons of dung water or biogas slurry or mixture of dung water and biogas slurry;
（2）除臭发酵剂1-1.2千克； (2) 1-1.2 kg of deodorant starter;
（3）复合型EM菌剂0.1-0.12千克，复合型EM菌剂含有光合菌群、乳酸菌群、酵母菌群、革兰氏菌群等五大类80余种对土壤、农作物有益的微生物菌群； (3) Compound EM bacterial agent 0.1-0.12 kg, the compound EM bacterial agent contains more than 80 kinds of microbial flora beneficial to soil and crops in five categories, including photosynthetic bacteria, lactic acid bacteria, yeast bacteria, and Gram bacteria ;
（4）红糖0.1-0.12千克； (4) Brown sugar 0.1-0.12 kg;
（5）硼铁锰锌磷铜钼元素，其中硼铁锰锌磷铜钼元素的总质量为原材料重量的0.005%,硼占该元素质量的10%至14%，铁占该元素质量的12%至16%，锰占该元素质量的15%至18%，锌占该元素质量的8%至12%，磷占该元素质量的20%至24%，铜占该元素质量的15%至18%，钼占该元素质量的12%至16%。 (5) Boron, iron, manganese, zinc, phosphorus, copper, and molybdenum elements, wherein the total mass of boron, iron, manganese, zinc, phosphorus, copper, and molybdenum elements is 0.005% of the weight of the raw materials, boron accounts for 10% to 14% of the mass of the element, and iron accounts for 12% of the mass of the element % to 16%, manganese accounts for 15% to 18% of the element's mass, zinc accounts for 8% to 12% of the element's mass, phosphorus accounts for 20% to 24% of the element's mass, copper accounts for 15% to 15% of the element's mass 18%, and molybdenum accounts for 12% to 16% of the mass of the element.
第二步，有氧除臭发酵： The second step, aerobic deodorization fermentation:
（1）将第一步中的除臭发酵剂配入粪水或沼液或粪水与沼液的混合物中，搅动均匀，此过程中进行除臭，抗有害病菌，降低COD；同时启动好氧生物系统快速修复、抑制、除灭有害病菌； (1) Mix the deodorizing fermentation agent in the first step into the dung water or biogas slurry or the mixture of dung water and biogas slurry, and stir evenly. During this process, deodorize, resist harmful bacteria, and reduce COD; at the same time, start up The oxygen biological system quickly repairs, inhibits and eliminates harmful bacteria;
2）每24小时搅动一次，72小时完毕。 2) Stir once every 24 hours and finish in 72 hours.
第三步，厌氧发酵优化处理； The third step is anaerobic fermentation optimization treatment;
（1）在第二步有氧处理完毕后池子中配入第一步中的复合型EM菌剂和红糖，搅动均匀，并进行封闭； (1) After the second step of aerobic treatment is completed, mix the compound EM bacteria agent and brown sugar in the first step into the pool, stir evenly, and seal it;
（2）每24小时搅动一次，72小时完毕； (2) Stir once every 24 hours and finish in 72 hours;
（3）发酵好的粪水或沼液或粪水与沼液混合物配入硼铁锰锌磷铜钼元素，硼铁锰锌磷铜钼元素总量按照1方粪水或沼液或粪水与沼液混合物配入0.35公斤，制成高效有机液肥，即可装桶或装袋使用。 (3) The fermented dung water or biogas slurry or the mixture of dung water and biogas slurry is mixed with boron, iron, manganese, zinc, phosphorus, copper, and molybdenum elements. Mix 0.35 kg with biogas slurry to make high-efficiency organic liquid fertilizer, which can be used in barrels or bags.
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| CN103695524A (en) * | 2013-12-20 | 2014-04-02 | 广西柳州浚业科技有限公司 | Biogas residue fermentation raw material |
| CN103951486A (en) * | 2014-03-28 | 2014-07-30 | 甘肃富民生态农业科技有限公司 | Plant nutrition regulation liquid fertilizer and its production method |
| CN105272472A (en) * | 2015-11-06 | 2016-01-27 | 海南大学 | Biogas slurry formula fertilizer through fermentation of primary pig manure and urine and preparation method thereof |
| CN105294312A (en) * | 2015-11-30 | 2016-02-03 | 高洁 | Method for preparing liquid biofertilizer through organic waste liquid |
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| CN105503288A (en) * | 2016-02-02 | 2016-04-20 | 湖北国源生物科技有限公司 | Method for preparing EM bio-organic fertilizer by use of biogass slurry and bio-organic fertilizer |
| CN106187528A (en) * | 2016-07-22 | 2016-12-07 | 北京西拓联合生态科技有限公司 | A kind of biological liquid fertilizer and preparation method thereof |
| CN106316525A (en) * | 2016-08-22 | 2017-01-11 | 广西壮族自治区林业科学研究院 | Biogas slurry enhanced liquid organic fertilizer preparation method |
| CN107778053A (en) * | 2017-11-15 | 2018-03-09 | 湖南耶啰耶兔业发展有限公司 | A kind of biology urine liquid manure and preparation method thereof |
| CN109721434A (en) * | 2019-03-15 | 2019-05-07 | 青岛汇君环境能源工程有限公司 | A kind of preparation process of the Liquid Fertilizer of biogas slurry compounding |
| CN110128181A (en) * | 2019-06-14 | 2019-08-16 | 武汉益锦祥生物环保有限公司 | A kind of production method and process units of the phycomycete fertilizer based on biogas slurry |
| CN110171994A (en) * | 2019-06-14 | 2019-08-27 | 余宗波 | Odorless high-valued biogas slurry fertilizer of one kind and preparation method thereof |
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| CN1482105A (en) * | 2003-07-24 | 2004-03-17 | 武汉工业学院 | Method for preparing organic fertilizer by fermenting saponin waste residue and waste water |
| CN1245356C (en) * | 2003-08-20 | 2006-03-15 | 丁科峰 | Preparing and extracting method for biological manure secondary fermentation |
| CN101074180A (en) * | 2007-06-15 | 2007-11-21 | 陈宗旺 | Technology for producing special organic biological manure of nutrient tea |
| KR100874136B1 (en) * | 2008-09-04 | 2008-12-17 | 기림아그로(주) | Liquid fertilizer production method |
| CN101891544B (en) * | 2010-07-15 | 2013-06-05 | 吴成祥 | Functional bioorganic and semi-organic fertilizers and preparation method thereof |
| CN102391031A (en) * | 2011-08-17 | 2012-03-28 | 河海大学 | Special biological organic fertilizer for organically cultivating paddies |
| CN102850096A (en) * | 2012-08-24 | 2013-01-02 | 温志明 | Method for producing organic fertilizer by using high-temperature anaerobic sludge, pig manure and chicken manure as raw materials |
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2013
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