CN104310705A - Comprehensive faces treatment method for community-type dry-manure-collection dairy farm with breeding stock of less than 500 - Google Patents
Comprehensive faces treatment method for community-type dry-manure-collection dairy farm with breeding stock of less than 500 Download PDFInfo
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- 238000000034 method Methods 0.000 title claims abstract description 26
- 235000013365 dairy product Nutrition 0.000 title claims abstract description 25
- 238000009395 breeding Methods 0.000 title claims abstract description 18
- 230000001488 breeding effect Effects 0.000 title claims abstract description 17
- 210000003608 fece Anatomy 0.000 claims abstract description 49
- 239000010871 livestock manure Substances 0.000 claims abstract description 46
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 17
- 238000005108 dry cleaning Methods 0.000 claims abstract description 11
- 239000005416 organic matter Substances 0.000 claims abstract description 11
- 238000011010 flushing procedure Methods 0.000 claims abstract description 10
- 238000005273 aeration Methods 0.000 claims abstract description 7
- 238000004140 cleaning Methods 0.000 claims abstract description 7
- 239000003337 fertilizer Substances 0.000 claims abstract description 7
- 239000007787 solid Substances 0.000 claims abstract description 5
- 210000002700 urine Anatomy 0.000 claims abstract description 5
- 235000003351 Brassica cretica Nutrition 0.000 claims abstract description 4
- 235000003343 Brassica rupestris Nutrition 0.000 claims abstract description 4
- 241000361919 Metaphire sieboldi Species 0.000 claims abstract description 4
- 241001465754 Metazoa Species 0.000 claims abstract description 4
- QKSKPIVNLNLAAV-UHFFFAOYSA-N bis(2-chloroethyl) sulfide Chemical compound ClCCSCCCl QKSKPIVNLNLAAV-UHFFFAOYSA-N 0.000 claims abstract description 4
- 210000004081 cilia Anatomy 0.000 claims abstract description 4
- 238000004332 deodorization Methods 0.000 claims abstract description 4
- 238000000855 fermentation Methods 0.000 claims abstract description 4
- 238000003973 irrigation Methods 0.000 claims abstract description 4
- 230000002262 irrigation Effects 0.000 claims abstract description 4
- 235000010460 mustard Nutrition 0.000 claims abstract description 4
- 239000000758 substrate Substances 0.000 claims abstract description 4
- 239000002351 wastewater Substances 0.000 claims description 7
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 6
- 238000009360 aquaculture Methods 0.000 claims description 4
- 244000144974 aquaculture Species 0.000 claims description 4
- 238000009313 farming Methods 0.000 claims description 4
- 244000025254 Cannabis sativa Species 0.000 claims description 3
- 241000196324 Embryophyta Species 0.000 claims description 3
- 238000010521 absorption reaction Methods 0.000 claims description 3
- 229910021529 ammonia Inorganic materials 0.000 claims description 3
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 claims description 3
- 230000009615 deamination Effects 0.000 claims description 3
- 238000006481 deamination reaction Methods 0.000 claims description 3
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 claims description 3
- 239000002994 raw material Substances 0.000 claims description 3
- 244000056139 Brassica cretica Species 0.000 claims 1
- 241000283690 Bos taurus Species 0.000 abstract description 19
- 239000010865 sewage Substances 0.000 abstract description 9
- 241000219198 Brassica Species 0.000 abstract description 3
- 238000012423 maintenance Methods 0.000 abstract description 2
- 244000144972 livestock Species 0.000 description 4
- 244000144977 poultry Species 0.000 description 4
- 238000003977 dairy farming Methods 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 2
- 238000003912 environmental pollution Methods 0.000 description 2
- 230000002265 prevention Effects 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 1
- 230000008092 positive effect Effects 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 230000001932 seasonal effect Effects 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F3/00—Fertilisers from human or animal excrements, e.g. manure
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F7/00—Fertilisers from waste water, sewage sludge, sea slime, ooze or similar masses
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/20—Nature of the water, waste water, sewage or sludge to be treated from animal husbandry
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/28—Anaerobic digestion processes
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- 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
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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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
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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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
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Abstract
一种存栏500头以下小区型干清粪奶牛场粪污处理方法,步骤如下:将挤奶厅的冲洗水、牛尿等通过暗沟收集经格栅过滤掉动物纤毛和草芥输送到厌氧反应器;经厌氧发酵处理后充分降解有机质,出水引至好氧池进行曝气处理,达到除臭和脱氨,剩余的水体通过混灌池合适的配比就可直接用于种植业利用;收集到的固体粪便通过清粪车直接输送到堆粪棚作为二次资源化利用,可作为蚯蚓养殖的基质、堆沤腐熟肥或直接作为肥料售出。本发明的优点是:该方法将粪便和污水分类收集分类处理,降低了粪污处理的投资成本和运行成本;通用性好、使用寿命长、适应范围广,可有效改善养殖场及周边的环境卫生;运行维护简单,可实现半自动化运行。
A method for treating manure and sewage in a dry-cleaning dairy farm with less than 500 cows. The steps are as follows: collect the flushing water and cow urine from the milking parlor through a dark ditch, filter out animal cilia and mustard through a grid, and transport them to an anaerobic reactor. ;After the anaerobic fermentation treatment, the organic matter is fully degraded, and the effluent is led to the aerobic tank for aeration treatment to achieve deodorization and deammonization. The remaining water can be directly used for planting through the appropriate ratio of the mixed irrigation tank; The obtained solid manure is directly transported to the manure shed by the manure cleaning truck for secondary resource utilization, and can be used as a substrate for earthworm breeding, composted decomposed manure or sold directly as fertilizer. The advantages of the present invention are: the method collects and classifies feces and sewage, which reduces the investment cost and operating cost of feces treatment; it has good versatility, long service life and wide application range, and can effectively improve the environment of the farm and its surroundings Hygienic; simple operation and maintenance, semi-automatic operation can be realized.
Description
技术领域 technical field
本发明本发明涉及奶牛场粪污综合处理技术,具体涉及一种存栏500头以下小区型干清粪奶牛场粪污综合处理方法。 The present invention The present invention relates to a technology for comprehensive treatment of manure in dairy farms, in particular to a method for comprehensive treatment of manure in dry-cleaned dairy farms with less than 500 cows in stock.
背景技术 Background technique
据农业部发布《全国优势农产品区域规划布局2008-2015》统计,目前,我国人均奶制品消费量仅相当于世界平均水平的1/4、发达国家的1/12,发展空间广阔。近年来,随着奶制品需求量的提升,在奶牛优势区的带动下,我国奶业持续高速发展,涌现出一批明星企业和知名品牌,取得了显著的成效,据畜牧年鉴统计2012年全国养殖量为1440万头,按照规划预计到2015年全国奶牛养殖量达到1700万头。随着养殖规模的不断扩大,集约化奶牛养殖场数量的增加,规模化奶牛场粪污造成的环境污染问题,尤其是以干清粪为主要清粪工艺的牧场型规模化奶牛养殖场所产生的大量高浓度养殖粪污,正引起社会的广泛关注。 According to the Ministry of Agriculture's "National Advantageous Agricultural Products Regional Planning and Layout 2008-2015" statistics, at present, my country's per capita dairy product consumption is only equivalent to 1/4 of the world's average level and 1/12 of that of developed countries, and there is broad room for development. In recent years, with the increase in the demand for dairy products, driven by the dairy cattle advantage area, my country's dairy industry has continued to develop at a high speed, and a number of star enterprises and well-known brands have emerged, and have achieved remarkable results. The breeding volume is 14.4 million. According to the plan, it is estimated that by 2015, the national dairy cow breeding volume will reach 17 million. With the continuous expansion of breeding scale and the increase in the number of intensive dairy farms, the environmental pollution caused by large-scale dairy farm manure, especially the pasture-type large-scale dairy farms that use dry manure as the main manure cleaning process A large amount of high-concentration farming manure is causing widespread concern in the society.
由于在产业发展过程产排的大量粪污未能得到及时有效的控制和利用,造成大量资源的浪费,并威胁到畜产品质量与养殖环境产地安全。为此,国家和地方政府出台了一系列法令规章、标准和规范来约束和促进行业的健康发展。2014年1月1日,国务院正式颁布《畜禽规模养殖污染防治条例》;农业部、环保部颁布实施了《畜禽场环境质量标准》、《畜禽养殖业污染物排放标准》、《畜禽养殖业污染防治技术规范》、《畜禽养殖业污染治理工程技术规范》等标准规范来约束和解决畜禽养殖污染问题。 Due to the large amount of manure generated and discharged during the industrial development process has not been effectively controlled and utilized in a timely manner, resulting in a large waste of resources and threatening the quality of livestock products and the safety of the breeding environment. To this end, the national and local governments have issued a series of laws, regulations, standards and norms to constrain and promote the healthy development of the industry. On January 1, 2014, the State Council officially promulgated the "Regulations on the Prevention and Control of Pollution from Large-scale Livestock and Poultry Breeding"; Poultry Breeding Industry Pollution Prevention and Control Technical Specifications, and Livestock and Poultry Breeding Industry Pollution Control Engineering Technical Specifications to constrain and solve livestock and poultry breeding pollution problems.
干清粪式规模化奶牛场养殖方式及其粪污收集方式在奶牛养殖业行业具有普遍性,小区型规模化奶牛养殖几乎全部采用干清粪工艺,该类型养殖场粪污治理,对促进整个奶牛养殖行业的健康发展发挥重要作用。与水冲粪奶牛养殖场粪污产排情况相比,粪便主要以固体的形式被收集和清运,养殖废水量也相对较少,且废水中有机质含量少,但如果不处理而任其随意排放同样也会造成较严重的环境污染,制定经济适用且有针对性的粪污处理工艺是本发明要解决的关键问题。 The dry-cleaning large-scale dairy farm breeding method and its manure collection method are common in the dairy farming industry. Almost all large-scale dairy farming in the community adopts the dry-cleaning process. The manure treatment of this type of farm is conducive to promoting the entire The healthy development of the dairy farming industry plays an important role. Compared with the production and discharge of manure in dairy farms with water flushing manure, the manure is mainly collected and transported in the form of solid, and the amount of aquaculture wastewater is relatively small, and the organic matter content in the wastewater is small, but if it is not treated and left at will The discharge will also cause serious environmental pollution, and the key problem to be solved by the present invention is to formulate an economical, applicable and targeted manure treatment process.
通过行业调研,干清粪式规模化奶牛场粪便主要来源于牛舍、运动场;干清粪工艺中废水主要来源于挤奶厅设备管路冲洗水、待挤厅地面冲洗水、牛尿,小区型奶牛场一般不喷淋。不同的养殖规模会产生不同数量的废水,相应的治理方式上也会有较大差异,本发明主要针对500头以下小区型规模化奶牛场制定相对应的处理方法。 Through industry research, the manure of large-scale dry-cleaning dairy farms mainly comes from cowsheds and sports fields; the waste water in the dry-cleaning process mainly comes from the flushing water of the milking parlor equipment pipeline, the floor flushing water of the parlor to be squeezed, cow urine, and the residential area. Large dairy farms generally do not spray. Different breeding scales will produce different amounts of wastewater, and the corresponding treatment methods will also be quite different. The present invention mainly formulates corresponding treatment methods for small-scale dairy farms with less than 500 cows.
发明内容 Contents of the invention
本发明的目的在于针对存栏量500头以下小区型干清粪奶牛场粪污产排特点和存在问题,提供一种存栏500头以下小区型干清粪奶牛场粪污综合处理方法,该方法粪污分类收集、分类处理,具有季节性适应能力和贮存和深度净化能力,可实现种养结合的综合粪污处理。 The purpose of the present invention is to provide a comprehensive treatment method for manure and sewage in small-scale dry-cleaning dairy farms with less than 500 cows in view of the characteristics and existing problems of manure production and discharge in small-scale dry-cleaning dairy farms with less than 500 cows. Sewage classification collection and classification treatment, with seasonal adaptability and storage and deep purification capabilities, can realize the comprehensive treatment of manure combined with planting and breeding.
本发明的技术方案: Technical scheme of the present invention:
一种存栏500头以下小区型干清粪奶牛场粪污处理方法,包括以下步骤: A method for treating manure and sewage of dry-cleaned dairy farms with less than 500 cows in stock, comprising the following steps:
1)首先将挤奶厅产生的设备冲洗水、待挤厅产生的地面冲洗水、牛尿和少量的牛粪由厅内暗沟收集,收集后经过格栅过滤掉动物纤毛和草芥等,再由暗管输送到厌氧反应器; 1) First, collect the equipment flushing water from the milking parlor, the ground flushing water from the parlor to be milked, cow urine and a small amount of cow manure from the underground ditch in the parlor, and filter out animal cilia and grass mustard through the grid after collection, and then The dark pipe is transported to the anaerobic reactor;
2)通过厌氧反应器的厌氧发酵处理后充分降解有机质,将绝大部分含氮有机质转化为氨氮,产生的沼气可作为清洁能源综合利用,出水引至好氧池进行曝气处理; 2) After the anaerobic fermentation treatment in the anaerobic reactor, the organic matter is fully degraded, and most of the nitrogen-containing organic matter is converted into ammonia nitrogen. The generated biogas can be used as clean energy for comprehensive utilization, and the effluent is led to the aerobic tank for aeration treatment;
3)在好氧池通过好氧处理达到除臭和脱氨的作用,曝气处理后的养殖废水有机质得到了有效降解,脱除了游离态的氨,剩余的水体将是适合植物吸收和利用的很好水肥资源,通过混灌池合适的配比就可直接用于种植业利用; 3) In the aerobic pool, deodorization and deamination are achieved through aerobic treatment. The organic matter of the aquaculture wastewater after aeration treatment has been effectively degraded, free ammonia has been removed, and the remaining water body will be very suitable for plant absorption and utilization. Good water and fertilizer resources can be directly used for planting through the appropriate ratio of mixed irrigation tanks;
4)牛舍和运动场收集到的固体粪便通过清粪车直接输送到堆粪棚作为二次资源化利用的原料储备,或者作为蚯蚓养殖的基质或堆沤腐熟肥、直接售卖最终作为肥料用于种植业。 4) The solid manure collected by cowsheds and sports fields is directly transported to the manure shed by the manure cleaning truck as a raw material reserve for secondary resource utilization, or as a substrate for earthworm breeding or composted manure, sold directly and finally used as fertilizer for crop farming.
the
本发明的优点和积极效果是: Advantage and positive effect of the present invention are:
1)该方法充分利用了存栏量500头以下小区型干清粪奶牛场粪污产排特点,已实现养殖废弃物资源化为最终目标,将粪便和污水分类收集分类处理,降低了粪污处理的投资成本和运行成本; 1) This method makes full use of the characteristics of excrement and sewage production and discharge in dry-cleaning dairy farms with a population of less than 500 cows, and has realized the ultimate goal of recycling breeding waste. The feces and sewage are collected and treated in a separate manner, reducing the need for manure treatment. investment and operating costs;
2)该方法通用性好、使用寿命长、适应范围广,可满足不同地区的存栏量500头以下小区型干清粪奶牛场粪污处理; 2) This method has good versatility, long service life, and wide application range, and can meet the manure treatment of dry-cleaning dairy farms in different regions with a population of less than 500 cows;
3)该方法可有效改善养殖场及周边的环境卫生,为发展清洁养殖提供了保障; 3) This method can effectively improve the environmental sanitation of the farm and its surroundings, and provide a guarantee for the development of clean farming;
4)该方法可实现半自动化运行,运行维护简单,整个系统的运行仅需要兼职操作即可,不需要安排固定人员。 4) This method can realize semi-automatic operation, and the operation and maintenance are simple. The operation of the whole system only needs part-time operation, and no fixed personnel are required.
the
附图说明 Description of drawings
图1为该牛场粪污处理方法的流程图。 Fig. 1 is the flow chart of this cattle farm manure treatment method.
the
具体实施方式 Detailed ways
实施例: Example:
一种用于存栏500头以下小区型干清粪奶牛场粪污综合处理方法,如图1所示,包括以下步骤: A method for comprehensive treatment of manure and sewage in small-scale dry-cleaning dairy farms with less than 500 cows in stock, as shown in Figure 1, comprising the following steps:
1)首先将挤奶厅产生的设备冲洗水、待挤厅产生的地面冲洗水、牛尿和少量的牛粪由厅内暗沟收集,收集后经过格栅过滤掉动物纤毛和草芥等,再由暗管输送到厌氧反应器; 1) First, collect the equipment flushing water from the milking parlor, the ground flushing water from the parlor to be milked, cow urine and a small amount of cow manure from the underground ditch in the parlor, and filter out animal cilia and grass mustard through the grid after collection, and then The dark pipe is transported to the anaerobic reactor;
2)通过厌氧反应器的厌氧发酵处理后充分降解有机质,将绝大部分含氮有机质转化为氨氮,产生的沼气可作为清洁能源综合利用,出水引至好氧池进行曝气处理; 2) After the anaerobic fermentation treatment in the anaerobic reactor, the organic matter is fully degraded, and most of the nitrogen-containing organic matter is converted into ammonia nitrogen. The generated biogas can be used as clean energy for comprehensive utilization, and the effluent is led to the aerobic tank for aeration treatment;
3)在好氧池通过好氧处理达到除臭和脱氨的作用,曝气处理后的养殖废水有机质得到了有效降解,脱除了游离态的氨,剩余的水体将是适合植物吸收和利用的很好水肥资源,通过混灌池合适的配比就可直接用于种植业利用; 3) In the aerobic pool, deodorization and deamination are achieved through aerobic treatment. The organic matter of the aquaculture wastewater after aeration treatment has been effectively degraded, free ammonia has been removed, and the remaining water body will be very suitable for plant absorption and utilization. Good water and fertilizer resources can be directly used for planting through the appropriate ratio of mixed irrigation tanks;
4)牛舍和运动场收集到的固体粪便则通过清粪车直接输送到堆粪棚作为二次资源化利用的原料储备,可以作为蚯蚓养殖的基质、可以直接堆沤腐熟肥、可以直接售卖最终作为肥料用于种植业。 4) The solid manure collected from cowsheds and sports grounds is directly transported to the manure shed by the manure cleaning truck as a raw material reserve for secondary resource utilization. It can be used as a substrate for earthworm breeding, can be directly stacked and decomposed manure, and can be directly sold for final use. Used as fertilizer for crops.
该方法充分结合了存栏500头以下小区型干清粪奶牛场的养殖工艺和清排粪工艺特点,将粪便和污水分类收集,降低了粪污处理的投资成本和运行成本。工艺通用性好,适应范围广,可有效改善养殖场及周边的环境卫生,工艺技术完善,使用良好,具有显著的技术及经济效果。 This method fully combines the characteristics of breeding technology and manure cleaning process of dry manure cleaning dairy farms with less than 500 cows on hand, collects manure and sewage by classification, and reduces the investment cost and operation cost of manure treatment. The process has good versatility and a wide range of applications, and can effectively improve the environmental sanitation of the farm and its surroundings. The process technology is perfect, it is well used, and it has significant technical and economic effects.
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Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106007311A (en) * | 2016-06-30 | 2016-10-12 | 宾阳县东洋养殖有限公司 | Environment-friendly ecological recycling method for pig manure |
Citations (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20030141245A1 (en) * | 2001-02-15 | 2003-07-31 | Fetterman Lewis M. | Method for the treatment of animal waste and products made therefrom |
JP2008200637A (en) * | 2007-02-21 | 2008-09-04 | Mizu Kankyo Kenkyusho:Kk | Water treatment plant, water treatment facility, and water treating method |
US20090114602A1 (en) * | 2007-11-01 | 2009-05-07 | Logan Andrew J | Biosolids-based food additive for animal feed, methods of production, and business application thereof |
CN101492230A (en) * | 2009-03-12 | 2009-07-29 | 农业部环境保护科研监测所 | Comprehensive processing process and system for cultivation wastewater |
CN101531437A (en) * | 2008-03-12 | 2009-09-16 | 中国科学院成都生物研究所 | Compound treatment method of wastewater in pig farm |
CN101759323A (en) * | 2009-12-24 | 2010-06-30 | 江西省科学院能源研究所 | Treatment combined process for pig farm waste water with high nitrogen content |
WO2012009462A9 (en) * | 2010-07-13 | 2012-05-03 | Ecologico-Logic, Inc. | Solid waste digestion system |
CN103086566A (en) * | 2012-12-17 | 2013-05-08 | 贵州长绿科技有限公司 | Method for processing aquaculture wastewater of pig farm |
CN103858829A (en) * | 2014-03-28 | 2014-06-18 | 南开大学 | Method for breeding earthworms through biomass solid waste |
CN104016557A (en) * | 2014-05-13 | 2014-09-03 | 湖南山河美生物环保科技股份有限公司 | Governance method for realizing resource utilization and zero pollution emission of piggery wastes |
CN104098236A (en) * | 2014-08-01 | 2014-10-15 | 天津乾益能源环境工程有限公司 | New wastewater treatment process of large livestock feeding farm |
-
2014
- 2014-10-21 CN CN201410560918.1A patent/CN104310705A/en active Pending
Patent Citations (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20030141245A1 (en) * | 2001-02-15 | 2003-07-31 | Fetterman Lewis M. | Method for the treatment of animal waste and products made therefrom |
JP2008200637A (en) * | 2007-02-21 | 2008-09-04 | Mizu Kankyo Kenkyusho:Kk | Water treatment plant, water treatment facility, and water treating method |
US20090114602A1 (en) * | 2007-11-01 | 2009-05-07 | Logan Andrew J | Biosolids-based food additive for animal feed, methods of production, and business application thereof |
CN101531437A (en) * | 2008-03-12 | 2009-09-16 | 中国科学院成都生物研究所 | Compound treatment method of wastewater in pig farm |
CN101492230A (en) * | 2009-03-12 | 2009-07-29 | 农业部环境保护科研监测所 | Comprehensive processing process and system for cultivation wastewater |
CN101759323A (en) * | 2009-12-24 | 2010-06-30 | 江西省科学院能源研究所 | Treatment combined process for pig farm waste water with high nitrogen content |
WO2012009462A9 (en) * | 2010-07-13 | 2012-05-03 | Ecologico-Logic, Inc. | Solid waste digestion system |
CN103086566A (en) * | 2012-12-17 | 2013-05-08 | 贵州长绿科技有限公司 | Method for processing aquaculture wastewater of pig farm |
CN103858829A (en) * | 2014-03-28 | 2014-06-18 | 南开大学 | Method for breeding earthworms through biomass solid waste |
CN104016557A (en) * | 2014-05-13 | 2014-09-03 | 湖南山河美生物环保科技股份有限公司 | Governance method for realizing resource utilization and zero pollution emission of piggery wastes |
CN104098236A (en) * | 2014-08-01 | 2014-10-15 | 天津乾益能源环境工程有限公司 | New wastewater treatment process of large livestock feeding farm |
Non-Patent Citations (1)
Title |
---|
覃环等: ""工厂化猪场的粪水处理方法"", 《广东农机》, no. 4, 31 December 1998 (1998-12-31) * |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106007311A (en) * | 2016-06-30 | 2016-10-12 | 宾阳县东洋养殖有限公司 | Environment-friendly ecological recycling method for pig manure |
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