CN105776611B - It is not digested object and organic fertilizer base fluid preparation method in removal anaerobic digestion solution - Google Patents
It is not digested object and organic fertilizer base fluid preparation method in removal anaerobic digestion solution Download PDFInfo
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Classifications
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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
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; AVICULTURE; APICULTURE; PISCICULTURE; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K1/00—Housing animals; Equipment therefor
- A01K1/015—Floor coverings, e.g. bedding-down sheets ; Stable floors
- A01K1/0157—Mats; Sheets
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/121—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
- C02F11/127—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering by centrifugation
-
- 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
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
-
- 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
-
- 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
-
- 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
- C02F1/38—Treatment of water, waste water, or sewage by centrifugal separation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/08—Multistage treatments, e.g. repetition of the same process step under different conditions
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/06—Nutrients for stimulating the growth of microorganisms
-
- 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
- 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
-
- 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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- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Environmental Sciences (AREA)
- Biodiversity & Conservation Biology (AREA)
- Microbiology (AREA)
- Mechanical Engineering (AREA)
- Animal Husbandry (AREA)
- Zoology (AREA)
- Fertilizers (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
本发明公开了一种分级去除厌氧消化液中大颗粒未被消化分解有机物和泥沙的方法和以去除了大颗粒未被消化分解有机物和泥沙后的厌氧消化液为原料制备有机液肥基液的方法。其中,分级处理分离出的大颗粒未被消化分解的植物纤维等有机物和泥沙等无机物用于固体沼肥或土壤调理剂的初始原料,分级处理获得的厌氧消化液沼渣、沼液用于制备有机液肥基液的初始原料。本发明所提供的方法能够将大颗粒未被消化分解的植物纤维等有机物和泥沙等无机物从厌氧消化液中去除,并利用去除大颗粒未被消化分解有机物和泥沙无机物后的厌氧消化液制备有机液肥基液产品,从而解决了厌氧消化液资源化再利用的瓶颈问题。
The invention discloses a method for classifying and removing large particles of undigested and decomposed organic matter and sediment in anaerobic digestion liquid and preparing organic liquid fertilizer by using the anaerobic digestion liquid after removing large particles of undigested and decomposed organic matter and sediment as raw materials Base method. Among them, the organic matter such as plant fibers such as large particles that have not been digested and decomposed by the classification process, and the inorganic matter such as sediment are used as the initial raw materials for solid biogas manure or soil conditioner, and the anaerobic digested liquid biogas residue and biogas slurry obtained by the classification process The starting material for the preparation of organic liquid fertilizer base liquid. The method provided by the invention can remove large particles of undigested and decomposed plant fibers and other inorganic substances such as silt from the anaerobic digestion solution, and utilize The anaerobic digestion solution is used to prepare organic liquid fertilizer base liquid products, thereby solving the bottleneck problem of resource reuse of anaerobic digestion solution.
Description
技术领域technical field
本发明涉及资源回收利用领域,具体涉及一种分级去除厌氧消化液中大颗粒未被消化分解有机物和泥沙的方法和以去除了大颗粒未被消化分解有机物和泥沙后的厌氧消化液为原料制备有机液肥基液的方法。The invention relates to the field of resource recovery and utilization, in particular to a method for graded removal of large particles of undigested and decomposed organic matter and sediment in anaerobic digestion liquid and anaerobic digestion after removing large particles of undigested and decomposed organic matter and sediment A method for preparing organic liquid fertilizer base liquid with liquid as raw material.
背景技术Background technique
厌氧发酵产沼气是有效利用包括畜禽粪便、作物秸秆等生物质资源获得生物质能源的重要途径之一。目前,随着产业化沼气的发展,制约大型工业化沼气工程经济效益的厌氧发酵副产物厌氧消化液(沼渣、沼液混合物)的有效利用和合理消纳已经成为影响大型沼气工程可持续商业化运行的瓶颈问题。厌氧消化液资源化利用的限制因素主要反映在如下方面:Biogas production by anaerobic fermentation is one of the important ways to effectively utilize biomass resources including livestock and poultry manure and crop straw to obtain biomass energy. At present, with the development of industrialized biogas, the effective utilization and reasonable consumption of anaerobic digestion by-products (biogas residue and biogas slurry mixture), which restricts the economic benefits of large-scale industrialized biogas projects, has become an issue that affects the sustainable development of large-scale biogas projects. Bottleneck problem of commercial operation. The limiting factors of resource utilization of anaerobic digestate are mainly reflected in the following aspects:
1、厌氧发酵副产物厌氧消化液普遍存在体量大、固形物浓度低等特点,成为限制厌氧消化液实现肥料化应用的关键问题。1. Anaerobic digestion liquid, a by-product of anaerobic fermentation, generally has the characteristics of large volume and low solid concentration, which has become a key problem that limits the application of anaerobic digestion liquid to fertilizer.
2、厌氧消化液(沼液)所含营养物质的稳定性问题。由于厌氧消化液自身的特点,普遍存在营养成分低、稳定性差等问题,导致生产成本高、不便于运输及施用。因此,稳定性决定了厌氧消化液作为营养液应用的输送范围和贮存时间,决定了厌氧消化液肥料化应用的经济性和可行性。2. Stability of nutrients contained in anaerobic digestion liquid (biogas slurry). Due to the characteristics of anaerobic digestion liquid, there are common problems such as low nutritional content and poor stability, resulting in high production costs and inconvenient transportation and application. Therefore, the stability determines the delivery range and storage time of the anaerobic digestate as a nutrient solution, and determines the economy and feasibility of the fertilizer application of the anaerobic digestate.
3、对于固液分离高湿固体(沼渣)转化为安全的固体沼肥,亟待解决的是高湿固体(沼渣)含水量高、腐植化程度低和禽畜粪便携带的病毒病原菌、杂草种子等有害物质的灭活问题。3. For solid-liquid separation and conversion of high-humidity solids (biogas residues) into safe solid biogas fertilizers, it is urgent to solve the high moisture content of high-humidity solids (biogas residues), low degree of humification, and virus pathogens and miscellaneous bacteria carried by poultry manure. Inactivation of harmful substances such as grass seeds.
4、对于固液分离滤液(沼液)转化为安全的液体沼肥,亟待解决的是沼液浓缩和其中生物活性物质的活性问题,如水溶性问题。尽管现代超滤、微滤、反渗透精细加工技术解决了沼液浓缩技术问题,但是由于沼液中有机成分复杂、养分不均衡,尤其是生物活性物质大部分处于水不溶状态,如蛋白质、氨基酸、腐植酸类物质。因此,必需对液体沼肥组分进行活化、激活其中的生物活性物质,螯合/络合微量元素。4. For the conversion of solid-liquid separation filtrate (biogas slurry) into safe liquid biogas fertilizer, the concentration of biogas slurry and the activity of biologically active substances, such as water solubility, need to be solved urgently. Although modern ultrafiltration, microfiltration, and reverse osmosis fine processing technologies have solved the problem of biogas slurry concentration technology, due to the complex organic components and unbalanced nutrients in biogas slurry, especially most of the biologically active substances are in a water-insoluble state, such as proteins and amino acids. , Humic acid substances. Therefore, it is necessary to activate the components of liquid biogas manure, activate the biologically active substances in it, and chelate/complex trace elements.
厌氧消化液是指畜禽排泄物、城镇生活污水处理厂生活污泥和农作物秸秆等有机废弃物生物质燃气(沼气)工程厌氧发酵产生的副产物。厌氧发酵是由众多微生物参与的非常复杂的分解与转化过程,料液中残留的可溶物很少,大部分可溶物主要是新产生的、种类繁多的有机物及各种离子。厌氧消化液固形物浓度一般在5%-8%,主要是由游离状态的水和植物纤维、泥沙、细菌、粘土、胶体、农药残留物、悬浮物及其含有腥臭气味的有机物组成。Anaerobic digestion solution refers to the by-products produced by anaerobic fermentation of organic waste such as livestock excrement, urban domestic sewage treatment plant domestic sludge and crop straw. Anaerobic fermentation is a very complex decomposition and conversion process involving many microorganisms. There are very few solubles left in the feed liquid, and most of the solubles are mainly newly produced, various organic substances and various ions. The solid concentration of anaerobic digestion liquid is generally 5%-8%, mainly composed of free water and plant fiber, sediment, bacteria, clay, colloid, pesticide residues, suspended matter and organic matter with a foul smell.
任何事物都具有其两重性。一方面,厌氧消化液未经无害化、稳定化处理直接施用于作物等农田土壤,不仅不符合农用卫生标准造成农田的二次污染,还会对作物生长条件及生长环境造成不利影响,况且直接施用量大,势必增加运输成本和劳动强度,更何况在非用肥季节得不到充分利用,造成多余的厌氧消化液的无序排放,又会进一步加剧环境污染和资源浪费。另一方面,厌氧消化液中含有多种无机养分和活性有机成分。无机养分包括氮、磷、钾、钙、镁等多种元素和少量微量元素。活性有机成分包括腐植酸、吲哚乙酸、乳酸菌、赤霉素、细胞分裂素等植物激素和B族维生素,还含有多种氨基酸、蛋白质、水解酶以及多种无机酸和某些抗菌素等。无机养分与有机成分之间互相协调作用以速效养分和生物农药的形式存在于厌氧消化液中,可直接迅速被农作物吸收和杀死有害病菌及虫卵。Everything has its duality. On the one hand, the anaerobic digestion solution is directly applied to farmland soil such as crops without harmless and stabilized treatment, which not only does not meet the agricultural hygiene standards and causes secondary pollution of the farmland, but also adversely affects the growth conditions and growth environment of crops. Moreover, the large amount of direct application will inevitably increase transportation costs and labor intensity, not to mention that it will not be fully utilized in non-fertilizer seasons, resulting in the disorderly discharge of excess anaerobic digestion liquid, which will further aggravate environmental pollution and waste of resources. On the other hand, the anaerobic digestate contains a variety of inorganic nutrients and active organic components. Inorganic nutrients include nitrogen, phosphorus, potassium, calcium, magnesium and other elements and a small amount of trace elements. Active organic ingredients include humic acid, indole acetic acid, lactic acid bacteria, gibberellin, cytokinin and other plant hormones and B vitamins, and also contain a variety of amino acids, proteins, hydrolytic enzymes, various inorganic acids and some antibiotics. The mutual coordination between inorganic nutrients and organic components exists in the anaerobic digestive juice in the form of quick-acting nutrients and biological pesticides, which can be directly and quickly absorbed by crops and kill harmful bacteria and insect eggs.
厌氧消化液经无害化、稳定化处理,作为沼肥应用,对小麦、豆类和蔬菜的蚜虫防治具有明显效果,对多种农作物病菌有较强抑制作用。因此,科学施用沼肥能提高土壤中有机质和营养元素的含量,改善土壤结构,提高土壤肥力。The anaerobic digestion solution is harmless and stabilized, and it is used as a biogas fertilizer. It has obvious effects on the control of aphids in wheat, beans and vegetables, and has a strong inhibitory effect on various crop pathogens. Therefore, the scientific application of biogas fertilizer can increase the content of organic matter and nutrient elements in the soil, improve the soil structure, and improve soil fertility.
因此,为了避免疾病传播和土壤污染,厌氧消化液作为肥料化应用需要进行无害化、稳定化处理后方可使用,这是厌氧消化液肥料化延伸应用的前提条件。其中,行之有效的办法就是分级处理,分离出大颗粒未被消化分解的、不稳定的有机物和无机成分,用于固体沼肥或土壤调理剂生产的初始原料。分离出水沼液经浓缩处理和活化,用于有机液肥生产的初始原料。厌氧消化液是一个复杂的固相、液相混合体,其中的植物纤维等未被消化物质的相对浓度很高,必须对其进行有效的过滤分离。尽管现代固液分离技术能够缓解厌氧消化液固液分离的技术问题,但是都无法解决厌氧消化液分级处理、精细分离的技术问题,都存在高能耗、使用寿命短、运行成本高等问题,均不能满足大规模处理利用厌氧消化液的生产要求。即便是传统的生物工程技术,如高温好氧发酵(堆肥)处理技术,也只能解决有机高湿固体分(沼渣)的处理问题,大量的、低浓度分离出水(沼液)仍然存在处理和消纳问题,仍然无法满足厌氧消化液肥料化应用的基本要求。因此,必须结合多层次、多元化的分离技术,集成、整合现有过滤分离技术,对厌氧消化液进行多级多层次过滤分级、浓缩,提高其中有机成分含量和生物活性,降低粗纤维和灰分含量,也就成为厌氧消化液肥料化利用必须攻克的技术难关。Therefore, in order to avoid the spread of diseases and soil pollution, the application of anaerobic digestive juice as a fertilizer needs to be harmless and stabilized before it can be used. This is a prerequisite for the extended application of anaerobic digested liquid fertilizer. Among them, the effective method is to classify and separate large particles that have not been digested and decomposed, unstable organic and inorganic components, and use them as initial raw materials for the production of solid biogas fertilizer or soil conditioner. The separated biogas slurry is concentrated and activated, and is used as the initial raw material for the production of organic liquid fertilizer. Anaerobic digestion solution is a complex mixture of solid phase and liquid phase, in which the relative concentration of undigested substances such as plant fibers is very high, which must be effectively filtered and separated. Although modern solid-liquid separation technology can alleviate the technical problems of solid-liquid separation of anaerobic digestion liquid, they cannot solve the technical problems of graded treatment and fine separation of anaerobic digestion liquid, and all have problems such as high energy consumption, short service life, and high operating costs. All cannot meet the production requirements of large-scale processing and utilization of anaerobic digestate. Even the traditional bioengineering technology, such as high-temperature aerobic fermentation (composting) treatment technology, can only solve the problem of organic high-humidity solids (biogas residue), and a large amount of low-concentration separated water (biogas slurry) still exists. However, it still cannot meet the basic requirements of the application of anaerobic digestate fertilizer. Therefore, it is necessary to combine multi-level and diversified separation technologies, integrate and integrate existing filtration and separation technologies, carry out multi-level and multi-level filtration, classification and concentration of anaerobic digestion liquid, increase the content of organic components and biological activity, reduce crude fiber and The ash content has also become a technical difficulty that must be overcome for the fertilization of anaerobic digested liquid.
发明内容Contents of the invention
本发明的第一个目的在于解决厌氧消化液回收利用过程中存在的上述问题,提供一种能够高效分离、去除厌氧消化液中大颗粒未被消化分解的、不稳定的有机物和无机成分的方法。The first object of the present invention is to solve the above-mentioned problems in the recycling process of anaerobic digestion liquid, and provide a method that can efficiently separate and remove unstable organic and inorganic components that have not been digested and decomposed by large particles in anaerobic digestion liquid Methods.
本发明的第二个目的在于提供利用去除了大颗粒未被消化分解的、不稳定的有机物和无机成分后的厌氧消化液为原料制备的有机液肥基液及其制备方法。The second object of the present invention is to provide an organic liquid fertilizer base liquid prepared by using the anaerobic digestion liquid after removing large particles of undigested and decomposed, unstable organic matter and inorganic components as raw material and its preparation method.
为达到以上目的,本发明提供了一种厌氧消化液分级去除大颗粒未被消化分解有机物和泥沙的方法,包括以下步骤:In order to achieve the above object, the present invention provides a method for anaerobic digestion solution to remove large particles of undigested and decomposed organic matter and sediment by classification, comprising the following steps:
a)一级过滤分离:利用12、14、16、18或20目过滤离心机对厌氧消化液进行一级过滤分离,获得一级滤渣和一级滤液,将所述一级滤渣置于一级大颗粒未被消化分解有机物和泥沙贮槽中,将所述一级滤液置于一级滤液贮槽中;a) Primary filtration and separation: use 12, 14, 16, 18 or 20 mesh filter centrifuges to perform primary filtration and separation of anaerobic digestion liquid to obtain primary filter residue and primary filtrate, and place the primary filter residue in a The first-level filtrate is placed in the first-level filtrate storage tank;
b)二级过滤分离:利用100、120或140目过滤离心机对所述一级滤液进行二级过滤离心分离,获得二级滤渣和二级滤液,将所述二级滤渣置于二级滤渣贮槽中,将所述二级滤液置于二级滤液贮槽中;b) Secondary filtration and separation: use a 100, 120 or 140 mesh filter centrifuge to carry out secondary filtration and centrifugal separation of the primary filtrate to obtain secondary filter residue and secondary filtrate, and place the secondary filter residue in the secondary filter residue In the storage tank, the secondary filtrate is placed in the secondary filtrate storage tank;
c)反向冲洗大颗粒未被消化分解有机物和泥沙:将二级滤液贮槽中的液体与一级未被消化分解有机物和泥沙贮槽中的大颗粒未被消化分解有机物和泥沙混合,获得反向冲洗混合液,利用12、14、16、18或20目过滤离心机对所述反向冲洗混合液进行一级过滤离心分离,获得一级一次冲洗大颗粒未被消化分解有机物和泥沙滤渣和一级一次冲洗滤液,将所述一级一次冲洗大颗粒未被消化分解有机物和泥沙滤渣置于一级大颗粒未被消化分解有机物和泥沙贮槽中,利用100、120或140目过滤离心机对所述一级一次冲洗滤液进行二级过滤离心分离,获得一级一次冲洗滤液的二级滤渣和一级一次冲洗滤液的二级滤液,将所述一级一次冲洗滤液的二级滤渣回到二级滤渣贮槽,将所述一级一次冲洗滤液的二级滤液回到二级滤液贮槽,完成一次大颗粒未被消化分解有机物和泥沙的反向冲洗过程,循环上述反向冲洗过程2-3次后回到一级未被消化分解有机物和泥沙贮槽中的为大颗粒未被消化分解有机物和泥沙等分离物、回到二级滤渣贮槽中的为去除了大颗粒未被消化分解有机物和泥沙的粗沼渣、回到二级滤液贮槽中的为去除了大颗粒未被消化分解有机物和泥沙的沼液。c) Backwash large particles of undigested and decomposed organic matter and sediment: combine the liquid in the secondary filtrate storage tank with the large particles of undigested and decomposed organic matter and sediment in the primary undigested and decomposed organic matter and sediment storage tank Mix to obtain a reverse flushing mixture, and use a 12, 14, 16, 18 or 20 mesh filter centrifuge to perform primary filtration and centrifugation on the reverse flushing mixture to obtain a primary flushing of large particles that have not been digested and decomposed organic matter and silt filter residue and primary flushing filtrate, place the primary large particle undigested and decomposed organic matter and silt storage tank in the primary primary flushing large particles of undigested and decomposed organic matter and silt storage tank, utilize 100, A 120 or 140 mesh filter centrifuge performs secondary filtration and centrifugation on the first-level primary flushing filtrate to obtain the secondary filter residue of the primary primary flushing filtrate and the secondary filtrate of the primary primary flushing filtrate, and the primary primary flushing filtrate The secondary filter residue of the filtrate is returned to the secondary filter residue storage tank, and the secondary filtrate of the first-level primary flushing filtrate is returned to the secondary filtrate storage tank to complete a reverse flushing process of large particles that have not been digested and decomposed organic matter and sediment , cycle the above backwashing process for 2-3 times and then return to the primary undigested and decomposed organic matter and sediment storage tank for large particles of undigested and decomposed organic matter and sediment, and return to the secondary filter residue storage tank Among them is the coarse biogas residue that has removed large particles of undigested and decomposed organic matter and sediment, and the biogas slurry that has removed large particles of undigested and decomposed organic matter and sediment is returned to the secondary filtrate storage tank.
在本发明中,所述厌氧消化液,为大型工业化沼气工程厌氧发酵副产物。所述大颗粒未被消化分解有机物主要为植物纤维,所述泥沙主要为原料携带进厌氧发酵系统的无机物。大颗粒指代12、14、16、18或20目筛的筛上物。In the present invention, the anaerobic digestion liquid is a by-product of anaerobic fermentation of a large-scale industrial biogas project. The large particles of undigested and decomposed organic matter are mainly plant fibers, and the silt is mainly inorganic matter carried into the anaerobic fermentation system by raw materials. Larger particles refer to the oversize of 12, 14, 16, 18 or 20 mesh sieves.
可选的,所述厌氧消化液是以牛粪、猪粪、鸡粪等畜禽粪污中的至少一种以及作物秸秆(例如玉米秸秆)为原料进行厌氧发酵产沼气后得到的副产物。Optionally, the anaerobic digestion solution is a by-product obtained after anaerobic fermentation of at least one of livestock and poultry manure such as cow manure, pig manure, chicken manure, and crop straw (such as corn straw) as raw materials to produce biogas. product.
其中,所述厌氧消化液中固含量为5-10质量%。Wherein, the solid content in the anaerobic digestion liquid is 5-10% by mass.
优选的,在一级过滤分离步骤中,所使用的过滤离心机的过滤介质为12、14或16目,电机转子转速为1400rmp。Preferably, in the primary filtration and separation step, the filter medium of the filter centrifuge used is 12, 14 or 16 mesh, and the motor rotor speed is 1400rmp.
其中,在反向冲洗步骤中,所述反向冲洗混合液中固含量为5-20质量%。Wherein, in the step of backwashing, the solid content in the backwashing mixed solution is 5-20% by mass.
本发明还提供了上述厌氧消化液分级处理去除大颗粒未被消化分解有机物和泥沙的方法在含大颗粒未被消化分解有机物和泥沙等无机物的厌氧消化液的资源化再利用中的应用。The present invention also provides a method for the above-mentioned anaerobic digestion liquid classification treatment to remove large particles of undigested and decomposed organic matter and sediment, and resource reuse of anaerobic digestion liquid containing inorganic matter such as large particles of undigested and decomposed organic matter and sediment in the application.
可选的,所述应用为回收利用大颗粒未被消化分解有机物和泥沙作为固体沼肥或土壤调理剂的初始原料。Optionally, the application is to recycle large particles of undigested and decomposed organic matter and sediment as initial raw materials for solid biogas fertilizer or soil conditioner.
所述应用为回收大颗粒未被消化分解有机物和泥沙作为有机固体沼肥系统的初始原料和/或畜禽养殖垫料和/或微生物的载体。The application is to recover large particles of undigested and decomposed organic matter and sediment as the initial raw material of an organic solid biogas fertilizer system and/or livestock and poultry breeding litter and/or a carrier of microorganisms.
可选的,所述应用为回收利用去除了大颗粒未被消化分解有机物和泥沙的粗沼渣和/或沼液中的生物活性物质和营养成分。Optionally, the application is to recycle bioactive substances and nutrients in coarse biogas residue and/or biogas slurry from which large particles of undigested and decomposed organic matter and sediment have been removed.
特别值得注意的是,本发明提供了一种以去除大颗粒未被消化分解有机物和泥沙的粗沼渣和/或沼液为原料制备有机液肥基液的方法,所述方法包括以下步骤:It is particularly worth noting that the present invention provides a method for preparing organic liquid fertilizer base liquid by removing large particles of coarse biogas residue and/or biogas slurry that have not been digested and decomposed organic matter and sediment as raw materials, and the method includes the following steps:
(1)去除大颗粒未被消化分解有机物和泥沙:利用本发明所述的厌氧消化液分级去除大颗粒未被消化分解有机物和泥沙的方法获得去除了大颗粒未被消化分解有机物和泥沙的粗沼渣以及去除了大颗粒未被消化分解有机物和泥沙的沼液;(1) Remove large particles of undigested and decomposed organic matter and silt: the method for removing large particles of undigested and decomposed organic matter and silt by using the anaerobic digestion liquid of the present invention removes large particles of undigested and decomposed organic matter and silt Coarse biogas residue of sediment and biogas slurry from which large particles of undigested and decomposed organic matter and sediment have been removed;
(2)反向浓缩:将粗沼渣和沼液在密闭容器中接触分散混合15-30min,获得固含量为10-30质量%的反向浓缩液;(2) Reverse concentration: contact, disperse and mix the coarse biogas residue and biogas slurry in a closed container for 15-30 minutes to obtain a reverse concentrated solution with a solid content of 10-30% by mass;
(3)激活生物活性物质:对所述反向浓缩液进行高频高剪切分散乳化处理60-120min,获得高生理活性厌氧消化浓缩液;(3) Activate biologically active substances: perform high-frequency high-shear dispersion and emulsification treatment on the reverse concentrated solution for 60-120 minutes to obtain a highly physiologically active anaerobic digestion concentrated solution;
(4)三级过滤分离:利用170或200目过滤离心机对所述高生理活性厌氧消化浓缩液进行三级过滤分离,获得三级滤渣和三级滤液,所述三级滤液为高生理活性有机液肥基液。(4) Three-stage filtration and separation: use a 170 or 200 mesh filter centrifuge to perform three-stage filtration and separation on the highly physiologically active anaerobic digestion concentrate to obtain a three-stage filter residue and a three-stage filtrate. Active organic liquid fertilizer base liquid.
其中,所述方法还包括将所述三级滤渣回到二级滤渣贮槽中与所述粗沼渣合并后,再与沼液接触分散混匀进行下一循环的反向浓缩处理。Wherein, the method further includes returning the third-stage filter residue to the secondary filter residue storage tank to combine with the coarse biogas residue, and then contacting biogas slurry to disperse and mix for the next cycle of reverse concentration treatment.
其中,在反向浓缩并激活生物活性物质的过程中,优选利用间歇式捷流分散混合机将所述去除大颗粒未被消化分解有机物和泥沙的粗沼渣与所述去除大颗粒未被消化分解有机物和泥沙的沼液充分分散混合15-30min,分散混合均匀的反向浓缩液优选进入管线式高剪切分散乳化机进行循环往复、高频、高剪切分散乳化60-120min,激活反向浓缩液中的生物活性物质。间歇式捷流分散混合机和管线式高剪切分散乳化机转子转速优选为2900转/分。Among them, in the process of reverse concentration and activation of biologically active substances, it is preferable to use a batch-type jet flow dispersing mixer to combine the coarse biogas residue from the removal of large particles that have not been digested and decomposed organic matter and sediment with the removal of large particles that have not been digested. The biogas slurry that digests and decomposes organic matter and sediment is fully dispersed and mixed for 15-30 minutes, and the uniformly dispersed and mixed reverse concentrate is preferably entered into a pipeline-type high-shear dispersing emulsifier for reciprocating, high-frequency, high-shear dispersing and emulsifying for 60-120 minutes. Activates biologically active substances in reverse concentrate. The rotor speed of the intermittent jet flow dispersing mixer and the pipeline high shear dispersing emulsifier is preferably 2900 rpm.
更具体的:容器内的物料在捷流式分散混合机高速旋转的转子带动下,物料中的水不溶物在转子导流腔的作用下产生一股强烈的液体垂直环流,迫使物料中的水不溶物在罐体容器内整体循环,达到宏观上的混合。同时,高速旋转的转子产生微观混合所要达到的剪切紊流,经过微观紊流混合处理的液体随着整体液流的循环被分散到罐体容器的各个角落,促使罐体容器里物料中的水不溶物都能被彻底分散混合,这与传统搅拌器的混合方式是完全不同的。More specifically: the material in the container is driven by the high-speed rotating rotor of the jet-flow dispersion mixer, and the water-insoluble matter in the material generates a strong vertical liquid circulation under the action of the rotor guide cavity, forcing the water in the material to The insoluble matter circulates in the tank container as a whole to achieve macroscopic mixing. At the same time, the high-speed rotating rotor produces the shear turbulent flow that microscopic mixing needs to achieve. The liquid that has been mixed with microscopic turbulent flow is dispersed to every corner of the tank container along with the circulation of the overall liquid flow, which promotes the turbulence in the material in the tank container. Water-insoluble substances can be thoroughly dispersed and mixed, which is completely different from the traditional mixer.
更进一步的:经捷流式分散混合机处理的被彻底分散混合的“反向浓缩液”进入管线式高剪切分散乳化机,经其高速旋转的转子所产生的高切线速度和高频机械效应作用下产生强劲的动能,又迫使“反向浓缩液”中的互不相溶的固相、液相、气相在定、转子狭窄的间隙中受到强烈的机械及液力剪切、离心挤压、液层摩擦、撞击撕裂和湍流等综合作用下,瞬间、均匀、精细、分散和乳化。去除大颗粒未被消化分解有机物和泥沙的反向浓缩液在通常情况下各个相是互不相溶的,管线式高剪切分散乳化机的作用是将容器内的混合液体高效、快速、均匀地从一个相或多个相分布到另一个连续相中,最终得到稳定的高品质产品。Further: the thoroughly dispersed and mixed "reverse concentrate" processed by the jet-flow dispersing mixer enters the pipeline-type high-shear dispersing emulsifier, and the high tangential speed and high-frequency mechanical force produced by its high-speed rotating rotor The strong kinetic energy is generated under the effect, and the immiscible solid phase, liquid phase, and gas phase in the "reverse concentrated solution" are forced to be subjected to strong mechanical and hydraulic shearing and centrifugal extrusion in the narrow gap between the stator and the rotor. Under the combined effects of pressure, liquid layer friction, impact tearing and turbulence, it can be instant, uniform, fine, dispersed and emulsified. The reverse concentrated liquid that removes large particles of undigested and decomposed organic matter and sediment is usually immiscible with each other. The role of the pipeline high-shear dispersing emulsifier is to efficiently, quickly and efficiently mix the liquid in the container. Evenly distributed from one phase or multiple phases to another continuous phase, and finally a stable high-quality product is obtained.
另一方面,去除大颗粒未被消化分解有机物和泥沙的沼渣的反向浓缩沼液在捷流式分散混合机和管线式高剪切分散乳化机联合作用下,“反向浓缩沼液”中的粗蛋白、大分子腐植酸(HA)等活性物质受到激烈碰撞、扯动,粗蛋白裂解出大量小分子游离氨基酸水溶物或水不溶物,大分子腐植酸(HA)裂解出大量小分子黄腐酸水溶物或水不溶物,溶解或分散在去除大颗粒未被消化分解有机物和泥沙的沼渣的反向浓缩沼液中,再经170或200目过滤离心机进行三级过滤分离,“三级滤渣”(细沼渣)回到“二级滤渣”(粗沼渣)贮槽进入下一循环反向浓缩处理,“三级滤液”即为一种具有高生理活性的有机液肥基液(母液)产品。On the other hand, the reverse concentrated biogas slurry that removes large particles of undigested and decomposed organic matter and sediment is combined with a jet-flow dispersing mixer and a pipeline-type high-shear dispersing emulsifier, "reverse concentrated biogas slurry Active substances such as crude protein and macromolecular humic acid (HA) in the "was subjected to violent collision and tearing, and the crude protein was cracked to produce a large number of small molecular free amino acid water-soluble or water-insoluble substances, and the macromolecular humic acid (HA) was cracked to produce a large number of small Molecular fulvic acid water-soluble or water-insoluble matter is dissolved or dispersed in the reverse concentrated biogas slurry that removes large particles of undigested and decomposed organic matter and sediment, and then undergoes three-stage filtration through a 170 or 200 mesh filter centrifuge Separation, the "tertiary filter residue" (fine biogas residue) returns to the "secondary filter residue" (coarse biogas residue) storage tank and enters the next cycle of reverse concentration treatment, and the "tertiary filtrate" is an organic substance with high physiological activity Liquid fertilizer base liquid (mother liquid) product.
利用本发明所述的制备方法获得的有机液肥基液也属于本发明的保护范围。The organic liquid fertilizer base liquid obtained by the preparation method of the present invention also belongs to the protection scope of the present invention.
本发明中的部分内容以牛粪、猪粪、鸡粪中的至少一种以及作物秸秆(主要为玉米秸秆)为原料进行厌氧发酵产沼气得到的副产物厌氧消化液的主要成分组成为例子进行说明,其主要大颗粒未被消化分解有机物主要为植物纤维,泥沙主要为原料或进料携带进厌氧发酵系统的无机物。但是需要注意的是,不能因此限制了本发明的应用范围,本发明也同时适用于其他含有大颗粒未被消化分解有机物和/或泥沙等无机物的厌氧消化液的处理。Part of the content of the present invention uses at least one of cow dung, pig manure, chicken manure and crop stalks (mainly corn stalks) as raw materials for anaerobic fermentation to produce biogas. The main components of the by-product anaerobic digestion liquid are as follows: An example is used to illustrate that the main undigested and decomposed organic matter is mainly plant fiber, and the sediment is mainly inorganic matter carried into the anaerobic fermentation system by raw materials or feed. However, it should be noted that the scope of application of the present invention cannot be limited by this, and the present invention is also applicable to the treatment of other anaerobic digestion liquids containing large particles of undigested and decomposed organic matter and/or inorganic matter such as sediment.
应当理解的是,在本发明中,一级、二级、三级等定语仅用于对不同处理过程和不同物料进行区分,并非用于严格的代表处理过程的特定顺序和获得物料的先后顺序。It should be understood that in the present invention, attributives such as primary, secondary, and tertiary are only used to distinguish different processing processes and different materials, and are not used to strictly represent the specific sequence of processing processes and the sequence of obtaining materials .
去除厌氧消化液中大颗粒未被消化分解有机物和泥沙的流程图如图1所示。以去除了大颗粒未被消化分解有机物和泥沙后的粗沼渣和沼液为原料制备有机液肥基液的流程图如图2所示。The flow chart of removing large particles of undigested and decomposed organic matter and sediment in the anaerobic digestion solution is shown in Figure 1. The flow chart of preparing organic liquid fertilizer base liquid from coarse biogas residue and biogas slurry after removing large particles of undigested and decomposed organic matter and sediment is shown in Figure 2.
本发明具有如下优点和有益效果:The present invention has following advantage and beneficial effect:
1、本发明是根据初始厌氧消化液的组分特征,选择了一条分级处理去除初始厌氧消化液中大颗粒未被消化分解有机物和泥沙的工艺路线,并可以利用其去除了大颗粒未被消化分解有机物和泥沙的厌氧消化液为原料制备有机液肥基液产品。其中,关键技术为“双反向”、“一激活”技术。1. According to the characteristics of the components of the initial anaerobic digestion liquid, the present invention selects a process route for graded treatment to remove large particles in the initial anaerobic digestion liquid that have not been digested and decomposed organic matter and sediment, and can use it to remove large particles The anaerobic digestion liquid that has not been digested and decomposed organic matter and sediment is used as a raw material to prepare organic liquid fertilizer base liquid products. Among them, the key technology is "double reverse" and "one activation" technology.
(1)反向冲洗技术。采用100、120或140目筛筛下的二级滤液贮槽中的液体作为大颗粒未被消化分解有机物和泥沙冲洗剂反向冲洗大颗粒未被消化分解有机物和泥沙2-3次,避免了大颗粒的未被消化分解有机物和泥沙附着“沼渣”带出系统。(1) Backwash technology. Use the liquid in the secondary filtrate storage tank under the 100, 120 or 140 mesh sieve as large particles of undigested and decomposed organic matter and sediment flushing agent to backwash the large particles of undigested and decomposed organic matter and sediment for 2-3 times, It avoids large particles of undigested and decomposed organic matter and silt attached "digest residue" from being carried out of the system.
(2)反向浓缩技术。去除大颗粒未被消化分解有机物和泥沙的二级滤液贮槽中的沼液中加入100、120或140目筛筛上、12、14、16、18或20目筛筛下的粗沼渣,提高了去除大颗粒未被消化分解有机物和泥沙的二级滤液贮槽中沼液的生物活性物质和营养成分的浓度。(2) reverse concentration technology. Add coarse biogas residue on 100, 120 or 140 mesh sieve, 12, 14, 16, 18 or 20 mesh sieve to the biogas slurry in the secondary filtrate storage tank to remove large particles that have not been digested and decomposed organic matter and sediment , Increase the concentration of biologically active substances and nutrients in the biogas slurry in the secondary filtrate storage tank that removes large particles of undigested and decomposed organic matter and sediment.
(3)活性物质激活技术。采用高频高剪切分散乳化技术激活反向浓缩沼液中的活性物质,提高了后续制备有机液肥基液(母液)产品的功效。(3) Active substance activation technology. The high-frequency high-shear dispersion emulsification technology is used to activate the active substances in the reverse concentrated biogas slurry, which improves the efficacy of the subsequent preparation of organic liquid fertilizer base liquid (mother liquid) products.
2、采用12、14、16、18或20目过滤离心机分离出初始厌氧消化液中的大颗粒未被消化分解有机物和泥沙,降低了有机液肥基液产品粗纤维、尤其是木质素含量和灰分,提高了去除大颗粒未被消化分解有机物和泥沙的厌氧消化液中粗蛋白、氨基酸、腐植酸等有机成分的含量及应用范围。该方法较之初始厌氧消化液粗蛋白质提高50%(占干基百分比),粗纤维降低50%(占干基百分比),解决了初始厌氧消化液中大颗粒未被消化分解有机物和泥沙含量高、处理处置难的问题,实现了初始厌氧消化液肥料化、商品化和优质化。2. Use 12, 14, 16, 18 or 20 mesh filter centrifuges to separate large particles in the initial anaerobic digestion liquid that have not been digested and decomposed organic matter and sediment, reducing the crude fiber, especially lignin, of organic liquid fertilizer base liquid products It improves the content and application range of organic components such as crude protein, amino acids, and humic acid in the anaerobic digestion solution that removes large particles of undigested and decomposed organic matter and sediment. Compared with the initial anaerobic digestion solution, the crude protein is increased by 50% (accounting for the percentage of dry basis), and the crude fiber is reduced by 50% (accounting for the percentage of dry basis), which solves the problem of undigested and decomposed organic matter and sludge of large particles in the initial anaerobic digestion solution. The problem of high sand content and difficult disposal has been realized, and the initial anaerobic digestion liquid has been fertilized, commercialized and high-quality.
3、本发明是根据初始厌氧消化液,特别以是牛粪、猪粪、鸡粪和作物秸秆(主要为玉米秸秆)为原料进行厌氧发酵产沼气得到的厌氧消化液的组成特征,选择了一条分级处理去除初始厌氧消化液中大颗粒的未被消化分解有机物和泥沙的工艺路线,从初始厌氧消化液中分离出的大颗粒未被消化分解有机物和泥沙作为有机固体沼肥系统的初始原料和/或畜禽养殖垫料和/或微生物的载体加以利用。3. The present invention is based on the compositional characteristics of the initial anaerobic digested liquid, especially the anaerobic digested liquid obtained by anaerobic fermentation with biogas produced from raw materials such as cow dung, pig manure, chicken manure and crop stalks (mainly corn stalks), A process route for graded treatment to remove large particles of undigested and decomposed organic matter and sediment in the initial anaerobic digestion liquid was selected, and the large particles of undigested and decomposed organic matter and sediment separated from the initial anaerobic digestion liquid were regarded as organic solids The initial raw materials of the biogas fertilizer system and/or livestock and poultry breeding litter and/or microbial carriers are used.
4、有机液肥基液的制备工艺选择了一条物理激活活性物质的工艺路线,有效提高了有机液肥基液(母液)产品中的各类氨基酸、腐植酸(尤其是黄腐酸)等有机酸含量和生态环境安全性,为厌氧消化液的协同处理工艺提供了基础。可应用于大规模生产,成本低、操作简单。4. The preparation process of organic liquid fertilizer base liquid chooses a process route of physically activating active substances, which effectively improves the content of various amino acids, humic acid (especially fulvic acid) and other organic acids in the organic liquid fertilizer base liquid (mother liquid) products And the safety of the ecological environment provides a basis for the synergistic treatment process of anaerobic digestion liquid. It can be applied to large-scale production, and has low cost and simple operation.
5、采用间歇式捷流分散混合机分散混合、管线式高剪切分散乳化机循环往复、高频分散乳化技术生产的有机液肥基液产品,具有较高的生理活性和较高的稳定性。其中含有丰富的小分子量氨基酸、黄腐酸等有机酸水溶物,不仅可以保持其产品pH、NPK和赘合态植物生长所需微量元素的稳定性,而且作为生长调节剂又能促进植物根系的发育,刺激植株的生长,促进光合作用。5. The organic liquid fertilizer base liquid product produced by intermittent jet flow dispersing mixer, pipeline high-shear dispersing emulsifying machine reciprocating, and high-frequency dispersing and emulsifying technology has high physiological activity and high stability. It is rich in small molecular weight amino acids, fulvic acid and other organic acid water-soluble substances, which can not only maintain the stability of its product pH, NPK and trace elements required for the growth of hypertrophic plants, but also promote the growth of plant roots as a growth regulator. Development, stimulate plant growth, promote photosynthesis.
6、有机液肥基液(母液)为170/200目筛的筛下悬浮液产品,不溶物固体颗粒粒径≤0.089mm/0.0740mm,可确保满足喷、滴灌机具的要求。6. The organic liquid fertilizer base liquid (mother liquid) is a suspension product under a 170/200 mesh sieve, and the particle size of insoluble solid particles is ≤0.089mm/0.0740mm, which can ensure that it meets the requirements of spray and drip irrigation equipment.
本发明集多种功能于一体,能够高效及时地将大量排出的厌氧消化液进行处理,净化环境,减少污染,提高经济效益,可广泛用于大型沼气工程厌氧发酵副产物厌氧消化液(沼渣、沼液混合物)的处理与处置过程。The invention integrates multiple functions, can efficiently and timely process a large amount of discharged anaerobic digestion liquid, purifies the environment, reduces pollution, and improves economic benefits, and can be widely used in large-scale biogas engineering anaerobic fermentation by-product anaerobic digestion liquid (biogas residue, biogas slurry mixture) treatment and disposal process.
下面结合实施例对本发明作进一步说明。The present invention will be further described below in conjunction with embodiment.
附图说明Description of drawings
图1为去除厌氧消化液中大颗粒未被消化分解有机物和泥沙的流程图。Figure 1 is a flow chart for removing large particles of undigested and decomposed organic matter and sediment in anaerobic digestion liquid.
图2以去除了大颗粒未被消化分解有机物和泥沙后的粗沼渣和沼液为原料制备有机液肥基液的流程图。Fig. 2 is a flow chart of preparing organic liquid fertilizer base liquid from coarse biogas residue and biogas slurry after removal of large particles of undigested and decomposed organic matter and sediment.
图1和图2中,(1)实线方向为正方向。(2)虚线方向为反方向,由反向冲洗和反向浓缩组成。(3)点划线方向为活性物质激活方向。In Fig. 1 and Fig. 2, (1) the solid line direction is the positive direction. (2) The direction of the dotted line is the opposite direction, which consists of reverse flushing and reverse concentration. (3) The direction of the dotted line is the activation direction of the active material.
具体实施方式Detailed ways
以下结合附图对本发明的具体实施方式进行详细说明。应当理解的是,此处所描述的具体实施方式仅用于说明和解释本发明,并不用于限制本发明。Specific embodiments of the present invention will be described in detail below in conjunction with the accompanying drawings. It should be understood that the specific embodiments described here are only used to illustrate and explain the present invention, and are not intended to limit the present invention.
实施例1:Example 1:
本实施例用于说明厌氧消化液分级处理并以其去大颗粒未被消化分解有机物和泥沙分离物(去除大颗粒未被消化分解有机物和泥沙后得到的粗沼渣和沼液)为原料制备有机液肥基液的方法,包括下列步骤:This example is used to illustrate the graded treatment of anaerobic digestion liquid and use it to remove large particles of undigested and decomposed organic matter and sediment (coarse biogas residue and biogas slurry obtained after removing large particles of undigested and decomposed organic matter and sediment) The method for preparing organic liquid fertilizer base liquid as raw material comprises the following steps:
(1)去除大颗粒未被消化分解有机物和泥沙:将厌氧消化液(固含量8%)经管道泵送进入LX-950-12目过滤离心机进行一级过滤分离。其中,“一级滤渣”(大颗粒未被消化分解有机物和泥沙)进入一级大颗粒未被消化分解有机物和泥沙贮槽、一级滤液进入一级滤液贮槽待处理。“一级滤液”由贮槽经管道泵送至LX-950-120目过滤离心机进行二级过滤分离处理。其中,120目筛筛上、12目筛筛下的“二级滤渣”(粗沼渣)进入二级滤渣贮槽、120目筛筛下的二级滤液进入二级滤液贮槽待处理。120目筛筛下的“二级滤液”作为“大颗粒未被消化分解有机物和泥沙”反向冲洗剂回到带搅拌的一级大颗粒未被消化分解有机物和泥沙贮槽中与大颗粒未被消化分解有机物和泥沙混合、搅拌稀释,控制固含量小于等于20%,搅拌10min,混合均匀,使大颗粒未被消化分解有机物和泥沙表面的附着物进入到二级滤液中,获得反向冲洗混合液,将反向冲洗混合液泵送进入LX-950-12目过滤离心机,进行第1次一级过滤离心反向冲洗“大颗粒未被消化分解有机物和泥沙”。一级一次冲洗大颗粒未被消化分解有机物和泥沙滤渣重新回到一级大颗粒未被消化分解有机物和泥沙贮槽中与其中的物料混合,第1次“一级一次冲洗滤液”再次回到120目过滤离心机进行二级过滤离心处理,获得一级一次冲洗滤液的二级滤渣和一级一次冲洗滤液的二级滤液。其中,一级一次冲洗滤液的二级滤渣回到二级滤渣贮槽与二级滤渣贮槽中的物料混合,一级一次冲洗滤液的二级滤液回到二级滤液贮槽与二级滤液贮槽中的物料混合,完成第1次大颗粒未被消化分解有机物和泥沙反向冲洗过程,再将此时一级大颗粒未被消化分解有机物和泥沙贮槽中的物料与此时二级滤液贮槽中的物料混合从而循环上述反向冲洗过程,反向冲洗过程共进行3次,结束后,一级大颗粒未被消化分解有机物和泥沙贮槽中的物料为沼渣去除率98%的大颗粒未被消化分解有机物和泥沙,二级滤渣贮槽中的物料和二级滤液贮槽中的物料为大颗粒未被消化分解有机物和泥沙去除率100%的粗沼渣和沼液。洁净的大颗粒的未被消化分解有机物和泥沙经烘干、粉碎回到畜禽养殖场做垫料回用或作为微生物的载体回到有机固体沼肥系统加以利用。(1) Remove large particles of undigested and decomposed organic matter and sediment: the anaerobic digestion solution (solid content 8%) is pumped into the LX-950-12 mesh filter centrifuge through the pipeline for primary filtration and separation. Among them, the "first-level filter residue" (large particles of undigested and decomposed organic matter and sediment) enters the first-level large-particle undigested and decomposed organic matter and sediment storage tank, and the first-level filtrate enters the first-level filtrate storage tank for treatment. The "primary filtrate" is pumped from the storage tank to the LX-950-120 mesh filter centrifuge for secondary filtration and separation treatment. Among them, the "secondary filter residue" (coarse biogas residue) on the 120-mesh sieve and under the 12-mesh sieve enters the secondary filter residue storage tank, and the secondary filtrate under the 120-mesh sieve enters the secondary filtrate storage tank for treatment. The "secondary filtrate" under the 120-mesh sieve is used as a backwashing agent for "large particles of undigested and decomposed organic matter and sediment" and returned to the primary large particle undigested and decomposed organic matter and sediment storage tank with stirring. The undigested and decomposed organic matter and sediment are mixed, stirred and diluted, the solid content is controlled to be less than or equal to 20%, stirred for 10 minutes, and mixed evenly, so that the large particles of undigested and decomposed organic matter and sediment surface attachments enter the secondary filtrate, Obtain the backwash mixture, pump the backwash mixture into the LX-950-12 mesh filter centrifuge, and perform the first primary filter centrifugal backwash "large particles that have not been digested and decomposed organic matter and sediment". First-level flushing of large particles of undigested and decomposed organic matter and sediment filter residues are returned to the first-level large particles of undigested and decomposed organic matter and sediment storage tanks to be mixed with the materials therein, and the first "first-level primary flushing filtrate" is repeated Get back to the 120-mesh filter centrifuge and carry out secondary filtration centrifugation to obtain the secondary filtrate of the primary primary flushing filtrate and the secondary filtrate of the primary primary primary flushing filtrate. Among them, the secondary filter residue of the first-level flushing filtrate returns to the secondary filter residue storage tank to mix with the materials in the secondary filter residue storage tank, and the secondary filtrate of the primary primary flushing filtrate returns to the secondary filtrate storage tank and the secondary filtrate storage tank. The materials in the tank are mixed to complete the first reverse flushing process of undigested and decomposed organic matter and sediment with large particles. The materials in the primary filtrate storage tank are mixed to circulate the above-mentioned reverse flushing process. The reverse flushing process is carried out 3 times. After the end, the primary large particles are not digested and decomposed. 98% of large particles have not been digested and decomposed organic matter and sediment, and the materials in the secondary filter residue storage tank and the material in the secondary filtrate storage tank are coarse biogas residues with 100% removal rate of large particles of undigested and decomposed organic matter and sediment and biogas slurry. The clean and large particles of undigested and decomposed organic matter and sediment are dried and crushed and returned to the livestock and poultry farm for litter reuse or as a carrier of microorganisms and returned to the organic solid biogas fertilizer system for utilization.
(2)有机液肥基液生产:完成反向冲洗任务的“去除大颗粒未被消化分解有机物和泥沙的沼液”由贮槽再经管道泵送至密闭、带有间歇式捷流分散混合机(上海弗鲁克FAB系列)的混合反应釜内,加入120目筛筛上、12目筛筛下的粗沼渣,控制固含量小于等于20%,充分搅拌混合15min后获得反向浓缩液,启动管线式高剪切分散乳化机(上海弗鲁克FDX1系列),进行高频高剪切分散乳化120min,获得高生理活性厌氧消化浓缩液,再经管道泵送至LX-950-170目过滤离心机进行三级过滤分离处理。其中,170目筛筛上、120目筛筛下的“三级滤渣”(细沼渣)回到二级滤渣贮槽进入下一循环反向浓缩处理,170目筛筛下的“三级滤液”即为高生理活性有机液肥基液(母液)产品。检测有机液肥基液产品中的生物活性物质和营养成分,其中,有机质含量100g/L,总养分(N+P2O5+K2O)含量60g/L。(2) Production of organic liquid fertilizer base liquid: the "biogas slurry that removes large particles of undigested and decomposed organic matter and sediment" that has completed the backwashing task is pumped from the storage tank to a closed, intermittent jet flow dispersion mixing Add the coarse biogas residue on the 120-mesh sieve and the 12-mesh sieve to the mixing reactor of the machine (Shanghai Fluke FAB series), control the solid content to be less than or equal to 20%, stir and mix for 15 minutes to obtain the reverse concentrate , Start the pipeline high-shear dispersing emulsifier (Shanghai Fluke FDX1 series), perform high-frequency high-shear dispersing and emulsifying for 120 minutes, obtain high physiological activity anaerobic digestion concentrate, and then pump it to LX-950-170 through pipeline A filter centrifuge is used for three-stage filtration and separation treatment. Among them, the "tertiary filter residue" (fine biogas residue) on the 170-mesh sieve and under the 120-mesh sieve is returned to the secondary filter residue storage tank to enter the next cycle of reverse concentration treatment, and the "tertiary filtrate" under the 170-mesh sieve "It is the base liquid (mother liquid) product of organic liquid fertilizer with high physiological activity. Detect the bioactive substances and nutritional components in the organic liquid fertilizer base liquid products, wherein the organic matter content is 100g/L, and the total nutrient (N+P 2 O 5 +K 2 O) content is 60g/L.
实施例2:Example 2:
本实施例用于说明厌氧消化液分级处理并以其去除大颗粒未被消化分解有机物和泥沙分离物(去除大颗粒未被消化分解有机物和泥沙后得到的粗沼渣和沼液)为原料制备有机液肥基液的方法,包括下列步骤:This example is used to illustrate the graded treatment of anaerobic digestion liquid and use it to remove large particles of undigested and decomposed organic matter and sediment separation (coarse biogas residue and biogas slurry obtained after removing large particles of undigested and decomposed organic matter and sediment) The method for preparing organic liquid fertilizer base liquid as raw material comprises the following steps:
(1)去除大颗粒未被消化分解有机物和泥沙:将厌氧消化液(固含量5%)经管道泵送进入LX-950-16目过滤离心机进行一级过滤分离。其中,“一级滤渣”(大颗粒未被消化分解有机物和泥沙)进入一级大颗粒未被消化分解有机物和泥沙贮槽、一级滤液进入一级滤液贮槽待处理。“一级滤液”由贮槽经管道泵送至LX-950-140目过滤离心机进行二级过滤分离处理。其中,140目筛筛上、16目筛筛下的“二级滤渣”(粗沼渣)进入二级滤渣贮槽、140目筛筛下的二级滤液进入二级滤液贮槽待处理。140目筛筛下的“二级滤液”作为“大颗粒未被消化分解有机物和泥沙”反向冲洗剂回到带搅拌的一级大颗粒未被消化分解有机物和泥沙贮槽中与大颗粒未被消化分解有机物和泥沙混合、搅拌稀释,控制固含量20%,搅拌10min,混合均匀,使大颗粒未被消化分解有机物和泥沙表面的附着物(沼渣)进入到二级滤液中,获得反向冲洗混合液,将反向冲洗混合液泵送进入LX-950-16目过滤离心机,进行第1次一级过滤离心反向冲洗“大颗粒未被消化分解有机物和泥沙”。一级一次冲洗大颗粒未被消化分解有机物和泥沙滤渣重新回到以及大颗粒未被消化分解有机物和泥沙贮槽中与其中的物料混合,第1次“一级一次冲洗滤液”再次回到140目过滤离心机进行二级过滤离心处理,获得一级一次冲洗滤液的二级滤渣和一级一次冲洗滤液的二级滤液。其中,一级一次冲洗滤液的二级滤渣回到二级滤渣贮槽与二级滤渣贮槽中的物料混合,一级一次冲洗滤液的二级滤液回到二级滤液贮槽与二级滤液贮槽中的物料混合,完成第1次大颗粒未被消化分解有机物和泥沙反向冲洗过程,再将此时一级大颗粒未被消化分解有机物和泥沙贮槽中的物料与此时二级滤液贮槽中的物料混合从而循环上述反向冲洗过程,反向冲洗过程共进行3次,结束后,一级大颗粒未被消化分解有机物和泥沙贮槽中的物料为沼渣去除率98%的大颗粒未被消化分解有机物和泥沙,二级滤渣贮槽中的物料和二级滤液贮槽中的物料分别为大颗粒未被消化分解有机物和泥沙去除率100%的粗沼渣和沼液。洁净的大颗粒未被消化分解有机物和泥沙经烘干、粉碎回到畜禽养殖场做垫料回用或作为微生物的载体回到有机固体沼肥系统加以利用。(1) Removal of large particles of undigested and decomposed organic matter and sediment: the anaerobic digestion solution (solid content 5%) is pumped through the pipeline into the LX-950-16 mesh filter centrifuge for primary filtration and separation. Among them, the "first-level filter residue" (large particles of undigested and decomposed organic matter and sediment) enters the first-level large-particle undigested and decomposed organic matter and sediment storage tank, and the first-level filtrate enters the first-level filtrate storage tank for treatment. The "primary filtrate" is pumped from the storage tank through the pipeline to the LX-950-140 mesh filter centrifuge for secondary filtration and separation treatment. Among them, the "secondary filter residue" (coarse biogas residue) on the 140-mesh sieve and under the 16-mesh sieve enters the secondary filter residue storage tank, and the secondary filtrate under the 140-mesh sieve enters the secondary filtrate storage tank for treatment. The "secondary filtrate" under the 140-mesh sieve is used as a backwashing agent for "large particles of undigested and decomposed organic matter and sediment" and returned to the primary large particle undigested and decomposed organic matter and sediment storage tank with agitation. Mix the undigested and decomposed organic matter with the sediment, stir and dilute, control the solid content to 20%, stir for 10 minutes, and mix evenly, so that the large particles of undigested and decomposed organic matter and the attachments (digest residue) on the surface of the sediment enter the secondary filtrate In the process, the backwash mixture is obtained, and the backwash mixture is pumped into the LX-950-16 mesh filter centrifuge for the first primary filtration centrifugal backwash "large particles are not digested and decomposed organic matter and sediment ". The first-level primary flushing of large particles of undigested and decomposed organic matter and sediment filter residues are returned and the large particles of undigested and decomposed organic matter and sediment storage tanks are mixed with the materials therein, and the first "first-level primary flushing filtrate" is returned again Go to a 140-mesh filter centrifuge for secondary filtration and centrifugation to obtain the secondary filter residue of the primary primary flushing filtrate and the secondary filtrate of the primary primary flushing filtrate. Among them, the secondary filter residue of the first-level flushing filtrate returns to the secondary filter residue storage tank to mix with the materials in the secondary filter residue storage tank, and the secondary filtrate of the primary primary flushing filtrate returns to the secondary filtrate storage tank and the secondary filtrate storage tank. The materials in the tank are mixed to complete the first reverse flushing process of undigested and decomposed organic matter and sediment with large particles. The materials in the first-stage filtrate storage tank are mixed to circulate the above-mentioned backwashing process. The backwashing process is carried out three times. 98% of large particles have not been digested and decomposed organic matter and sediment, and the materials in the secondary filter residue storage tank and the materials in the secondary filtrate storage tank are respectively coarse biogas with 100% large particle undigested and decomposed organic matter and sediment removal rate slag and sludge. The clean large particles that have not been digested and decomposed organic matter and sediment are dried and crushed and returned to the livestock and poultry farm for litter reuse or as a carrier of microorganisms and returned to the organic solid biogas fertilizer system for utilization.
(2)有机液肥基液生产:完成反向冲洗任务的“去除大颗粒未被消化分解有机物和泥沙的沼液”由贮槽再经管道泵送至密闭、带有间歇式捷流分散混合机(上海弗鲁克FAB系列)的混合反应釜内,加入140目筛筛上、16目筛筛下的粗沼渣,控制固含量小于等于20%,充分分散混合30min后获得反向浓缩液,启动管线式高剪切分散乳化机(上海弗鲁克FDX1系列),进行高频高剪切分散乳化60min,获得高生理活性厌氧消化浓缩液,再经管道泵送至LX-950-200目过滤离心机进行三级过滤分离处理。其中,200目筛筛上、140目筛筛下的“三级滤渣”(细沼渣)回到二级滤渣贮槽进入下一循环反向浓缩处理,200目筛筛下的“三级滤液”即为高生理活性有机液肥基液(母液)产品。检测有机液肥基液产品中的生物活性物质和营养成分,其中,有机质含量120g/L,总养分(N+P2O5+K2O)含量65g/L。(2) Production of organic liquid fertilizer base liquid: the "biogas slurry that removes large particles of undigested and decomposed organic matter and sediment" that has completed the backwashing task is pumped from the storage tank to a closed, intermittent jet flow dispersion mixing Add the coarse biogas residue on the 140-mesh sieve and the 16-mesh sieve to the mixing reactor of the machine (Shanghai Fluke FAB series), control the solid content to be less than or equal to 20%, fully disperse and mix for 30 minutes to obtain the reverse concentrate , start the pipeline high-shear dispersing emulsifier (Shanghai Fluke FDX1 series), carry out high-frequency high-shear dispersing and emulsifying for 60 minutes, obtain the concentrated liquid of anaerobic digestion with high physiological activity, and then pump it to LX-950-200 through pipeline A filter centrifuge is used for three-stage filtration and separation treatment. Among them, the "tertiary filter residue" (fine biogas residue) on the 200-mesh sieve and under the 140-mesh sieve is returned to the secondary filter residue storage tank to enter the next cycle of reverse concentration treatment, and the "tertiary filtrate" under the 200-mesh sieve "It is the base liquid (mother liquid) product of organic liquid fertilizer with high physiological activity. The biologically active substances and nutritional components in the organic liquid fertilizer base liquid products were detected. Among them, the organic matter content was 120g/L, and the total nutrient (N+P 2 O 5 +K 2 O) content was 65g/L.
虽然,上文中已经用一般性说明及具体实施方案对本发明作了详尽的描述,但在本发明基础上,可以对之作一些修改或改进,这对本领域技术人员而言是显而易见的。因此,在不偏离本发明精神的基础上所做的这些修改或改进,均属于本发明要求保护的范围。Although the present invention has been described in detail with general descriptions and specific embodiments above, it is obvious to those skilled in the art that some modifications or improvements can be made on the basis of the present invention. Therefore, the modifications or improvements made on the basis of not departing from the spirit of the present invention all belong to the protection scope of the present invention.
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