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CN104430187A - Method for treating sludge in vermiculture - Google Patents

Method for treating sludge in vermiculture Download PDF

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Publication number
CN104430187A
CN104430187A CN201410257421.2A CN201410257421A CN104430187A CN 104430187 A CN104430187 A CN 104430187A CN 201410257421 A CN201410257421 A CN 201410257421A CN 104430187 A CN104430187 A CN 104430187A
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layer
sludge
earthworm
residues
earthworms
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雍毅
叶宏
刘金议
尹朝阳
吴怡
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SICHUAN INSTITUTE OF ENVIRONMENTAL PROTECTION SCIENCE
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SICHUAN INSTITUTE OF ENVIRONMENTAL PROTECTION SCIENCE
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    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01KANIMAL HUSBANDRY; AVICULTURE; APICULTURE; PISCICULTURE; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
    • A01K67/00Rearing or breeding animals, not otherwise provided for; New or modified breeds of animals
    • A01K67/30Rearing or breeding invertebrates
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B2101/00Type of solid waste
    • B09B2101/018Animal meals

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  • Life Sciences & Earth Sciences (AREA)
  • Environmental Sciences (AREA)
  • Animal Behavior & Ethology (AREA)
  • Zoology (AREA)
  • Animal Husbandry (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Mushroom Cultivation (AREA)

Abstract

本发明属于污泥处理领域中的一种蚯蚓养殖处理污泥的方法,是将污泥与农业废弃物拌混后,进行发酵预处理,降温,添加到蚯蚓养殖床,通过蚯蚓采食消化,将污泥转化为蚯蚓粪,得到蚯蚓及蚯蚓粪两种产品,蚯蚓养殖床由不渗水的墙体围成,墙体内的床体从底部到上部的竖面构造依次为防渗层、调节层和养殖层;调节层底部设置穿孔排水管和穿孔布气管;养殖层表面层为稻草帘、银杏叶和药渣的复合层。本发明克服了现有蚯蚓处理污泥技术尚未形成一套完整处置系统的缺陷,提供的蚯蚓养殖处理污泥的方法使污泥处理过程中的污染源得到了控制,蚯蚓活力提升,污泥处理量增加,使大田蚯蚓养殖技术实现了规模化和规范化。

The invention belongs to the field of sludge treatment, and relates to a method for treating sludge by earthworm breeding. After mixing the sludge with agricultural waste, it performs fermentation pretreatment, cools down, adds it to an earthworm breeding bed, and feeds and digests it through earthworms. Transform the sludge into vermicompost to obtain two products: earthworm and vermicompost. The vermiculture bed is surrounded by impermeable walls. layer and cultivation layer; perforated drainage pipes and perforated cloth air pipes are arranged at the bottom of the adjustment layer; the surface layer of the cultivation layer is a composite layer of straw curtains, ginkgo leaves and medicinal residues. The invention overcomes the defect that the existing earthworm sludge treatment technology has not yet formed a complete disposal system, and the provided method for earthworm breeding sludge treatment controls the pollution source in the sludge treatment process, improves the vitality of earthworms, and reduces the sludge treatment capacity. The increase has enabled the scale and standardization of field earthworm culture technology.

Description

蚯蚓养殖处理污泥的方法Method for treating sludge by earthworm breeding

技术领域 technical field

本发明属于污泥处理领域,具体涉及一种蚯蚓养殖处理污泥的方法。 The invention belongs to the field of sludge treatment, and in particular relates to a method for treating sludge by earthworm breeding.

背景技术 Background technique

我国污泥处理事业起步较晚,重“水”轻“泥”现象长期存在,目前现有污水处理行业中拥有焚烧、综合利用、深度脱水填埋等稳定处理设施的不到1/4,处理工艺和配套设备较为完善的不到1/10,其中能够正常运行的为数不多;我国传统的污泥独立填埋处置技术存在基建投资大、负荷低、运行管理难度大、运行经验缺乏等问题。和垃圾混合填埋对垃圾堆体性质影响大,给垃圾堆体带来安全隐患,堵塞垃圾场渗沥液收集系统。我国现有的污水处理厂,按国家现有标准,污泥绝大部分未能得到妥善处置;污泥处置已经成为污水处理厂设计、运行中必须优先考虑的重要环节。 my country's sludge treatment business started late, and the phenomenon of focusing on "water" and neglecting "mud" has existed for a long time. At present, less than a quarter of the existing sewage treatment industry has stable treatment facilities such as incineration, comprehensive utilization, and deep dehydration landfill. Less than 1/10 of the technology and supporting equipment are relatively complete, and few of them can operate normally; my country's traditional sludge independent landfill disposal technology has problems such as large infrastructure investment, low load, difficult operation and management, and lack of operating experience. . Mixed landfill with garbage has a great impact on the properties of the garbage dump, brings safety hazards to the garbage dump, and blocks the leachate collection system of the garbage dump. In my country's existing sewage treatment plants, according to the existing national standards, most of the sludge has not been properly disposed of; sludge disposal has become an important link that must be given priority in the design and operation of sewage treatment plants.

蚯蚓处理污泥技术是一种利用蚯蚓——微生物人工生态系统处理污泥的方法,它利用蚯蚓的生态功能,最终达到污泥减量和稳定,而其中的大田蚯蚓养殖技术,因其投资成本低,管理方便等优势,受到了越来越多的重视与应用。 Earthworm sludge treatment technology is a method of sludge treatment using earthworms-microbial artificial ecosystems. It utilizes the ecological functions of earthworms to finally achieve sludge reduction and stabilization. Among them, the field earthworm breeding technology, because of its investment cost Low cost, easy management and other advantages have received more and more attention and application.

尽管如此,蚯蚓处理污泥技术仍然没有得到大规模的应用,一些关键的问题依然没有解决,例如污泥接纳要求、污泥预处理、污泥处置过程中参数控制、产品利用、污染防治体系建立等,尚未形成一套完整的处置系统;同时利用蚯蚓处理污泥的工程实例缺乏,因此有待于更加深入的研究。 However, earthworm sludge treatment technology has not yet been applied on a large scale, and some key issues have not been resolved, such as sludge acceptance requirements, sludge pretreatment, parameter control during sludge disposal, product utilization, and establishment of pollution prevention and control systems etc. A complete set of disposal system has not yet been formed; at the same time, there is a lack of engineering examples of using earthworms to treat sludge, so more in-depth research is needed.

发明内容 Contents of the invention

本发明的目的是为了克服现有蚯蚓处理污泥技术尚未形成一套完整处置系统的缺陷,提供一种污泥处理过程中污染源得到控制,蚯蚓活力提升,污泥处理量增加,可实现规模化和规范化的蚯蚓养殖处理污泥的方法。 The purpose of the present invention is to overcome the defect that the existing earthworm sludge treatment technology has not yet formed a complete disposal system, to provide a sludge treatment process in which the pollution source is controlled, the vitality of the earthworms is improved, and the amount of sludge treatment is increased, which can realize large-scale And standardized methods of earthworm breeding sludge treatment.

本发明的目的是通过以下技术方案来实现的: The purpose of the present invention is achieved through the following technical solutions:

本发明的蚯蚓养殖处理污泥的方法,是将污泥与农业废弃物拌混后,进行发酵预处理,降温,添加到蚯蚓养殖床,作为蚯蚓的养殖食料,控制蚯蚓养殖床的pH值、温度和湿度,通过蚯蚓采食消化,将污泥转化为蚯蚓粪,得到蚯蚓及蚯蚓粪两种产品,其特征在于蚯蚓养殖床由不渗水的墙体(1)围成,墙体(1)上有顶盖,墙体(1)内的床体从底部到上部的竖面构造依次为防渗层、调节层(2)和养殖层(3);调节层(2)为卵石层,卵石层底部设置穿孔排水管(6)和穿孔布气管(7),穿孔排水管(6)与墙体(1)外的收集池(8)相连通,穿孔布气管(7)与穿孔排水管(6)相连;调节层(2)和养殖层(3)之间有土工布(9);养殖层(3)表面层为稻草帘、银杏叶和药渣的复合层;墙体(1)上设置有穿墙管头(10)。 The method for treating sludge in earthworm breeding of the present invention is to mix the sludge with agricultural waste, carry out fermentation pretreatment, lower the temperature, add it to the earthworm breeding bed, and use it as the breeding food for earthworms to control the pH value of the earthworm breeding bed, temperature and humidity, through feeding and digestion by earthworms, the sludge is converted into vermicompost, and two products of earthworms and vermicompost are obtained. There is a top cover, and the vertical structure of the bed body in the wall (1) from the bottom to the upper part is an anti-seepage layer, an adjustment layer (2) and a culture layer (3); the adjustment layer (2) is a pebble layer, and the pebble layer Perforated drainage pipe (6) and perforated air distribution pipe (7) are arranged at the bottom of the layer, the perforated drainage pipe (6) is connected with the collection pool (8) outside the wall (1), and the perforated air distribution pipe (7) is connected with the perforated drainage pipe ( 6) are connected; there is a geotextile (9) between the adjustment layer (2) and the cultivation layer (3); the surface layer of the cultivation layer (3) is a composite layer of straw curtains, ginkgo leaves and medicinal residues; A wall-penetrating pipe head (10) is provided.

上述方案中,所述农业废弃物为农田残留物、果园残留物、农副产品加工业中的残余物和食品制造业中的残余物中的一种或多种的混合。 In the above solution, the agricultural waste is a mixture of one or more of farmland residues, orchard residues, residues from agricultural and by-product processing industries, and residues from food manufacturing.

上述方案中,所述农田残留物为秸秆和蔬菜的残体;果园残留物为腐烂的果实、果实外壳、果树的枝条和落叶;农副产品加工业中的残余物和食品制造业中的残余物为蔬菜残体、果实残体、蘑菇渣和锯末。 In the above scheme, the farmland residues are residues of straw and vegetables; orchard residues are rotten fruits, fruit shells, branches and fallen leaves of fruit trees; residues in the agricultural and sideline product processing industry and residues in the food manufacturing industry For vegetable residues, fruit residues, mushroom residue and sawdust.

上述方案中,所述污泥与农业废弃物拌混,其碳氮比(C/N)控制在20:1~30:1,含水率控制在40%~60%。 In the above scheme, the sludge is mixed with agricultural waste, the carbon-to-nitrogen ratio (C/N) is controlled at 20:1-30:1, and the moisture content is controlled at 40%-60%.

上述方案中,所述防渗层最下层为压实土壤层(4),压实土壤层之上为膨润土改性层或防渗膜(5)。 In the above solution, the lowermost layer of the anti-seepage layer is a compacted soil layer (4), and above the compacted soil layer is a modified bentonite layer or an anti-seepage membrane (5).

上述方案中,所述药渣由山楂、黄芩、斑地锦、麦芽和白头翁组成,其重量比=1:0.3~0.5:0.2~0. 35:0.3~0.4:0.1~0. 15。 In the above scheme, the medicinal dregs are composed of hawthorn, scutellaria baicalensis, broccoli, malt and pulsatilla, with a weight ratio of 1:0.3~0.5:0.2~0.35:0.3~0.4:0.1~0.15.

上述方案中,所述穿墙管头(10)安装有堵头(11)。 In the above solution, the wall-piercing pipe head (10) is equipped with a plug (11).

上述方案中,所述收集池(8)与污水处理设施相连。 In the above solution, the collection pool (8) is connected to the sewage treatment facility.

本发明的蚯蚓养殖污泥处理的方法,处理的污泥为城市生活污水处理厂产生的污泥,畜牧业、农副食品加工业、食品制造业、酒、饮料和精制茶制造业生产活动中废水处理产生的污泥,同时还可对部分农业废弃物进行处置。蚯蚓养殖过程中,为保证蚯蚓最佳生存环境,需要进行人工喷水等调温和调湿措施,因此养殖床底部会产生部分渗滤液,这部分渗滤液经管道收集至收集池,由于养殖床下部设置了防渗系统,因此不会对下部土壤及地下水造成污染;同时厂区内还会产生部分生活污水。这些废水经收集后送至污水处理设施进行处理。处理后的废水满足《城市污水再生利用  城市杂用水水质》(GB/T 18921)后排至清水池,除余氯后,作为养殖床调湿、降温水。污水处理设施应采取二级生物处理工艺+深度处理工艺,并可选用人工湿地、快渗池等自然净化工艺。在污泥贮存期间以及进行发酵预处理期间会有大量臭气产生,其主要成分为含硫化合物、含氯化合物等,臭气经密闭收集后通过风机送入养殖床底部布气管道内,经布气系统均匀进入调节层,在调节层中有害成分被附着在卵石上的生物群落吸附和转化,完成脱臭;由于床内气体流速较小,气体中的有害物质可被调节层中的微生物充分吸收,在达到养殖层时,浓度较小,不会对蚯蚓造成危害。在进入调节层前,可对气体进行加湿,以增加后续气体吸附效果。 According to the method for treating earthworm breeding sludge of the present invention, the sludge to be treated is the sludge produced by urban domestic sewage treatment plants, in the production activities of animal husbandry, agricultural and sideline food processing industry, food manufacturing industry, wine, beverage and refined tea manufacturing industry The sludge generated from wastewater treatment can also be used to dispose of some agricultural waste. In the process of earthworm breeding, in order to ensure the best living environment for earthworms, temperature and humidity adjustment measures such as artificial water spraying are required. Therefore, part of the leachate will be generated at the bottom of the culture bed, and this part of leachate will be collected to the collection pool through pipelines. Because the lower part of the culture bed An anti-seepage system is installed, so it will not pollute the lower soil and groundwater; at the same time, some domestic sewage will be generated in the factory area. The wastewater is collected and sent to sewage treatment facilities for treatment. The treated wastewater meets the requirements of "Urban Sewage Recycling, Urban Miscellaneous Water Quality" (GB/T 18921) and is discharged to the clear water pool. After removing residual chlorine, it is used as water for humidity control and cooling of the breeding bed. Sewage treatment facilities should adopt secondary biological treatment process + advanced treatment process, and natural purification processes such as artificial wetlands and quick seepage pools can be used. During the sludge storage period and the fermentation pretreatment period, a large amount of odor will be produced, and its main components are sulfur-containing compounds and chlorine-containing compounds. The gas system enters the conditioning layer evenly, and the harmful components in the conditioning layer are absorbed and transformed by the biological communities attached to the pebbles to complete deodorization; due to the low gas flow rate in the bed, the harmful substances in the gas can be fully absorbed by the microorganisms in the conditioning layer , when it reaches the culture layer, the concentration is small and will not cause harm to earthworms. Before entering the adjustment layer, the gas can be humidified to increase the subsequent gas adsorption effect.

本发明的有益效果在于: The beneficial effects of the present invention are:

1、解决了城市生活污泥处置问题,可将生活污泥资源化综合利用,减少污泥对环境造成的破坏和危害,减少了污泥处理处置过程中高耗能、高污染、高成本的风险。 1. Solved the problem of urban domestic sludge disposal, and can comprehensively utilize domestic sludge as a resource, reduce the damage and harm caused by sludge to the environment, and reduce the risk of high energy consumption, high pollution and high cost in the process of sludge treatment and disposal .

2、减少农业废弃物的污染。秸秆、菇渣已成为产地难以处置的废弃物,其污染程度与日俱增。而城市污水处理厂产生的污泥一般含水率在80%左右,且碳氮比(C/N)较低,无法满足初步堆肥及后续蚯蚓养殖的需求。本发明采用秸秆、蘑菇渣等农业废弃物作为污泥的配料,并经过研究确定了其最佳配比,使其适合了蚯蚓养殖的需求,既处理了污泥,又处理了农业废弃物。 2. Reduce the pollution of agricultural waste. Straw and mushroom residues have become wastes that are difficult to dispose of in production areas, and their pollution is increasing day by day. However, the sludge produced by urban sewage treatment plants generally has a water content of about 80% and a low carbon-to-nitrogen ratio (C/N), which cannot meet the needs of initial composting and subsequent earthworm breeding. The invention adopts agricultural wastes such as straws and mushroom slags as the ingredients of the sludge, and the optimal proportion is determined through research, so that it is suitable for the needs of earthworm breeding, and both the sludge and the agricultural wastes are processed.

3、本发明处置系统完整配套,废水、臭气得到处理,防止了二次污染。 3. The disposal system of the present invention is completely matched, waste water and odor are treated, and secondary pollution is prevented.

4、本发明的蚯蚓养殖床,透气性好,易于控制pH值、温度和湿度,蚯蚓的患病率明显降低,不仅单位面积污泥处理量大,而且蚯蚓增殖率高,比传统的蚯蚓养殖污泥处理系统具有明显的优势。 4. The earthworm breeding bed of the present invention has good air permeability, is easy to control pH value, temperature and humidity, and the disease rate of earthworms is significantly reduced. Not only is the sludge treatment amount per unit area large, but also the earthworm proliferation rate is high, which is higher than that of traditional earthworm cultivation. Sludge treatment systems have clear advantages.

因此,本发明克服了现有蚯蚓处理污泥技术尚未形成一套完整处置系统的缺陷,提供的蚯蚓养殖处理污泥的方法使污泥处理过程中的污染源得到了控制,蚯蚓活力提升,污泥处理量增加,使大田蚯蚓养殖技术实现了规模化和规范化。 Therefore, the present invention overcomes the defect that the existing earthworm treatment sludge technology has not yet formed a complete disposal system, and the provided method for earthworm breeding and treatment sludge can control the pollution source in the sludge treatment process, the vitality of earthworms is improved, and the sludge The increase in processing capacity has enabled large-scale and standardized field earthworm culture technology.

附图说明 Description of drawings

图1是本发明的工艺流程图。 Fig. 1 is a process flow diagram of the present invention.

图2是本发明的蚯蚓养殖床床体结构(剖面)示意图。 Fig. 2 is a schematic diagram of the structure (section) of the earthworm breeding bed of the present invention.

图3是本发明的蚯蚓养殖床平面结构示意图。 Fig. 3 is a schematic diagram of the planar structure of the earthworm breeding bed of the present invention.

图4是本发明中的废水处理回用流程图。 Fig. 4 is a flowchart of wastewater treatment and reuse in the present invention.

附图中,1:墙体;2:调节层;3:养殖层;4:压实土壤层;5:膨润土改性层或防渗膜;6:穿孔排水管;7:穿孔布气管;8:收集池;9:土工布;10:穿墙管头;11:堵头;12:墙外地面;13:风机。 In the drawings, 1: wall; 2: regulation layer; 3: culture layer; 4: compacted soil layer; 5: modified bentonite layer or anti-seepage membrane; 6: perforated drainage pipe; 7: perforated air pipe; 8 : collection pool; 9: geotextile; 10: pipe head through the wall; 11: plug; 12: ground outside the wall; 13: fan.

具体实施例 specific embodiment

下面结合附图及实施例进一步详述本发明,但本发明不仅限于所述实施例。 The present invention will be described in further detail below in conjunction with the drawings and embodiments, but the present invention is not limited to the embodiments.

实施例一 Embodiment one

本例的大田养殖蚯蚓处理污泥的方法是将污泥与农业废弃物拌混后,进行发酵预处理,降温,添加到蚯蚓养殖床,作为蚯蚓的养殖食料,控制蚯蚓养殖床的pH值、温度和湿度,通过蚯蚓采食消化,将污泥转化为蚯蚓粪,得到蚯蚓及蚯蚓粪两种产品,其特征在于蚯蚓养殖床由不渗水的墙体1围成,墙体1上有顶盖,墙体1内的床体从底部到上部的竖面构造依次为防渗层、调节层2和养殖层3;调节层2为卵石层,卵石层底部设置穿孔排水管6和穿孔布气管7,穿孔排水管6与墙体1外的收集池8相连通,穿孔布气管7与穿孔排水管6相连;调节层2和养殖层3之间有土工布9;养殖层3表面层为稻草帘、银杏叶和药渣的复合层;墙体1上设置有穿墙管头10。 The method of treating sludge in the field cultured earthworms of this example is to mix the sludge with agricultural waste, carry out fermentation pretreatment, cool down, add it to the earthworm breeding bed, and use it as the breeding food for earthworms to control the pH value, temperature and humidity, through feeding and digestion by earthworms, the sludge is converted into vermicompost, and two products of earthworms and vermicompost are obtained. , the vertical structure of the bed in the wall 1 from the bottom to the upper part is an anti-seepage layer, an adjustment layer 2 and a culture layer 3; the adjustment layer 2 is a pebble layer, and the bottom of the pebble layer is provided with a perforated drainage pipe 6 and a perforated air distribution pipe 7 , the perforated drainage pipe 6 is connected with the collection pool 8 outside the body of wall 1, and the perforated air pipe 7 is connected with the perforated drainage pipe 6; there is a geotextile 9 between the regulating layer 2 and the culture layer 3; the surface layer of the culture layer 3 is a straw curtain , a composite layer of ginkgo leaves and medicinal residues; the wall 1 is provided with a wall-piercing pipe head 10 .

农业废弃物为农田残留物、果园残留物、农副产品加工业中的残余物和食品制造业中的残余物中的一种或多种的混合。 Agricultural waste is a mixture of one or more of farmland residues, orchard residues, agricultural by-product processing residues, and food manufacturing residues.

农田残留物为秸秆和蔬菜的残体;果园残留物为腐烂的果实、果实外壳、果树的枝条和落叶;农副产品加工业中的残余物和食品制造业中的残余物为蔬菜残体、果实残体、蘑菇渣和锯末。 Farmland residues are straw and vegetable residues; orchard residues are rotten fruits, fruit shells, branches and fallen leaves of fruit trees; residues in agricultural and by-product processing industries and food manufacturing Debris, mushroom residue and sawdust.

污泥与农业废弃物拌混,其碳氮比(C/N)控制在20:1~30:1,含水率控制在40%~60%。 When mixing sludge with agricultural waste, the carbon-to-nitrogen ratio (C/N) is controlled at 20:1~30:1, and the moisture content is controlled at 40%~60%.

防渗层最下层为压实土壤层4,压实土壤层之上为膨润土改性层5。 The lowest layer of the anti-seepage layer is a compacted soil layer 4, and above the compacted soil layer is a modified bentonite layer 5.

药渣由山楂、黄芩、斑地锦、麦芽和白头翁组成,其重量比=1:0.3~0.5:0.2~0. 35:0.3~0.4:0.1~0. 15。 The medicinal dregs are composed of hawthorn, scutellaria, brocade, malt and pulsatilla, with a weight ratio of 1:0.3~0.5:0.2~0.35:0.3~0.4:0.1~0.15.

穿墙管头10安装有堵头11。 The wall-piercing pipe head 10 is equipped with a plug 11 .

收集池8与污水处理设施相连。 The collecting pool 8 is connected with the sewage treatment facilities.

污泥运至厂区后,应送至污泥贮存区存放,贮存区建成密闭设施,地面进行硬化、防渗处理。贮存区设置污泥渗滤液引流通道或装置,将渗滤液引入集水池内,不得随意排放;贮存区内设置引风机,将贮存区内气体送至除臭设施进行处理,除臭设施采用生物处理等低能耗工艺。贮存设施应能够容纳至少7天的污泥量。蚯蚓是腐食性的动物,同时污泥中含有病原微生物等很多有毒有害物质,为减小污泥等原料对蚯蚓的影响,必须对原料进行预处理,预处理可采用好氧静态堆肥等耗时短、投资低的堆肥工艺。原料进行好氧堆肥后,当堆肥体温度达到55℃,且时间持续5天后,即可满足原料腐熟及无害化要求,此时应终止堆肥过程,以免造成营养物质的损失。初步腐熟原料经过降温后,便可作为蚯蚓食料。污泥在进行堆肥处理前,应添加秸秆、蘑菇渣等对其进行碳氮比(C/N)、含水率等的调节。 After the sludge is transported to the factory area, it should be sent to the sludge storage area for storage. The storage area is built into a closed facility, and the ground is hardened and anti-seepage treatment. Sludge leachate drainage channels or devices are set up in the storage area to introduce the leachate into the sump, and no random discharge is allowed; an induced draft fan is installed in the storage area to send the gas in the storage area to the deodorization facility for treatment, and the deodorization facility adopts biological treatment and other low energy consumption processes. Storage facilities should be able to hold at least 7 days' worth of sludge. Earthworms are scavenging animals. At the same time, the sludge contains many toxic and harmful substances such as pathogenic microorganisms. In order to reduce the impact of sludge and other raw materials on earthworms, the raw materials must be pretreated. Pretreatment can be time-consuming such as aerobic static composting. Short, low-investment composting process. After aerobic composting of raw materials, when the temperature of the compost body reaches 55°C and lasts for 5 days, the requirements of raw material decomposing and harmlessness can be met. At this time, the composting process should be terminated to avoid loss of nutrients. After the preliminary decomposed raw materials are cooled, they can be used as earthworm food. Before the sludge is composted, straw and mushroom slag should be added to adjust the carbon-nitrogen ratio (C/N) and moisture content.

蚯蚓通过采食添加到养殖床的食料,在自身得到增殖的同时将污泥等转化为蚯蚓粪,通过对蚯蚓及蚯蚓粪的适实采收,得到蚯蚓及蚯蚓粪两种产品,经过加工处理后,外卖销售。在养殖过程中,采取上部加料方法,添加的食料被转化为蚓粪后,不进行采收,继续在上部添加食料,直到床体高度约为1.0~1.5m左右时,才对蚯蚓粪进行采收。 Earthworms feed on the food added to the breeding bed, and transform the sludge into vermicompost while multiplying themselves. Through proper harvesting of earthworms and vermicompost, two products of earthworms and vermicompost are obtained, which are processed. After that, takeaway sales. During the breeding process, the method of feeding from the upper part is adopted. After the added food is converted into vermicompost, it will not be harvested, and the food will continue to be added to the upper part until the bed height is about 1.0~1.5m. receive.

养殖场(厂)地形常多为不规则形状,为了便于养殖床区布置与管理,宜将养殖区分为若干养殖单元模块,然后将养殖床按模块式布置在养殖区内。 The terrain of the farm (factory) is often irregular. In order to facilitate the layout and management of the breeding bed area, it is advisable to divide the breeding area into several farming unit modules, and then arrange the breeding beds in the breeding area in a modular manner.

在蚯蚓养殖区内养殖模块宜呈矩阵式排列,每列养殖模块之间设宽不小于1m的人工通道,每行养殖模块之间设宽不小于3m的便道,通道和便道两侧分别设置排水沟,养殖模块内设蚯蚓养殖床。每个养殖单元模块四周搭建遮棚,进行遮雨遮阴,并应保持气体流通。 In the earthworm breeding area, the breeding modules should be arranged in a matrix. An artificial channel with a width of not less than 1m should be set between each row of breeding modules, and a walkway with a width of not less than 3m should be set between each row of breeding modules. ditch, and an earthworm breeding bed is arranged in the breeding module. A shelter is built around each culture unit module to keep out the rain and shade, and the gas circulation should be maintained.

养殖床建设完成后,底部铺设一层秸秆(玉米、小麦、油菜等),厚度约为10cm,起到导气作用,上部增设30cm蚯蚓粪,作为不利条件下蚯蚓的缓冲层,上部为蚯蚓采食层;同时床体高度达到80cm后,添加食料时,应在床体四周添加多孔性的秸秆等食料。添加的食料被转化为蚓粪后,不进行采收,继续在上部添加食料,直到床体高度约为1.0~1.5m左右时,才对蚯蚓粪进行采收,采收后应保留底部30cm后的蚯蚓粪层。 After the construction of the breeding bed is completed, a layer of straw (corn, wheat, rapeseed, etc.) is laid on the bottom with a thickness of about 10cm, which acts as a gas guide, and 30cm of vermicompost is added on the upper part as a buffer layer for earthworms under unfavorable conditions. food layer; at the same time, when the height of the bed body reaches 80cm, when adding food materials, porous straw and other food materials should be added around the bed body. After the added food is converted into vermicompost, do not harvest it, and continue to add food to the upper part until the bed height is about 1.0~1.5m, then harvest the vermicompost, and keep the bottom 30cm after harvesting. layer of vermicompost.

银杏叶内中的类黄酮物质对动物的循环系统、脑功能改善有良好的作用,作为而层的覆盖组分,除有利于调节空气,改善土壤外,主要是可以提高蚯蚓的免疫力,增加其抗病能力。经对比,发现没有投放银杏叶的养植床,其蚯蚓的患病率高出5%以上。 The flavonoids in Ginkgo biloba have a good effect on improving the circulatory system and brain function of animals. As the covering component of the layer, in addition to helping to adjust the air and improve the soil, it can mainly improve the immunity of earthworms and increase its disease resistance. After comparison, it was found that the prevalence rate of earthworms was more than 5% higher in the planting beds without ginkgo leaves.

养植床面层铺设的药渣,由山楂、黄芩、斑地锦、麦芽和白头翁组成,除了有利于调节空气,改善土壤外,各种药渣均能发挥一定的药效,对预防蚯蚓的细菌性败血病,细菌性肠胃病等肠道疾病有协同作用,而且上述药渣易得,也解决了药厂的废物污染问题。经对比发现,没有投放上述药渣的养殖床,其蚯蚓的患病率高出10%。 The dregs laid on the surface of the planting bed are composed of hawthorn, scutellaria, brocade, malt and pulsatilla. In addition to helping to adjust the air and improve the soil, all kinds of dregs can exert a certain medicinal effect, which is beneficial to the prevention of earthworms. Bacterial septicemia, bacterial gastrointestinal disease and other intestinal diseases have a synergistic effect, and the above-mentioned medicinal residues are easy to get, which also solves the waste pollution problem of pharmaceutical factories. After comparison, it was found that the disease rate of earthworms was 10% higher in the breeding beds without the above-mentioned medicinal residues.

养殖床上铺设有横向和/或纵向的通气管,通气管内设置有温度调节装置,增加基床的透气性,调节基床水分,有利于蚯蚓的生长繁殖。 Horizontal and/or vertical ventilation pipes are laid on the breeding bed, and a temperature regulating device is arranged in the ventilation pipes to increase the air permeability of the bed and adjust the moisture of the bed, which is beneficial to the growth and reproduction of earthworms.

采用该种蚯蚓养殖方式,较高的床体可以增加单位面积的蚯蚓密度,提高污泥处置量,节省土地资源;一定厚度的蚯蚓粪层可以作为蚯蚓的缓冲区,当食料及外界环境变化时,蚯蚓均可逃逸至层,不致出现蚯蚓逃逸现象;较高的床体上部一般不会被暴雨淹没,同时床体四周设置的通气层,蚯蚓可将该区域作为避难缓冲区,因此不会出现因通气性差,出现的蚯蚓逃逸及死亡现象。 With this kind of earthworm culture method, the higher bed body can increase the density of earthworms per unit area, increase the amount of sludge disposal, and save land resources; a certain thickness of earthworm manure layer can be used as a buffer zone for earthworms. , earthworms can escape to the layer, and there will be no phenomenon of earthworm escape; the upper part of the higher bed body will generally not be submerged by heavy rain, and at the same time, the ventilation layer set around the bed body, earthworms can use this area as a refuge buffer zone, so there will be no Due to poor ventilation, earthworms escape and die.

采用该种蚯蚓养殖方式,蚯蚓放养密度为0.5~1kg/m2;食料冬季15~20天添加一次,夏季7~10天添加一次,一次食料添加量厚度约为4~5cm。蚯蚓每60天可采收一次,蚯蚓采收密度为2.5~3.5kg/m2,每年每亩地收获蚯蚓1.0~1.5吨;蚯蚓粪一年采收两次(3~4月、8~9月),每年每亩地可收获蚯蚓粪80~ 140吨,采收后应保留底部30cm后的蚯蚓粪层。采用此种养殖方式,每年每亩地可处理200~400吨污泥。 With this earthworm breeding method, the stocking density of earthworms is 0.5-1kg/m 2 ; the food is added once every 15-20 days in winter and every 7-10 days in summer, and the thickness of the food added at one time is about 4-5cm. Earthworms can be harvested once every 60 days, and the harvesting density of earthworms is 2.5~3.5kg/m 2 , and 1.0~1.5 tons of earthworms can be harvested per mu of land every year; months), 80-140 tons of vermicompost can be harvested per mu of land per year, and the vermicompost layer at the bottom 30 cm should be retained after harvesting. With this breeding method, 200-400 tons of sludge can be treated per mu of land per year.

实施例二 Embodiment two

本例的大田养殖蚯蚓处理污泥的方法除防渗层最下层为压实土壤层4,压实土壤层之上为防渗膜5,防渗膜5为土工膜加土工布外,其余同实施例一。 The method for the field breeding earthworm of this example to process sludge is except that the bottom layer of the anti-seepage layer is a compacted soil layer 4, and above the compacted soil layer is an anti-seepage film 5, and the anti-seepage film 5 is a geomembrane plus a geotextile, and all the others are the same Embodiment one.

Claims (8)

1.一种蚯蚓养殖处理污泥的方法,是将污泥与农业废弃物拌混后,进行发酵预处理,降温,添加到蚯蚓养殖床,作为蚯蚓的养殖食料,控制蚯蚓养殖床的pH值、温度和湿度,通过蚯蚓采食消化,将污泥转化为蚯蚓粪,得到蚯蚓及蚯蚓粪两种产品,其特征在于蚯蚓养殖床由不渗水的墙体(1)围成,墙体(1)上有顶盖,墙体(1)内的床体从底部到上部的竖面构造依次为防渗层、调节层(2)和养殖层(3);调节层(2)为卵石层,卵石层底部设置穿孔排水管(6)和穿孔布气管(7),穿孔排水管(6)与墙体(1)外的收集池(8)相连通,穿孔布气管(7)与穿孔排水管(6)相连;调节层(2)和养殖层(3)之间有土工布(9);养殖层(3)表面层为稻草帘、银杏叶和药渣的复合层;墙体(1)上设置有穿墙管头(10)。 1. A method for earthworm breeding to treat sludge, which is to mix the sludge with agricultural waste, carry out fermentation pretreatment, lower the temperature, add it to the earthworm breeding bed, and control the pH value of the earthworm breeding bed as the breeding food for earthworms , temperature and humidity, the sludge is converted into vermicompost through feeding and digestion by earthworms, and two products of earthworms and vermicompost are obtained. ) has a top cover, and the vertical structure of the bed body in the wall (1) from the bottom to the upper part is an anti-seepage layer, an adjustment layer (2) and a breeding layer (3); the adjustment layer (2) is a pebble layer, The bottom of the pebble layer is provided with a perforated drainage pipe (6) and a perforated air distribution pipe (7). The perforated drainage pipe (6) is connected to the collection pool (8) outside the wall (1). (6) are connected; there is a geotextile (9) between the adjustment layer (2) and the culture layer (3); the surface layer of the culture layer (3) is a composite layer of straw curtains, ginkgo leaves and medicinal residues; the wall (1) A wall-piercing pipe head (10) is arranged on it. 2.根据权利要求1所述的蚯蚓养殖处理污泥的方法,其特征在于所述农业废弃物为农田残留物、果园残留物、农副产品加工业中的残余物和食品制造业中的残余物中的一种或多种的混合。 2. The method for earthworm culture treatment sludge according to claim 1, characterized in that the agricultural waste is farmland residues, orchard residues, residues in the agricultural and sideline product processing industry and residues in the food manufacturing industry One or more of the mixture. 3.根据权利要求2所述的蚯蚓养殖处理污泥的方法,其特征在于所述农田残留物为秸秆和蔬菜的残体;果园残留物为腐烂的果实、果实外壳、果树的枝条和落叶;农副产品加工业中的残余物和食品制造业中的残余物为蔬菜残体、果实残体、蘑菇渣和锯末。 3. the method for earthworm culture treatment sludge according to claim 2, is characterized in that said farmland residue is the residue of stalks and vegetables; orchard residue is rotten fruit, fruit shell, branches and fallen leaves of fruit trees; Residues in the agricultural and sideline product processing industry and food manufacturing industry are vegetable residues, fruit residues, mushroom residues and sawdust. 4.根据权利要求1所述的蚯蚓养殖处理污泥的方法,其特征在于所述污泥与农业废弃物拌混,其碳氮比控制在20:1~30:1,含水率控制在40%~60%。 4. The method for treating sludge by earthworm breeding according to claim 1, characterized in that the sludge is mixed with agricultural waste, the carbon-nitrogen ratio is controlled at 20:1~30:1, and the moisture content is controlled at 40 %~60%. 5.根据权利要求1所述的蚯蚓养殖处理污泥的方法,其特征在于所述防渗层最下层为压实土壤层(4),压实土壤层之上为膨润土改性层或防渗膜(5)。 5. The method for treating sludge in earthworm breeding according to claim 1, characterized in that the lowest layer of the anti-seepage layer is a compacted soil layer (4), and above the compacted soil layer is a bentonite modified layer or anti-seepage Membrane (5). 6.根据权利要求1所述的蚯蚓养殖处理污泥的方法,其特征在于所述药渣由山楂、黄芩、斑地锦、麦芽和白头翁组成,其重量比=1:0.3~0.5:0.2~0. 35:0.3~0.4:0.1~0. 15。 6. The method for treating sludge by earthworm breeding according to claim 1, characterized in that the dregs are composed of hawthorn, scutellaria baicalensis, brocade, malt and Pulsatilla pulsatilla, and the weight ratio is 1:0.3~0.5:0.2~ 0.35: 0.3~0.4: 0.1~0.15. 7.根据权利要求1所述的蚯蚓养殖处理污泥的方法,其特征在于所述穿墙管头(10)安装有堵头(11)。 7. The method for treating sludge in earthworm breeding according to claim 1, characterized in that the wall-piercing pipe head (10) is equipped with a plug (11). 8.根据权利要求1所述的蚯蚓养殖处理污泥的方法,其特征在于所述收集池(8)与污水处理设施相连。 8. The method for treating sludge in earthworm breeding according to claim 1, characterized in that the collection pool (8) is connected to a sewage treatment facility.
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CN112840940A (en) * 2021-02-03 2021-05-28 黄明甲 Ecological restoration method for tailing pond
CN114128588A (en) * 2021-11-10 2022-03-04 湖南新泰和绿色农业集团有限公司 Production equipment and method for root control substrate based on solving continuous cropping obstacles of facility vegetables

Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0853878A1 (en) * 1997-01-16 1998-07-22 Ecoflor S.r.l. Earthworm breeding plant
EP0999194A2 (en) * 1998-11-02 2000-05-10 Glas Anois Teo Waste treatment system
CN101074142A (en) * 2007-06-20 2007-11-21 上海裕麒环境技术服务有限公司 Method for circulating and reutilizing sludge during process of sewage
CN201079732Y (en) * 2007-08-11 2008-07-02 青岛天人环境工程有限公司 Ecological type ground imbedded exhaust gas deodorization device
CN101412573A (en) * 2008-11-15 2009-04-22 伏小勇 Method for processing city life sludge by using angleworm
CN101857346A (en) * 2010-05-24 2010-10-13 北京龙威昌生物科技有限公司 Biological processing technology of earthworms contained in municipal sludge
CN102503018A (en) * 2010-11-07 2012-06-20 郑鉴忠 Method for eliminating organic waste through circulation of fish, vegetable and earthworm
CN202449951U (en) * 2011-11-25 2012-09-26 郑鉴忠 System for biological precipitation-purifying digestion and biological cyclic utilization of organic waste and sewage
CN202449971U (en) * 2012-02-29 2012-09-26 杭州师范大学 Earthworm composting processing device for municipal sludge
CN102786195A (en) * 2012-08-02 2012-11-21 浙江大学 Method for synchronously treating hydrocotyle verticillata and dewatered sludge by utilizing Peace-II earthworms
CN102792920A (en) * 2011-05-23 2012-11-28 四川绿山生物科技有限公司 Method for breeding earthworms for large-scale biological treatment on sludge and earthworm culturing system
CN103073088A (en) * 2013-02-03 2013-05-01 大连涌清水处理技术有限公司 Continuous adsorption system for sewage treatment process

Patent Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0853878A1 (en) * 1997-01-16 1998-07-22 Ecoflor S.r.l. Earthworm breeding plant
EP0999194A2 (en) * 1998-11-02 2000-05-10 Glas Anois Teo Waste treatment system
CN101074142A (en) * 2007-06-20 2007-11-21 上海裕麒环境技术服务有限公司 Method for circulating and reutilizing sludge during process of sewage
CN201079732Y (en) * 2007-08-11 2008-07-02 青岛天人环境工程有限公司 Ecological type ground imbedded exhaust gas deodorization device
CN101412573A (en) * 2008-11-15 2009-04-22 伏小勇 Method for processing city life sludge by using angleworm
CN101857346A (en) * 2010-05-24 2010-10-13 北京龙威昌生物科技有限公司 Biological processing technology of earthworms contained in municipal sludge
CN102503018A (en) * 2010-11-07 2012-06-20 郑鉴忠 Method for eliminating organic waste through circulation of fish, vegetable and earthworm
CN102792920A (en) * 2011-05-23 2012-11-28 四川绿山生物科技有限公司 Method for breeding earthworms for large-scale biological treatment on sludge and earthworm culturing system
CN202449951U (en) * 2011-11-25 2012-09-26 郑鉴忠 System for biological precipitation-purifying digestion and biological cyclic utilization of organic waste and sewage
CN202449971U (en) * 2012-02-29 2012-09-26 杭州师范大学 Earthworm composting processing device for municipal sludge
CN102786195A (en) * 2012-08-02 2012-11-21 浙江大学 Method for synchronously treating hydrocotyle verticillata and dewatered sludge by utilizing Peace-II earthworms
CN103073088A (en) * 2013-02-03 2013-05-01 大连涌清水处理技术有限公司 Continuous adsorption system for sewage treatment process

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
蔡玉琪等: "蚯蚓对秸秆-污泥混合物的消解转化效果", 《农业环境科学学报》, no. 06, 20 June 2009 (2009-06-20) *

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106035243B (en) * 2016-06-16 2018-11-13 辽宁华电环保科技有限公司 The method for utilizing domestic sludge breeding earthworm in greenhouse as bed base using cow dung
CN106035243A (en) * 2016-06-16 2016-10-26 辽宁华电环保科技有限公司 Method for breeding earthworm in greenhouse by using domestic sludge with cow dung as bed substrate
CN106508821A (en) * 2016-11-29 2017-03-22 朱少忠 Method for breeding earthworms through combination of wastewater from cassava starch factories with municipal refuse
CN107347480A (en) * 2017-04-18 2017-11-17 湖南绿源青峰生态农业科技有限公司 Breeding integration ecological system
CN108623341B (en) * 2018-05-14 2021-08-13 谢飞 An automatic vermicompost sludge disposal system and its application method
CN108623341A (en) * 2018-05-14 2018-10-09 四川顶丰生物科技有限公司 A kind of automation earthworm biological compost sludge treatment system and its application process
CN109503225A (en) * 2018-12-26 2019-03-22 上海海事大学 A kind of reduction sludge Vermicomposting strong greenhouse gas N2The method of O discharge
CN110395863A (en) * 2019-07-30 2019-11-01 南京师范大学 A kind of earthworm reactor and its sludge resource treatment method
CN110395863B (en) * 2019-07-30 2024-03-26 南京师范大学 Earthworm reactor and sludge recycling treatment method thereof
CN112250269A (en) * 2020-11-09 2021-01-22 重庆市浩骞农业发展有限责任公司 Feeding method of biochemical system
CN112262823A (en) * 2020-11-13 2021-01-26 重庆市浩骞农业发展有限责任公司 Light, temperature and humidity control system of sludge biochemical system for earthworm breeding cooperative treatment
CN112840940A (en) * 2021-02-03 2021-05-28 黄明甲 Ecological restoration method for tailing pond
CN114128588A (en) * 2021-11-10 2022-03-04 湖南新泰和绿色农业集团有限公司 Production equipment and method for root control substrate based on solving continuous cropping obstacles of facility vegetables
CN114128588B (en) * 2021-11-10 2023-08-11 湖南新泰和绿色农业集团有限公司 Production equipment and method for root control matrix based on continuous cropping obstacle of facility vegetables

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