CN203360242U - Oil sludge treatment system - Google Patents
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- CN203360242U CN203360242U CN201320467278.0U CN201320467278U CN203360242U CN 203360242 U CN203360242 U CN 203360242U CN 201320467278 U CN201320467278 U CN 201320467278U CN 203360242 U CN203360242 U CN 203360242U
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- 239000010802 sludge Substances 0.000 title claims abstract description 74
- 238000000197 pyrolysis Methods 0.000 claims abstract description 32
- 239000002351 wastewater Substances 0.000 claims abstract description 19
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 18
- 239000000571 coke Substances 0.000 claims abstract description 17
- 239000007788 liquid Substances 0.000 claims abstract description 13
- 239000013049 sediment Substances 0.000 claims abstract description 8
- 239000007789 gas Substances 0.000 claims description 27
- 238000010438 heat treatment Methods 0.000 claims description 11
- 238000003763 carbonization Methods 0.000 claims description 5
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 3
- 238000001816 cooling Methods 0.000 claims description 3
- 229910052757 nitrogen Inorganic materials 0.000 claims 1
- 239000003344 environmental pollutant Substances 0.000 abstract description 11
- 231100000719 pollutant Toxicity 0.000 abstract description 11
- 238000011084 recovery Methods 0.000 abstract description 4
- 238000009833 condensation Methods 0.000 abstract 1
- 230000005494 condensation Effects 0.000 abstract 1
- 239000003921 oil Substances 0.000 description 31
- 238000000034 method Methods 0.000 description 18
- 230000008569 process Effects 0.000 description 5
- 239000007787 solid Substances 0.000 description 5
- 238000002485 combustion reaction Methods 0.000 description 4
- 238000004064 recycling Methods 0.000 description 4
- 239000010865 sewage Substances 0.000 description 4
- 238000000638 solvent extraction Methods 0.000 description 4
- 239000002699 waste material Substances 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- 230000005611 electricity Effects 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 230000008901 benefit Effects 0.000 description 2
- 238000006065 biodegradation reaction Methods 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 238000007605 air drying Methods 0.000 description 1
- 239000002956 ash Substances 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000005336 cracking Methods 0.000 description 1
- 239000010779 crude oil Substances 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 229910001873 dinitrogen Inorganic materials 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000003546 flue gas Substances 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 239000003960 organic solvent Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000003208 petroleum Substances 0.000 description 1
- 238000006068 polycondensation reaction Methods 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000007670 refining Methods 0.000 description 1
- 239000003079 shale oil Substances 0.000 description 1
- 238000004904 shortening Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 238000009270 solid waste treatment Methods 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000002912 waste gas Substances 0.000 description 1
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/40—Valorisation of by-products of wastewater, sewage or sludge processing
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- Treatment Of Sludge (AREA)
Abstract
本实用新型公开了一种油泥处理系统,油泥处理系统包括沉降设备、给料装置、干馏装置、旋风分离器、冷凝装置、离心分离机与锅炉。沉降设备用以将油泥分离为油水层与油泥沉淀物,给料装置用以接收与输送油泥沉淀物。干馏装置用以将油泥沉淀物分解为干馏气体与半焦。旋风分离器用以分离干馏气体与半焦。冷凝装置用以冷却干馏气体为冷凝液体与不凝结气体。离心分离机用以分离冷凝液体为回收油层与废水层。锅炉分别连接于沉降设备、旋风分离器、冷凝装置与离心分离机,用以接收油水层、半焦、不凝结气体与废水层,并将其燃烧降解。本实用新型兼具了污染物处理与能源回收的功用,并且拥有良好的经济性。
The utility model discloses an oil sludge treatment system. The oil sludge treatment system comprises a settling device, a feeding device, a dry distillation device, a cyclone separator, a condensation device, a centrifugal separator and a boiler. The settling equipment is used to separate the sludge into oil-water layer and sludge sediment, and the feeding device is used to receive and transport the sludge sediment. The dry distillation unit is used to decompose the oil sludge into dry distillation gas and semi-coke. The cyclone separator is used to separate dry distillation gas and semi-coke. The condensing device is used to cool the dry distillation gas into condensed liquid and non-condensable gas. The centrifuge is used to separate the condensed liquid into recovered oil layer and waste water layer. The boiler is respectively connected to the settling equipment, cyclone separator, condensing device and centrifuge to receive the oil-water layer, semi-coke, non-condensable gas and waste water layer, and burn and degrade them. The utility model combines the functions of pollutant treatment and energy recovery, and has good economy.
Description
技术领域technical field
本实用新型属于废弃物处理领域,具体地说,涉及一种油泥处理系统。The utility model belongs to the field of waste treatment, in particular to an oil sludge treatment system.
背景技术Background technique
页岩油泥是在油母页岩干馏炼油中,形成的具有一定热值(15000kJ/kg)、含油率较高(40%以上)的固体污染物。产率一般为页岩原油产量的0.3~0.5%,同时油泥难以自然降解,堆放易污染土壤和地下水。Shale sludge is a solid pollutant with a certain calorific value (15000kJ/kg) and a high oil content (above 40%) formed in the dry distillation of kerogen shale. The yield is generally 0.3-0.5% of shale crude oil production, and at the same time, oil sludge is difficult to degrade naturally, and it is easy to pollute soil and groundwater when stacked.
目前含油污泥等固体废弃物的处理技术,主要有焚烧法、溶剂萃取、生物降解法和热化学法等,这些方法的不足之处可以概括为两类:一类如焚烧法和生物降解法,着力于控制污染物排放,忽略了资源回收利用或能源回收效率有限;另一类如溶剂萃取法和热化学法,能最大限度地回收资源,却难以控制废水、废渣对环境的二次污染。这些方法皆无法在环境和效益之间取得平衡。现以焚烧法和溶剂萃取法为例,具体阐述两类处理工艺的情况。At present, solid waste treatment technologies such as oily sludge mainly include incineration, solvent extraction, biodegradation, and thermochemical methods. The shortcomings of these methods can be summarized into two categories: one such as incineration and biodegradation. , focusing on controlling pollutant emissions, ignoring resource recycling or limited energy recovery efficiency; the other, such as solvent extraction and thermochemical methods, can maximize resource recovery, but it is difficult to control the secondary pollution of waste water and waste residues to the environment . None of these methods can strike a balance between environment and benefit. Taking the incineration method and solvent extraction method as examples, the situation of the two types of treatment processes is described in detail.
所谓焚烧法,是将油泥经过脱水、降粘、风干处理后制成类煤燃料,在锅炉中与煤混合燃烧,达到回收利用油泥热值的目的,所产生的烟气经过净化处理,使之达到排放的标准。它的不足之处是,焚烧产生二次污染,油泥所含油分未得到合理化利用。溶剂萃取法是根据“相似兼容”原理,选取合适的有机溶剂来萃取油泥中的有机物,然后再通过蒸馏回收萃取液中的油分。该方法的优点是工艺简单,萃取剂可以重复使用,缺点是萃取剂价格昂贵,循环使用过程中出现部分损失,经处理后的油泥依然达不到现行的固体污染物的排放标准。The so-called incineration method is to make oil sludge into coal-like fuel after dehydration, viscosity reduction, and air-drying treatment, and burn it with coal in the boiler to achieve the purpose of recycling the heat value of oil sludge. The flue gas produced is purified to make it Meet emission standards. Its shortcoming is that incineration produces secondary pollution, and the oil contained in the sludge has not been rationally utilized. The solvent extraction method is based on the principle of "similarity and compatibility", selects a suitable organic solvent to extract the organic matter in the sludge, and then recovers the oil in the extract by distillation. The advantage of this method is that the process is simple, and the extractant can be reused. The disadvantage is that the extractant is expensive, and some losses occur during recycling, and the treated sludge still cannot meet the current discharge standards for solid pollutants.
实用新型内容Utility model content
有鉴于此,本实用新型所要解决的技术问题是提供了一种油泥处理系统,从而解决上述公知油泥处理技术无法兼具油泥的回收利用以及符合污染物排放标准的问题。In view of this, the technical problem to be solved by the utility model is to provide an oil sludge treatment system, so as to solve the problem that the above-mentioned known oil sludge treatment technology cannot have both oil sludge recycling and compliance with pollutant discharge standards.
为了解决上述技术问题,本实用新型公开了一种油泥处理系统,包括一沉降设备、一给料装置、一干馏装置、一旋风分离器、一冷凝装置、一离心分离机以及一锅炉。沉降设备用以接收油泥,并且将油泥分离为油水层与油泥沉淀物。给料装置连接于沉降设备与干馏装置之间,用以接收与输送油泥沉淀物。干馏装置接收所述油泥沉淀物,并且分解所述油泥沉淀物为干馏气体与半焦。旋风分离器分别连接于干馏装置与冷凝装罝,用以接收并分离干馏气体与半焦。冷凝装置接收与冷却干馏气体,使干馏气体形成冷凝液体与不凝结气体。离心分离机连接于冷凝装置,用以接收冷凝液体,并且分离冷凝液体为回收油层与废水层。锅炉分别连接于沉降设备、旋风分离器、冷凝装置与离心分离机,用以接收油水层、半焦、不凝结气体与废水层,并将其燃烧降解。In order to solve the above technical problems, the utility model discloses an oil sludge treatment system, which includes a settling device, a feeding device, a dry distillation device, a cyclone separator, a condensing device, a centrifuge and a boiler. Settling equipment is used to receive sludge and separate sludge into oil-water layer and sludge sediment. The feeding device is connected between the settling equipment and the dry distillation device, and is used for receiving and transporting oil sludge. The dry distillation device receives the oil sludge and decomposes the oil sludge into dry distillation gas and semi-coke. The cyclone separator is respectively connected to the carbonization device and the condensing device to receive and separate the carbonization gas and semi-coke. The condensing device receives and cools the dry distillation gas, so that the dry distillation gas forms condensed liquid and non-condensable gas. The centrifuge is connected to the condensing device to receive the condensed liquid and separate the condensed liquid into recovered oil layer and waste water layer. The boiler is respectively connected to the settling equipment, cyclone separator, condensing device and centrifuge to receive the oil-water layer, semi-coke, non-condensable gas and waste water layer, and burn and degrade them.
与现有的方案相比,本实用新型所获得的技术效果:Compared with the existing scheme, the technical effects obtained by the utility model are as follows:
本实用新型的油泥处理系统,通过干馏装置以热解为基础的处理方式,有效地促进乳化严重的油泥沉淀物在剧烈的温度条件下完成油、水、灰的分离,同时还以可伴随微波加热的方式,让油泥沉淀物的内部产生热源,从而缩短干馏时间。此外,在处理过程中,对油泥上层污水和其他污水进行废水焚烧,能彻底消除污染。再者,将干馏产生的半焦和低温瓦斯送入锅炉内燃烧发电,除了能回收能量外,又可以防止废渣废气对环境的污染,从而达到污染物零排放的功效,因此能够符合污染物的排放标准。同时,本实用新型的油泥处理系统还可以和炼油装置配套,共享设备(例如锅炉),从而减少公用设备的投资,使整体成本大幅降低。The oil sludge treatment system of the utility model effectively promotes the separation of oil, water, and ash of the heavily emulsified oil sludge sediment under severe temperature conditions through the pyrolysis-based treatment method of the retort device, and can also be accompanied by microwave The way of heating can generate a heat source inside the sludge deposit, thereby shortening the dry distillation time. In addition, in the process of treatment, waste water incineration of the upper layer of sludge and other sewage can completely eliminate pollution. Furthermore, the semi-coke and low-temperature gas produced by dry distillation are fed into the boiler for combustion to generate electricity. In addition to recovering energy, it can also prevent the pollution of waste residue and waste gas to the environment, thereby achieving the effect of zero emission of pollutants, so it can meet the requirements of pollutants. Emission Standards. At the same time, the oil sludge treatment system of the utility model can also be matched with an oil refinery unit and share equipment (such as a boiler), thereby reducing the investment in public equipment and greatly reducing the overall cost.
附图说明Description of drawings
图1为本实用新型的一实施例的油泥处理系统的平面示意图;以及Figure 1 is a schematic plan view of an oil sludge treatment system according to an embodiment of the present invention; and
图2为本实用新型的一实施例的油泥处理方法的流程图。Fig. 2 is a flow chart of an oil sludge treatment method according to an embodiment of the present invention.
具体实施方式Detailed ways
以下将配合图式及实施例来详细说明本实用新型的实施方式,藉此对本实用新型如何应用技术手段来解决技术问题并达成技术功效的实现过程能充分理解并据以实施。The implementation of the utility model will be described in detail below in conjunction with the drawings and examples, so that the implementation process of how the utility model uses technical means to solve technical problems and achieve technical effects can be fully understood and implemented accordingly.
请参照图1和图2,本实用新型的一实施例所揭示的油泥处理系统包括一沉降设备10、一给料装置20、一干馏装置30、一旋风分离器40、一冷凝装置50、一离心分离机60以及一锅炉70。Please refer to Fig. 1 and Fig. 2, the sludge treatment system disclosed by an embodiment of the present utility model includes a
沉降设备10连接于一油泥排放设备80,用以接收油泥排放设备80输出的油泥,例如石油油泥、污水处理厂的油泥等,在本实施例中是以页岩油泥作为举例说明,但并不以此为限。沉降设备10还将所述油泥分离为油水层与油泥沉淀物。The
给料装置20连接于沉降设备10与干馏装置30之间,用以接收与输送所述油泥沉淀物。其中给料装置20包括一给料斗210与通过氮气密封的一给料机220(例如螺旋给料机),给料斗210连接于沉降设备10,给料机220连接于干馏装置30。The
干馏装置30连接于所述给料装置20,用以接收所述油泥沉淀物,并且分解所述油泥沉淀物为干馏气体与半焦。在本实施例中,干馏装置30可以是但并不局限于微波滚筒干馏装置,其包括一滚筒310以及配置于滚筒310内的一推料叶片320(例如螺旋推料叶片)与一微波加热区330,其中滚筒310连接于给料装置20的给料机220与旋风分离器40之间;所述油泥沉淀物于所述滚筒310内通过所述推料叶片320输送至所述微波加热区330,所述微波加热区330用以热处理所述油泥沉淀物。The
旋风分离器40连接于所述干馏装置30,用以接收与分离所述干馏气体与所述半焦。The
冷凝装置50连接于旋风分离器40与离心分离机60之间,用以接收与冷却所述干馏气体为冷凝液体与不凝结气体。The
离心分离机60连接于所述冷凝装置50,用以接收所述冷凝液体,并且分离所述冷凝液体为回收油层与废水层。The
锅炉70通过输送管路分别连接于沉降设备10、旋风分离器40、冷凝装置50与离心分离机60,并且于锅炉70与旋风分离器40之间的输送管路410内还供应有高压气体。所述锅炉70接收并燃烧所述油水层、所述半焦、所述不凝结气体与所述废水层。在本实施例中,所述锅炉可以是但并不局限于循环流化床锅炉,其包括一喷嘴,用以接收所述油水层与所述废水层,并且将所述油水层与所述废水层喷洒于所述锅炉中。The
在应用上,首先从油泥排放设备80输送油泥至油泥处理系统的沉降设备10(S101),使油泥在沉降设备10内通过重力作用分离为上层的油水层(例如有机污水)以及下层的油泥沉淀物(S102)。接着,将上层的油水层输送至锅炉70内进行废水燃焚烧(S103),使废水中的污染物被彻底降解,其中为了提高燃烧效率,锅炉70还配置有一喷嘴710,例如雾化喷嘴,通过喷嘴710接收油水层并且将其喷洒于锅炉70内燃烧,以促进燃烧效率。同时,将下层的油泥沉淀物输送至给料装置20的给料斗210,然后在氮气密封的状态下,经由料装置20的给料机220输送至干馏装置30的滚筒310内(S104)。In terms of application, the sludge is first transported from the
接着,在推料叶片320的作用下,使滚筒310内的油泥沉淀物进入到微波加热区330进行热处理,通过微波加热区330提供450~520℃的热处理温度对油泥沉淀物均匀加热,使油泥沉淀物发生一系列裂解、缩聚反应,从而产生高温的干馏气体和残余的半焦(S105)。之后,输送干馏气体和半焦至旋风分离器40内进行气固分离(S106),当干馏气体和半焦在旋风分离器40中完成气体和固体分离后,从旋风分离器40分离下来的半焦由高压气体送入锅炉70,进行燃烧发电(S107);而干馏气体分部于旋风分离器40的上部,并且被输送至冷凝装置50中进行冷却,使干馏气体受到低温作用而形成冷凝液体与不凝结气体(S108),其中不凝结气体被输送至锅炉内和半焦一起燃烧发电(S109),而冷凝液体被输送到离心分离机60进行油水分离,从而获得上层的回收油层(页岩油)与下层的废水层(S110)。接着,将废水层排放至输送管路内,使废水层随着来自沉降设备的油水层通过喷嘴喷入锅炉内焚烧(S111)。最后,收集回收油层于一储存槽内备用(S112)。Next, under the action of the pushing
基于上述,本实用新型的油泥处理系统,以热解为基础油泥处理方式,能把油泥进行废物利用,既减少固体污染物,又完成了资源回收,并且拥有良好的经济性。此外,整个处理过程所产生的高化学需氧量(COD)污水、有害气体及残余的固体污染物(半焦)均被焚烧,因此可达到污染物零排放的功效。同时本实用新型的油泥处理系统还可以和炼油装置配套,例如共享锅炉,而最大限度的减少公用设备的投入,从而拥有良好的经济性。Based on the above, the oil sludge treatment system of the present invention uses pyrolysis as the basic oil sludge treatment method, which can use the oil sludge for waste, reduces solid pollutants, completes resource recovery, and has good economy. In addition, the high chemical oxygen demand (COD) sewage, harmful gases and residual solid pollutants (semi-coke) generated during the entire treatment process are all incinerated, so that zero discharge of pollutants can be achieved. At the same time, the oil sludge treatment system of the utility model can also be matched with oil refining equipment, such as sharing boilers, so as to minimize the investment in public equipment, thereby having good economy.
上述说明示出并描述了本实用新型的若干优选实施例,但如前所述,应当理解本实用新型并非局限于本文所披露的形式,不应看作是对其他实施例的排除,而可用于各种其他组合、修改和环境,并能够在本文所述实用新型构想范围内,通过上述教导或相关领域的技术或知识进行改动。而本领域人员所进行的改动和变化不脱离本实用新型的精神和范围,则都应在本实用新型所附权利要求的保护范围内。The above description shows and describes several preferred embodiments of the present utility model, but as mentioned above, it should be understood that the present utility model is not limited to the form disclosed herein, and should not be regarded as excluding other embodiments, but can be used In various other combinations, modifications and environments, and can be modified by the above teachings or skills or knowledge in related fields within the scope of the utility model concept described herein. However, changes and changes made by those skilled in the art do not depart from the spirit and scope of the utility model, and should all be within the protection scope of the appended claims of the utility model.
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
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CN103420555A (en) * | 2013-08-01 | 2013-12-04 | 中国大唐集团科学技术研究院有限公司 | Oil sludge treating system and method |
CN107062873A (en) * | 2014-04-09 | 2017-08-18 | 邹玉华 | A kind of continuous drying system and its method of work |
CN107376802A (en) * | 2017-09-15 | 2017-11-24 | 四川宏图普新微波科技有限公司 | The technique of clean operation in a kind of holding chamber for microwave cracking damaged tire |
CN108800189A (en) * | 2018-06-21 | 2018-11-13 | 西安热工研究院有限公司 | A method of handling greasy filth danger wastes using station boiler |
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2013
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Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
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CN103420555A (en) * | 2013-08-01 | 2013-12-04 | 中国大唐集团科学技术研究院有限公司 | Oil sludge treating system and method |
CN103420555B (en) * | 2013-08-01 | 2015-07-15 | 中国大唐集团科学技术研究院有限公司 | Oil sludge treating system and method |
CN107062873A (en) * | 2014-04-09 | 2017-08-18 | 邹玉华 | A kind of continuous drying system and its method of work |
CN107062865A (en) * | 2014-04-09 | 2017-08-18 | 邹玉华 | A kind of continuous drying system |
CN107062865B (en) * | 2014-04-09 | 2019-10-29 | 邹玉华 | A kind of continuous drying system recycled for petrol and diesel oil or machine oil |
CN107376802A (en) * | 2017-09-15 | 2017-11-24 | 四川宏图普新微波科技有限公司 | The technique of clean operation in a kind of holding chamber for microwave cracking damaged tire |
CN108800189A (en) * | 2018-06-21 | 2018-11-13 | 西安热工研究院有限公司 | A method of handling greasy filth danger wastes using station boiler |
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