WO2009094904A1 - A method for treating high cod wastewater - Google Patents

A method for treating high cod wastewater Download PDF

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Publication number
WO2009094904A1
WO2009094904A1 PCT/CN2009/000108 CN2009000108W WO2009094904A1 WO 2009094904 A1 WO2009094904 A1 WO 2009094904A1 CN 2009000108 W CN2009000108 W CN 2009000108W WO 2009094904 A1 WO2009094904 A1 WO 2009094904A1
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Prior art keywords
wastewater
coke
anaerobic
active coke
biogas
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PCT/CN2009/000108
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French (fr)
Chinese (zh)
Inventor
Dawei Zhang
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Dawei Zhang
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Publication of WO2009094904A1 publication Critical patent/WO2009094904A1/en

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • C02F3/286Anaerobic digestion processes including two or more steps
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/16Regeneration of sorbents, filters
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Definitions

  • the invention belongs to the technical field of wastewater treatment, and in particular relates to a method for treating high COD waste water by using anaerobic and active coke. Background technique
  • COD Chemical Oxygen Demand
  • the common methods for treating high COD wastewater are anaerobic method and active coke filtration adsorption method.
  • the anaerobic treatment of high COD wastewater has a small footprint, low investment, and low processing cost.
  • the disadvantage of the anaerobic method is that the treated water COD, chromaticity and other indicators cannot meet the discharge standard, and the anaerobic treatment process per 1 kg COD anaerobic treatment produces 0.3m 3 -0.5m 3 biogas, as biogas generated enough economic lot, can not be achieved recycling commonly used method flaring process, that is a waste of energy and air pollution.
  • the wastewater is treated by activated coke filtration adsorption method.
  • the treated water COD can reach 50mg/l or less, and the chroma can reach 5 times (dilution factor) below, which can fully meet the environmental emission standards.
  • the disadvantage of the activated coke filtration adsorption method is that the treatment cost is high, and the main reason for the high treatment cost is that in the process of treating wastewater, the regeneration of each ton of saturated activated coke needs to consume 1.7-1.9 million kcal of heat, equivalent to about 243-271 kg of standard coal. Therefore, the energy cost of saturated activated coke regeneration accounts for 70-80% of the total cost of wastewater treatment by activated coke filtration. Summary of the invention
  • the COD wastewater treatment method provided by the present invention is characterized in that the wastewater is subjected to anaerobic treatment, then subjected to active coke adsorption treatment, and biogas generated during anaerobic treatment is collected.
  • the method wherein the wastewater is wastewater treated by a sedimentation tank.
  • the method wherein the wastewater is wastewater treated by a regulating tank.
  • the invention combines two methods of anaerobic and active coke adsorption to treat high COD wastewater, that is, the active coke filtration adsorption deep treatment overcomes the defect that the water quality after the anaerobic treatment method fails to meet the discharge standard, and at the same time, the anaerobic treatment
  • the biogas produced in the process is used as an energy source for the regeneration of saturated activated coke in the active coke filtration adsorption method, which can not only reduce the regeneration cost of the saturated activated coke, but also reduce the cost of the activated coke filtration adsorption process, and can save the cost. Energy, the above methods have not been reported so far.
  • Figure 1 is a schematic flow chart of the present invention.
  • the technical conditions and equipment used in the two methods of anaerobic treatment and active coke adsorption in the present invention are well-known techniques, and the precipitation and the technical conditions and equipment used for regulating the water quality before the anaerobic treatment are also Known technology.
  • the novelty and inventive concept of the present invention consists in combining two well-known techniques, anaerobic treatment and active coke adsorption treatment, and using biogas generated during anaerobic treatment as a fuel for regenerating saturated coke.
  • the technical solution of the present invention is: (1) First, the wastewater is pretreated by an anaerobic method to convert most of the organic matter in the wastewater into biogas; (2) the water after the anaerobic treatment is used.
  • the active coke filtration adsorption method is deeply treated to make the treated water quality meet the environmental emission standard or the enterprise water reuse standard; (3)
  • the biogas generated in the anaerobic treatment process is used as the energy source for the saturated activated coke regeneration in the active coke filtration adsorption method.
  • the wastewater 1 of the present invention enters the sedimentation tank 2, and the water after the precipitation treatment flows to the adjustment tank 3; the water in the adjustment tank 3 is sent to the anaerobic reaction device 5 by the water pump 4, in the anaerobic reaction device 5 Under the action of acid-producing bacteria and methanogens in the anaerobic reaction device 5, most of the biodegradable substances in the wastewater are oxidized to synthesize the biogas 10, and the water treated by the anaerobic reaction device 5 flows into the collecting pool. 6.
  • the wastewater in the collecting tank 6 is sent to the active coke processing device 8 by the water pump 7, and the water treated by the active coke treating device 8 flows into the clear water tank 9.
  • the active coke of the invention is made of anthracite, lean coal, lean coal, coking coal, fat coal, gas coal, long flame coal, lignite, semi-coke, coke or basket carbon, and is dried, retorted, carbonized and activated.
  • iodine adsorption value is 400mg / g ⁇ 800mg/go
  • the wastewater 1 is subjected to an anaerobic reactor 5 pretreatment and an active coke treatment unit. After deep treatment, the water quality fully meets the environmental emission standards.
  • the activated coke in the active coke processing device 8 becomes saturated active coke after being used for a certain period of time, and it is necessary to transport the saturated active coke 12 to the active coke regeneration device 13 for regeneration.
  • the invention collects the biogas 10 generated by the anaerobic reaction device 5 into the biogas storage cabinet 11, and the biogas storage cabinet 11 is a well-known device; the biogas 10 is discharged under the pressure of the biogas storage cabinet 11, and is transported to the activated coke through the pipeline.
  • the device 13 serves as an energy source required for the active coke regeneration device 13 to operate.
  • the anaerobic reaction apparatus 5 employed in the present invention is a well-known apparatus and may be a UASB anaerobic reactor, an anaerobic reaction tank (Patent No.: CN97227787.0, Bulletin No. CN2309334) or / and an IC anaerobic reactor.
  • the active coke processing apparatus 8 employed in the present invention may be an activated coke adsorption bed (Patent No.: ZL 2006 2 0022884.1) or / and an active coke adsorption tank (Patent No.: ZL 2006 2 0022883.7).
  • An ideal apparatus is an active coke adsorption tank provided by the patent number ZL 2006 2 0022883.7.
  • the apparatus for treating active coke is not strictly limited as long as it can satisfy the regeneration of activated coke by using biogas as a fuel.
  • the present invention specifically recommends a device for regenerating a saturated activated coke according to the present invention.
  • the detailed structure and working principle of the device can be found in the active semi-coke filter adsorbent processing apparatus disclosed in Patent Application No. 200710062831.1. In order to assist the person skilled in the art to further understand the present invention, a brief description of the apparatus will be given below.
  • the active semi-coke filter adsorption material processing device comprises a feeding bin, a screw feeder, a gas collecting device, a roller, a supporting roller ring, a transmission ring gear, a heating chamber wall, a reducer, a frequency conversion motor, a heating chamber, and a smoke exhaust port.
  • low-pressure gas burner temperature measuring device, turning plate, discharging device, small roller, steam input pipe, observation hole, feeding temperature measuring device, discharge temperature measuring device, sealing device composition, combustion air fan, dust removal device, It consists of residual hot water jacket, induced draft fan, gas discharge machine and unit casing.
  • the roller making material of the active semi-coke filter adsorption material processing equipment is made of heat-resistant stainless steel, can withstand the high temperature of the unit during operation, and can resist general acid-base salt corrosion.
  • the drum has a diameter of 600 mm to 2,000 mm and a length of 18,000 to 28,000 mm.
  • a sealing device is installed at a portion of the drum that is in contact with the heating chamber, and the sealing device is of a labyrinth or a steam type.
  • Each side of the drum is provided with a small roller of 1 meter length, and the inner wall of the drum is provided with a spoon-shaped turning plate.
  • the material of the material is the same as that of the drum.
  • the inner wall of the drum is in direct contact with the material, and the upper and lower materials are alternately heated and heated uniformly.
  • the hot gas generated in the drying and retorting stage of the material is collected by the gas collecting device at the front end of the drum and sent to the low-pressure gas burner for combustion.
  • the cooling section is taken in, and it is naturally cooled until it is discharged.
  • the roller has one supporting roller ring from the front and rear ends, and the outer wall of the roller is inlaid with the transmission gear ring, which is driven by the reducer and the variable frequency motor.
  • the drum design speed is 0.5 ⁇ 1.5r/min, and the frequency conversion stepless speed regulation.
  • the drum is mounted at an angle of 2°.
  • In the middle of the unit is a heating chamber, which externally heats the outer wall of the drum.
  • a burner is mounted on both side walls of the heating chamber, and the combustion blower provides air required for combustion.
  • the burner is located at the lower portion of the drum to prevent the flame from being blown directly into contact with the drum.
  • the burners are set up according to the temperature curve by 10 ⁇ 16, which are arranged on the two side walls of the heating chamber.
  • the temperature of each section of the heating chamber is controlled by adjusting the air supply volume of each burner to ensure the preparation process of the active semi-coke filter adsorbent. Temperature, warming time and constant temperature time.
  • the lining of the heating chamber wall is a combination of lightweight high-aluminum brick and high-aluminum fiber.
  • the top of the heating chamber is a high-alumina poly-light brick flat ceiling. It is easy to disassemble when the drum is repaired.
  • the lightweight insulation material between the heating chamber side wall and the unit casing is , the amount of heat dissipation is small, and the temperature rises quickly.
  • the unit casing is made of steel and steel.
  • the flue gas in the heating chamber of the active semi-coke filter adsorption processing equipment is discharged from the exhaust port installed at the top of the unit, the exhaust port is connected with the residual hot water jacket and the induced draft fan, the induced draft fan adopts frequency conversion speed regulation, and the residual hot water jacket is used for recycling smoke. Heat in the gas, lower the temperature of the flue gas, and heat the steam boiler to replenish water.
  • a plurality of temperature measuring devices are installed on both sides of the heating chamber wall to detect the temperature of each temperature section, and a temperature measuring device is installed at the head and the tail of the unit to detect the feeding temperature and the discharging temperature.
  • the unit is provided with a control cabinet and a control cabinet. Install 20 digital display meters, frequency conversion motor inverter and induced draft fan inverter and screw feeder inverter, power switch and low voltage electrical appliances.
  • the mixed gas such as hot gas generated during the processing of the material in the drum is collected by the gas collecting device at the front end of the drum, and is processed by the dust removing device, and then sent to the low-pressure gas burner of the unit for combustion.
  • a sealing device is arranged between the gas collecting device and the drum, and the sealing device can be a labyrinth or a steam type.
  • the fuel required for the operation of the active semi-coke filter sorbent processing equipment uses the biogas produced during the operation of the anaerobic reactor 6 and the mixed gas produced during the operation of the activated semi-coke filter sorbent processing equipment.
  • the front end of the drum of the active semi-coke filter adsorption processing equipment is equipped with a screw feeder and a feeding bin, and the feeding speed of the screw feeder is adjusted by the frequency conversion controller.
  • a discharge device is installed at the rear end of the drum, and an observation hole and a steam inlet pipe are provided at the end surface of the drum.
  • a sealing device is arranged between the discharging device and the drum, and the sealing device can be a labyrinth or a steaming type.
  • the invention utilizes the invention to treat chemical pulping wastewater of papermaking enterprises.
  • the wastewater 1 enters the sedimentation tank 2, and the residence time of the wastewater 1 in the sedimentation tank is 2-3 hours, and the water after the precipitation treatment flows to the adjustment tank 3; in the adjustment tank 3, NaOH or HC1 is added to adjust the appropriate reaction pH. Value and investment Add N, P nutrient salts.
  • the complex water-insoluble matrix in the wastewater is converted by the extracellular enzyme secreted by the microorganism into a smaller, water-soluble matrix, ie a hydrolysis reaction.
  • the water in the conditioning tank 3 is sent to the anaerobic reactor 5 by the water pump 4. Under the action of acid-producing bacteria and methanogens in the anaerobic reaction device 5, most of the biodegradable substances in the wastewater are oxidized to synthesize the biogas 10.
  • the wastewater is treated by the anaerobic reactor 5 and then flows into the collecting tank. 6.
  • the COD in the water is 1500mg/l, and the COD removal rate is over 75%.
  • the water in the catchment tank 6 is treated by the active coke treatment device 8 and then flows into the clear water pool.
  • the COD content in the water is 70mg/l, the turbidity is 5Ftu, and the chromaticity is 5 times, which meets the environmental emission standards and the standard of papermaking water;
  • the active coke processing device 8 discharges 16 tons of saturated activated coke 12 per day, and delivers the above-mentioned saturated active coke 12 to the active coke regeneration device 13 for regeneration.

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  • Life Sciences & Earth Sciences (AREA)
  • Microbiology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
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  • Water Treatment By Sorption (AREA)

Abstract

A method for treating high COD wastewater is provided, which comprises treating the wastewater in an anaerobic tank (5), and adsorbing pollutants from an anaerobic effluent in an active coke tank (8), collecting the biogas (10) produced by the anaerobic treatment to a storage closet (11), and feeding the biogas (10) to an active coke regeneration device (13) as a fuel for regenerating the saturated-active coke.

Description

髙 COD废水处理方法 技术领域  髙 COD wastewater treatment method
本发明属于废水处理技术领域,具体地涉及一种采用厌氧及活性焦处理高 COD废 水的方法。 背景技术  The invention belongs to the technical field of wastewater treatment, and in particular relates to a method for treating high COD waste water by using anaerobic and active coke. Background technique
在环保工作中, 人们采用 COD(Chemical Oxygen Demand)用作衡量水中有机物质 含量多少的指标。 目前, 常见的对高 COD废水进行处理的方法, 一是采用厌氧法, 二 是采用活性焦过滤吸附法。  In environmental protection work, COD (Chemical Oxygen Demand) is used as an indicator to measure the amount of organic matter in water. At present, the common methods for treating high COD wastewater are anaerobic method and active coke filtration adsorption method.
采用厌氧法处理高 COD废水, 占地面积小、 投资少、 处理成本低, 厌氧法的不足 之处是处理后的水 COD、 色度等指标无法达到排放标准, 而且在厌氧处理过程中, 每 厌氧处理 1公斤 COD产生 0.3m3-0.5m3沼气, 由于产生的沼气不够经济批量, 无法实 现回收利用, 通常采用火炬燃烧的方法处理, 即浪费了能源又造成空气污染。 The anaerobic treatment of high COD wastewater has a small footprint, low investment, and low processing cost. The disadvantage of the anaerobic method is that the treated water COD, chromaticity and other indicators cannot meet the discharge standard, and the anaerobic treatment process per 1 kg COD anaerobic treatment produces 0.3m 3 -0.5m 3 biogas, as biogas generated enough economic lot, can not be achieved recycling commonly used method flaring process, that is a waste of energy and air pollution.
采用活性焦过滤吸附法处理废水, 处理后的水 COD可达到 50mg/l以下, 色度可 达到 5倍 (稀释倍数) 以下, 完全能够满足环保排放标准。 活性焦过滤吸附法的不足 之处是处理费用高, 导致处理费用高的主要原因是处理废水过程中, 每吨饱和活性焦 再生需要消耗 170-190万 kcal热量, 折合标煤约 243-271公斤, 因此, 饱和活性焦再 生的能源费用占活性焦过滤吸附法处理废水总费用的 70-80%。 发明内容  The wastewater is treated by activated coke filtration adsorption method. The treated water COD can reach 50mg/l or less, and the chroma can reach 5 times (dilution factor) below, which can fully meet the environmental emission standards. The disadvantage of the activated coke filtration adsorption method is that the treatment cost is high, and the main reason for the high treatment cost is that in the process of treating wastewater, the regeneration of each ton of saturated activated coke needs to consume 1.7-1.9 million kcal of heat, equivalent to about 243-271 kg of standard coal. Therefore, the energy cost of saturated activated coke regeneration accounts for 70-80% of the total cost of wastewater treatment by activated coke filtration. Summary of the invention
本发明的目的在于提供一种 COD废水处理方法, 以克服公知技术中存在的缺陷。 为实现上述目的, 本发明提供的 COD废水处理方法, 是将废水经由厌氧处理后, 再经活性焦吸附处理, 并收集厌氧处理时产生的沼气。  It is an object of the present invention to provide a COD wastewater treatment method that overcomes the deficiencies found in the prior art. In order to achieve the above object, the COD wastewater treatment method provided by the present invention is characterized in that the wastewater is subjected to anaerobic treatment, then subjected to active coke adsorption treatment, and biogas generated during anaerobic treatment is collected.
所述的方法, 其中, 所述的废水是经过沉淀池处理的废水。  The method, wherein the wastewater is wastewater treated by a sedimentation tank.
所述的方法, 其中, 所述的废水是经过调节池处理的废水。  The method, wherein the wastewater is wastewater treated by a regulating tank.
本发明是将厌氧和活性焦吸附两种方法结合起来处理高 COD废水, 即, 活性焦 过滤吸附法深处理克服厌氧处理方法处理后水质达不到排放标准的缺陷, 同时将厌氧 处理过程中产生沼气用作活性焦过滤吸附法中饱和活性焦再生的能源, 不仅能够降低 饱和活性焦的再生成本, 从而降低活性焦过滤吸附法处理废水的成本, 而且可以节约 能源, 以上方法至今尚未见报导。 附图说明 The invention combines two methods of anaerobic and active coke adsorption to treat high COD wastewater, that is, the active coke filtration adsorption deep treatment overcomes the defect that the water quality after the anaerobic treatment method fails to meet the discharge standard, and at the same time, the anaerobic treatment The biogas produced in the process is used as an energy source for the regeneration of saturated activated coke in the active coke filtration adsorption method, which can not only reduce the regeneration cost of the saturated activated coke, but also reduce the cost of the activated coke filtration adsorption process, and can save the cost. Energy, the above methods have not been reported so far. DRAWINGS
图 1为本发明的流程示意图。  Figure 1 is a schematic flow chart of the present invention.
图中标记: 1-废水、 2-沉淀池、 3-调节池、 4-水泵、 5-厌氧反应装置、 6-集水池、 7-水泵、 8-活性焦处理装置、 9-清水池、 10-沼气、 11-沼气储气柜、 12-饱和活性焦、 13- 活性焦再生装置。 具体实施方式 下面通过实施例, 并结合附图, 对本发明的技术方案作进一步具体的说明。 在说 明书中, 相同或相似的附图标号指示相同或相似的部件。 下述参照附图对本发明实施 方式的说明旨在对本发明的总体发明构思进行解释, 而不应当理解为对本发明的一种 限制。  Marked in the figure: 1- Wastewater, 2-precipitation tank, 3-regulation tank, 4-water pump, 5-anaerobic reactor, 6-sink, 7-water pump, 8-active coke treatment unit, 9-clearing tank, 10-biogas, 11-biogas storage cabinet, 12-saturated activated coke, 13-active coke regeneration device. BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the technical solutions of the present invention will be further specifically described by way of embodiments and with reference to the accompanying drawings. In the specification, the same or similar reference numerals indicate the same or similar parts. The description of the embodiments of the present invention is intended to be illustrative of the present invention, and is not to be construed as limiting.
需要说明的是, 本发明中厌氧处理和活性焦吸附两方法使用的技术条件和设备均 为公知技术, 并且在厌氧处理前进行的沉淀以及调节水质所采用的技术条件和设备也 均为公知技术。 而本发明的新颖性和创造性在于将厌氧处理和活性焦吸附处理两种公 知技术结合在一起,并将厌氧处理时产生的沼气作为对饱和的活性焦进行再生的燃料。  It should be noted that the technical conditions and equipment used in the two methods of anaerobic treatment and active coke adsorption in the present invention are well-known techniques, and the precipitation and the technical conditions and equipment used for regulating the water quality before the anaerobic treatment are also Known technology. The novelty and inventive concept of the present invention consists in combining two well-known techniques, anaerobic treatment and active coke adsorption treatment, and using biogas generated during anaerobic treatment as a fuel for regenerating saturated coke.
具体地说, 本发明的技术方案是: (1 ) 首先釆用厌氧法对废水进行预处理, 将废 水中的大部分有机物转化成沼气; (2 ) 将经过厌氧处理后的水, 使用活性焦过滤吸附 法进行深处理, 使处理后的水质达到环保排放标准或企业回用水标准; (3 ) 将厌氧处 理过程中产生沼气用作活性焦过滤吸附法中饱和活性焦再生的能源。  Specifically, the technical solution of the present invention is: (1) First, the wastewater is pretreated by an anaerobic method to convert most of the organic matter in the wastewater into biogas; (2) the water after the anaerobic treatment is used. The active coke filtration adsorption method is deeply treated to make the treated water quality meet the environmental emission standard or the enterprise water reuse standard; (3) The biogas generated in the anaerobic treatment process is used as the energy source for the saturated activated coke regeneration in the active coke filtration adsorption method.
参见图 1 , 本发明的废水 1进入沉淀池 2, 经过沉淀处理后的水流至调节池 3 ; 调 节池 3中的水再用水泵 4送至厌氧反应装置 5 , 在厌氧反应装置 5中, 在厌氧反应装 置 5中的产酸菌、 甲烷菌的作用下, 废水中的绝大部分可生物降解的物质被氧化合成 了沼气 10, 经厌氧反应装置 5处理后的水流入集水池 6。  Referring to Fig. 1, the wastewater 1 of the present invention enters the sedimentation tank 2, and the water after the precipitation treatment flows to the adjustment tank 3; the water in the adjustment tank 3 is sent to the anaerobic reaction device 5 by the water pump 4, in the anaerobic reaction device 5 Under the action of acid-producing bacteria and methanogens in the anaerobic reaction device 5, most of the biodegradable substances in the wastewater are oxidized to synthesize the biogas 10, and the water treated by the anaerobic reaction device 5 flows into the collecting pool. 6.
集水池 6中的废水用水泵 7输送到活性焦处理装置 8, 经过活性焦处理装置 8处 理后的水流入清水池 9。  The wastewater in the collecting tank 6 is sent to the active coke processing device 8 by the water pump 7, and the water treated by the active coke treating device 8 flows into the clear water tank 9.
本发明的活性焦为采用无烟煤、 贫煤、 瘦煤、 焦煤、 肥煤、 气煤、 长焰煤、 褐煤、 半焦、焦炭或篮炭为原料,经过干燥、干馏、碳化、活化后制成,碘吸附值为 400mg/g〜 800mg/g o The active coke of the invention is made of anthracite, lean coal, lean coal, coking coal, fat coal, gas coal, long flame coal, lignite, semi-coke, coke or basket carbon, and is dried, retorted, carbonized and activated. , iodine adsorption value is 400mg / g ~ 800mg/go
废水 1经过厌氧反应装置 5预处理和活性焦处理装置 8深处理后, 水质完全达到 环保排放标准。  The wastewater 1 is subjected to an anaerobic reactor 5 pretreatment and an active coke treatment unit. After deep treatment, the water quality fully meets the environmental emission standards.
活性焦处理装置 8中的活性焦经过一定时间使用后成为饱和活性焦, 需要将饱和 活性焦 12输送到活性焦再生装置 13中进行再生。  The activated coke in the active coke processing device 8 becomes saturated active coke after being used for a certain period of time, and it is necessary to transport the saturated active coke 12 to the active coke regeneration device 13 for regeneration.
本发明将厌氧反应装置 5产生的沼气 10收集至沼气储气柜 11内,沼气储气柜 11 为公知设备; 沼气 10在沼气储气柜 11的压力下排出, 通过管道输送到活性焦再生装 置 13, 作为活性焦再生装置 13运行时所需的能源。  The invention collects the biogas 10 generated by the anaerobic reaction device 5 into the biogas storage cabinet 11, and the biogas storage cabinet 11 is a well-known device; the biogas 10 is discharged under the pressure of the biogas storage cabinet 11, and is transported to the activated coke through the pipeline. The device 13 serves as an energy source required for the active coke regeneration device 13 to operate.
本发明采用的厌氧反应装置 5为公知设备, 可以是 UASB厌氧反应器、 厌氧反应 池 (专利号: CN97227787.0, 公告号 CN2309334 ) 或 /和 IC厌氧反应器。  The anaerobic reaction apparatus 5 employed in the present invention is a well-known apparatus and may be a UASB anaerobic reactor, an anaerobic reaction tank (Patent No.: CN97227787.0, Bulletin No. CN2309334) or / and an IC anaerobic reactor.
本发明采用的活性焦处理装置 8 可以是活性焦吸附床 (专利号: ZL 2006 2 0022884.1 ) 或 /和活性焦吸附罐 (专利号: ZL 2006 2 0022883.7)。 较理想的设备是采 用专利号为 ZL 2006 2 0022883.7.提供的活性焦吸附罐。  The active coke processing apparatus 8 employed in the present invention may be an activated coke adsorption bed (Patent No.: ZL 2006 2 0022884.1) or / and an active coke adsorption tank (Patent No.: ZL 2006 2 0022883.7). An ideal apparatus is an active coke adsorption tank provided by the patent number ZL 2006 2 0022883.7.
其中, 活性焦处理的装置没有严格的限定, 只要能满足以沼气为燃料进行活性焦 再生即可。本发明具体地推荐一种本发明采用的用于饱和活性焦进行再生处理的装置, 该装置的详细结构和工作原理可参阅专利申请号: 200710062831.1 公开的活性半焦过 滤吸附料加工设备。 为了有助于本领域技术人员进一步了解本发明, 下面对该装置作 一简要描述。  Among them, the apparatus for treating active coke is not strictly limited as long as it can satisfy the regeneration of activated coke by using biogas as a fuel. The present invention specifically recommends a device for regenerating a saturated activated coke according to the present invention. The detailed structure and working principle of the device can be found in the active semi-coke filter adsorbent processing apparatus disclosed in Patent Application No. 200710062831.1. In order to assist the person skilled in the art to further understand the present invention, a brief description of the apparatus will be given below.
该该活性半焦过滤吸附料加工设备, 由加料仓、 螺旋给料机、 集气装置、 滚筒、 支撑滚圈、 传动齿圈、 加热室壁、 减速机、 变频电机、 加热室、 排烟口、 低压煤气燃 烧嘴、 测温装置、 翻料板、 出料装置、 小滚筒、 蒸汽输入管、 观察孔、 进料测温装置、 出料测温装置、 密封装置组成、 助燃风机、 除尘装置、 余热水套、 引风机、 煤气排送 机、 机组外壳等组成。  The active semi-coke filter adsorption material processing device comprises a feeding bin, a screw feeder, a gas collecting device, a roller, a supporting roller ring, a transmission ring gear, a heating chamber wall, a reducer, a frequency conversion motor, a heating chamber, and a smoke exhaust port. , low-pressure gas burner, temperature measuring device, turning plate, discharging device, small roller, steam input pipe, observation hole, feeding temperature measuring device, discharge temperature measuring device, sealing device composition, combustion air fan, dust removal device, It consists of residual hot water jacket, induced draft fan, gas discharge machine and unit casing.
该活性半焦过滤吸附料加工设备的滚筒制作材料选用耐热不锈钢, 能够承受机组 运行时的高温, 能够抵御一般酸碱盐腐蚀。 滚筒直径为 600mm〜2,000mm , 长度 18,000〜28,000mm。  The roller making material of the active semi-coke filter adsorption material processing equipment is made of heat-resistant stainless steel, can withstand the high temperature of the unit during operation, and can resist general acid-base salt corrosion. The drum has a diameter of 600 mm to 2,000 mm and a length of 18,000 to 28,000 mm.
滚筒两端与加热室接触的部位安装密封装置, 密封装置采用迷宫式或蒸汽式。 滚 筒两端各带 1米长的小滚筒, 滚筒内壁安装挖勺状翻料板, 翻料板材质与滚筒相同, 滚筒内壁与物料直接接触, 上、 下层物料交替受热, 加热均匀。 物料在滚筒内干燥及 干馏阶段产生的热煤气, 由滚筒前端的集气装置收集后送至低压煤气燃烧嘴燃烧。 物 料出活化段后迸入降温段, 自然冷却, 直至出料。 滚筒由前后端各有 1个支撑滚圈, 滚筒外壁镶嵌传动齿轮圈, 由减速机、 变频电机驱动。 滚筒设计转速 0.5〜1.5r/min, 变频无级调速。 滚筒安装倾角为 2°。 在机组中部为加热室, 由外部加热滚筒外壁。 加 热室两侧壁上安装有燃烧嘴, 由助燃风机提供燃烧时所需的空气, 燃烧嘴位于滚筒下 部, 避免燃烧嘴喷出的火焰直接与滚筒接触。燃烧嘴按照温度曲线共设 10〜16支, 在 加热室两侧壁上交叉布置, 通过调节各个燃烧嘴的供气量控制加热室内各段的温度, 保证活性半焦过滤吸附料制备工艺要求的温度、 升温时间和恒温时间。 A sealing device is installed at a portion of the drum that is in contact with the heating chamber, and the sealing device is of a labyrinth or a steam type. Each side of the drum is provided with a small roller of 1 meter length, and the inner wall of the drum is provided with a spoon-shaped turning plate. The material of the material is the same as that of the drum. The inner wall of the drum is in direct contact with the material, and the upper and lower materials are alternately heated and heated uniformly. The hot gas generated in the drying and retorting stage of the material is collected by the gas collecting device at the front end of the drum and sent to the low-pressure gas burner for combustion. Object After the activation section is discharged, the cooling section is taken in, and it is naturally cooled until it is discharged. The roller has one supporting roller ring from the front and rear ends, and the outer wall of the roller is inlaid with the transmission gear ring, which is driven by the reducer and the variable frequency motor. The drum design speed is 0.5~1.5r/min, and the frequency conversion stepless speed regulation. The drum is mounted at an angle of 2°. In the middle of the unit is a heating chamber, which externally heats the outer wall of the drum. A burner is mounted on both side walls of the heating chamber, and the combustion blower provides air required for combustion. The burner is located at the lower portion of the drum to prevent the flame from being blown directly into contact with the drum. The burners are set up according to the temperature curve by 10~16, which are arranged on the two side walls of the heating chamber. The temperature of each section of the heating chamber is controlled by adjusting the air supply volume of each burner to ensure the preparation process of the active semi-coke filter adsorbent. Temperature, warming time and constant temperature time.
加热室壁内衬为轻质高铝砖和高铝纤维混合结构,加热室顶部为高铝聚轻砖平吊 顶, 维修滚筒时拆卸方便, 加热室侧墙与机组外壳之间为轻质保温材料, 蓄散热量少, 升温快。 机组外壳为型钢、 钢板结构。  The lining of the heating chamber wall is a combination of lightweight high-aluminum brick and high-aluminum fiber. The top of the heating chamber is a high-alumina poly-light brick flat ceiling. It is easy to disassemble when the drum is repaired. The lightweight insulation material between the heating chamber side wall and the unit casing is , the amount of heat dissipation is small, and the temperature rises quickly. The unit casing is made of steel and steel.
活性半焦过滤吸附料加工设备加热室内的烟气由机组顶部安装的排烟口排出,排 烟口与余热水套、 引风机连接, 引风机采用变频调速, 余热水套用于回收烟气中的热 量、 降低烟气温度、 加热蒸汽锅炉补水。  The flue gas in the heating chamber of the active semi-coke filter adsorption processing equipment is discharged from the exhaust port installed at the top of the unit, the exhaust port is connected with the residual hot water jacket and the induced draft fan, the induced draft fan adopts frequency conversion speed regulation, and the residual hot water jacket is used for recycling smoke. Heat in the gas, lower the temperature of the flue gas, and heat the steam boiler to replenish water.
加热室壁两侧上安装多个测温装置, 检测每个温度段的温度, 在机组头、 尾安装 有测温装置, 检测进料温度和出料温度, 机组设 1台控制柜, 控制柜内安装 20个数显 表,变频电机变频器和引风机变频器和螺旋给料机变频器以及电源开关及低压电器等。  A plurality of temperature measuring devices are installed on both sides of the heating chamber wall to detect the temperature of each temperature section, and a temperature measuring device is installed at the head and the tail of the unit to detect the feeding temperature and the discharging temperature. The unit is provided with a control cabinet and a control cabinet. Install 20 digital display meters, frequency conversion motor inverter and induced draft fan inverter and screw feeder inverter, power switch and low voltage electrical appliances.
滚筒内的物料在加工过程中产生的热煤气等混合气体由滚筒前端集气装置收集, 并经除尘装置处理后由煤气排送机, 将热煤气送至机组低压煤气燃烧嘴燃烧。 集气装 置与滚筒之间设有密封装置, 密封装置可以采用迷宫式、 蒸汽式。  The mixed gas such as hot gas generated during the processing of the material in the drum is collected by the gas collecting device at the front end of the drum, and is processed by the dust removing device, and then sent to the low-pressure gas burner of the unit for combustion. A sealing device is arranged between the gas collecting device and the drum, and the sealing device can be a labyrinth or a steam type.
活性半焦过滤吸附料加工设备运行所需的燃料采用厌氧反应装置 6运行时产生的 沼气 12和活性半焦过滤吸附料加工设备运行过程中产生的混合气体。  The fuel required for the operation of the active semi-coke filter sorbent processing equipment uses the biogas produced during the operation of the anaerobic reactor 6 and the mixed gas produced during the operation of the activated semi-coke filter sorbent processing equipment.
活性半焦过滤吸附料加工设备滚筒的前端安装有螺旋给料机、 加料仓, 螺旋给料 机加料速度通过变频控制器调整。 滚筒的后端安装有出料装置, 滚筒的端面设有观察 孔及蒸汽通入管。 出料装置与滚筒之间设有密封装置, 密封装置可以采用迷宫式、 蒸 汽式。 实施例 1  The front end of the drum of the active semi-coke filter adsorption processing equipment is equipped with a screw feeder and a feeding bin, and the feeding speed of the screw feeder is adjusted by the frequency conversion controller. A discharge device is installed at the rear end of the drum, and an observation hole and a steam inlet pipe are provided at the end surface of the drum. A sealing device is arranged between the discharging device and the drum, and the sealing device can be a labyrinth or a steaming type. Example 1
采用本发明处理造纸企业化学制浆废水。  The invention utilizes the invention to treat chemical pulping wastewater of papermaking enterprises.
废水 1进入沉淀池 2, 废水 1在沉淀池中的停留时间为 2-3小时, 经过沉淀处理 后的水流至调节池 3; 在调节池 3中, 投加 NaOH或 HC1, 调整合适的反应 pH值和投 加 N、 P营养盐。 在此, 废水中复杂的不溶于水的基质被微生物所分泌的胞外酶转化 为较小的、 可溶于水的基质, 即水解反应。 调节池 3中的水再用水泵 4送至厌氧反应 装置 5。 在厌氧反应装置 5 中的产酸菌、 甲烷菌的作用下, 废水中的绝大部分可生物 降解的物质被氧化合成了沼气 10。 The wastewater 1 enters the sedimentation tank 2, and the residence time of the wastewater 1 in the sedimentation tank is 2-3 hours, and the water after the precipitation treatment flows to the adjustment tank 3; in the adjustment tank 3, NaOH or HC1 is added to adjust the appropriate reaction pH. Value and investment Add N, P nutrient salts. Here, the complex water-insoluble matrix in the wastewater is converted by the extracellular enzyme secreted by the microorganism into a smaller, water-soluble matrix, ie a hydrolysis reaction. The water in the conditioning tank 3 is sent to the anaerobic reactor 5 by the water pump 4. Under the action of acid-producing bacteria and methanogens in the anaerobic reaction device 5, most of the biodegradable substances in the wastewater are oxidized to synthesize the biogas 10.
本实施例运行参数:  The operating parameters of this embodiment:
1 ) 每天处理造纸废水 5,000吨。 进入沉淀池 2的废水 lCOD 6,000mg/l;  1) Process papermaking wastewater of 5,000 tons per day. Wastewater entering sedimentation tank 2 lCOD 6,000mg/l;
2)废水经过厌氧反应装置 5预处理后流入集水池 6,水中的 COD 1500mg/l,COD 去除率达 75%以上;  2) The wastewater is treated by the anaerobic reactor 5 and then flows into the collecting tank. 6. The COD in the water is 1500mg/l, and the COD removal rate is over 75%.
3 ) 集水池 6中的水经过活性焦处理装置 8深处理后流入清水池 9, 水中 COD含 量 70mg/l、 浊度 5Ftu、 色度 5倍, 达到环保排放标准和造纸用水的标准;  3) The water in the catchment tank 6 is treated by the active coke treatment device 8 and then flows into the clear water pool. 9. The COD content in the water is 70mg/l, the turbidity is 5Ftu, and the chromaticity is 5 times, which meets the environmental emission standards and the standard of papermaking water;
4) 活性焦处理装置 8每天卸出 16吨饱和活性焦 12, 将上述饱和活性焦 12输送 到活性焦再生装置 13进行再生,活性焦再生装置 13每再生 1吨饱和活性焦 12需热量 185.5万 kcal, 每天再生 16吨饱和活性焦 12所需总热量为: Q-185.5万 kcal/吨 xl6吨 =2,968万 kcal;  4) The active coke processing device 8 discharges 16 tons of saturated activated coke 12 per day, and delivers the above-mentioned saturated active coke 12 to the active coke regeneration device 13 for regeneration. The activated coke regeneration device 13 requires 1.85 million calories per 1 ton of saturated active coke 12 Kcal, the total heat required to regenerate 16 tons of saturated activated coke 12 per day is: Q-185.5 kcal/ton xl6 tons = 29.68 million kcal;
5 ) 厌氧反应装置 5运行过程中, 每天产生 9,460 Nm3沼气 10, 每 Nm3甲烷沼气 10的发热量为 2,720Kcal/m3, 9,460Nm3沼气 12总热量为 2,545万 kcal。 活性焦再生装 置 13每天运行所需热量的其余部分, 由其运行时滚筒内有机物热解产生的可燃混合气 提供。 5 during operation of the device 5) in the anaerobic reactor to produce biogas per day 9,460 Nm 3 10, heat generation per 10 Nm 3 methane gas was 2,720Kcal / m 3, 12 of the total heat 9,460Nm 3 biogas Wan 2,545 kcal. The remainder of the heat required to operate the activated coke regeneration unit 13 per day is provided by a combustible mixture of pyrolysis of organic matter in the drum during its operation.
虽然本总体发明构思的一些实施例已被显示和说明,本领域普通技术人员将理解, 在不背离本总体发明构思的原则和精神的情况下, 可对这些实施例做出改变, 本发明 的范围以权利要求和它们的等同物限定。  While some embodiments of the present general inventive concept have been shown and described, it will be understood by those of ordinary skill in the art that the present invention may be modified without departing from the principles and spirit of the present general inventive concept. The scope is defined by the claims and their equivalents.

Claims

权 利 要 求 Rights request
1、 一种 COD废水处理方法, 将废水经由厌氧处理后, 再采用活性焦过滤吸附处 理。 1. A method for treating COD wastewater, which is subjected to anaerobic treatment, and then subjected to active coke filtration adsorption treatment.
2、 如权利要求 1所述的方法, 其中, 将厌氧处理废水过程中产生的沼气收集后, 输送到活性焦再生装置作为活性焦再生时所需的能源。  2. The method according to claim 1, wherein the biogas generated in the anaerobic treatment of the wastewater is collected and sent to the active coke regeneration device as an energy source required for active coke regeneration.
PCT/CN2009/000108 2008-01-24 2009-01-23 A method for treating high cod wastewater WO2009094904A1 (en)

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JPS51122945A (en) * 1975-04-18 1976-10-27 Ebara Infilco Co Ltd Process for treating waste water
CN1120026A (en) * 1995-08-04 1996-04-10 陆炎培 Processing of four-time recovery and two-stage treatment of paper pulping waste liquid
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JPS51122945A (en) * 1975-04-18 1976-10-27 Ebara Infilco Co Ltd Process for treating waste water
CN1120026A (en) * 1995-08-04 1996-04-10 陆炎培 Processing of four-time recovery and two-stage treatment of paper pulping waste liquid
JP2003300035A (en) * 2002-04-04 2003-10-21 Livestock Industry's Environmental Improvement Organization Methane fermentation treatment system and denitrification method of its digested liquid
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