CN107973503A - Integral type granule sludge vulcanizes decalcification device and method - Google Patents
Integral type granule sludge vulcanizes decalcification device and method Download PDFInfo
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- 239000010802 sludge Substances 0.000 title claims abstract description 76
- 238000000034 method Methods 0.000 title claims abstract description 9
- 239000008187 granular material Substances 0.000 title description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 110
- 239000007788 liquid Substances 0.000 claims abstract description 89
- 239000002253 acid Substances 0.000 claims abstract description 80
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims abstract description 64
- 229910052717 sulfur Inorganic materials 0.000 claims abstract description 58
- 239000011593 sulfur Substances 0.000 claims abstract description 58
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 42
- 238000004073 vulcanization Methods 0.000 claims abstract description 37
- 238000009826 distribution Methods 0.000 claims abstract description 34
- 238000003860 storage Methods 0.000 claims abstract description 31
- 238000000926 separation method Methods 0.000 claims abstract description 17
- 238000004062 sedimentation Methods 0.000 claims abstract description 13
- 238000005273 aeration Methods 0.000 claims description 12
- 239000002245 particle Substances 0.000 claims description 12
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 claims description 11
- 238000001514 detection method Methods 0.000 claims description 11
- 239000000243 solution Substances 0.000 claims description 11
- 238000005486 sulfidation Methods 0.000 claims description 11
- 238000006243 chemical reaction Methods 0.000 claims description 10
- 239000011259 mixed solution Substances 0.000 claims description 7
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims description 6
- 239000011575 calcium Substances 0.000 claims description 6
- 229910052791 calcium Inorganic materials 0.000 claims description 6
- 238000005554 pickling Methods 0.000 claims description 5
- 238000004140 cleaning Methods 0.000 claims description 3
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 abstract description 8
- 241000894006 Bacteria Species 0.000 abstract description 6
- 238000004519 manufacturing process Methods 0.000 abstract description 6
- 229910000019 calcium carbonate Inorganic materials 0.000 abstract description 4
- 238000004064 recycling Methods 0.000 abstract description 2
- 238000010924 continuous production Methods 0.000 abstract 1
- 238000004090 dissolution Methods 0.000 abstract 1
- 238000005987 sulfurization reaction Methods 0.000 abstract 1
- 239000007789 gas Substances 0.000 description 9
- 238000010992 reflux Methods 0.000 description 6
- 239000002351 wastewater Substances 0.000 description 4
- 230000029087 digestion Effects 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000002308 calcification Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 238000001556 precipitation Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000009280 upflow anaerobic sludge blanket technology Methods 0.000 description 2
- 238000004065 wastewater treatment Methods 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 239000003653 coastal water Substances 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 208000021302 gastroesophageal reflux disease Diseases 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 239000008188 pellet Substances 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 238000012827 research and development Methods 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
Classifications
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/02—Biological treatment
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- Life Sciences & Earth Sciences (AREA)
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- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
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- Organic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Molecular Biology (AREA)
- Biological Treatment Of Waste Water (AREA)
- Treatment Of Sludge (AREA)
Abstract
本发明公开了一种一体式颗粒污泥硫化脱钙装置及方法。装置主体由集泥区、布水区、脱钙区、硫化区和循环区组成。集泥区设集泥室和导泥管;布水区设进水管和布水室;脱钙区设颗粒污泥室和沉淀分离室;硫化区设供气室、硫粒床和环形贮酸室;循环区设酸液循环系统和混合液循环系统。通过硫化区的作用,实现硫酸的持续产生;通过脱钙区的作用,实现碳酸钙的持续溶解;通过循环区的作用,实现硫酸液的循环利用;通过集泥区的作用,实现脱钙后颗粒污泥的输出。本发明将硫化产酸与颗粒污泥脱钙融于一体,装置结构紧凑;以硫化细菌产酸,成本低廉,只需对硫粒床进行曝气,硫化菌即能将单质硫氧化成硫酸;以酸液溶解脱钙,酸量可控,可减轻颗粒污泥损伤。
The invention discloses an integrated granular sludge vulcanization and decalcification device and method. The main body of the device is composed of mud collection area, water distribution area, decalcification area, vulcanization area and circulation area. In the mud collection area, there are mud collection chambers and mud guide pipes; in the water distribution area, there are water inlet pipes and water distribution chambers; in the decalcification area, there are granular sludge chambers and sedimentation separation chambers; in the vulcanization area, there are air supply chambers, sulfur bed and annular acid storage chambers ; The circulation area is equipped with an acid liquid circulation system and a mixed liquid circulation system. Through the function of the vulcanization zone, the continuous production of sulfuric acid is realized; through the function of the decalcification zone, the continuous dissolution of calcium carbonate is realized; through the function of the circulation zone, the recycling of sulfuric acid solution is realized; Output of granular sludge. The invention integrates acid production by sulfuration and decalcification of granular sludge, and the device has a compact structure; the acid is produced by sulfur bacteria, and the cost is low, and the sulfur bacteria can oxidize elemental sulfur into sulfuric acid only by aerating the sulfur bed; The decalcification is dissolved with acid solution, and the amount of acid is controllable, which can reduce the damage of granular sludge.
Description
技术领域technical field
本发明涉及一种颗粒污泥脱钙装置,尤其涉及一种一体式颗粒污泥硫化脱钙装置及方法。The invention relates to a granular sludge decalcification device, in particular to an integrated granular sludge sulfide decalcification device and method.
背景技术Background technique
人类生活和生产活动排放大量有机废水,导致我国湖泊、河流以及近海等水体严重污染。作为一类经济高效的废水处理技术,UASB、EGSB和IC反应器广泛应用于有机废水处理。有机废水,特别是工业有机废水普遍含钙。在厌氧生物处理过程中,有机污染物转化为二氧化碳,与钙结合,产生碳酸钙,分布于颗粒污泥内部和表面,可通过影响传质而影响活性。钙化颗粒污泥积累于反应器内,既降低了装置的有效容积,增大了厌氧消化工程的成本,也限制了厌氧消化技术的应用。Human life and production activities discharge a large amount of organic wastewater, resulting in serious pollution of lakes, rivers and coastal waters in my country. As a class of cost-effective wastewater treatment technologies, UASB, EGSB, and IC reactors are widely used in organic wastewater treatment. Organic wastewater, especially industrial organic wastewater generally contains calcium. During anaerobic biological treatment, organic pollutants are converted into carbon dioxide, combined with calcium to produce calcium carbonate, which is distributed inside and on the surface of granular sludge, which can affect activity by affecting mass transfer. Calcified granular sludge accumulates in the reactor, which not only reduces the effective volume of the device, increases the cost of anaerobic digestion engineering, but also limits the application of anaerobic digestion technology.
厌氧颗粒污泥是厌氧消化微生物的自然聚集体,UASB、EGSB和IC反应器的效能与厌氧颗粒污泥的活性密切相关。防止厌氧颗粒污泥钙化,促使钙化厌氧颗粒污泥脱钙,无疑有利于保持厌氧颗粒污泥的功能,助力高效厌氧反应器的持续运行。迄今为止,工程上应对颗粒污泥污泥钙化的主要手段是对废水进行化学除钙预处理或增大对反应器内钙化颗粒污泥的更换频率,前者需要添加大量药剂,后者需要补充大量高效污泥,成本较高。研发经济有效的颗粒污泥防钙除钙方法,已成为保障厌氧消化技术发展的当务之急。本发明以低廉大宗的硫粒作为物料,通过生物硫化产生硫酸,再以硫酸溶解碳酸钙,产酸量可控,脱钙产物无污染,处理过程低成本,具有很好的推广应用前景。Anaerobic granular sludge is a natural aggregate of anaerobic digesting microorganisms, and the performance of UASB, EGSB, and IC reactors is closely related to the activity of anaerobic granular sludge. Preventing calcification of anaerobic granular sludge and promoting decalcification of calcified anaerobic granular sludge will undoubtedly help maintain the function of anaerobic granular sludge and help the continuous operation of high-efficiency anaerobic reactors. So far, the main means to deal with the calcification of granular sludge in engineering is to carry out chemical decalcification pretreatment of wastewater or increase the replacement frequency of calcified granular sludge in the reactor. The former needs to add a large amount of chemicals, and the latter needs to add a large amount of High-efficiency sludge has a higher cost. Research and development of cost-effective methods for calcium prevention and decalcification of granular sludge has become an urgent task to ensure the development of anaerobic digestion technology. The invention uses cheap and bulky sulfur particles as materials, produces sulfuric acid through biological vulcanization, and then dissolves calcium carbonate with sulfuric acid, so that the amount of acid produced is controllable, the decalcification product is pollution-free, the treatment process is low-cost, and has good prospects for popularization and application.
发明内容Contents of the invention
本发明的目的是克服现有技术的不足,提供一种一体式颗粒污泥硫化脱钙装置。本发明所采用的具体技术方案如下:The purpose of the present invention is to overcome the deficiencies of the prior art and provide an integrated granular sludge sulfidation and decalcification device. The concrete technical scheme that the present invention adopts is as follows:
一体式颗粒污泥硫化脱钙装置,装置主体由下至上依次分为集泥区、布水区、脱钙区和硫化区,循环区独立于装置主体,用于连通布水区和脱钙区以及布水区和硫化区;集泥区通过导泥管从下到上依次连接导泥水泵、止水阀和倒锥形集泥室底部;布水区从下到上设进水管和布水器,进水管上设置有进水水泵;脱钙区侧壁上设置有若干个pH检测口,脱钙区从下到上分为颗粒污泥脱钙反应室和沉淀分离室,沉淀分离室上方设置泥水分离器,泥水分离器上方的装置侧壁上设有带控制阀的出水管;硫化区底部通过多孔滤板与脱钙区分隔,硫化区中部通过筒形外壁包裹形成硫粒床,硫粒床的外壁底部与装置主体内壁之间通过环形的挡水板密封,硫粒床底部设置由输气管和管式微孔曝气头组成的供气装置,硫粒床内设用于支撑硫粒的多孔底板,硫粒床上面设顶空室,顶空室连通用于排出尾气的尾气管;硫粒床外围包裹有环形贮酸室,用于收集从硫粒床中溢流出的硫酸液;循环区设酸液回流管、酸液回流泵、混合液回流管和混合液回流泵,脱钙区上部通过混合液回流管和混合液回流泵回流至布水区,环形贮酸室通过酸液回流管和酸液回流泵通入布水区中。Integrated granular sludge vulcanization and decalcification device, the main body of the device is divided into sludge collection area, water distribution area, decalcification area and vulcanization area from bottom to top. The circulation area is independent of the main body of the device and is used to connect the water distribution area and decalcification area. And the water distribution area and vulcanization area; the mud collection area is connected with the mud guide pump, water stop valve and the bottom of the inverted cone mud collection chamber from bottom to top through the mud guide pipe; the water distribution area is provided with water inlet pipes and water distributors from bottom to top , the inlet pipe is provided with an inlet water pump; several pH detection ports are arranged on the side wall of the decalcification area, and the decalcification area is divided into a granular sludge decalcification reaction chamber and a sedimentation separation chamber from bottom to top, and a settling separation chamber is set above the sedimentation separation chamber Sludge water separator, the side wall of the device above the mud water separator is provided with an outlet pipe with a control valve; the bottom of the vulcanization zone is separated from the decalcification zone by a porous filter plate, and the middle part of the vulcanization zone is wrapped by a cylindrical outer wall to form a sulfur bed. The bottom of the outer wall of the bed and the inner wall of the main body of the device are sealed by an annular water baffle. The bottom of the sulfur bed is equipped with an air supply device consisting of a gas delivery pipe and a tubular microporous aeration head. A porous bottom plate, a headspace chamber is arranged on the sulfur bed, and the headspace room is connected to the tail gas pipe for exhausting the tail gas; the sulfur bed is surrounded by an annular acid storage room, which is used to collect the sulfuric acid liquid overflowing from the sulfur bed; The circulation area is equipped with an acid liquid return pipe, an acid liquid return pump, a mixed liquid return pipe and a mixed liquid return pump. The upper part of the decalcification area is returned to the water distribution area through the mixed liquid return pipe and the mixed liquid return pump. The return pipe and the acid return pump lead into the water distribution area.
该方案还可以进一步采用如下优选方式:This scheme can also further adopt the following preferred mode:
所述的集泥区、布水区、脱钙区与硫化区的体积之比1~1.5:1:8~10:1.5~2。The volume ratio of the mud collection area, water distribution area, decalcification area and vulcanization area is 1-1.5:1:8-10:1.5-2.
所述的环形贮酸室底部与硫粒床多孔底板持平,贮酸室酸液高度控制在硫粒床高度的10%~20%;硫粒床和环形贮酸室的体积之比为1:0.8~1。The bottom of the annular acid storage chamber is on the same level as the porous bottom plate of the sulfur granular bed, and the height of the acid liquid in the acid storage chamber is controlled at 10% to 20% of the height of the sulfur granular bed; the volume ratio between the sulfur granular bed and the annular acid storage chamber is 1: 0.8~1.
所述的脱钙区中颗粒污泥脱钙反应室和沉淀分离室的体积之比为1:0.3~0.4;泥水分离器的挡板与装置主体侧壁的夹角为30°~40°;沉淀分离室内出水管与脱钙区顶部的垂直距离为5~10cm;脱钙区沿高度方向等距设三个pH检测口,底端的pH检测口与进水管的垂直距离为15~20cm。The volume ratio between the granular sludge decalcification reaction chamber and the sedimentation separation chamber in the decalcification zone is 1:0.3-0.4; the included angle between the baffle plate of the mud-water separator and the side wall of the main body of the device is 30°-40°; The vertical distance between the outlet pipe in the precipitation separation chamber and the top of the decalcification area is 5-10cm; the decalcification area is equipped with three pH detection ports equidistant along the height direction, and the vertical distance between the pH detection port at the bottom and the water inlet pipe is 15-20 cm.
所述的酸液回流管的进液端与硫化区底部的垂直距离为5~10cm;混合液回流管的进液端与脱钙区顶部的垂直距离为10~15cm。The vertical distance between the liquid inlet end of the acid liquid return pipe and the bottom of the vulcanization zone is 5-10 cm; the vertical distance between the liquid inlet end of the mixed liquid return pipe and the top of the decalcification area is 10-15 cm.
整个颗粒污泥硫化脱钙装置的高径比为5~7:1,集泥区、布水区和硫化区的高径比为0.5~1:1,脱钙区的高径比为3~4:1。The height-to-diameter ratio of the whole granular sludge sulfidation and decalcification device is 5-7:1, the height-to-diameter ratio of the sludge collection area, water distribution area and vulcanization area is 0.5-1:1, and the height-to-diameter ratio of the decalcification area is 3-7:1. 4:1.
所述的倒锥形集泥室底角为50°~70°;进水管与该室顶部的垂直距离为5~10cm;酸液回流管和混合液回流管的出液端与进水管的垂直距离为5~10cm。The bottom angle of the inverted conical mud collecting chamber is 50°~70°; the vertical distance between the water inlet pipe and the top of the chamber is 5~10cm; The distance is 5-10cm.
所述的硫粒床中可充填有单质硫颗粒,脱钙区中可充填有颗粒污泥。The sulfur particle bed may be filled with elemental sulfur particles, and the decalcification zone may be filled with granular sludge.
所述的硫粒床外壁顶部设有溢流堰。An overflow weir is provided on the top of the outer wall of the sulfur bed.
一种利用上述装置的颗粒污泥硫化脱钙方法,其步骤如下:A method for sulfidation and decalcification of granular sludge utilizing the above device, the steps are as follows:
打开止水阀,利用导泥水泵将钙化颗粒污泥通过导泥管打入反应器脱钙区中,关闭止水阀;进水水泵设定一流量值进水,当装置内液面持续上升至脱钙区顶部时,调整进水流量值使得液面缓缓上升通过多孔滤板进入硫化区;输气管开始曝气并通过管式微孔曝气头进入硫粒床内,硫粒床内开始产酸,硫酸液通过溢流堰流入环形贮酸室内并不断积累,当贮酸室液面达到控制液面高度上限时,停止曝气,并关闭进水水泵;打开混合液回流泵和酸液回流泵,待贮酸室内液面达到控制液面高度下限时,关闭酸液回流泵;保持混合液回流使得硫酸液可以多次利用,脱钙区进行持续酸洗脱钙,多次循环清洗之后,关闭混合液回流泵,打开进水水泵和出水管控制阀,将酸洗后的混合液排出,除钙后的颗粒污泥通过导泥管排出并继续下一轮循环。Open the water stop valve, use the mud guide pump to drive the calcified granular sludge into the decalcification area of the reactor through the mud guide pipe, close the water stop valve; set a flow value for the water inlet pump, and when the liquid level in the device continues to rise When it reaches the top of the decalcification zone, adjust the inflow flow rate so that the liquid level rises slowly through the porous filter plate and enters the vulcanization zone; the gas pipeline starts to aerate and enters the sulfur bed through the tubular microporous aeration head, and the sulfur bed Acid production starts, and sulfuric acid liquid flows into the annular acid storage chamber through the overflow weir and accumulates continuously. When the liquid level of the acid storage chamber reaches the upper limit of the controlled liquid level, stop aeration and turn off the water inlet pump; turn on the mixed liquid return pump and acid Liquid reflux pump, when the liquid level in the acid storage chamber reaches the lower limit of the controlled liquid level, turn off the acid reflux pump; keep the mixed liquid reflux so that the sulfuric acid solution can be used multiple times, and the decalcification area is continuously acid-washed and decalcified, and repeated cycle cleaning After that, turn off the mixed liquid return pump, open the water inlet pump and the outlet pipe control valve, discharge the mixed liquid after pickling, and discharge the granular sludge after decalcification through the mud guide pipe to continue the next cycle.
本发明与现有技术相比具有的有益效果:1、将硫化产酸与颗粒污泥脱钙融于一体,装置结构紧凑,脱钙操作方便,便于推广使用;2、以硫化细菌产酸,成本低廉,只需对硫粒床进行曝气,硫化菌即能将单质硫氧化成硫酸;3、以酸液溶解脱钙,酸量可控,可减轻对颗粒污泥的损伤。Compared with the prior art, the present invention has beneficial effects: 1. The acid production by sulfidation and the decalcification of granular sludge are integrated, the device has a compact structure, the decalcification operation is convenient, and it is easy to popularize and use; 2. The acid is produced by sulfide bacteria, The cost is low, and the sulfide bacteria can oxidize elemental sulfur into sulfuric acid only by aerating the sulfur granular bed; 3. Dissolving decalcification with acid solution, the acid amount is controllable, which can reduce the damage to granular sludge.
附图说明Description of drawings
图1是一体式颗粒污泥硫化脱钙装置结构图;Figure 1 is a structural diagram of an integrated granular sludge sulfidation and decalcification device;
图2是布水区俯视图。Figure 2 is a top view of the water distribution area.
图中:集泥区Ⅰ、布水区Ⅱ、脱钙区Ⅲ、硫化区Ⅳ、循环区Ⅴ、导泥水泵1、导泥管2、止水阀3、倒锥形集泥室4、pH检测口5、布水器6、颗粒污泥脱钙反应室7、沉淀分离室8、泥水分离器9、挡水板10、输气管11、管式微孔曝气头12、多孔底板13、硫粒床14、溢流堰15、顶空室16、尾气管17、贮酸室液面控制高度线18、环形贮酸室19、多孔滤板20、控制阀21、出水管22、混合液回流管23、酸液回流管24、酸液回流泵25、混合液回流泵26、进水管27、进水水泵28。In the figure: mud collection area Ⅰ, water distribution area Ⅱ, decalcification area Ⅲ, vulcanization area Ⅳ, circulation area Ⅴ, mud guide pump 1, mud guide pipe 2, water stop valve 3, inverted cone mud collection chamber 4, pH Detection port 5, water distributor 6, granular sludge decalcification reaction chamber 7, sedimentation separation chamber 8, mud-water separator 9, water retaining plate 10, air pipe 11, tubular microporous aeration head 12, porous bottom plate 13, Sulfur bed 14, overflow weir 15, headspace chamber 16, tail gas pipe 17, liquid level control height line of acid storage chamber 18, annular acid storage chamber 19, porous filter plate 20, control valve 21, outlet pipe 22, mixed liquid Return pipe 23, acid liquid return pipe 24, acid liquid return pump 25, mixed liquid return pump 26, water inlet pipe 27, water inlet water pump 28.
具体实施方式Detailed ways
下面结合附图和具体实施例对本发明做进一步阐述和说明。The present invention will be further elaborated and illustrated below in conjunction with the accompanying drawings and specific embodiments.
如图1和2所示,一体式颗粒污泥硫化脱钙装置中,装置主体由下至上依次分为集泥区Ⅰ、布水区Ⅱ、脱钙区Ⅲ和硫化区Ⅳ,循环区Ⅴ独立于装置主体,用于连通布水区Ⅱ和脱钙区Ⅲ以及布水区Ⅱ和硫化区Ⅳ。各部分的具体结构如下:集泥区Ⅰ通过导泥管2从下到上依次连接导泥水泵1、止水阀3和倒锥形集泥室4底部。布水区Ⅱ从下到上设进水管27和布水器6,进水管27上设置有进水水泵28。脱钙区Ⅲ侧壁上等距设置有三个pH检测口5,脱钙区Ⅲ从下到上分为颗粒污泥脱钙反应室7和沉淀分离室8,沉淀分离室8上方设置泥水分离器9,泥水分离器9上方的硫化脱钙装置侧壁上设有带控制阀21的出水管22。硫化区Ⅳ底部通过多孔滤板20与脱钙区Ⅲ分隔,硫化区Ⅳ中部通过无底无盖的筒形外壁包裹形成硫粒床14。硫粒床14中充填有单质硫颗粒,脱钙区Ⅲ中充填有颗粒污泥。硫粒床14的外壁底部与装置主体内壁之间通过环形的挡水板10密封,使挡水板10下方的水在挡水板10的引导下进入硫粒床14;硫粒床14底部设置由输气管11和管式微孔曝气头12组成的供气装置,硫粒床14内设用于支撑硫粒的多孔底板13,硫粒床14上面设顶空室16,顶空室16连通用于排出尾气的尾气管17;硫粒床14外壁顶部设有溢流堰15,硫粒床14外围包裹有环形贮酸室19,用于收集从硫粒床14中溢流出的硫酸液,环形贮酸室19可由硫粒床14外壁与装置主体内壁夹持而成。循环区Ⅴ设酸液回流管24、酸液回流泵25、混合液回流管23和混合液回流泵26,脱钙区Ⅲ上部通过混合液回流管23和混合液回流泵26回流至布水区Ⅱ,环形贮酸室19通过酸液回流管24和酸液回流泵25接入混合液回流管23中,并通过布水器6分布至脱钙区Ⅲ。As shown in Figures 1 and 2, in the integrated granular sludge sulfidation and decalcification device, the main body of the device is divided into sludge collection area I, water distribution area II, decalcification area III and vulcanization area IV from bottom to top, and circulation area V is independent In the main body of the device, it is used to connect the water distribution area II and the decalcification area III, as well as the water distribution area II and the vulcanization area IV. The specific structure of each part is as follows: the mud collecting area I connects the mud guiding water pump 1, the water stop valve 3 and the bottom of the inverted cone mud collecting chamber 4 sequentially through the mud guiding pipe 2 from bottom to top. The water distribution area II is provided with a water inlet pipe 27 and a water distributor 6 from bottom to top, and a water inlet pump 28 is arranged on the water inlet pipe 27 . Three pH detection ports 5 are equidistantly arranged on the side wall of the decalcification area III, and the decalcification area III is divided into a granular sludge decalcification reaction chamber 7 and a sedimentation separation chamber 8 from bottom to top, and a mud-water separator is arranged above the sedimentation separation chamber 8 9. An outlet pipe 22 with a control valve 21 is provided on the side wall of the sulfide decalcification device above the sludge separator 9 . The bottom of vulcanization zone IV is separated from decalcification zone III by a porous filter plate 20 , and the middle part of vulcanization zone IV is wrapped by a cylindrical outer wall without bottom and cover to form a sulfur bed 14 . The sulfur particle bed 14 is filled with elemental sulfur particles, and the decalcification zone III is filled with granular sludge. The bottom of the outer wall of the sulfur bed 14 and the inner wall of the main body of the device are sealed by an annular water retaining plate 10, so that the water below the water retaining plate 10 enters the sulfur bed 14 under the guidance of the water retaining plate 10; An air supply device consisting of a gas delivery pipe 11 and a tubular microporous aeration head 12. A porous bottom plate 13 for supporting sulfur particles is arranged inside the sulfur particle bed 14. A headspace chamber 16 is arranged on the sulfur particle bed 14, and a headspace chamber 16 It is connected with the tail gas pipe 17 for discharging tail gas; the top of the outer wall of the sulfur bed 14 is provided with an overflow weir 15, and the periphery of the sulfur bed 14 is wrapped with an annular acid storage chamber 19 for collecting the sulfuric acid liquid overflowing from the sulfur bed 14 , The annular acid storage chamber 19 can be formed by clamping the outer wall of the sulfur bed 14 and the inner wall of the main body of the device. Circulation area Ⅴ is equipped with acid liquid return pipe 24, acid liquid return pump 25, mixed liquid return pipe 23 and mixed liquid return pump 26, and the upper part of decalcification area III returns to the water distribution area through the mixed liquid return pipe 23 and the mixed liquid return pump 26 II, the annular acid storage chamber 19 is connected to the mixed liquid return pipe 23 through the acid liquid return pipe 24 and the acid liquid return pump 25, and distributed to the decalcification area III through the water distributor 6.
另外,在上述装置中,各部件的参数可设置如下:集泥区Ⅰ、布水区Ⅱ、脱钙区Ⅲ与硫化区Ⅳ的体积之比1~1.5:1:8~10:1.5~2。环形贮酸室19底部与硫粒床多孔底板13持平,贮酸室酸液高度控制在硫粒床高度的10%~30%,可预先划设一条贮酸室液面控制高度线18,以便于控制。硫粒床14和环形贮酸室19的体积之比为1:0.8~1。脱钙区Ⅲ中颗粒污泥脱钙反应室7和沉淀分离室8的体积之比为1:0.3~0.4;泥水分离器9的挡板与装置主体侧壁的夹角为30°~40°;沉淀分离室8内出水管22与脱钙区Ⅲ顶部的垂直距离为5~10cm;脱钙区Ⅲ最底端的pH检测口5与进水管27的垂直距离为15~20cm。酸液回流管24的进液端与硫化区Ⅳ底部的垂直距离为5~10cm;混合液回流管23的进液端与脱钙区Ⅲ顶部的垂直距离为10~15cm。管式微孔曝气头12与多孔底板13的垂直距离为5~10cm,多孔滤板20与输气管的垂直距离为5~10cm。整个颗粒污泥硫化脱钙装置的高径比为5~7:1,集泥区Ⅰ、布水区Ⅱ和硫化区Ⅳ的高径比为0.5~1:1,脱钙区Ⅲ的高径比为3~4:1。倒锥形集泥室4底角为50°~70°;进水管27与该室顶部的垂直距离为5~10cm;酸液回流管24和混合液回流管23的出液端与进水管27的垂直距离为5~10cm。In addition, in the above-mentioned device, the parameters of each component can be set as follows: the volume ratio of mud collection area I, water distribution area II, decalcification area III and vulcanization area IV is 1~1.5:1:8~10:1.5~2 . The bottom of the annular acid storage chamber 19 is equal to the porous bottom plate 13 of the sulfur granule bed, and the height of the acid liquid in the acid storage chamber is controlled at 10% to 30% of the height of the sulfur granule bed. in control. The volume ratio of the sulfur bed 14 and the annular acid storage chamber 19 is 1:0.8-1. In the decalcification area III, the volume ratio of the granular sludge decalcification reaction chamber 7 and the sedimentation separation chamber 8 is 1:0.3-0.4; the included angle between the baffle plate of the mud-water separator 9 and the side wall of the main body of the device is 30°-40° The vertical distance between the outlet pipe 22 in the precipitation separation chamber 8 and the top of the decalcification area III is 5-10 cm; the vertical distance between the pH detection port 5 at the bottom of the decalcification area III and the water inlet pipe 27 is 15-20 cm. The vertical distance between the liquid inlet end of the acid return pipe 24 and the bottom of vulcanization zone IV is 5-10 cm; the vertical distance between the liquid inlet end of the mixed liquid return pipe 23 and the top of the decalcification zone III is 10-15 cm. The vertical distance between the tubular microporous aeration head 12 and the porous bottom plate 13 is 5-10 cm, and the vertical distance between the porous filter plate 20 and the gas delivery pipe is 5-10 cm. The height-to-diameter ratio of the entire granular sludge sulfidation and decalcification device is 5-7:1, the height-to-diameter ratio of the sludge collection area I, water distribution area II and vulcanization area IV is 0.5-1:1, and the height-to-diameter ratio of the decalcification area III The ratio is 3-4:1. The bottom angle of the inverted cone mud collecting chamber 4 is 50°~70°; the vertical distance between the water inlet pipe 27 and the top of the chamber is 5~10cm; The vertical distance is 5-10cm.
本发明中硫化区Ⅳ曝气供氧,利用硫化细菌将硫氧化成硫酸,储存于环形贮酸室19中;借助酸液循环系统,将硫酸液泵入布水区Ⅱ,借助混合液循环系统,进行脱钙区Ⅲ的混合液回流,以酸液脱除颗粒污泥内部和表面的碳酸钙,恢复颗粒污泥的传质能力。本发明的主要系统工作如下:In the present invention, the vulcanization zone IV is aerated to supply oxygen, sulfur is oxidized into sulfuric acid by sulfur bacteria, and stored in the annular acid storage chamber 19; the sulfuric acid solution is pumped into the water distribution zone II by means of the acid liquid circulation system, and the sulfuric acid liquid is pumped into the water distribution area II by means of the mixed liquid circulation system , carry out the reflux of the mixed solution in the decalcification zone III, remove the calcium carbonate inside and on the surface of the granular sludge with acid solution, and restore the mass transfer capacity of the granular sludge. The main system work of the present invention is as follows:
硫化区Ⅳ为产酸系统,主要包括多孔滤板20、挡水板10、输气管11、管式微孔曝气头12、多孔底板13、硫粒床14、环形贮酸室19、溢流堰15、顶空室16、尾气管17。脱钙区Ⅲ上升的水流通过多孔滤板20进入硫粒床14,空气通过输气管11和管式微孔曝气头12进入硫粒床14内,在供氧充足的状况下,硫化细菌将硫粒床14内的单质硫转化为硫酸。产生的酸液通过溢流堰15流入环形贮酸室19内,环形贮酸室19底部设有酸液回流管24,酸液回流管24用于连通布水区Ⅱ和硫化区Ⅳ。Vulcanization zone IV is an acid production system, mainly including porous filter plate 20, water retaining plate 10, air pipe 11, tubular microporous aeration head 12, porous bottom plate 13, sulfur bed 14, annular acid storage room 19, overflow Weir 15, headspace chamber 16, exhaust pipe 17. The rising water flow in the decalcification zone III enters the sulfur granular bed 14 through the porous filter plate 20, and the air enters the sulfur granular bed 14 through the air pipe 11 and the tubular microporous aeration head 12. Under the condition of sufficient oxygen supply, the sulfide bacteria will The elemental sulfur in the sulfur pellet bed 14 is converted to sulfuric acid. The generated acid flows into the annular acid storage chamber 19 through the overflow weir 15, and the bottom of the annular acid storage chamber 19 is provided with an acid return pipe 24, which is used to connect the water distribution area II and the vulcanization area IV.
脱钙区Ⅲ为颗粒污泥脱钙系统,主要包括颗粒污泥脱钙反应室7、pH检测口5、沉淀分离室8、泥水分离器9和出水管22。回流的硫酸液和混合液通过布水器6均匀的进入颗粒污泥脱钙反应室7进行脱钙反应,沉淀分离区8进行泥水分离。多次酸洗后的混合液通过出水管22排出,pH检测口5中可以安装pH检测计,用于监测pH反映脱钙系统的工作状态。Decalcification zone III is a granular sludge decalcification system, which mainly includes a granular sludge decalcification reaction chamber 7 , a pH detection port 5 , a sedimentation separation chamber 8 , a mud-water separator 9 and an outlet pipe 22 . The returning sulfuric acid solution and mixed solution uniformly enter the granular sludge decalcification reaction chamber 7 through the water distributor 6 for decalcification reaction, and the sedimentation separation zone 8 performs mud-water separation. The mixed solution after multiple picklings is discharged through the outlet pipe 22, and a pH detector can be installed in the pH detection port 5 to monitor the pH to reflect the working status of the decalcification system.
布水区Ⅱ为液体均匀混合系统,主要包括进水管27和布水器6。回流的硫酸液以及混合液与布水器6连接,并通过布水器6进入脱钙区Ⅲ,通过回流泵的流量调节保证进入脱钙区的酸液pH控制在既能够除钙又不会对颗粒污泥造成损伤的范围内。Water distribution area II is a uniform liquid mixing system, mainly including water inlet pipe 27 and water distributor 6 . The returning sulfuric acid solution and the mixed solution are connected to the water distributor 6, and enter the decalcification area III through the water distributor 6, and the flow adjustment of the reflux pump ensures that the pH of the acid solution entering the decalcification area is controlled to be able to decalcify without decalcification. Within the scope of causing damage to granular sludge.
集泥区Ⅰ为颗粒污泥的输入与输出系统。主要包括导泥水泵1、止水阀3、导泥管2和倒锥形集泥室4。通过导泥管2将钙化颗粒污泥打入反应器内,关闭止水阀3;颗粒污泥脱钙处理过后,打开止水阀3,利用导泥水泵1将颗粒污泥通过导泥管2排出。Sludge collection area I is the input and output system of granular sludge. It mainly includes a mud guide pump 1, a water stop valve 3, a mud guide pipe 2 and an inverted cone mud collection chamber 4. Put the calcified granular sludge into the reactor through the mud guide pipe 2, and close the water stop valve 3; after the granular sludge decalcification treatment, open the water stop valve 3, and use the mud guide water pump 1 to pass the granular sludge through the mud guide pipe 2 discharge.
循环区Ⅴ为酸液循环利用系统,主要包括酸液回流管24、酸液回流泵25、混合液回流管23和混合液回流泵26。酸液回流管24用于连通布水区Ⅱ和硫化区Ⅳ,混合液回流管22用于连通布水区Ⅱ和脱钙区Ⅲ。Circulation area V is an acid liquid recycling system, which mainly includes an acid liquid return pipe 24 , an acid liquid return pump 25 , a mixed liquid return pipe 23 and a mixed liquid return pump 26 . The acid liquid return pipe 24 is used to connect the water distribution area II and the vulcanization area IV, and the mixed liquid return pipe 22 is used to connect the water distribution area II and the decalcification area III.
基于上述装置,本发明还提供一种一体式颗粒污泥硫化脱钙方法,步骤如下:Based on the above-mentioned device, the present invention also provides an integrated granular sludge sulfide decalcification method, the steps are as follows:
打开止水阀3,利用导泥水泵1将钙化颗粒污泥通过导泥管2打入反应器脱钙区Ⅲ中,关闭止水阀3;进水水泵28设定一流量值进水,当装置内液面持续上升至脱钙区Ⅲ顶部时,调整进水流量值使得液面缓缓上升通过多孔滤板20进入硫化区Ⅳ;输气管11开始曝气并通过管式微孔曝气头12进入硫粒床14内,硫粒床14内开始产酸,硫酸液通过溢流堰15流入环形贮酸室19内并不断积累,当贮酸室液面达到控制液面高度上限(约为硫粒床高度的20%~30%)时,停止曝气,并关闭进水水泵28;打开混合液回流泵26和酸液回流泵25,待贮酸室19内液面达到控制液面高度下限(约为硫粒床高度的10%~15%)时,关闭酸液回流泵25;保持混合液回流使得硫酸液可以多次利用,脱钙区Ⅲ进行持续酸洗脱钙,多次循环清洗之后,关闭混合液回流泵26,打开进水水泵28和出水管控制阀21,将酸洗后的混合液排出,除钙后的颗粒污泥通过导泥管2排出并继续下一轮循环。Open the water stop valve 3, use the mud guide pump 1 to drive the calcified granular sludge into the decalcification zone III of the reactor through the mud guide pipe 2, and close the water stop valve 3; the water inlet pump 28 sets a flow value to enter water, when When the liquid level in the device continues to rise to the top of the decalcification zone III, adjust the influent flow rate so that the liquid level rises slowly through the porous filter plate 20 and enters the vulcanization zone IV; 12 into the sulfur grain bed 14, acid production begins in the sulfur grain bed 14, and the sulfuric acid solution flows into the annular acid storage chamber 19 through the overflow weir 15 and accumulates continuously. When the liquid level of the acid storage chamber reaches the upper limit of the control liquid level (about 20%~30% of the sulfur bed height), stop the aeration, and close the inlet water pump 28; open the mixed liquid return pump 26 and the acid liquid return pump 25, until the liquid level in the acid storage chamber 19 reaches the control liquid level When the lower limit (about 10% to 15% of the height of the sulfur bed), close the acid liquid reflux pump 25; keep the mixed liquid reflux so that the sulfuric acid liquid can be used repeatedly, and the decalcification zone III carries out continuous acid elution and decalcification, repeated cycles After cleaning, close the mixed liquid return pump 26, open the water inlet pump 28 and the outlet pipe control valve 21, discharge the mixed liquid after pickling, and discharge the granular sludge after decalcification through the mud guide pipe 2 and continue the next cycle .
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CN116200261A (en) * | 2023-03-10 | 2023-06-02 | 广东能源集团科学技术研究院有限公司 | Aeration pipe and aerator |
CN116200261B (en) * | 2023-03-10 | 2024-03-29 | 广东能源集团科学技术研究院有限公司 | Aeration pipe and aerator |
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