CN116177798A - Natural running water ozone ultrafiltration membrane water purification treatment method - Google Patents
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 91
- 239000012528 membrane Substances 0.000 title claims abstract description 49
- 238000000108 ultra-filtration Methods 0.000 title claims abstract description 42
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 title claims abstract description 19
- 238000000746 purification Methods 0.000 title claims abstract description 17
- 238000000034 method Methods 0.000 title claims abstract description 14
- 239000007788 liquid Substances 0.000 claims abstract description 40
- 239000002893 slag Substances 0.000 claims abstract description 34
- 241000195493 Cryptophyta Species 0.000 claims abstract description 20
- 238000005345 coagulation Methods 0.000 claims abstract description 20
- 230000015271 coagulation Effects 0.000 claims abstract description 20
- 239000000203 mixture Substances 0.000 claims abstract description 13
- 238000002156 mixing Methods 0.000 claims abstract description 9
- 238000005192 partition Methods 0.000 claims abstract description 9
- 239000008213 purified water Substances 0.000 claims abstract description 7
- 238000004140 cleaning Methods 0.000 claims abstract description 6
- 239000013049 sediment Substances 0.000 claims abstract description 3
- 230000001112 coagulating effect Effects 0.000 claims abstract 4
- 238000001914 filtration Methods 0.000 claims abstract 2
- 239000008394 flocculating agent Substances 0.000 claims abstract 2
- 239000000919 ceramic Substances 0.000 claims description 4
- 238000007667 floating Methods 0.000 claims description 4
- 239000002033 PVDF binder Substances 0.000 claims description 2
- 239000004810 polytetrafluoroethylene Substances 0.000 claims description 2
- 229920001343 polytetrafluoroethylene Polymers 0.000 claims description 2
- 229920002981 polyvinylidene fluoride Polymers 0.000 claims description 2
- HBMJWWWQQXIZIP-UHFFFAOYSA-N silicon carbide Chemical compound [Si+]#[C-] HBMJWWWQQXIZIP-UHFFFAOYSA-N 0.000 claims description 2
- 229910010271 silicon carbide Inorganic materials 0.000 claims description 2
- 238000007599 discharging Methods 0.000 claims 1
- 230000003373 anti-fouling effect Effects 0.000 abstract description 4
- 230000000903 blocking effect Effects 0.000 abstract description 2
- 230000000694 effects Effects 0.000 description 6
- 239000002245 particle Substances 0.000 description 6
- 238000005189 flocculation Methods 0.000 description 5
- 230000016615 flocculation Effects 0.000 description 5
- 238000010586 diagram Methods 0.000 description 3
- 239000003651 drinking water Substances 0.000 description 3
- 235000020188 drinking water Nutrition 0.000 description 3
- 229940037003 alum Drugs 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 239000011148 porous material Substances 0.000 description 2
- 230000001932 seasonal effect Effects 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 238000013019 agitation Methods 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000000701 coagulant Substances 0.000 description 1
- 238000009295 crossflow filtration Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- -1 floating objects Substances 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 238000005065 mining Methods 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 238000009287 sand filtration Methods 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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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
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/24—Treatment of water, waste water, or sewage by flotation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/444—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/50—Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5281—Installations for water purification using chemical agents
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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
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/78—Treatment of water, waste water, or sewage by oxidation with ozone
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/007—Contaminated open waterways, rivers, lakes or ponds
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Abstract
Description
技术领域technical field
本发明涉及净水处理技术领域,特别涉及一种自然流水臭氧超滤膜净水处理方法。The invention relates to the technical field of water purification treatment, in particular to a natural flowing water ozone ultrafiltration membrane water purification treatment method.
背景技术Background technique
《生活饮用水卫生标准(GB5749-2022)》于2022年3月发布,2023年4月1日执行。该标准删除了小型集中式和分散式供水部分水质指标及限值的暂行规定,意味着城乡供水水质要求同质化。对小型集中式和分散式供水水质提出了更高的要求。小型集中式和分散式供水主要分布于农村、牧区、矿区以及远离城镇市政管网配套的工厂,往往自然条件上具有水源水质差、易爆发藻类、季节性变化大的特点,管理上又缺乏专业管理人员。使得传统的混凝、沉淀、砂滤工艺难以稳定达标。超滤膜处理净水处理方法具有净水出水浊度低,水质较好的优点从而引起重视。但常规的全流量超滤膜净水工艺对原水的预处理要求较高,否则膜孔易堵塞影响正常使用。错流过滤能解决膜孔堵塞问题,但能耗高,运行费用大也使得其难以推广使用。急需一种除藻效率高、抗污堵能力强、预处理运行简单的净水处理工艺。自清洗过滤器是一种利用滤网直接拦截液体中的杂质,漂浮物,颗粒物等,同时降低水的浊度,减少污垢,同时保障后面设备正常工作及使用寿命的精密设备,它具有可自动排污的特点。The Hygienic Standard for Drinking Water (GB5749-2022) was released in March 2022 and will be implemented on April 1, 2023. The standard deletes the provisional provisions on water quality indicators and limit values for small-scale centralized and decentralized water supply, which means that the water quality requirements for urban and rural water supply are homogeneous. Higher requirements are put forward for the water quality of small centralized and decentralized water supply. Small-scale centralized and decentralized water supply is mainly distributed in rural areas, pastoral areas, mining areas, and factories far away from urban municipal pipe networks. Natural conditions often have the characteristics of poor water quality, prone to algae outbreaks, and large seasonal changes, and lack professionalism in management. manager. It makes it difficult for the traditional coagulation, sedimentation, and sand filtration processes to meet the standards stably. The water purification treatment method of ultrafiltration membrane treatment has the advantages of low turbidity of purified water effluent and good water quality, which has attracted attention. However, the conventional full-flow ultrafiltration membrane water purification process requires high pretreatment of raw water, otherwise the membrane pores are easily blocked and affect normal use. Cross-flow filtration can solve the problem of membrane pore clogging, but its high energy consumption and high operating costs also make it difficult to promote its use. There is an urgent need for a water purification process with high algae removal efficiency, strong anti-fouling ability, and simple pretreatment operation. The self-cleaning filter is a precision device that uses the filter to directly intercept impurities, floating objects, particles, etc. in the liquid, while reducing the turbidity of the water, reducing dirt, and at the same time ensuring the normal operation and service life of the subsequent equipment. It has automatic The characteristics of sewage.
发明内容Contents of the invention
本发明要解决的技术问题是,提供一种除藻效率高、抗污堵能力强、预处理运行简单的超滤膜净水工艺。The technical problem to be solved by the present invention is to provide an ultrafiltration membrane water purification process with high algae removal efficiency, strong anti-fouling ability and simple pretreatment operation.
为解决上述技术问题,本发明采用以下技术方案,一种自然流水臭氧超滤膜净水处理方法,其特征在于采用以下步骤:In order to solve the problems of the technologies described above, the present invention adopts the following technical solutions, a natural flowing water ozone ultrafiltration membrane water purification treatment method, which is characterized in that the following steps are adopted:
S1、将含藻的自流水注入混凝箱,向混凝箱中加入絮凝剂,反应一定时间后得混凝液;S1. Inject algae-containing artesian water into the coagulation tank, add flocculant into the coagulation tank, and react for a certain period of time to obtain a coagulation solution;
S2、将所述混凝液进入循环除渣箱,所述循环除渣箱内设有隔板,所述循环除渣箱上部设有排渣管,底部设有排泥管,所述混凝液在循环除渣箱内形成竖向循环流,藻类漂浮物由排渣管排出,沉淀物从底部排泥管排出;除渣后所得清夜从循环除渣箱中部的出水管排出,所述清夜经气液混合泵与臭氧进行混合形成气水混合物;S2. Put the coagulation liquid into the circulating slag removal box, the inside of the circulating slagging removal box is provided with a partition, the upper part of the circulating slagging removal box is provided with a slag discharge pipe, and the bottom is provided with a mud discharge pipe. The liquid forms a vertical circulation flow in the circulating slag removal box, the algae floating matter is discharged from the slagging discharge pipe, and the sediment is discharged from the bottom mud discharge pipe; The gas-liquid mixing pump is mixed with ozone to form a gas-water mixture;
S3、所述气水混合物经自清洗过滤器过滤后进入超滤膜净化器;经超滤膜净化器过滤后的净水从超滤膜净化器上部的净水管流出,超滤膜前形成的溶气液经过回流管回流至循环除渣箱。S3, the gas-water mixture enters the ultrafiltration membrane purifier after being filtered by the self-cleaning filter; the purified water filtered by the ultrafiltration membrane purifier flows out from the water purification pipe on the upper part of the ultrafiltration membrane purifier, and forms in front of the ultrafiltration membrane The dissolved gas liquid is returned to the circulating slag removal box through the return pipe.
进一步,所述循环除渣箱内藻类及浮渣的上浮动力由回流管进入的溶气液释放溶解气体所产生。Furthermore, the upward floating force of algae and scum in the circulating scum removal box is generated by the release of dissolved gas from the gas-dissolving liquid entering the return pipe.
所述自清洗过滤器为常规的标准工业产品。The self-cleaning filter is a conventional standard industrial product.
进一步,所述超滤膜为陶瓷超滤膜或碳化硅超滤膜或PTFE超滤膜或PVDF超滤膜。Further, the ultrafiltration membrane is a ceramic ultrafiltration membrane, a silicon carbide ultrafiltration membrane, a PTFE ultrafiltration membrane, or a PVDF ultrafiltration membrane.
如图1、图2、图3所示,本发明首先将含藻自然流水、絮凝剂经混凝箱混合均匀,形成具有颗粒矾花的混凝液。混凝液进入循环除渣箱2,循环除渣箱的进水管3与出水管4之间设置隔板5阻挡,回流的溶气液通过位于进水管3上方的回流管6进入循环除渣箱2中部,溶气液进入循环除渣箱2后由于压力降低,原来溶解于溶气液中的气体释放形成微小气泡,气泡将溶气液及含藻自然流水中较轻的颗粒物上浮至循环除渣箱2上部,浮渣通过循环除渣箱1顶部的排渣管7排出。同时由于气泡的带动作用,混凝液向上流动翻过隔板后向下流动进入出水管4,由于气泡作用,提升的水量远大于出水量,剩余水量继续向下流动,并从隔板底部空间转入进水管3入口侧,由此循环除渣箱1内形成上下环流有利于絮凝剂的均匀搅拌。由于环流的作用,部分较重的颗粒物被带至循环除渣箱2底部,通过排泥管9排出。As shown in Fig. 1, Fig. 2 and Fig. 3, the present invention first mixes algae-containing natural running water and flocculant evenly through a coagulation tank to form a coagulation liquid with granular alum flowers. The coagulation liquid enters the circulating
除渣后所得清液经气液混合泵10与臭氧均匀混合,在压力情况下部分臭氧溶入絮凝液中,以气泡的形式均匀分布于絮凝液内,分散形成气水混合液。气水混合液先经过自清洗过滤器11进行过滤,然后从超滤膜净化器12底部进入,然后均布上升进入超滤膜净化通道13。过滤后的净水在压力作用下从净水管14流出。被超滤膜截留的浓缩液和气体沿膜表面冲刷,汇聚于回流管6,回流至循环除渣箱2。The clear liquid obtained after slag removal is uniformly mixed with ozone through the gas-
本发明利用臭氧的强氧化能力和气流搅动作用,减缓了超滤膜表面的结垢和污堵问题。The invention utilizes the strong oxidation ability of the ozone and the agitation effect of the air flow to slow down the problems of fouling and fouling on the surface of the ultrafiltration membrane.
本发明利用溶气液中溶解的臭氧,一方面杀死藻类,另一方面利用压力减小气体释放从而浮选出藻类和较轻的浮渣,提升了超滤前的预处理除藻效果。The invention utilizes the dissolved ozone in the gas-dissolved liquid to kill algae on the one hand, and on the other hand utilizes pressure to reduce gas release to float out algae and lighter scum, thereby improving the algae removal effect of pretreatment before ultrafiltration.
本发明通过气液混合泵11将清夜和臭氧泵入超滤膜净化器12,一方面使得臭氧和清夜在管道内混合均匀,另一方面也可以为气水混合液提升加压,解决自然流水不带压力或压力不足的问题。The present invention pumps clear water and ozone into the ultrafiltration membrane purifier 12 through the gas-
本发明利用气液混合泵均匀混合臭氧的同时,也将大的絮凝颗粒打碎为细小颗粒,避免堵塞膜净化器通道。The invention utilizes the gas-liquid mixing pump to evenly mix the ozone, and at the same time breaks the large flocculation particles into fine particles, so as to avoid blocking the channel of the membrane purifier.
综上所述,本发明具有除藻效率高、抗污堵能力强、预处理运行简单等有益效果。To sum up, the present invention has the beneficial effects of high algae removal efficiency, strong anti-fouling ability, simple pretreatment operation and the like.
附图说明Description of drawings
图1为本发明工艺流程示意图。Fig. 1 is a schematic diagram of the process flow of the present invention.
图2为循环除渣箱结构示意图。Figure 2 is a schematic diagram of the structure of the circulating slag removal box.
图3超滤膜净化器结构示意图。Fig. 3 Schematic diagram of the ultrafiltration membrane purifier.
实施方式Implementation
结合附图对本发明一种自然流含藻原水的超滤膜净水处理方法,做进一步说明,下面结合实施例对本发明作进一步详述:In conjunction with accompanying drawing, a kind of ultrafiltration membrane water purification treatment method of natural flow containing algae raw water of the present invention is further described, and the present invention is described in further detail below in conjunction with embodiment:
实施例1:为某平原地区农村供水系统,取水水源河道水,原水浊度15~200NTU,季节性藻类爆发,日供水量100m3/d,处理按5.0m3/hr。供水水质要求达到《生活饮用水卫生标准(GB5749-2022)》标准。如图1、图2、图3所示,净水步骤如下:河道水作为原水(含藻自然流水)以5.0m3/h流量进入混凝箱1,原水与絮凝剂在混凝箱内经过一定时间的反应形成具有颗粒状矾花的混凝液。混凝液进入循环除渣箱2,循环除渣箱的进水管3与出水管4之间设置隔板5阻挡,回流的溶气液(流量:0.50m3/h)通过位于原水进水管3上方的回流管6进入混凝箱1中部,溶气液进入混凝箱1后由于压力降低,原来溶解于溶气液中的气体释放形成微小气泡,气泡将溶气液及原水中较轻的颗粒物上浮至混凝箱表面,浮渣通过池顶排渣管7排出。同时由于气泡的带动作用原水向上流动翻过隔板后向下流动进入出水管4,由于气泡作用提升的水量远大于出水量,剩余水量继续向下流动,并从隔板底部空间转入原水入口侧,由此混凝箱内形成上下环流有利于絮凝剂的均匀搅拌。由于环流的作用部分较重的颗粒物被带至混凝箱底部,通过排泥管9排出。除渣后清液经气液混合泵10与臭氧均匀混合,在压力情况下部分臭氧溶入絮凝液中,部分气泡的形式均匀分布于絮凝液内分散形成气水混合液。气水混合液从净化器12底部进入,气水均布上升进入超滤膜净化通道13。所述超滤膜采用陶瓷膜,净水在压力作用下透过陶瓷膜从净水管14流出,流量为:5.0m3/h。被膜截留的浓缩液(流量:0.50m3/h)和气体沿膜表面冲刷,汇聚于回流管6,回流至前端循环除渣箱2。经过净化后的出水,其浊度为1NTU以下,达到《生活饮用水卫生标准(GB5749-2022)》的要求。Example 1: It is a rural water supply system in a plain area. The source of water intake is river water. The turbidity of raw water is 15-200NTU. Seasonal algal blooms occur. The daily water supply is 100m3/d, and the treatment is 5.0m3/hr. The quality of water supply shall meet the standard of "Drinking Water Hygienic Standard (GB5749-2022)". As shown in Figure 1, Figure 2, and Figure 3, the water purification steps are as follows: river water enters the coagulation tank 1 at a flow rate of 5.0m3/h as raw water (natural flow water containing algae), and the raw water and flocculant pass through the coagulation tank for a certain period of time. The reaction of time forms a coagulant with granular alum flowers. The coagulation liquid enters the circulating
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CN108911274A (en) * | 2018-09-03 | 2018-11-30 | 湖南先瑞环境技术有限公司 | One heavy metal species reactor and the process for treating heavy-metal waste water including the heavy metal reactor |
CN211770680U (en) * | 2019-12-25 | 2020-10-27 | 江苏达格水务有限公司 | Water purification system combining pressure ozone with ultrafiltration and activated carbon filtration |
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2023
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