WO2018112884A1 - 一种用于污水处理设备的除磷载体及方法 - Google Patents
一种用于污水处理设备的除磷载体及方法 Download PDFInfo
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- WO2018112884A1 WO2018112884A1 PCT/CN2016/111712 CN2016111712W WO2018112884A1 WO 2018112884 A1 WO2018112884 A1 WO 2018112884A1 CN 2016111712 W CN2016111712 W CN 2016111712W WO 2018112884 A1 WO2018112884 A1 WO 2018112884A1
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- WO
- WIPO (PCT)
- Prior art keywords
- phosphorus removal
- removal carrier
- agent
- cover
- dephosphorization agent
- Prior art date
Links
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 title claims abstract description 113
- 229910052698 phosphorus Inorganic materials 0.000 title claims abstract description 113
- 239000011574 phosphorus Substances 0.000 title claims abstract description 113
- 239000010865 sewage Substances 0.000 title claims abstract description 41
- 238000000034 method Methods 0.000 title claims abstract description 19
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 75
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 43
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 33
- 229910052742 iron Inorganic materials 0.000 claims description 17
- 239000004744 fabric Substances 0.000 claims description 15
- 230000005484 gravity Effects 0.000 claims description 14
- 229910052751 metal Inorganic materials 0.000 claims description 14
- 239000002184 metal Substances 0.000 claims description 14
- 238000013268 sustained release Methods 0.000 claims description 13
- 239000012730 sustained-release form Substances 0.000 claims description 13
- 239000004746 geotextile Substances 0.000 claims description 3
- 229910001220 stainless steel Inorganic materials 0.000 claims description 3
- 239000010935 stainless steel Substances 0.000 claims description 3
- 238000012423 maintenance Methods 0.000 abstract description 8
- 238000012986 modification Methods 0.000 abstract description 3
- 230000004048 modification Effects 0.000 abstract description 3
- 238000013265 extended release Methods 0.000 abstract 1
- 238000007789 sealing Methods 0.000 abstract 1
- 239000012229 microporous material Substances 0.000 description 8
- 239000005871 repellent Substances 0.000 description 8
- 239000000126 substance Substances 0.000 description 7
- 239000007788 liquid Substances 0.000 description 4
- 239000007787 solid Substances 0.000 description 4
- 239000013589 supplement Substances 0.000 description 4
- 239000003814 drug Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 229910019142 PO4 Inorganic materials 0.000 description 2
- 239000008186 active pharmaceutical agent Substances 0.000 description 2
- 238000005273 aeration Methods 0.000 description 2
- AZDRQVAHHNSJOQ-UHFFFAOYSA-N alumane Chemical class [AlH3] AZDRQVAHHNSJOQ-UHFFFAOYSA-N 0.000 description 2
- 239000002131 composite material Substances 0.000 description 2
- 238000005868 electrolysis reaction Methods 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- 150000002505 iron Chemical class 0.000 description 2
- -1 iron ions Chemical class 0.000 description 2
- RUTXIHLAWFEWGM-UHFFFAOYSA-H iron(3+) sulfate Chemical compound [Fe+3].[Fe+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O RUTXIHLAWFEWGM-UHFFFAOYSA-H 0.000 description 2
- 229910000360 iron(III) sulfate Inorganic materials 0.000 description 2
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 description 2
- 239000010452 phosphate Substances 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 238000010992 reflux Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 1
- 229920000388 Polyphosphate Polymers 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- 239000013043 chemical agent Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 229940079593 drug Drugs 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000016615 flocculation Effects 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 238000006068 polycondensation reaction Methods 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 239000001205 polyphosphate Substances 0.000 description 1
- 235000011176 polyphosphates Nutrition 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 230000001502 supplementing effect Effects 0.000 description 1
- 230000002459 sustained effect Effects 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B65—CONVEYING; PACKING; STORING; HANDLING THIN OR FILAMENTARY MATERIAL
- B65D—CONTAINERS FOR STORAGE OR TRANSPORT OF ARTICLES OR MATERIALS, e.g. BAGS, BARRELS, BOTTLES, BOXES, CANS, CARTONS, CRATES, DRUMS, JARS, TANKS, HOPPERS, FORWARDING CONTAINERS; ACCESSORIES, CLOSURES, OR FITTINGS THEREFOR; PACKAGING ELEMENTS; PACKAGES
- B65D1/00—Rigid or semi-rigid containers having bodies formed in one piece, e.g. by casting metallic material, by moulding plastics, by blowing vitreous material, by throwing ceramic material, by moulding pulped fibrous material or by deep-drawing operations performed on sheet material
- B65D1/02—Bottles or similar containers with necks or like restricted apertures, designed for pouring contents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F5/00—Softening water; Preventing scale; Adding scale preventatives or scale removers to water, e.g. adding sequestering agents
- C02F5/08—Treatment of water with complexing chemicals or other solubilising agents for softening, scale prevention or scale removal, e.g. adding sequestering agents
Definitions
- the invention relates to the technical field of sewage treatment, and in particular to a phosphorus removal carrier and a method for sewage treatment equipment.
- Nitrogen and phosphorus nutrients in water are the main causes of eutrophication of water bodies.
- the phosphorus in the water mainly comes from the sewage discharged into the water body. Therefore, removing phosphorus from sewage is an important way to improve the water environment.
- phosphorus removal methods for domestic sewage mainly include chemical phosphorus removal, electrochemical phosphorus removal and biological phosphorus removal.
- biological phosphorus removal requires the construction of alternating anaerobic and aerobic links, relying on polyphosphate bacteria to excessively take up phosphorus in aerobic conditions, and removing phosphorus from sewage by discharging phosphorus-rich excess sludge. Due to the complicated control of biological phosphorus removal process, it is generally used less in sewage treatment equipment.
- Chemical phosphorus removal refers to the formation of insoluble phosphate precipitates by the addition of chemical agents, which are then removed from the wastewater by solid-liquid separation.
- Conventional chemical dephosphorization requires the provision of medicinal facilities or equipment, including storage devices for pharmaceuticals, dissolution and dosing devices for pharmaceuticals, and some measures such as mixing and flocculation devices, which will undoubtedly greatly increase costs.
- the Chinese patent document with the application number 201410624036.7 provides a phosphorus removal method for a sewage treatment device, which is installed on a return pipe of a sewage treatment device by using a slow release phosphorus removal agent, and does not require a dedicated person to administer the drug. But its shortcoming lies in the implementation process:
- Chemical phosphorus removal generally requires a chemical mixing process.
- the method of installing the slow release phosphorus removal agent on the return pipe of the sewage treatment equipment is only to dissolve the phosphorus removal agent by the slight power of the gas stripping reflux liquid, which is not conducive to the phosphorus removal.
- Complete mixing of the agent with water, the utilization rate of the phosphorus removal agent is low;
- the method of installing the slow release phosphorus removal agent on the return pipe of the sewage treatment equipment limits the storage amount of the slow release phosphorus removal agent, and it is easy to cause frequent addition of the phosphorus removal agent;
- the preferred conditions for chemical phosphorus removal are low SS and low DS environments.
- the way in which the phosphorus removal agent and the reflux liquid are refluxed to the previous process often results in an unsuitable environment for the phosphorus removal agent (high SS and high DS environment). Causes waste of dephosphorization agent.
- Electrochemical phosphorus removal is carried out by electrolysis, which uses electricity to produce iron ions or aluminum ions to form insoluble phosphate precipitates, and then removes phosphorus from the sewage by solid-liquid separation.
- the disadvantage is that the energy consumption of the electrolytic plate and the electrolysis device need to be frequently replaced.
- the above-mentioned existing phosphorus removal method requires installation of an additional phosphorus removal device, is subject to installation space, power consumption, etc., and thus is not suitable for upgrading of existing sewage treatment equipment.
- the invention designs a completely new structure, so that it can be suspended in the sewage during the process of releasing the dephosphorization agent, and the phosphorus removal agent is exhausted and floats up to the water surface, no need to modify the existing sewage treatment equipment, and the use period is long and easy to maintain. .
- a phosphorus removal carrier for sewage treatment equipment comprising:
- the inside of the casing has a storage compartment for containing a phosphorus removal agent, and the storage compartment has a dephosphorization agent;
- One end of the storage compartment is sealed by a cover, and the other end is a sustained release interface for releasing the dephosphorization agent;
- the shell is in a suspended state in the sewage when the dephosphorization agent is not depleted;
- the casing When the dephosphorization agent is exhausted, the casing is in a floating state in the sewage.
- the phosphorus removal carrier can be used as a carrier for microorganisms when used, and chemical phosphorus removal can be achieved when the phosphorus removal agent is dissolved.
- the phosphorus removal agent may be a solid iron salt or an aluminum salt.
- the phosphorus removal agent is a solid polymeric high-polymerized ferric sulfate.
- a side of the casing adjacent to the cover is provided with a floating body.
- the sustained release interface comprises a microplate and a water filter fabric disposed outside the microplate, and the storage compartment is sequentially sealed with the microplate and the water filter fabric;
- the position of the metal iron block is closer to the floating center of the phosphorus removal carrier than the center of gravity of the phosphorus removal carrier;
- the distance of the slow release interface from the center of gravity of the phosphorus removal carrier is smaller than the distance of the slow release interface from the center of the phosphorus removal carrier.
- the microplate is a stainless steel plate with a through hole having a diameter of 0.3-0.8 mm.
- the water filter fabric is a nonwoven geotextile.
- the cover and/or the storage bin are of iron.
- the cover and/or the storage compartment contain a metal iron block.
- the position of the metal iron block is closer to the floating center of the phosphorus removal carrier; that is, the distance of the metal iron block from the center of gravity of the phosphorus removal carrier is smaller than the distance of the slow release interface from the center of the phosphorus removal carrier.
- the housing is provided with a floating body.
- the floating body is located near a side of the casing close to the cover, and the floating body does not coincide with the center of gravity and the floating center of the phosphorus removal carrier.
- the density is 0.94 to 0.97 g/cm 3
- the density is 0.80 to 0.90 g/cm 3 .
- the phosphorus removal carrier can automatically float to the water surface when the dephosphorization agent is depleted by the difference in density, so that the maintenance personnel can identify and supplement it.
- the present invention also provides a method for utilizing the above phosphorus removal carrier, which mainly comprises the following steps:
- the shell is suspended in the sewage, and after the dephosphorization agent is exhausted, the shell floats on the water surface;
- the shell contains the dephosphorization agent, it is in a suspended state.
- the dephosphorization agent When the dephosphorization agent is exhausted, it automatically floats out of the water surface, and it is not necessary to frequently observe the content of the phosphorus removal agent in the casing, which is very convenient.
- Figure 1 is a schematic view of the structure of the present invention
- Figure 2 is a front view of the present invention
- Figure 3 is a plan view of the present invention.
- Figure 4 is a view showing an application state when the phosphorus removal agent is not depleted
- Figure 5 is a schematic view showing the state of the dephosphorization agent when it is exhausted
- Figure 6 is a partial enlarged view of I in Figure 2;
- Figure 7 is a partial enlarged view of II in Figure 2;
- Embodiment A phosphorus removal carrier for a sewage treatment device, the structure of which is shown in Figures 1-3, 6 and 7, and includes:
- a housing 1 for attaching a biofilm a housing 1 for storing a phosphorus removal agent 4 therein;
- the housing 1 should be selected as a ball as much as possible in order to control the center of gravity and the center of buoyancy.
- the two ends of the storage compartment 2 are respectively a cover 3 and a sustained release interface 5;
- the cover 3 can be opened and closed for supplementing the phosphorus removal agent 4;
- the cover 3 is made of metal iron, nickel-plated on the surface, or may contain metal iron blocks inside;
- the phosphorus removal agent 4 is a solid polymer ferric sulfate
- the sustained release interface 5 is the only contact interface between the phosphorus removal agent 4 in the storage bin 2 and the water surrounding the phosphorus removal carrier;
- the sustained release interface 5 is a two-layer composite structure composed of a microporous material 6 and a water-repellent fabric 7;
- the microporous material 6 is in contact with the phosphorus removing agent 4, and is a stainless steel microperforated plate having a thickness of 0.4-0.6 mm and a perforation diameter of 0.3-0.8 mm;
- the water-repellent fabric 7 is in contact with water surrounding the phosphorus-removing carrier, and is a 0.5-1.0 mm thick water-filtered nonwoven geotextile;
- the housing 1 has a floating body 8 on the side close to the cover 3 .
- the outer side of the water-repellent fabric 7 is further provided with a fixing ring 9 for preventing the water-repellent fabric 7 and the microporous material 6 from falling off.
- the floating body 8 is fixed to the casing 1 and has a ring shape.
- the function of the floating body 8 is to make the center of gravity and the floating center of the phosphorus removal carrier do not coincide, so that the cover 3 of the metal-containing iron block (not shown) is biased toward the lighter side of the phosphorus removal carrier (ie, the float is biased).
- the cover 3 of the metal-containing iron block (not shown) is biased toward the lighter side of the phosphorus removal carrier (ie, the float is biased).
- the phosphorus removal carrier On the side of the heart, when the dephosphorization agent is depleted and the phosphorus removal carrier automatically floats to the surface of the water, the phosphorus removal carrier is exposed to the water surface with the side of the metal iron block 3, so that the maintenance personnel can float to the magnet by using the magnet.
- the phosphorus removal carrier on the water surface is removed from the water.
- the slow release interface 5 is located on the lighter side of the phosphorus removal carrier (ie, on the side opposite to the floating center). When there is no aeration power in the water, the buoyancy of the water and the gravity of the phosphorus removal carrier are sustained. The direction of the interface 5 is outward facing downward, which can reduce the probability of the surface of the sustained-release interface 5 accumulating impurities.
- the working principle of the invention is to treat the dephosphorization agent by treating the biofilm carrier with water.
- the phosphorus removal carrier comprises a storage compartment 2 for storing the phosphorus removal agent.
- the storage bin 2 can be opened and closed to supplement the dephosphorization agent 4.
- the phosphorus removal agent 4 is a solid iron salt or an aluminum salt.
- the phosphorus removal agent 4 in the storage bin 2 is in contact with the water surrounding the phosphorus removal carrier only through the sustained release interface 5.
- the sustained release interface 5 is a composite structure of a microporous material and a water-repellent fabric.
- the microporous material 6 and the water-repellent fabric 7 enable the phosphorus removal agent to be slowly released into the surrounding sewage 10.
- the water-repellent fabric 7 also blocks insoluble impurities in the water, thereby protecting the microporous material 6 from being clogged.
- the phosphorus removal carrier stores the dephosphorization agent, the density is close to that of water.
- the dephosphorization agent is exhausted, the density is less than water, and the dephosphorization carrier can automatically float to the water surface when the dephosphorization agent is exhausted, so that the maintenance personnel can recognize ,supplement.
- the position of the floating body 8 is designed to be biased toward the side having the metal iron block (ie, the upper portion of the casing 1), and the side away from the slow release interface (ie, the lower portion of the casing 1) to make the phosphorus removal carrier
- the center of gravity and the heart of the heart do not coincide.
- On the lighter side of the phosphorus removal carrier ie, on the side of the floating center, there is a metal iron block, which is convenient for the dephosphorization agent to be depleted, and the phosphorus removal carrier is automatically floated to the water surface, and the phosphorus removal carrier is exposed to the surface of the metal iron block. It is convenient for maintenance personnel to use a magnet to remove the phosphorus removal carrier floating to the water surface from the water.
- the slow release interface 5 is on the heavier side of the phosphorus removal carrier (ie, on the side of the center of gravity), and when there is no aeration and the like in the water, the direction of the interface is slowed down under the action of the buoyancy of the water and the gravity of the water. With the outside facing down, the probability of polycondensation of the surface of the sustained release interface can be reduced.
- the dephosphorization carrier in the state of use, that is, when the dephosphorization agent 4 is stored in the storage bin, the dephosphorization carrier is in a suspended state.
- the phosphorus removal carrier in the end state of use, that is, when the dephosphorization agent stored in the storage bin is exhausted, the phosphorus removal carrier is in a floating state, and one side of the metal iron block cover 3 is exposed to the water surface, which is convenient for maintenance personnel.
- the phosphorus removal carrier floating to the surface of the water is removed from the water by a magnet.
- the device can be directly thrown into the sewage treatment tank for phosphorus removal, and there is no need to modify the sewage treatment equipment, and it is not necessary to pick up and observe the quality of the dephosphorization agent, and automatically float when the dephosphorization agent is exhausted. Once replenished, it can be reused.
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Abstract
一种用于污水处理设备的除磷载体及方法,属于污水处理相关技术领域。主要包括:壳体(1),所述壳体壳体(1)内部具有用于容纳除磷剂(4)的储存仓(2),储存仓(2)内具有除磷剂(4);所述储存仓(2)的一端被仓盖(3)密闭,另一端为用于释放除磷剂(4)的缓释界面(5);其使用方法为,向储存仓(2)中加入除磷剂(4),密封仓盖(3),将壳体(1)抛入水处理池,释放除磷剂(4)的过程中悬浮于污水中,除磷剂(4)耗尽后上浮至水面,用磁铁将壳体(1)捞出,重新装载除磷剂(4)。无需对现有污水处理设备进行改造,使用周期长,易于维护。
Description
本发明涉及污水处理相关技术领域,具体的说,是涉及一种用于污水处理设备的除磷载体及方法。
水体中的氮、磷营养元素是引起水体富营养化的主要诱因。其中,水体中的磷主要来自排入水体的污水。因此,去除污水中的磷是改善水环境的重要途径。
目前,用于生活污水的除磷方法主要有化学除磷、电化学除磷及生物除磷。其中,生物除磷需要构造交替厌氧、好氧环节,依靠聚磷菌在好氧状态下过量地摄取磷,经过排放富磷剩余污泥去除污水的磷。因生物除磷工艺控制复杂,一般在污水处理设备应用较少。
化学除磷是指通过投加化学试剂形成不溶性的磷酸盐沉淀物,然后通过固液分离将磷从污水中去除。常规化学除磷需要配备加药设施或设备,包括药剂的储存装置、药剂的溶解与投加装置,有的还需要药剂混合与絮凝装置等措施,这无疑会极大的提高成本。
申请号为201410624036.7的中国专利文献提供了一种用于污水处理设备的除磷方法,其采用缓释除磷剂安装在污水处理设备的回流管上,不用专人值守投药。但其不足在于实施过程中:
1、需要增加额外的药剂桶或其他方式将缓释除磷剂储存并安装在污水处理设备中;
2、化学除磷一般需要药剂混合工序,将缓释除磷剂安装在污水处理设备的回流管上的方式只是利用气提回流液的微小动力对除磷剂进行了溶解,不利于实现除磷剂与水的完全混合,除磷剂的利用率较低;
3、将缓释除磷剂安装在污水处理设备的回流管上的方式限制了缓释除磷剂的存储量,容易造成需要频繁地添加除磷剂;
4、化学除磷的较佳条件是低SS和低DS环境,除磷剂与回流液回流至前续工序的方式往往造成除磷剂的投入环境不适宜(高SS和高DS环境),容易造成除磷剂的浪费。
电化学除磷采用电解方式,利用电能电解产生铁离子或铝离子生成不溶性的磷酸盐沉淀物,然后通过固液分离将磷从污水中去除。其不足在于需要频繁更换电解极板、电解装置的能耗较高。
此外,上述既有除磷方法因为都需要安装额外的除磷装置,受制于安装空间、电耗等原因,因而都不适用于既有污水处理设备的提标改造。
因此,如何设计一种便于在既有污水处理设备中采用、使用时间长、维护频次低且无
需对污水处理设备改造的除磷装置,是本领域技术人员亟需解决的问题。
发明内容
本发明的目的是为克服上述现有技术的不足,提供一种用于污水处理设备的除磷载体。本发明通过设计全新的结构,使其可以在释放除磷剂的过程中悬浮于污水中,除磷剂耗尽后上浮至水面,无需对现有污水处理设备进行改造,使用周期长,易于维护。
为了达成上述目的,本发明采用如下技术方案:
一种用于污水处理设备的除磷载体,包括:
壳体,
所述壳体内部具有用于容纳除磷剂的储存仓,储存仓内具有除磷剂;
所述储存仓的一端被仓盖密闭,另一端为用于释放除磷剂的缓释界面;
其中,
所述除磷剂未耗尽时壳体在污水中处于悬浮状态;
所述除磷剂耗尽时壳体在污水中处于漂浮状态。
除磷载体在使用时可成为微生物的载体,其除磷剂溶解时能实现化学除磷。根据不同的选择,所述除磷剂可采用固体型铁盐或铝盐。
作为较佳的选择,所述除磷剂采用固体状高分子聚合硫酸铁。
优选的,所述壳体靠近仓盖的一侧设置有浮体。
优选的,所述缓释界面包括微孔板及设置于微孔板外侧的滤水织物,储存仓依次与微孔板和滤水织物密闭连接;
相比除磷载体的重心而言,金属铁块的位置更靠近除磷载体的浮心;
即所述缓释界面距除磷载体重心的距离小于缓释界面距除磷载体浮心的距离。
优选的,所述微孔板为不锈钢板,其带有孔径为0.3-0.8mm的通孔。
优选的,所述滤水织物为无纺土工织物。
优选的,所述仓盖和/或储存仓为铁质。
优选的,所述仓盖和/或储存仓内含有金属铁块。相比除磷载体的重心而言,金属铁块的位置更靠近除磷载体的浮心;即所述金属铁块距除磷载体重心的距离小于缓释界面距除磷载体浮心的距离。
优选的,所述壳体上设置有浮体。
优选的,所述浮体位于靠近壳体中靠近仓盖的一侧,浮体使除磷载体的重心和浮心不重合。
壳体内存储有除磷剂时,密度为0.94-0.97g/cm3,当除磷剂耗尽时,密度为
0.80-0.90g/cm3。
通过密度的差异实现除磷剂耗尽时除磷载体能自动漂浮至水面上,以便于维护人员识别、补充。
在提供上述结构方案的同时,本发明还提供了一种利用上述除磷载体的方法,主要包括如下步骤:
A、打开仓盖,向储存仓内加入除磷剂;
B、密闭仓盖,并将壳体抛入污水处理池;
C、壳体悬浮于污水中,除磷剂耗尽后,壳体漂浮于水面;
D、利用磁铁将壳体捞出,重新装载除磷剂。
本发明的有益效果是:
(1)能够直接在污水处理设备中广泛应用,以替换或补充现有的载体。无需较大改造,不需要额外配备加药设施或设备就能实现既有无除磷功能的污水处理设备的提标改造,使其具备除磷功能。
(2)依靠微孔材料及滤水型织物实现除磷剂的物理性缓释,与采用化学性缓释的除磷剂(例如缓释除磷剂)相比,能够储存的除磷剂的纯度更高(缓释除磷剂等需要添加额外的缓释原料,往往造成除磷剂的稀释),因而容量更大,使用时间更长、维护频次更低。
(3)壳体含有除磷剂时处于悬浮状态,当除磷剂耗尽时自动浮出水面,不需要对壳体内的除磷剂含量频繁观测,十分方便。
(4)无需为除磷过程提供额外的供电。
图1是本发明的结构示意图;
图2是本发明的主视图;
图3是本发明的俯视图;
图4是除磷剂未耗尽时的应用状态图;
图5是除磷剂耗尽时的状态示意图;
图6是图2中I处的局部放大图;
图7是图2中II处的局部放大图;
图中,1.壳体,2.储存仓,3.仓盖,4.除磷剂,5.缓释界面,6.微孔材料,7.滤水型织物,8.浮体,9.固定环,10.污水。
下面将结合附图对本发明进行详细说明。
实施例:一种用于污水处理设备的除磷载体,其结构如图1-3、图6和图7所示,包括:
具有用于附着生物膜的壳体1;壳体1内具有用于存储除磷剂4的储存仓2;
壳体1应尽量选择为球型,以便于控制重心和浮心。
所述储存仓2的两端分别为仓盖3和缓释界面5;
所述仓盖3可打开和关闭,用于补充除磷剂4;
所述仓盖3为金属铁材质、表面镀镍,也可以内部含有金属铁块;
所述除磷剂4采用固体状高分子聚合硫酸铁;
所述缓释界面5是储存仓2内的除磷剂4与除磷载体周围的水的唯一接触界面;
所述缓释界面5为由微孔材料6与滤水型织物7组成的2层复合结构;
所述微孔材料6与除磷剂4接触,为厚度0.4-0.6mm,穿孔直径0.3-0.8mm的不锈钢微穿孔板;
滤水型织物7与除磷载体周围的水接触,为0.5-1.0mm厚滤水型无纺土工织物;
所述壳体1上靠近仓盖3一侧有浮体8。
其中,所述滤水型织物7外侧还设置有固定环9,固定环9用于防止滤水型织物7和微孔材料6脱落。
浮体8固定在壳体1上,为环形。浮体8的作用是使所述除磷载体的重心和浮心不重合,使所述含金属铁块(图中未示出)的仓盖3偏向除磷载体较轻的一侧(即偏向浮心一侧),便于除磷剂耗尽、除磷载体自动漂浮至水面上时,除磷载体以所述含金属铁块的仓盖3的一侧露出水面,便于维护人员利用磁铁将漂浮至水面的除磷载体从水中捞出。
所述缓释界面5位于除磷载体较轻的一侧(即偏向浮心一侧),当水中无曝气等扰动力量时,在水的浮力和除磷载体自身重力的作用下,缓释界面5的方向为外面朝下,可降低所述缓释界面5表面积聚杂质的概率。
本发明的工作原理是:利用水处理生物膜载体来储存除磷剂。除磷载体包含一个用于储存除磷剂的储存仓2。储存仓2可以打开和关闭,从而补充除磷剂4。该除磷剂4采用固体型铁盐或铝盐。
在使用时,储存仓2内的除磷剂4与除磷载体周围的水仅通过缓释界面5接触。该缓释界面5为微孔材料及滤水型织物的复合结构。微孔材料6及滤水型织物7使除磷剂能够缓慢的释放至周围的污水10中。
滤水型织物7还能阻隔水中的不溶性杂质,从而保护微孔材料6不被堵塞。除磷载体在存储有除磷剂时,密度与水接近,当除磷剂耗尽时,密度小于水,实现除磷剂耗尽时除磷载体能自动漂浮至水面上,以便于维护人员识别、补充。
较佳的选择为,浮体8的位置设计为偏向有金属铁块的一侧(即壳体1的上部),而远离缓释界面的一侧(即壳体1的下部),使除磷载体重心和浮心不重合。在除磷载体较轻的一侧(即偏向浮心一侧)有金属铁块,便于除磷剂耗尽、除磷载体自动漂浮至水面上时,除磷载体以金属铁块一侧露出水面,便于维护人员利用磁铁将漂浮至水面的除磷载体从水中捞出。
所述缓释界面5在除磷载体较重的一侧(即偏向重心一侧),当在水中无曝气等扰动力量时,在水的浮力和自身重力的作用下,缓释界面的方向为外面朝下,可降低所述缓释界面表面积聚杂质的概率。
如图4所示,本发明在使用状态,即储存仓存储有除磷剂4时,除磷载体处于悬浮状态。
如图5所示,本发明在使用结束状态,即储存仓存储的除磷剂耗尽时,除磷载体处于漂浮状态,且含金属铁块的仓盖3的一侧露出水面,便于维护人员利用磁铁将漂浮至水面的除磷载体从水中捞出。
采用了上述结构后,本装置可以直接抛入污水处理池中进行除磷,且无需对污水处理设备进行改造,也无需捞起观测除磷剂质量,当除磷剂耗尽时自动上浮,进行再次补充后即可重复使用。
对所公开的实施例的上述说明,使本领域专业技术人员能够实现或使用本发明。对实施例的多种修改对本领域的专业技术人员来说将是显而易见的,本文中所定义的一般原理可以在不脱离本发明的精神或范围的情况下,在其它实施例中实现,未予以详细说明和局部放大呈现的部分,为现有技术,在此不进行赘述。因此,本发明将不会被限制于本文所示的这些实施例,而是要符合与本文所公开的原理和特点相一致的最宽的范围。
Claims (10)
- 一种用于污水处理设备的除磷载体,其特征在于,包括:壳体,所述壳体内部具有用于容纳除磷剂的储存仓,储存仓内具有除磷剂;所述储存仓的一端被仓盖密闭,另一端为用于释放除磷剂的缓释界面;其中,所述除磷剂未耗尽时壳体在污水中处于悬浮状态;所述除磷剂耗尽时壳体在污水中处于漂浮状态。
- 根据权利要求1所述的除磷载体,其特征在于,所述壳体靠近仓盖的一侧设置有浮体。
- 根据权利要求1所述的除磷载体,其特征在于,所述缓释界面包括微孔板及设置于微孔板外侧的滤水织物,储存仓依次与微孔板和滤水织物密闭连接;所述缓释界面距除磷载体重心的距离小于缓释界面距除磷载体浮心的距离。
- 根据权利要求1所述的除磷载体,其特征在于,所述微孔板为不锈钢板,其带有孔径为0.3-0.8mm的通孔。
- 根据权利要求1所述的除磷载体,其特征在于,所述滤水织物为无纺土工织物。
- 根据权利要求1所述的除磷载体,其特征在于,所述仓盖和/或储存仓为铁质。
- 根据权利要求1所述的除磷载体,其特征在于,所述仓盖和/或储存仓内含有金属铁块;所述金属铁块距除磷载体重心的距离小于缓释界面距除磷载体浮心的距离。
- 根据权利要求1所述的除磷载体,其特征在于,所述壳体上设置有浮体。
- 根据权利要求1所述的除磷载体,其特征在于,所述浮体位于靠近壳体中靠近仓盖的一侧,浮体使除磷载体的重心和浮心不重合。
- 一种利用权利要求1-9任一项所述的除磷载体的方法,其特征在于,步骤如下:A、打开仓盖,向储存仓内加入除磷剂;B、密闭仓盖,并将壳体抛入污水处理池;C、壳体悬浮于污水中,除磷剂耗尽后,壳体漂浮于水面;D、利用磁铁将壳体捞出,重新装载除磷剂。
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