CN111229252A - Novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects - Google Patents

Novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects Download PDF

Info

Publication number
CN111229252A
CN111229252A CN202010161285.2A CN202010161285A CN111229252A CN 111229252 A CN111229252 A CN 111229252A CN 202010161285 A CN202010161285 A CN 202010161285A CN 111229252 A CN111229252 A CN 111229252A
Authority
CN
China
Prior art keywords
parts
autotrophic
efficiency catalytic
efficiency
novel iron
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202010161285.2A
Other languages
Chinese (zh)
Inventor
陈斌
杨继勇
胡西龙
寇天亮
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Beijing Horlzontec Environment Protection Technology Co ltd
Original Assignee
Beijing Horlzontec Environment Protection Technology Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Beijing Horlzontec Environment Protection Technology Co ltd filed Critical Beijing Horlzontec Environment Protection Technology Co ltd
Priority to CN202010161285.2A priority Critical patent/CN111229252A/en
Publication of CN111229252A publication Critical patent/CN111229252A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/89Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals
    • B01J23/8933Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/8993Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with chromium, molybdenum or tungsten
    • 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
    • C02F1/70Treatment of water, waste water, or sewage by reduction
    • C02F1/705Reduction by metals
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • C02F2101/166Nitrites
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/06Controlling or monitoring parameters in water treatment pH
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/16Total nitrogen (tkN-N)

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Catalysts (AREA)

Abstract

The invention provides a novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects, which comprises the following raw materials in parts by weight: 40.000 to 98.000 parts of zero-valent iron, 5.000 to 28.000 parts of activated carbon powder, 4.500 to 17.500 parts of water glass, 1.000 to 6.000 parts of Portland cement and 0.500 to 6.000 parts of multi-element metal catalyst; the invention provides a method for increasing NO in sewage3 The reduction efficiency of N is reduced, the inhibition of the pH of the water body on the reduction reaction is reduced, and NO in the reduction process can be reduced2 -N and NH4 +A novel iron substrate high-efficiency catalytic denitrification carrier generated by N and has good treatment effect within the pH value of 6-9And the TN removal is realized in the true sense, and the purification effect on the phosphorus in the sewage is good.

Description

Novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects
Technical Field
The invention relates to sewage treatment, in particular to a novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects.
Background
NO in environmental water of China3 -The pollution of-N is continuously increased, and the sewage plant drainage is NO in the environmental water body3 -One of the main sources of-N. Domestic sewage treatment plant drainageIn the nitrogen as NO3 -the-N is mainly 28-68% of the Total Nitrogen (TN), and if the-N is directly discharged into an environmental water body, the eutrophication of the water body is caused, and the black and smelly water body can be caused. Thus, NO3 -The removal of-N has become an important issue for sewage plant drainage TN emission control.
It is generally considered that when BOD is contained in the wastewater5And when the/TN is less than 3-5, the sewage is low in carbon-nitrogen ratio. However, after the domestic sewage is subjected to secondary treatment in a sewage plant, BOD is consumed in large quantities, resulting in BOD of the discharged water5the/TN is only 0.3-0.8, belonging to typical sewage with low carbon-nitrogen ratio, and the sewage is difficult to realize deep denitrification by utilizing the traditional biological denitrification process. If a physicochemical method such as reverse osmosis, ion exchange, electrodialysis and the like is adopted, a certain denitrification effect can be achieved in sewage treatment, but the method has the defects of high investment, high energy consumption, generation of concentrated water and the like, and is not suitable for deep denitrification treatment of sewage plant drainage.
The working principle of the domestic iron matrix carrier is that zero-valent iron can be used for rapidly reducing NO3 -N, although having a certain purifying effect, is seriously affected by the pH of the water, and it is often necessary to adjust the pH to 4 to 5 or less and reduce the product with NH4 +predominantly-N, TN removal is difficult to achieve. Reduction of NO to increase zero-valent iron3 -Efficiency of N, reduction of NO with nano zero valent iron (nZVI)3 --N, greatly increasing the reduction of NO by zero-valent iron3 -The efficiency of N while reducing the influence of pH on the rate of the reduction reaction. However, the passivation rate of nZVI in the reaction is fast, and the reduction product is still NH4+N is dominant, and the production cost of nZVI is much higher than that of ordinary zero-valent iron (ZVI), so the technology is not yet put into practical use. Therefore, the development of a novel deep denitrification technology with high efficiency, low consumption and no secondary pollution is of great significance.
Disclosure of Invention
The invention aims to provide a novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects, so as to solve the problems in the background technology.
In order to achieve the purpose, the invention provides the following technical scheme:
a novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects comprises the following raw materials in parts by weight: 40.000 to 98.000 parts of zero-valent iron, 5.000 to 28.000 parts of activated carbon powder, 4.500 to 17.500 parts of water glass, 1.000 to 6.000 parts of Portland cement and 0.500 to 6.000 parts of multi-element metal catalyst.
As a further scheme of the invention: the composite material comprises the following raw materials in parts by weight: 55.000-83.000 parts of zero-valent iron, 8.000-25.000 parts of activated carbon powder, 7.500-14.500 parts of water glass, 2.000-5.000 parts of Portland cement and 1.500-5.000 parts of multi-original metal catalyst.
As a further scheme of the invention: the multi-element metal catalyst comprises the following raw materials in parts by weight: 0.300-2.100 parts of manganese, 0.010-0.100 part of vanadium, 0.010-0.120 part of zinc, 0.010-0.800 part of titanium, 0.100-0.850 part of copper, 0.001-0.100 part of cobalt, 0.0010.050 parts of nickel, 0.010-0.100 part of chromium, 0.001-0.150 part of gallium, 0.010-0.120 part of strontium, 0.005-0.100 part of zirconium, 0.002-0.080 part of rubidium, 0.001-0.050 part of niobium, 0.001-0.050 part of yttrium, 0.001-0.050 part of molybdenum, 0.010-0.800 part of barium, 0.001-0.020 part of cerium, 0.001-0.020 part of cesium and 0.001-0.020 part of platinum.
Compared with the prior art, the invention has the beneficial effects that:
the invention provides a method for increasing NO in sewage3 -The reduction efficiency of N is reduced, the inhibition of the pH of the water body on the reduction reaction is reduced, and NO in the reduction process can be reduced2 -N and NH4 +The novel iron substrate high-efficiency catalytic denitrification carrier generated by the N has a good treatment effect within the pH value range of 6-9, realizes TN removal in the true sense, and has a good purification effect on phosphorus in sewage. Iron-based high-efficiency catalytic denitrification carrier added with multi-metal catalyst for raw water NO with different pH values3 -The removal rate of-N is 90-95%, and the method can be used for removing nitrate Nitrogen (NO) in sewage water3 --N) the removal efficiency is greatly increased; nitrite (NO) during reduction2 -N) and ammonium (NH)4 +-N) the generation rate is low, and no secondary pollution is caused to the water body; has low passivation rate, can maintain activity for a long time in the use process, and further reducesThe cost is low, and the carrier is not hardened; the device is not influenced by the carbon-nitrogen ratio of water, the use temperature and the application range; the investment is low, the energy consumption is low, and no waste water or sludge is generated; meanwhile, the method also has high purification efficiency on phosphorus, and the efficiency can reach 85-95%.
Detailed Description
The technical solution of the present patent will be described in further detail with reference to the following embodiments.
A novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects comprises the following raw materials in parts by weight: 40.000 to 98.000 parts of zero-valent iron, 5.000 to 28.000 parts of activated carbon powder, 4.500 to 17.500 parts of water glass, 1.000 to 6.000 parts of Portland cement and 0.500 to 6.000 parts of multi-element metal catalyst. The main raw material of the iron-based high-efficiency catalytic denitrification carrier is zero-valent iron, and the zero-valent iron is mixed with a multi-element metal catalyst, a foaming agent and an adhesive to prepare a carrier with the diameter of 5-50mm, and the carrier is placed into a roasting furnace and roasted at the high temperature of 900-1100 ℃; wherein, the zero-valent iron is iron powder; one part of the activated carbon powder reacts to produce gas in the roasting process and plays the role of a foaming agent, and the other part of the activated carbon powder does not participate in the reaction and is left in the iron-matrix carrier finished product; the adhesive is mainly water glass and common Portland cement, and mainly plays a role in bonding and forming raw materials. The multi-element metal catalyst is prepared by mixing a fourth period transition metal element (manganese, vanadium, zinc, titanium, copper, cobalt, nickel, chromium and gallium), a fifth period transition metal element (strontium, zirconium, rubidium, niobium, molybdenum and yttrium), a sixth period transition metal element (barium, cesium and platinum) and cerium according to a certain proportion.
Specifically, the feed comprises the following raw materials in parts by weight: 55.000-83.000 parts of zero-valent iron, 8.000-25.000 parts of activated carbon powder, 7.500-14.500 parts of water glass, 2.000-5.000 parts of Portland cement and 1.500-5.000 parts of multi-original metal catalyst.
Specifically, the multi-element metal catalyst comprises the following raw materials in parts by weight: 0.300-2.100 parts of manganese, 0.010-0.100 part of vanadium, 0.010-0.120 part of zinc, 0.010-0.800 part of titanium, 0.100-0.850 part of copper, 0.001-0.100 part of cobalt, 0.0010.050 parts of nickel, 0.010-0.100 part of chromium, 0.001-0.150 part of gallium, 0.010-0.120 part of strontium, 0.005-0.100 part of zirconium, 0.002-0.080 part of rubidium, 0.001-0.050 part of niobium, 0.001-0.050 part of yttrium, 0.001-0.050 part of molybdenum, 0.010-0.800 part of barium, 0.001-0.020 part of cerium, 0.001-0.020 part of cesium and 0.001-0.020 part of platinum.
The iron substrate high-efficiency catalytic denitrification carrier added with the multi-metal catalyst is used for carrying out NO treatment on raw water with different pH values3 -The removal rate of-N is 90-95%, and the method can be used for removing nitrate Nitrogen (NO) in sewage water3 --N) the removal efficiency is greatly increased; nitrite (NO) during reduction2 -N) and ammonium (NH)4 +-N) the generation rate is low, and no secondary pollution is caused to the water body; the passivation rate is low, the activity can be maintained for a long time in the use process, the cost is further reduced, and the carrier is not hardened; the device is not influenced by the carbon-nitrogen ratio of water, the use temperature and the application range; the investment is low, the energy consumption is low, and no waste water or sludge is generated; meanwhile, the method also has high purification efficiency on phosphorus, and the efficiency can reach 85-95%.
Although the preferred embodiments of the present patent have been described in detail, the present patent is not limited to the above embodiments, and various changes can be made without departing from the spirit of the present patent within the knowledge of those skilled in the art.

Claims (3)

1. A novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects is characterized by comprising the following raw materials in parts by weight: 40.000 to 98.000 parts of zero-valent iron, 5.000 to 28.000 parts of activated carbon powder, 4.500 to 17.500 parts of water glass, 1.000 to 6.000 parts of Portland cement and 0.500 to 6.000 parts of multi-element metal catalyst.
2. The novel iron matrix high-efficiency catalytic carrier with the autotrophic and heterotrophic coupling effect according to claim 1 is characterized by comprising the following raw materials in parts by weight: 55.000-83.000 parts of zero-valent iron, 8.000-25.000 parts of activated carbon powder, 7.500-14.500 parts of water glass, 2.000-5.000 parts of Portland cement and 1.500-5.000 parts of multi-original metal catalyst.
3. The novel iron matrix high-efficiency catalytic carrier with the autotrophic and heterotrophic coupling effect according to claim 1, wherein the multi-element metal catalyst comprises the following raw materials in parts by weight: 0.300-2.100 parts of manganese, 0.010-0.100 part of vanadium, 0.010-0.120 part of zinc, 0.010-0.800 part of titanium, 0.100-0.850 part of copper, 0.001-0.100 part of cobalt, 0.0010.050 parts of nickel, 0.010-0.100 part of chromium, 0.001-0.150 part of gallium, 0.010-0.120 part of strontium, 0.005-0.100 part of zirconium, 0.002-0.080 part of rubidium, 0.001-0.050 part of niobium, 0.001-0.050 part of yttrium, 0.001-0.050 part of molybdenum, 0.010-0.800 part of barium, 0.001-0.020 part of cerium, 0.001-0.020 part of cesium and 0.001-0.020 part of platinum.
CN202010161285.2A 2020-03-10 2020-03-10 Novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects Pending CN111229252A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202010161285.2A CN111229252A (en) 2020-03-10 2020-03-10 Novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202010161285.2A CN111229252A (en) 2020-03-10 2020-03-10 Novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects

Publications (1)

Publication Number Publication Date
CN111229252A true CN111229252A (en) 2020-06-05

Family

ID=70880251

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202010161285.2A Pending CN111229252A (en) 2020-03-10 2020-03-10 Novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects

Country Status (1)

Country Link
CN (1) CN111229252A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114602521A (en) * 2022-02-22 2022-06-10 北京和众大成环保科技有限公司 Multi-element catalytic composite carrier based on cementite-carbon system

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102951708A (en) * 2012-09-24 2013-03-06 潍坊海洁环保设备有限公司 Multielement catalysis iron-carbon micro-electrolysis filler and preparation method thereof
CN103145234A (en) * 2013-03-22 2013-06-12 北京交通大学 Aerobic bio-particle carrier for directly removing ammonia nitrogen from sewage with low carbon nitrogen ratio and preparation method thereof
WO2015109899A1 (en) * 2014-01-21 2015-07-30 北京师范大学 Method for quickly and effectively removing heavy metals in water body
CN109110862A (en) * 2018-09-20 2019-01-01 北京师范大学 A kind of denitrogenation dephosphorizing material and preparation method thereof
CN109650561A (en) * 2019-02-26 2019-04-19 清华大学 A kind of denitrification functions filler and its preparation and application

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102951708A (en) * 2012-09-24 2013-03-06 潍坊海洁环保设备有限公司 Multielement catalysis iron-carbon micro-electrolysis filler and preparation method thereof
CN103145234A (en) * 2013-03-22 2013-06-12 北京交通大学 Aerobic bio-particle carrier for directly removing ammonia nitrogen from sewage with low carbon nitrogen ratio and preparation method thereof
WO2015109899A1 (en) * 2014-01-21 2015-07-30 北京师范大学 Method for quickly and effectively removing heavy metals in water body
CN109110862A (en) * 2018-09-20 2019-01-01 北京师范大学 A kind of denitrogenation dephosphorizing material and preparation method thereof
CN109650561A (en) * 2019-02-26 2019-04-19 清华大学 A kind of denitrification functions filler and its preparation and application

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114602521A (en) * 2022-02-22 2022-06-10 北京和众大成环保科技有限公司 Multi-element catalytic composite carrier based on cementite-carbon system

Similar Documents

Publication Publication Date Title
CN108483655B (en) Method for deep denitrification by coupling shortcut nitrification and denitrification with anaerobic ammonia oxidation and sulfur autotrophic denitrification
Han et al. Effect of sludge-fly ash ceramic particles (SFCP) on synthetic wastewater treatment in an A/O combined biological aerated filter
CN101830558B (en) Method for cultivating anaerobic ammonium oxidation granular sludge
CN108946944A (en) The method that short-cut denitrification promotes the removal of waste water total nitrogen
CN114230021A (en) Biological composite filler and preparation method and application thereof
CN105347618A (en) Biological denitrogenation system for waste water containing high ammonia nitrogen
CN204125291U (en) A kind of Waste Water Treatment
CN113415881B (en) Device and method for realizing autotrophic nitrogen and synchronous phosphorus recovery of domestic sewage by using granular sludge with hydroxyapatite as crystal nucleus
CN108191056B (en) Desulfurization and denitrification method for desulfurization and denitrification wastewater and ammonia nitrogen wastewater
CN102515352A (en) Method for removing ammonia nitrogen from industrial waste water produced in synthetic ammonia industry
CN111592090A (en) Application method of red mud-based heterogeneous Fenton catalyst for advanced wastewater treatment
CN111229252A (en) Novel iron matrix high-efficiency catalytic carrier with autotrophic and heterotrophic coupling effects
CN114455703A (en) Method for treating heavy metal-containing organic wastewater by biochar-loaded zero-valent iron coupling sulfate reduction
CN111892161B (en) Method for rapidly starting anaerobic ammonia oxidation by using inorganic composite powder carrier
CN106630417A (en) Method for removing nitrogen and phosphorus in wastewater by low cost
CN109289503B (en) Ammonia-containing waste gas treatment method
CN105668755A (en) Method for resourcefully using vanadium extracting wastewater for producing ammonia-hydrocarbon denitrifying agent
CN107487841A (en) A kind of denitrification integrates coupling dephosphorization and the waste water treatment process of Anammox
CN103613135A (en) Integrated utilization environmental-pollution-controlling new technology for ammonium molybdate production waste water
JPS585118B2 (en) Yuukiseihaisuino
CN113087144A (en) Method for preparing denitrification carbon source by adopting blue algae
CN113213625A (en) Carbonate type ammonia oxidation process and strengthening technology thereof
CN109987782B (en) Printing and dyeing wastewater treatment method and device
CN112358041A (en) Granular sludge culture method for synchronous denitrification and methanogenesis and COD removal
CN111453841A (en) Preparation method of slow-release carbon source hollow rod

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
WD01 Invention patent application deemed withdrawn after publication
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20200605