CN108328800A - A kind of removal waste water of heat-engine plant heavy metal ion method - Google Patents
A kind of removal waste water of heat-engine plant heavy metal ion method Download PDFInfo
- Publication number
- CN108328800A CN108328800A CN201810175282.7A CN201810175282A CN108328800A CN 108328800 A CN108328800 A CN 108328800A CN 201810175282 A CN201810175282 A CN 201810175282A CN 108328800 A CN108328800 A CN 108328800A
- Authority
- CN
- China
- Prior art keywords
- fluidized bed
- desulfurization wastewater
- naoh solution
- waste water
- heavy metal
- 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
Links
Classifications
-
- 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
-
- 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
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
-
- 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
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/281—Treatment of water, waste water, or sewage by sorption using inorganic sorbents
-
- 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
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- 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
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Removal Of Specific Substances (AREA)
Abstract
The invention belongs to waste water of heat-engine plant water treatment field more particularly to a kind of removal waste water of heat-engine plant heavy metal ion methods.A kind of removal waste water of heat-engine plant heavy metal ion method, this method are applied to desulfurization wastewater and are completed before entering recovery processing, be as follows:(1) desulfurization wastewater is entered into the first fluidized bed from bottom, is wherein filled with quartz sand filter media in the first fluidized bed, connection NaOH solution tank, KMnO in the bottom of the first fluidized bed4NaOH solution tank NaOH, while desulfurization wastewater enters the first fluidized bed from bottom, NaOH solution, KMnO4Solution enters the first fluidized bed together from first fluidized bed bottom;Conventionally the pH in the first fluidized bed is controlled between 7.5~11.The sludge density that the method for the invention enables the technique to generate reaches 2.5~3.0kg/L, and dewatered moisture is less than 20%, and compared with the traditional chemical precipitation method, the sludge quantity that fluidized bed process generates will be less than 25%.
Description
Technical field
The invention belongs to waste water of heat-engine plant water treatment field more particularly to a kind of removal waste water of heat-engine plant heavy metal ion sides
Method.
Background technology
Heavy metals in industrial wastewater is passing through multiple tracks metallochemistry and electrochemistry to environmental hazard most serious, heavy metal wastewater thereby
After process, the metallic elements such as zinc, copper, chromium, nickel, cadmium in water all occur with atomic valence, are directly discharged in environment, can pass through
Prolonged cumulative effect endangers the health of people.Minamata disease and bone aching are just respectively by mercurous and contaminated wastewater ring containing cadmium
Caused by border.Therefore, it is necessary to processing heavy metal wastewater thereby of adopting an effective measure.
The waste water that heavy metal ion is contained in thermal power plant is mainly desulfurization wastewater, there is plurality of heavy metal element, as Cr,
As, Cd, Pb, Hg, Cu etc..
Conventional processing method is exactly:Desulfurization wastewater is directly entered neutralization reaction pond, into reaction tank be added NaOH or
Ca(OH)2Equal alkaline matters, by the Fe in desulfurization wastewater3+、Zn2+、Ni2+、Cu2+、Cr3+Hydrogen is generated Deng most of heavy metal ion
Oxide removal;Organic sulfur, which is added, makes the Hg in waste water2+、Pb2+Plasma becomes sulfide precipitation;Adding flocculant will give up
Thin small and scattered particle and colloidal substance coacervating large particle precipitate in water;Waste water after coagulation enters clarifying basin, into
Row sedimentation, discharge after supernatant is up to standard, sludge carry out concentration.
But desulfurization wastewater is handled using above-mentioned method, process route is complicated, is controlled in actual use
The desulfurization wastewater operating condition of many power plant and unstable in journey.Therefore, exploitation new process reduces operating cost, improves operation
Stability is unavoidable.
Invention content
It is asked for process route is complicated, operating condition is unstable existing for heavy metal ion in current removal desulfurization wastewater
The defect of topic and its solution, to effectively remove heavy metal ion in desulfurization wastewater, the present invention provides a kind of removal thermal power plant
Desulfurization wastewater heavy metal ion method can easily control process conditions using the method for the invention, and it is useless especially to improve desulfurization
The safe and stable operation quality of water process.
A kind of removal waste water of heat-engine plant heavy metal ion method of the present invention, includes the following steps:
A kind of removal waste water of heat-engine plant heavy metal ion method, it is complete before entering recovery processing that this method is applied to desulfurization wastewater
At being as follows:
(1) desulfurization wastewater is entered into the first fluidized bed from bottom, wherein quartz sand filter media is filled in the first fluidized bed, first
Bottom connection NaOH solution tank, the KMnO of fluid bed4NaOH solution tank NaOH, while desulfurization wastewater enters the first fluidized bed from bottom,
NaOH solution, KMnO4Solution enters the first fluidized bed together from first fluidized bed bottom;;By the addition for controlling NaOH solution
Amount controls the pH in the first fluidized bed between 7.5~11;
(2) treated, and desulfurization wastewater enters second fluidized bed to step (1);Addition by controlling NaOH solution will be first-class
The pH changed in bed is controlled between 4.5~7.0;
(3) treated, and desulfurization wastewater enters buffer pool to step (2), the buffer cycles in buffer pool, while sampling and measuring is through slow
Rush pond treated that desulfurization wastewater is recycled if the following conditions meet simultaneously;If being unsatisfactory for any of which
When one condition, the circular treatment of next step is carried out;The condition includes:Ni contents are less than 1mg/L;Cd contents are less than
1.5mg/L;Zn contents are less than 1mg/L;Hg contents are less than 0.05mg/L;
(4) desulfurization wastewater that recycling condition is unsatisfactory in step (3) is repeated into step (1)-(3), until sampling and measuring desulfurization is useless
Until water meets recycling condition.
Using the method for the invention, when desulfurization wastewater passes through the first fluidized bed, divalent manganesetion and ferrous ion are inhaled
It is attached in the heavy metal ion dissolved in desulfurization wastewater, in oxidant KMnO4Under the action of be oxidized to manganese dioxide and hydrogen-oxygen
Change iron, and one layer of coating is formed in metal surface, since manganese dioxide and iron hydroxide have very inorganic dissolved ion
Strong characterization of adsorption makes the soluble ion adsorbed be copolymerized into particle and settles down shape by increasing continuously this layer of coating
At sludge, the sludge density that the method for the invention enables the technique to generate reaches 2.5~3.0kg/L, and dewatered moisture is low
In 20%, compared with the traditional chemical precipitation method, the sludge quantity that fluidized bed process generates is up to 22-25%.
Description of the drawings
Fig. 1 is the attachment structure schematic diagram of equipment involved by the method for the invention.
Fig. 1-the first fluidized bed;2- second fluidized beds;3- buffer pools;4-KMnO4NaOH solution tank NaOH;5-NaOH NaOH solution tank NaOHs.
Specific implementation mode
A kind of removal waste water of heat-engine plant heavy metal ion method, this method are applied to desulfurization wastewater and are entering recovery processing
Preceding completion, is as follows:
(1) desulfurization wastewater is entered into the first fluidized bed 1 from bottom, is wherein filled with quartz sand filter media in the first fluidized bed 1,
Bottom connection NaOH solution tank 5, the KMnO4 NaOH solution tank NaOHs 4 of one fluid bed 1, desulfurization wastewater enter the same of the first fluidized bed 1 from bottom
When, NaOH solution, KMnO4Solution enters the first fluidized bed 1 together from 1 bottom of the first fluidized bed;;By controlling NaOH solution
Addition controls the pH in the first fluidized bed 1 between 7.5~11;Will be disengaged from waste water the heavy metal ion such as Ni, Cd, Zn into
Row removes for the first time;
(2) treated that desulfurization wastewater enters second fluidized bed 2 for step (1),;By controlling the addition of NaOH solution by first
PH in fluid bed 1 is controlled between 4.5~7.0;Cl ions are made to form complicated complexing under fluid bed effect with Hg ions
Object.
(3) treated that desulfurization wastewater enters buffer pool 3 for step (2), the buffer cycles in buffer pool 3, while sampling survey
Measure buffered pond 3 treated that desulfurization wastewater is recycled if the following conditions meet simultaneously;If be unsatisfactory for
When one condition of any of which, the circular treatment of next step is carried out;The condition includes:Ni contents are less than 1mg/L;Cd contents
Less than 1.5mg/L;Zn contents are less than 1mg/L;Hg contents are less than 0.05mg/L;
(4) desulfurization wastewater that recycling condition is unsatisfactory in step (3) is repeated into step (1)-(3), until sampling and measuring desulfurization is useless
Until water meets recycling condition.
After the method for the invention to desulfurization wastewater handle repeatedly, the removal rate point of the heavy metals such as Ni, Cd, Zn
Not Wei 99%, 92%, the removal rate of 97% or more, Hg can also reach 96% or more.
The system of removal waste water of heat-engine plant heavy metal ion of the present invention, including the sequentially connected first fluidized bed 1, the
Two fluid beds 2 and buffer pool 3, wherein the first fluidized bed 1 equipped with the arrival end being connected with desulfurization wastewater, NaOH solution tank 5,
KMnO4 NaOH solution tank NaOHs 4 are connected to 1 bottom of the first fluidized bed by pipeline respectively, and quartz sand filter media is filled in the first fluidized bed 1.
Claims (1)
1. a kind of removal waste water of heat-engine plant heavy metal ion method, it is characterised in that this method is entering back applied to desulfurization wastewater
It completes, is as follows before receiving processing:
(1) desulfurization wastewater is entered into the first fluidized bed from bottom, wherein quartz sand filter media is filled in the first fluidized bed, first
Bottom connection NaOH solution tank, the KMnO of fluid bed4NaOH solution tank NaOH, while desulfurization wastewater enters the first fluidized bed from bottom,
NaOH solution, KMnO4Solution enters the first fluidized bed together from first fluidized bed bottom;By the addition for controlling NaOH solution
PH in the first fluidized bed is controlled between 7.5~11;
(2) treated, and desulfurization wastewater enters second fluidized bed to step (1),;By controlling the addition of NaOH solution by first
PH in fluid bed is controlled between 4.5~7.0;
(3) treated, and desulfurization wastewater enters buffer pool to step (2), the buffer cycles in buffer pool, while sampling and measuring is through slow
Rush pond treated that desulfurization wastewater is recycled if the following conditions meet simultaneously;If being unsatisfactory for any of which
When one condition, the circular treatment of next step is carried out;The condition includes:Ni contents are less than 1mg/L;Cd contents are less than
1.5mg/L;Zn contents are less than 1mg/L;Hg contents are less than 0.05mg/L;
(4) desulfurization wastewater that recycling condition is unsatisfactory in step (3) is repeated into step (1)-(3), until sampling and measuring desulfurization is useless
Until water meets recycling condition.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201810175282.7A CN108328800A (en) | 2018-03-02 | 2018-03-02 | A kind of removal waste water of heat-engine plant heavy metal ion method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201810175282.7A CN108328800A (en) | 2018-03-02 | 2018-03-02 | A kind of removal waste water of heat-engine plant heavy metal ion method |
Publications (1)
Publication Number | Publication Date |
---|---|
CN108328800A true CN108328800A (en) | 2018-07-27 |
Family
ID=62930309
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201810175282.7A Pending CN108328800A (en) | 2018-03-02 | 2018-03-02 | A kind of removal waste water of heat-engine plant heavy metal ion method |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN108328800A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109019985A (en) * | 2018-09-17 | 2018-12-18 | 上海禾元环保集团有限公司 | A kind of processing method of oil-containing heavy metal wastewater thereby industry |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102145947A (en) * | 2011-02-24 | 2011-08-10 | 哈尔滨工业大学 | Water treatment method for removing Tl<+> and/or Cd2<+> by producing nanometer iron and manganese oxides in situ |
CN102311190A (en) * | 2011-08-19 | 2012-01-11 | 深圳市水务(集团)有限公司 | Method for removing thallium from drinking water by enhanced conventional water treatment process |
WO2012042282A1 (en) * | 2010-09-28 | 2012-04-05 | Loufakis Chemicals S.A. | A method for the synthesis of tetravalent manganese feroxyhite for arsenic removal from water |
WO2016111739A1 (en) * | 2015-01-06 | 2016-07-14 | Ecolab Usa Inc. | Process for removal of selenium from water by dithionite ions |
-
2018
- 2018-03-02 CN CN201810175282.7A patent/CN108328800A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2012042282A1 (en) * | 2010-09-28 | 2012-04-05 | Loufakis Chemicals S.A. | A method for the synthesis of tetravalent manganese feroxyhite for arsenic removal from water |
CN102145947A (en) * | 2011-02-24 | 2011-08-10 | 哈尔滨工业大学 | Water treatment method for removing Tl<+> and/or Cd2<+> by producing nanometer iron and manganese oxides in situ |
CN102311190A (en) * | 2011-08-19 | 2012-01-11 | 深圳市水务(集团)有限公司 | Method for removing thallium from drinking water by enhanced conventional water treatment process |
WO2016111739A1 (en) * | 2015-01-06 | 2016-07-14 | Ecolab Usa Inc. | Process for removal of selenium from water by dithionite ions |
Non-Patent Citations (2)
Title |
---|
NIELSEN P,ET AL: "Continuous removal of heavy metals from FGD wastewater in a fluidized bed without sludge generation.", 《WAT SCI TECH》 * |
路希鑫: "新生态铁锰氧化物和新生态锰氧化物去除水中痕量汞的效能及机理", 《中国博士学位论文全文数据库工程科技Ⅱ辑》 * |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109019985A (en) * | 2018-09-17 | 2018-12-18 | 上海禾元环保集团有限公司 | A kind of processing method of oil-containing heavy metal wastewater thereby industry |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
AU2010295313B2 (en) | Zero valent iron/iron oxide mineral/ferrous iron composite for treatment of a contaminated fluid | |
CN102503030A (en) | System for treating heavy metal wastewater | |
Sun et al. | Zero-valent iron for the abatement of arsenate and selenate from flowback water of hydraulic fracturing | |
KR102550935B1 (en) | Compositions and methods for the treatment and purification of aqueous wastewater streams | |
US20120241381A1 (en) | Method and apparatus for removal of selenium from water | |
US20140069872A1 (en) | Method for removing molybdate from water using an activated iron treatment system | |
Li et al. | FeOOH and nZVI combined with superconducting high gradient magnetic separation for the remediation of high-arsenic metallurgical wastewater | |
CN102234161A (en) | Method for treating high-concentration arsenic-containing wastewater | |
CN105016532A (en) | Treatment method of low concentration waste water with complexing copper | |
Thackston et al. | Lead removal with adsorbing colloid flotation | |
Trus et al. | Innovative method for water deiron ions using capillary material | |
CN108328800A (en) | A kind of removal waste water of heat-engine plant heavy metal ion method | |
Shahedi et al. | An overview of the application of electrocoagulation for mine wastewater treatment | |
CN102531094A (en) | Treatment method of wastewater containing heavy metal ions or phosphorus | |
US9994964B2 (en) | System and method for removal of metals from solution | |
RU2534108C2 (en) | Method of sorption purification of industrial running sewage and drinking water from copper cations on glauconite | |
CN100462311C (en) | Method for the removal of metals from a metal-containing aqueous medium | |
Kalin et al. | Ecological water treatment processes for underground uranium mine water: Progress after three years of operating a constructed wetland | |
JP6517570B2 (en) | Heavy metal individual separation and recovery apparatus and heavy metal individual separation and recovery method | |
Gan et al. | Efficient Removal of Antimony (V) from Antimony Mine Wastewater by Micrometer Zero-Valent Iron | |
Mohammed et al. | Remediation of heavy metals by using industrial waste by products in acid mine drainage | |
Mohammed et al. | Remediation of AMD using industrial waste adsorbents | |
Yang | Removal of Selenium From Wastewater Using ZVI and Hybrid ZVI/Iron Oxide Process | |
Ganchev et al. | Combined local system for joint purification of drinking water from iron and arsenic with limitation of the harmful substances level in rinse water | |
Okonji | Development of Adsorption Based Technology for Removal of Selenium from Industrial Wastewater |
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 | ||
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20180727 |