CN105060455B - It is a kind of that the photocatalytic method for removing Heavy Metals in Waters organic pollution can be cooperateed with based on Natural pyrite - Google Patents

It is a kind of that the photocatalytic method for removing Heavy Metals in Waters organic pollution can be cooperateed with based on Natural pyrite Download PDF

Info

Publication number
CN105060455B
CN105060455B CN201510460447.1A CN201510460447A CN105060455B CN 105060455 B CN105060455 B CN 105060455B CN 201510460447 A CN201510460447 A CN 201510460447A CN 105060455 B CN105060455 B CN 105060455B
Authority
CN
China
Prior art keywords
pyrite
malachite green
catalyst
heavy metal
heavy metals
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.)
Active
Application number
CN201510460447.1A
Other languages
Chinese (zh)
Other versions
CN105060455A (en
Inventor
刁增辉
徐向荣
孙毓鑫
刘珊
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.)
South China Sea Institute of Oceanology of CAS
Original Assignee
South China Sea Institute of Oceanology of CAS
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 South China Sea Institute of Oceanology of CAS filed Critical South China Sea Institute of Oceanology of CAS
Priority to CN201510460447.1A priority Critical patent/CN105060455B/en
Publication of CN105060455A publication Critical patent/CN105060455A/en
Application granted granted Critical
Publication of CN105060455B publication Critical patent/CN105060455B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Catalysts (AREA)

Abstract

The present invention discloses a kind of photocatalytic method that can be cooperateed with based on Natural pyrite and remove Heavy Metals in Waters organic pollution.Catalyst pyrite in the photocatalytic system, pyrite photocatalytic system is constituted after broken, grinding, sieving with ultraviolet light.The pyrite photocatalysis technology being related in the present invention, the collaboration that can be applied to Heavy Metals in Waters Cr (VI) and organic matter malachite green is removed, under ultraviolet light, malachite green and Cr (VI) clearance can reach 97% and more than 52% respectively.Pyrite photochemical catalyst has preferable repeat performance, after being reused through five times, preferable reactivity can also be kept, catalyst is fully used, the catalytic reaction operating condition being related in reaction is simple, catalyst raw material is cheap and easy to get, the pollution control theory based on the treatment of wastes with processes of wastes against one another, with preferable application prospect.

Description

One kind can cooperate with removal Heavy Metals in Waters-organic pollution based on Natural pyrite Photocatalytic method
Technical field:
The present invention relates to the method for treating water containing heavy metal-organic contamination, and in particular to one kind is based on natural yellow iron Ore deposit can cooperate with the photocatalytic method of removal Heavy Metals in Waters-organic pollution.
Background technology:
At present, developing rapidly with industry, the quick raising of economic level, the thing that the mankind ask for and discharged from nature Matter has also reached unprecedented level, considerably beyond the capacity of environment in itself, so as to cause the serious broken of Environment-Ecosystem It is bad, occur in that a series of problem of environmental pollution.In face of current severe environmental pollution situation, some are such as chemical precipitation method, thing Traditional environment restoring methods such as reason absorption method, chemical oxidization method, microorganism treatment are applied to current contaminated environment In medium, although these environment restoring methods all serve significant role to the current control of environmental pollution, these tradition Environment remediation technology all exist to some extent efficiency it is low, can not thoroughly by environmental contaminants remove or it is innoxious, easy Produce new pollution sources;Or using opereating specification it is narrow, be suitable only for specific pollutant;It is uncomfortable or energy consumption is too high, material cost is expensive Close the limitation in terms of large-scale promotion application.Thus, exploitation is efficiently, low energy consumption, low cost, environment applied widely repair Multiple Treatment process has turned into current scientific research environmental administration and has been badly in need of one of important topic of solution.
However, a kind of extensive concern for being light-catalysed technology increasingly by environmental worker, it is from 20th century 70 The emerging environment remediation Treatment process that age progressively grows up, it utilizes semiconductor oxide materials surface under light illumination Can by activation characteristic, the free radical of strong oxidizing property is produced using luminous energy, can efficiently oxidation Decomposition has in a short time Machine thing, or kill bacterium, eliminate gas with foreign flavor, or the heavy metal ion of electron reduction high price is produced, reduction heavy metal ion Toxicity.Due to photocatalysis technology have the advantages that simple to operate, reaction thoroughly, energy consumption cost is low, efficiency high and nonhazardous, recognized To be a kind of environment remediation Treatment process of most application prospect, the reparation for having been widely used for various kinds environmental pollution medium is controlled Reason field.However, the scavenging effect of photocatalysis technology is directly related to photocatalyst material, and at present, TiO2Conductor photocatalysis Technology is considered most stable, the most ripe.Except TiO2And its it is material modified outside, other photochemical catalysts such as ZnO, Al2O3、SnO2、Co3O4Deng and various composite material photocatalysts be also widely used in environmental pollution repairing and treating field, and Show good environment remediation effect.It is reported that pyrite (FeS2) can also be yellow as a kind of photocatalytic semiconductor material Iron ore band structure determines that it has good photoelectric properties, the existing phase for pyrite being applied to catalytic degradation organic pollution Close report.Moreover, pyrite particle also has good absorption property, can adsorb pollutant and remove, in addition, yellow iron Ore deposit also has stronger reproducibility, and the heavy metal ion of high price such as Cr (VI) can be reduced to Cr (III), reduces heavy metal ion Toxicity.Therefore, have in terms of having the environment remediation improvement of oxidation and the pyrite of reduction characteristic in pollution medium concurrently good Application potential.
In fact, pyrite is metal sulfide ore most commonly seen on the earth, and be prevalent in various ores and In mine tailing, and the oxidation of this mineral discharges substantial amounts of iron ion and sulfuric acid, is the main cause of acid wastewater in mine formation.And And, the economic use value of pyrite is cheap, is normally thought of as the waste minerals after mining ore dressing.However, in recent years Come, substantial amounts of domestic and international researcher directly use or transformation waste material come thing of curbing environmental pollution, and pass through experiment acquisition Good effect.Environmental pollution improvement's theory of this " treatment of wastes with processes of wastes against one another " by refuse reclamation is increasingly by people's Extensive concern.As the pyrite of mine solid waste, in terms of the improvement that should can be also applied in environmental contaminants.
However, industrial pollution source mainly has heavy metal and organic matter at present, heavy metal mainly has chromium, lead and cadmium etc., and has Machine thing mainly has phenol, chlorophenol and dyestuff etc..Pollution in actual environment is often that various heavy and organic contamination are deposited jointly A kind of combined pollution, the pollution of heavy metal-organic composite is the pollution type that biggest threat is produced to environment, in current rigorous Situation under, the environmental improvement of heavy metal-organic composite contamination characteristics is extremely urgent.Existing most of environment remediation skills Art is both for simple by heavy metal or Organic Pollution water body, and therefore, striving to find one kind can be while removes in water body The efficient context restorative procedure of heavy metal-organic contamination has become the most important subject under discussion of Environmental Science.Based on pyrite half Conductor has photochemical catalytic oxidation and reduction characteristic concurrently, using pyrite as photochemical catalyst, and collaboration removes weight in water body under ultraviolet lighting Metal-organic pollution, however, up to the present, similar patented technology has not been reported.
The content of the invention:
It is an object of the invention to provide a kind of reaction condition is simple and easy to apply, reaction is thorough, energy consumption cost is low, efficiency high profit The photocatalysis method of removal Heavy Metals in Waters-organic pollution can be cooperateed with Natural pyrite.This method can be cooperateed with effectively Heavy metal Cr (VI) and organic matter malachite green are removed, the harm of Cr (VI) and malachite green to environment is reduced;And catalyst Pyrite, which has, preferably reuses stability, and one is provided for complicated heavy metal-organic composite pollution law Plant " treatment of wastes with processes of wastes against one another " river harnessing ideas.
The present invention's can cooperate with the photocatalytic method of removal Heavy Metals in Waters-organic pollution based on Natural pyrite, its It is characterised by, comprises the following steps that:
(1), first catalyst pyrite is crushed, ground, sieved, makes its particle radius in 20~40 μ ms;
(2), water pH value of the regulation containing heavy metal Cr (VI) and organic matter malachite green;
(3), under ultraviolet light conditions, into the water body containing heavy metal Cr (VI) and organic matter malachite green, step is added Suddenly (1) treated catalyst pyrite, is reacted, and redox collaboration removes Cr (VI) and malachite green in water body.
It is preferred that, the pH value of step (2) is 2~7.
Further preferably, the pH value of step (2) is 3.
The described water body containing heavy metal Cr (VI) and organic matter malachite green, it is preferable that Cr (VI) mass concentration is 2.5~30mg/L.
The described water body containing heavy metal Cr (VI) and organic matter malachite green, it is preferable that the mass concentration of malachite green For 30mg/L.
Ultraviolet light conditions described in step (3), it is preferable that ultraviolet ray intensity is 10~20W.
Treated catalyst pyrite is added described in step (3), preferably dosage is 0.5~1.5g/L.
Progress described in step (3) is reacted, and the reaction time is preferably 100~120min.
The present invention concerted reaction principle be:Highly toxic Cr (VI) is converted into the low Cr of toxicity by reduction (Ⅲ);And then destroy chromophore by oxidation generates small organic molecule to malachite green, and it is eventually converted into water and two Carbonoxide.Water pollutant concentration after being handled through collaboration is effectively reduced, and alleviates the pressure of subsequent treatment.
It is right after being handled by the method for the present invention the water body containing heavy metal Cr (VI) and organic matter malachite green Catalyst pyrite carries out centrifugation recovery, and catalyst pyrite is reused number of times and can reach five times.
Compared with prior art, the present invention has advantages below and beneficial effect:
1st, reaction condition is simple to operate:The present invention is that catalyst Huang is added in containing Cr (VI) and the water body of malachite green Effectively it can be removed simultaneously under iron ore, normal temperature and pressure;
2nd, processing cost is low:Compared to other photochemical catalysts such as TiO2, the pyrite used in the present invention is mine solid waste, It is cheap and easily-available, and processing procedure is easy, and the environmental improvement theory of the treatment of wastes with processes of wastes against one another has a good application prospect;
3rd, react thorough:In 120min, malachite green realizes more than 97% degraded, and effectively mineralising is dioxy Change carbon and water;And Cr (VI) then has more than 52% to be converted into Cr (III), toxicity is effectively reduced;
4th, it is applicable object scope wide:The present invention is applicable not only to going for the polluted-water containing Cr (VI) or malachite green Remove, be also adapted to the removal of the polluted-water simultaneously containing Cr (VI) and malachite green.
Brief description of the drawings:
Fig. 1 is influences of the different pH to Cr (VI) and malachite green removal effect;
Fig. 2 is influence of the different catalysts amount to Cr (VI) and malachite green removal effect;
Fig. 3 is the influence that different pollutant concentrations compare Cr (VI) and malachite green removal effect;
Fig. 4 is that pyrite photocatalysis cooperates with the reuse effect for removing Cr (VI) and malachite green;
Embodiment:
Following examples are that the present invention is further illustrated, rather than limitation of the present invention.
The concentration of Cr (VI) ion in the examples below, in water sample is determined using diphenyl carbazide spectrophotometry (GB7467-87):In Cr (VI) sample solution after 10mL dilutions, 0.5mL 1 is separately added into:1 sulfuric acid solution and 0.5mL 1:1 phosphoric acid solution, shakes up;2mL 200mg/L diphenylcarbazide solution is added, is shaken up, develop the color 5~10min, At 540nm wavelength, reference is done with water, absorbance is determined.The clearance of Cr (VI) is calculated by absorbance.And malachite green Concentration use UV-VIS spectrophotometry, wavelength be 618nm locate measure absorbance change calculate its clearance.
Embodiment 1:
First catalyst pyrite is crushed, ground, sieved, makes its particle radius in 20~40 μ ms;Regulation Water pH value 2~7 containing heavy metal Cr (VI) and organic matter malachite green;It is heavy to 10mg/L is contained under ultraviolet light conditions In the water body of metal Cr (VI) and 30mg/L organic matter malachite greens, treated catalyst pyrite 1.0g/L is added, 10 Under~20W ultraviolet lights, average rate stirring is kept, is reacted, react 100~120min, redox collaboration removes water body In Cr (VI) and malachite green.Determine the change of Cr (VI) and malachite green concentration in the front and rear water body of reaction.
In the result of embodiment 1 as shown in figure 1, as seen from Figure 1, after reaction 120min, Cr (VI) and malachite green Downward trend is presented with pH rise for clearance, wherein, malachite green and Cr (VI) the clearance highest in pH=3, 97.3% and 53.1% are respectively reached.
Comparative example 1:
In this comparative example, the water body containing malachite green is individually handled using pyrite as different from Example 1, it is past Reactor adds the malachite green solution that concentration is 30mg/L, and pH value of solution regulation to 3, other conditions are same as Example 1.It is right The result of ratio 1 is as shown in table 1, as can be seen from Table 1, when pyrite individually handles malachite green solution, the removal of malachite green Rate is 76.9%, and when removing Cr (VI) and malachite green at the same time, its clearance has reached that 97.3%, Cr (VI) presence has Effect promotes the efficiency of pyrite photocatalysis malachite green, and Cr (VI) can also realize synchronous removal.
Comparative example 2:
In this comparative example, the water body containing Cr (VI) is individually handled using pyrite as different from Example 1, it is past anti- Device is answered to add Cr (VI) solution that concentration is 10mg/L, pH value of solution regulation to 3, other conditions are same as Example 1.Comparative example As shown in table 1, as can be seen from Table 1, when pyrite individually handles Cr (VI) solution, Cr (VI) clearance is 2 results 28.5%, and Cr (VI) and malachite green compound tense are being removed, its clearance has reached 53.1%, and the presence of malachite green is effective Pyrite photocatalysis Cr (VI) efficiency is promoted, and malachite green can also realize that synchronous high-efficiency is removed.
Table 1. compares for the Cr (VI) and malachite green removal effect under different technology conditions
Embodiment 2:
Difference from Example 1 is that the initial pH value of regulation polluted-water is 3, the dosage of catalyst pyrite For 0.5~1.5g/L, the change of Cr (VI) and malachite green concentration in the front and rear water body of reaction is determined.In the result of embodiment 2 such as Fig. 2 Shown, as seen from Figure 2, after reaction 120min, malachite green and Cr (VI) clearance are with pyrite photochemical catalyst The increase of dosage and elevated trend is presented, when dosage be 1.0g/L when, malachite green and Cr (VI) clearance are several Maximum is reached, when dosage is more than 1.0g/L, malachite green and Cr (VI) clearance no longer change.
Embodiment 3:
Difference from Example 1 is that the concentration ratio that adjust malachite green and Cr (VI) is 12:1~1:1, determine The change of Cr (VI) and malachite green concentration in the front and rear water body of reaction.In the result of embodiment 3 as shown in figure 3, can be seen by Fig. 3 Go out, reaction 120min after, Cr (VI) clearance declines with the reduction of concentration ratio, and the removal of malachite green take the lead in The reduction of concentration ratio and rise, when concentration ratio is more than 3:When 1, the clearance of malachite green but with the reduction of concentration ratio under Drop.Therefore, when malachite green/Cr (VI) is 3:When 1, malachite green and Cr (VI) clearance have respectively reached maximum.
Embodiment 4:
Difference from Example 1 is that the initial pH value of regulation polluted-water is 3, and reacted pyrite is carried out Reclaim five times and reused, the change of Cr (VI) and malachite green concentration in the front and rear water body of reaction is determined every time.Implementing The result of example 4 is as shown in figure 4, as seen from Figure 4, when photocatalysis reuses first three time, catalyst also maintains very in itself High activity, malachite green and Cr (VI) clearance are respectively maintained at 95% and 51% level above.After the 4th time, two The clearance of person occurs in that downward trend, but after reusing the 5th time, malachite green and Cr (VI) clearance 76.5% and 39.4% can also be reached, pyrite keeps preferable catalytic activity.

Claims (1)

1. the photocatalytic method of removal Heavy Metals in Waters-organic pollution can be cooperateed with based on Natural pyrite, it is characterised in that tool Body step is as follows:
(1), first catalyst pyrite is crushed, ground, sieved, makes its particle radius in 20~40 μ ms;
(2) water pH value containing heavy metal Cr (VI) and organic matter malachite green, is adjusted to 3;
(3), under ultraviolet light conditions, into the water body containing heavy metal Cr (VI) and organic matter malachite green, step (1) is added Treated catalyst pyrite, is reacted, and redox collaboration removes Cr (VI) and malachite green in water body;
The described water body containing heavy metal Cr (VI) and organic matter malachite green, Cr (VI) mass concentration is 30mg/L;
Ultraviolet light conditions described in step (3), ultraviolet ray intensity is 10~20W;
The treated catalyst pyrite of step (1) is added described in step (3), dosage is 0.5~1.5g/L;
Progress described in step (3) is reacted, and the reaction time is 100~120min.
CN201510460447.1A 2015-07-29 2015-07-29 It is a kind of that the photocatalytic method for removing Heavy Metals in Waters organic pollution can be cooperateed with based on Natural pyrite Active CN105060455B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510460447.1A CN105060455B (en) 2015-07-29 2015-07-29 It is a kind of that the photocatalytic method for removing Heavy Metals in Waters organic pollution can be cooperateed with based on Natural pyrite

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510460447.1A CN105060455B (en) 2015-07-29 2015-07-29 It is a kind of that the photocatalytic method for removing Heavy Metals in Waters organic pollution can be cooperateed with based on Natural pyrite

Publications (2)

Publication Number Publication Date
CN105060455A CN105060455A (en) 2015-11-18
CN105060455B true CN105060455B (en) 2017-08-25

Family

ID=54490046

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510460447.1A Active CN105060455B (en) 2015-07-29 2015-07-29 It is a kind of that the photocatalytic method for removing Heavy Metals in Waters organic pollution can be cooperateed with based on Natural pyrite

Country Status (1)

Country Link
CN (1) CN105060455B (en)

Families Citing this family (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105458294B (en) * 2016-01-18 2018-11-23 中国科学院南海海洋研究所 A kind of iron standby nano zero valence iron and the preparation method and application thereof using in acidic mine waste water
CN106957078B (en) * 2017-02-17 2020-06-12 湖南有色金属研究院 Method for degrading residual agent in beneficiation wastewater by photocatalytic semiconductor sulfide ore based on iron-oxidizing bacteria
CN107611009B (en) * 2017-08-30 2020-10-13 尚妙根 Preparation method of zinc oxide composite semiconductor material
CN108439533B (en) * 2018-05-03 2020-07-28 温州大学苍南研究院 Method for treating trivalent chromium complex wastewater by reducing composite medicament and combining ultraviolet light and synchronously recycling chromium
CN110918102A (en) * 2019-12-10 2020-03-27 桂林理工大学 Preparation method of graphene oxide modified metal sulfide composite photocatalyst
CN112642576B (en) * 2020-09-17 2022-02-01 中南大学 Selective oxidation and flotation separation method for pyrite gangue in sulfide ore
CN112206790B (en) * 2020-11-12 2022-04-22 厦门理工学院 Preparation method and application of modified pyrite with photocatalytic performance
CN113060817B (en) * 2021-03-18 2022-08-16 中南大学 Method for treating chromium-containing electroplating wastewater by using mineral modified material
CN113880218B (en) * 2021-10-12 2022-11-29 中南大学 Utilize organic dyestuff effluent disposal system of pyrite tailing
NL2031328B1 (en) 2022-03-18 2023-09-29 Univ Wageningen Process for the generation of hydrogen sulfide in the presence of pyrite as catalyst
CN114702117B (en) * 2022-05-20 2023-08-29 中国地质大学(北京) Method for simultaneously removing mine heavy metals and organic pollutants by utilizing iron-containing solid wastes

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1040968A (en) * 1988-09-06 1990-04-04 厦门大学 A kind of method of photocatalysis treatment of waste water

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1040968A (en) * 1988-09-06 1990-04-04 厦门大学 A kind of method of photocatalysis treatment of waste water

Also Published As

Publication number Publication date
CN105060455A (en) 2015-11-18

Similar Documents

Publication Publication Date Title
CN105060455B (en) It is a kind of that the photocatalytic method for removing Heavy Metals in Waters organic pollution can be cooperateed with based on Natural pyrite
Li et al. Microwave-enhanced Mn-Fenton process for the removal of BPA in water
Kositzi et al. Solar photocatalytic treatment of simulated dyestuff effluents
CN108993475B (en) Ternary composite material heterogeneous light Fenton catalyst and preparation and application thereof
CN112194236A (en) Method for treating salt-containing degradation-resistant wastewater by activating peroxymonosulfate through biochar-copper oxide composite material
CN102690005A (en) Method for treating organic wastewater through photoelectric catalytic oxidation
CN109721148A (en) A kind of catalytic ozonation water treatment technology and application method that ability is cut down with bromate of heterojunction boundary electron transmission induction
Gaur et al. Recent advances in the elimination of persistent organic pollutants by photocatalysis
CN108341477A (en) The method of Combined Treatment industrial emissions
CN111974404A (en) Photo-assisted BiFe1-xCuxO3Method for treating residual ciprofloxacin in water body by activated peroxymonosulfate
CN105458294A (en) Nanometer zero-valent iron prepared from iron in acid mine wastewater and preparing method and application thereof
Muthukumar et al. Process optimization, characterization and economic evaluation of nanoparticles derived from galvanic sludge for photodegradation of 4-nitrophenol under natural sunlight
CN105174423B (en) A kind of coal chemical industry biochemical tail water processing method
CN111410237B (en) Method for recycling waste polluted biomass
CN106277274B (en) Method for treating heavy metal ion-containing wastewater by mixing pyrite and zero-valent iron
CN108479741A (en) A kind of sludge prepares method and catalyst and the application of heterogeneous lightwave CATV catalyst
CN115608322B (en) Preparation and application methods of regenerable adsorbent for cooperatively removing heavy metals and new organic pollutants in water
US5332508A (en) Reversible photodeposition and dissolution of metal ions
CN111215116A (en) 3D defect carbon nitride photocatalytic material and preparation method and application thereof
Al Mashari et al. Characterization and Photocatalytic Treatment of Oil Produced Water Using TiO2
CN112225305B (en) Vanadium-titanium blast furnace waste residue powder, preparation method thereof and method for removing antibiotics by using vanadium-titanium blast furnace waste residue powder
Khader et al. Recent Advances in Photocatalytic Advanced Oxidation Processes for Organic Compound Degradation: A Review
CN105174527B (en) Method for carrying out selective oxidation treatment on beneficiation wastewater
Hudaya et al. THE SIMULTANEOUS REMOVAL OF CYANIDE AND CADMIUM IONS FROM ELECTROPLATING WASTEWATER USING UV/TIO 2 PHOTOCATALYSIS.
Weldegebrieal et al. 5 Photocatalytic degradation of organic contaminants in wastewater treatment

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant