CN1105797A - Flocculant composition for removing trihalomethane and its precursors - Google Patents
Flocculant composition for removing trihalomethane and its precursors Download PDFInfo
- Publication number
- CN1105797A CN1105797A CN94190129A CN94190129A CN1105797A CN 1105797 A CN1105797 A CN 1105797A CN 94190129 A CN94190129 A CN 94190129A CN 94190129 A CN94190129 A CN 94190129A CN 1105797 A CN1105797 A CN 1105797A
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- China
- Prior art keywords
- water
- soluble
- agglutinant
- composition
- salt
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- 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.)
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Classifications
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
- C02F1/5245—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
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- Chemical & Material Sciences (AREA)
- Inorganic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
This invention relates to a flocculent composition which so functions as an effective flocculant for flocculating and removing floating matter and detrimental metals when added to industrial wastes, sewage, raw water of service water, etc., removes effectively THMs and their precursors, and serves as a water purification agent. The present invention provides a novel flocculant composition which contains water-soluble aluminum salts, water-soluble iron salts and water-soluble magnesium salts in the proportions of Al, Fe, and Mg of 1, 0.01 to 2, and 0.01 to 2, respectively, in terms of atomic weight, and the sum of their oxides, Al2O3, Fe2O3, and MgO, amounts to 1 to 15 wt%.
Description
The present invention relates to the field of purification at the water source etc. of sanitary wastewaters such as various industrial wastewaters such as chemistry, metal, fiber, papermaking, food, urban sewage and tap water.
Have before inorganic system and the organic system as general agglutinant.The former has Tai-Ace S 150 (Al
2(SO
4)
3), POLY ALUMINIUM CHLORIDE (hereinafter to be referred as PAS) etc., various macromolecular compounds are arranged among the latter.Flocculant composition of the present invention (hereinafter to be referred as composition) belongs to inorganic system.
As the agglutinant of inorganic system, require aggegation effect height to suspended substance, the residual quantity of poisonous metal after handling in the water and aluminium, iron etc. is low.More require low residual quantity at tap water in the processing at water source.
In tap water is handled with the water source, use the inorganic agglutinant of aluminium system mostly, have the problem of the aluminium of residual minim in the water after handling, we can say that also this is the reason of Alzheimer's disease.
And, now in the water of tap water, have CHCl
3, CHCl
2Br, CHClBr
2, CHBr
3Deng the problem of three methyl halides (hereinafter to be referred as THMs), the viewpoint from health care is regarded as worldwide problem, so just becoming the standard of restriction.
Because the aluminium of the inorganic system of the general use of the processing at tap water water source is agglutinant, so remove THM with it
sAnd the precursor of humic acid (Humic Acid) etc. is difficult.
For head it off, not using becomes THM
sGenerate the chlorine sterilization of reason, attempt the part use and utilize ozone or ClO
2Deng the oxidation disinfection method.Yet these sterilant have its security still unconfirmed, and the problem of ultra-high price of its handling.
The objective of the invention is, provide and add in industrial wastewater, the sanitary wastewater etc., when effectively agglutinant works as the aggegation of suspended substance, the removal of poisonous metal etc., become and remove THM effectively
sAnd the flocculant composition of the water purification agent of the tap water of precursor etc.
The inventor etc. are in order to solve aforesaid technical background and problem, and reach its purpose, carried out secular experimental study, found that, by using water-soluble aluminum salt and water-soluble molysite and water-soluble magnesium salt, press atomic molar ratio, with respect to Al1, contain Fe0.01-2.2, Mg0.01-2, its oxide compound Al
2O
3, Fe
2O
3, MgO adds up to the new flocculant composition of 1-15% (weight), can address the above problem this surprising fact effectively.
The raw material of composition
As the raw material of the present composition, use the water soluble salt of aluminium, iron, magnesium.For these salts, the solid matter and the solution shape of anhydride, hydrate, double salt etc. can use.In addition, in the environment of the state of oxidation, use the solution of the reactant that obtains with inorganic salt such as hydrochloric acid, nitric acid, sulfuric acid (mineral acid) independent aluminium, iron, magnesium metal or their mixture of processing or anhydride, the hydrate that this solution drying is obtained, exemplifying particularly, is AlCl as Al salt
3-6H
2O, Al (NO
3)
3, Al
2(SO
4)
3, Al
2(SO
4)
3-18H
2O, Al (NH
4) (SO
4)
2-18H
2O etc. as Fe salt, it is desirable to 3 valency Fe salt, FeCl
3, FeCl
3-6H
2O, Fe (NO
3)
3, Fe
2(SO
4)
3, Fe
2(SO
4)
3XH
2O, Fe (NH
4) (SO
4)
26-12H
2O or divalent Fe salt, FeSO
47H
2O etc.As Mg salt MgCl is arranged
2, MgCl
26H
2O, MgSO
4, MgSO
47H
2Anhydrides such as O, hydrate, double salt etc.
In addition, also can use the mineral acid resolvent that contains Al, Fe, Mg mineral.For example, vermiculite (Vvrmiculite) generally contains Al
2O
310-18%, Fe
2O
310-18%, MgO5-20%, other oxide compound and 44-75% such as moisture.
The mineral acid resolvent of these mineral can use.
The composition of agglutinant
Agglutinant of the present invention is pressed atomic molar ratio, with respect to Al1, contains Fe0.01-2, Mg0.01-2, its oxide compound Al
2O
3, Fe
2O
3, MgO the composition that adds up to 1-15% (weight) be suitable, effect is little beyond this scope.
The conditioning agent of these compositions be by the mixing of various water-soluble Al, Fe, Mg or contain the resolvent of Al, Fe, Mg mineral and in this resolvent supplementary feed dissolubility Al, Fe, Mg salt prepare.
Agglutinant make usage
The present composition make usage, use with the method identical with general inorganic agglutinant.Though also can use as solid mixt, use to well to make its aqueous solution.
In waste water and water source, add composition solution while stirring, pH is adjusted to about 7, leave standstill after the stirring, make suspended substance and other material aggegations, separate according to usual method.
The usage quantity of composition
The usage quantity of the present composition is according to contaminated water source degree, turbidity and different, as following, and comprehensive purifying effect height.
As this composition, press atomic molar ratio, with respect to Al1, the aqueous solution that adds up to 5-10% (weight) concentration of Fe0.1-0.3, Mg0.1-0.3, oxide compound with respect to waste water, water source, uses to add about 50-300ppm, and its effect is good.
The effect of invention
The aggegation effect
As the Tai-Ace S 150 of general inorganic agglutinant, PAC etc. is good agglutinant, but also requires better aggegation effect.
The present composition possesses THM
sAnd the removal ability of precursor, not poor such as above-mentioned described common goods aspect cohesive force, can expect the mutual effect that Al, Fe, Mg coexist on the contrary.Promptly owing to the existence of Fe salt, throw out increases, because the possibility of performance ensemble tendency is big, so improved the sedimentation speed of throw out, has improved the effect of purifying waste water.
The existence of Mg more encourages this tendency.
The removal effect of metal species
Original inorganic agglutinant has the ability of removing poisonous metal, but since the kind difference at waste water, water source, the tendency that these metals have trace to exist.
The ability of the removal poisonous metal of the present composition is poor unlike common goods, and the cohesive force that produces owing to the interaction of Al, Fe, Mg improves, and the effect that these metals are removed in expection improves.In addition, the remaining quantity of Al, Fe in the water after agglutinant is handled is micro-, reaches negligible degree.
THM
sAnd the removal effect of precursor
According to above-mentioned such, common agglutinant is removed THM
sAnd precursor is inconvenient.
This THM
sHave global restriction tendency, its limits value is below the 50-100ppb.
The inventor can remove THM effectively in order to develop
sAnd precursor, test.Enumerating one of this test for example descends.
Test conditions 1) corpse or other object for laboratory examination and chemical testing sample-artificial kaolin turbidity 50mg/l
Humic acid 5mg/l
2) adjust pH 7.0
3) water temperature is 13.2 ℃
4) add chlorine liquid concentration (cl concn) 10mg/l
5) 1 hour duration of contact of chlorine
6) agglutinant addition 215ppm
Trial value
Table 1
Trial value
The agglutinant kind | Oxide concentration (%) | Agglutinant addition (ppm) | The residual amount of THMS |
????PAC ????Al 2(SO 4) 3Al, Fe salt mixture Al, Fe, Mg mixture | ??Al 2O 310 " 8 Al; Fe oxide compound 8 Al; Fe, Mg oxide compound 8 | ?????215 ?????″ ?????????″ ?????????″ | ?????120.4 ?????69.5 ?????28.6 ?????19.3 |
Test-results is as shown in table 1 to be compared with common agglutinant like that, can learn the THM of Al, Fe system and Al, Fe, Mg system
sResidual amount significantly low.
Because the THM of Al, Fe, Mg system
sResidual amount is significantly lower than Al, Fe system, and the inventor etc.s are in order to confirm the effect of Mg, with following condition fixedly Al, Fe, makes the Mg activation, experimentizes, and the concentration of each composition when oxide compound always measures when being 8%, obtains result as shown in Figure 1.
As seeing, find along with the Mg amount increases remaining THM at Fig. 1
sAmount reduces, and the effect of Mg is very significant.
Provide the present composition according to such surprising discovery, thought THM
sRemoval effect be very remarkable.
Economical effectiveness
The present composition has removal THM when showing good aggegation effect
sAnd the ability of precursor, and aspect cost of material, comparing with Al salt, Fe, Mg salt are cheaper.In addition, also can utilize the mineral that contain Al, Fe, Mg, its economic benefit is big.
The simple declaration of accompanying drawing
Fig. 1 is the THM that the interpolation ratio of Mg is followed in expression
sThe graphic representation of removal effect.
Enumerate embodiments of the invention below
Embodiment 1
With following condition the sample that should check in waste water and the tap water water source is experimentized.
1. implementation condition 1) check a) artificial kaolin turbidity 50mg/l of sample
B) Hg, Cd, Cr, each 1mg/l of Pd concentration
C) humic acid 5mg/l
2) adjust pH 7.0
3) water temperature is 15 ℃
4) chlorine treatment solution cl concn 10mg/l
5) 1 hour duration of contact of chlorine
6) assay method-atomic absorption spectroscopy photometer agglutinant addition 286ppm7)
THM
s-gas chromatography
The ECD detector
2. measured value
Table 2
The agglutinant kind | Atomic molar ratio | Oxide concentration (%) | The residual amount of THMS | The residual amount of Al.Fe (PPm) | Metal removal rate (%) | ||||
??Al∶Fe∶Mg | ??(ppb) | ????Al | ????Fe | ??Cd | ??Cr | ??Hg | ??Pb | ||
??PAC | ??1 | ????Al 2O 3?10 | ??77.7 | ????0.11 | ????0.02 | ??99.5 | ??100 | ??63 | ??100 |
Al, Fe system | ??1∶0.2∶0 | ????Al 2O 3?8 ????Fe 2O 3 | ??22.5 | ????0.10 | ????0.02 | ??99.8 | ??99.5 | ??76 | ??100 |
Present composition Al.Fe.Mg system | ??1∶02∶0.1 | ????Al 2O 3????Fe 2O 3?8 ????MgO | ??8.4 | ????ND | ????0.01 | ??99.7 | ??100 | ??78 | ??100 |
(ND): can not detect
As shown in table 2, composition of the present invention is compared with common goods as agglutinant, shows equal or the THMs on it removes effect.
Embodiment 2
Producing vermiculite (Al with mineral acid treatment Korea S
2O
310-12, Fe
2O
311-13, MgO6-7, other materials 73-68wt%) extract (proportion 1.18, Al
2O
32.1, Fe
2O
31.8, MgO0.63, other oxide compounds 0.43wt%) in add various salts, experimentize with the condition identical with embodiment 1.
But the add-on of various agglutinants is 200ppm.
Table 3
The agglutinant kind | Atomic molar ratio Al: Fe: Mg | Oxide concentration (%) | The residual amount of THMS (PPb) | Al, the residual amount of Fe (PPm) | Metal removal rate (%) | ||||
????Al | ????Fe | ??Cd | ??Cr | ??Mg | ??Pb | ||||
???Al 2(SO 4) 3 | ????1 | ?????Al 2O 3?8 | ???59.8 | ????0.25 | ????0.02 | ??99.6 | ??99.7 | ??70 | ??100 |
???Al 2, Fe system | ????1∶0.2∶0 | ?????Al 2O 3?8 ?????Fe 2O 3 | ???26.9 | ????0.06 | ????0.01 | ??99.8 | ??99.3 | ??72 | ??100 |
Present composition Al, Fe, Mg system | ????1∶0.2∶0.1 | ?????Al 2O 3?????Fe 2O 3?8 ?????MgO | ???19.7 | ????ND | ????0.01 | ??99.7 | ??100 | ??75 | ??100 |
(ND): can not detect
(ND): can not detect
As in table 3, seeing, even composition of the present invention is made adjustment as agglutinant from the sour resolvent of mineral, compare with goods in the past, also show equal or the effect on it, THM
sThe removal effect height.In addition, use the hydrochloric acid of vermiculite or the extracting solution of nitric acid to show identical degree.
Embodiment 3
With vermiculite and inorganic acid reaction and extractives (the atomic molar ratio Al: Fe: Mg=1: 1 of the present composition that obtains, 14: 0.34, oxide compound adds up to 5wt%), add the industrial wastewater (pH4 that contains heavy metal to 300ppm, Cr5ppm, Ni8ppm) in, adjust to pH7 with lime oil, handle according to customary way, can be purified liquid (pH7, Cr0.45, Ni0.67ppm) this moment.
This has sufficient decontamination effect improving as inorganic agglutinant as can be seen.
Embodiment 4
At urban sewage (pH6.5, SS120ppm, BOD210ppm, coliform (410 * 10
5/ 100ml) in, add the sulfuric acid reaction thing (atomic molar ratio Al, Fe, Mg=1: 0.27: 0.07, oxide compound total 8.7wt%) of vermiculite with 100ppm, pH is adjusted to 7.0, the result who handles with usual method, be purified liquid (pH7.0, SS 10.2, BOD 17ppm, coliform (4 * 10
2/ 100ml).Show sufficient decontamination effect improving as inorganic agglutinant as can be seen.Original paper lacks accompanying drawing
Claims (2)
1. can remove the heavy metal in the water and the flocculant composition of three methyl halides and precursor thereof efficiently, it contains water-soluble aluminum salt and water-soluble molysite and water-soluble magnesium salt, presses atomic molar ratio, with respect to Al1, contains Fe0.01-2, Mg0.01-2, its oxide compound Al
2O
3, Fe
2O
3, MgO add up to 1-15% (weight).
2. the agglutinant of the water-soluble aluminum salt of claim 1 and water-soluble molysite and water-soluble magnesium salt, wherein be to append water-soluble aluminum salt and water-soluble molysite and water-soluble magnesium salt respectively in the mineral acid resolvent of the vermiculite (vermiculite) of the mineral that contain aluminium, iron, magnesium, the ratio of Al, Fe, Mg of adjusting claim 1 is to making with claim 1 same concentrations.
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR3995/1993 | 1993-03-16 | ||
KR3995/93 | 1993-03-16 | ||
KR1019930003995A KR960008085B1 (en) | 1993-03-16 | 1993-03-16 | Coagulant for tri-halomethane elimination |
Publications (2)
Publication Number | Publication Date |
---|---|
CN1105797A true CN1105797A (en) | 1995-07-26 |
CN1070721C CN1070721C (en) | 2001-09-12 |
Family
ID=19352245
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN94190129A Expired - Fee Related CN1070721C (en) | 1993-03-16 | 1994-03-09 | Flocculant composition for removing trihalomethane and its precursors |
Country Status (5)
Country | Link |
---|---|
JP (1) | JP2788552B2 (en) |
KR (1) | KR960008085B1 (en) |
CN (1) | CN1070721C (en) |
RU (1) | RU94046154A (en) |
WO (1) | WO1994021349A1 (en) |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2004502621A (en) * | 1999-12-02 | 2004-01-29 | ミノックス コーポレイション ユーエスエイ | Inorganic oxide liquid concentrate for water and wastewater treatment |
US7473409B2 (en) * | 2006-08-30 | 2009-01-06 | Veolia Es Technical Solutions L.L.C. | Process for recycling waste acid |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS57184489A (en) * | 1981-05-08 | 1982-11-13 | Asahi Glass Co Ltd | Purification of waste water containing turbid substance and phosphorus component |
JPS62234511A (en) * | 1986-04-02 | 1987-10-14 | Jitsuo Inagaki | Flocculating agent for precipitation |
JPS6344993A (en) * | 1986-08-12 | 1988-02-25 | Asao Shimanishi | Method for removing organic substance of the like dissolved in sewage |
CN1009990B (en) * | 1988-04-09 | 1990-10-17 | 冶金工业部建筑研究总院 | Mg-fe compound type waste-water processing agent and its production method |
-
1993
- 1993-03-16 KR KR1019930003995A patent/KR960008085B1/en not_active IP Right Cessation
-
1994
- 1994-03-09 WO PCT/KR1994/000018 patent/WO1994021349A1/en unknown
- 1994-03-09 CN CN94190129A patent/CN1070721C/en not_active Expired - Fee Related
- 1994-03-09 RU RU94046154/25A patent/RU94046154A/en unknown
- 1994-03-09 JP JP6520886A patent/JP2788552B2/en not_active Expired - Lifetime
Also Published As
Publication number | Publication date |
---|---|
RU94046154A (en) | 1996-12-20 |
WO1994021349A1 (en) | 1994-09-29 |
KR940021432A (en) | 1994-10-17 |
KR960008085B1 (en) | 1996-06-19 |
CN1070721C (en) | 2001-09-12 |
JP2788552B2 (en) | 1998-08-20 |
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