CA1241524A - Abatement of indoor formaldehyde vapour and other indoor gaseous pollutants - Google Patents

Abatement of indoor formaldehyde vapour and other indoor gaseous pollutants

Info

Publication number
CA1241524A
CA1241524A CA000472473A CA472473A CA1241524A CA 1241524 A CA1241524 A CA 1241524A CA 000472473 A CA000472473 A CA 000472473A CA 472473 A CA472473 A CA 472473A CA 1241524 A CA1241524 A CA 1241524A
Authority
CA
Canada
Prior art keywords
formaldehyde
coating
indoor
filter
water soluble
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.)
Expired
Application number
CA000472473A
Other languages
French (fr)
Inventor
Hyman D. Gesser
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to CA000472473A priority Critical patent/CA1241524A/en
Priority to US07/235,493 priority patent/US4892719A/en
Application granted granted Critical
Publication of CA1241524A publication Critical patent/CA1241524A/en
Expired legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/72Organic compounds not provided for in groups B01D53/48 - B01D53/70, e.g. hydrocarbons
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/508Sulfur oxides by treating the gases with solids
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/52Hydrogen sulfide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/54Nitrogen compounds
    • B01D53/56Nitrogen oxides

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
  • Treating Waste Gases (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

ABSTRACT
Indoor pollutants such as formaldehyde can be removed from a house by a reactive method consisting of a coating on a furnace filter in a forced air heating system. The coating is a polymeric substance with specific functional groups which react with the pollutant and which in the case of formaldehyde or other aldehydes such as acrolein or acetaldehyde would be a polymeric amine such as polyethylenimine. In other cases it is possible to incorporate such polymeric amines into a paint which when applied to walls and ceilings can act as a reactive "sink" for aldehydes.

Description

TIE AB.~,Tl.~lEr.l (`,F INI~()OR, F( R~I~LDEHYDE VAPOUR ~NI) OTHER in R c.~sr~ POI,LUT/~NTS
2~15~4 ABSTRACT
Indoor pollutants such as formaldehyde can be removed from a house by a reactive method consisting of a coating on a furnace filter in a forced air heating system. The coating is a polymeric substance with specific functional groups which react with the pollutant and which in the case of formaldehyde or other aldehydes such as acrolein or acetaldehyde would be a polymeric amine such as polyethylenimine. In other cases it is possible to incorporate such polymeric amines into a paint which when applied to walls and ceilings can act as a reactive "sink" for aldehydes.

BACKGROUND OF THE INVENTION
This invention is related to a simple, new and useful method whereby some or all of a specific indoor pollutant can be removed.
Conventional methods usually involve the adsorption of such pollutants onro ac-,ivated surfaces such as charcoal, silica gel, alumina or other materials with large surface areas, (see R. E. Goddard & J. A.
Coles, Canadian Patent #626,216 and J. W. ~asmark Jr., M. L. Dooley A. I. Jones, U.S. Patent #4,227,904).
Another conventional method is to use a solution to react with the speeifie gas, see M. A. Rise, Canadian Patent #643,062).
Such methods are usually non-specific and quite expensive to produee and operate. In the case where aqueous solutions are used the air beeomes saturated with water and hlgher humidity levels result. In the case of adsorption systems, the pollutant, usually present in tracc quantities, must complete with oxygen, nitrogen, carbon dioxide and 5~
wear in the air in order to be adsorbed to a signiflcant cxtent. The adsorption i9 also eempcrature depcndent and not always complete as ar &S che pollutant is concerned.
Tllough Gaylord (US #4,374,~14) has described a reactive coating to remove formaldehyde, his polyhydric water-solublc polymers requires moisture as well as an acidic or basic catalyst to effect reaction between formaldehyde and the coated polymer. Furthermore, the reduction of formaldehyde by Gaylord is far from complcte and residual levels are in excess of the acceptad TLV level of O.l ppm. This invention describes a method whereby the levels of aldehyde and in particular formaldehyde can be reduced to levels far below the Toxic level (TLV =
O.10 ppm).

So RY OF T-~E INVENTION
.
The present invention describes a simple and efficient method of removing indoor pollutants by allowing them to react with a polymeric substance which contains a specific functional groups which react with and form chemical b^nds with the specific pollutant. Different functional groups can be used for different pollutants. Acidic carboxylic acid groups (-COOH) or sulfonic acid groups (-SO3H) can rewove basic gases such as ammonia, or amines, whereas basic groups such as amines can remove acidic gases such as hydrogen halides.
Since the polymer is non-volatile and of high molecular weight the product of the reaction between the pollutant and the functionalized polymer is a solid and the result is that the pollutant is removed from the air. The polymer, which can be coated onto an air filter or incorporated into a paint, does not contribute gases to the air nor is its reactivity impaired by the presence of other gases. The use of two coated filters in series, each treated with different functionalized polymers could be used to remove different pollutants. Similarly using ceiling paint which has different reactive polymer than that used in wall paint may similarly remove different gases.

DESCRIPTION OF THE PREFERRED ~BODI~ T
I have shown that a typical pollutant such as formilldehyde, which mav come from che decomposition of uraa-formflldeh~dc foam insulation or 12~52~
from the resin used in plywood or particle hoard, can be removed by passing toe air in the house through a fiber-glass filtcr coated with a thin layer of a polymeric amine such 2S polyethylenimine.
ol~ethylenimine is a water soluble polymer with primary and secondary amine functional groups which react with aldehydes as well as acidic gases.
Many houses use a forced air furnace as a means of supplying heat.
Such furnaces heat air which is clrculated through the house by means of a fan and which usually includes a filter to remove the dust and particulate matter in the house. By coating such a filter with a polymeric substance having suitable functional groups, it is possible to remove the pollutant from the air as it is circulated through the filter. Open cell polyurethane foam filters can also be treated in this manner. The coated filter must be replaced periodically, usually after about a month, more or less, depending on the concentration of the pollutant in the air, the size of the house, the size of the filter and the amount of polymeric coating applied.

Example 1.
The air in a two storey house was analyzed during a three month period and was shown to have formaldehyde levels of from 0.030 to O.lOQ
ppm due to the presence of urea-formaldehyde foam insulation. A
fiber-glass filter, 20" x 25" x 1" was coated with about 6 grams of polyethylenimine. This was done by spraying the filter with about 150 mL of a 5% solution of the polymer in water and allowing the filter to dry. The filter was then installed in the furnace and the`furnace fan run for one week. Analysis for formaldehyde in the air then gave undetectable levels, i.e. less than 0.001 ppm.

Example 2.
The air in a three storey split-level house was analyzed for formaldehyde and was shown to have levels of from 0.050 to 0.140 ppm due to the presence of urea-formaldehyde foam insulation. A fiber-glass filter 16" x 20" x 1" was treated with about 150 mL of a 5~ solutinn of polyethylenimine and allowed to dry leaving about 6.5 grams of polymer on the filter. The filter was then installed in the furnace and the fan ~LZ~ i24 run. After one wee tho levels of formaldehyde in the air were shown to be 0.008, 0.000, 0.000 end o.noo ppm.

Other polymeric amines and some hydrazines which are cqually effective in trapping aldehydes are polyvinylamine and polyethylene hydrazine though many Gore can be prepared.

TABI,E 1 Results of Formaldehyde Abatement in House with Treated Furnace Filters 1) Polyethyleneimine Condition [HCH0l~L/L

House A. Initial 0.090 After Filter in Use 6 days0.005 After 4 days without filter 0.083 After Filter in Use 5 days0.010 House B. Initial 0.102 After Filter in Use 12 days 0.036 After 6 days without filter 0.084 -I After Filter in Use 6 days0.005 :
2) Polyethylenehydrazine souse C. Initial 0.159 After Filter in Use 4 days0.064 After Filter in Use 3 more days 0.005 House D. Initial 0.136 After Filter in Use 4 days 0.013 Table l shows the results of some additional tests on two typical housas.
The reactive coating on the surface of the filter can soon become exhausted by reaction and for the coating to be of further use, the pollutant must diffuse through the solidified coating. This is a slow process and as a result the effectiveness of the coRting i8 thus reduced. This dcfect can bc nllevlnted by softening the coating with a 5~ 41~524 plasticirer such as ethylene gl~col, glycerol9 diethylelleglycol or propylene glyco]. These water solublc polyols allow the reactive polymer to diffuse within the coating and allows the exchange betwcen surface and bulk material.
It is also possible for the functionalizecl polymer to be incorporated into a paint that is applied to the walls and ceilings of a house. The pollutants can diffuse through the outer layer of the paint and react with the polymer forming chemical bonds thereby being removed from the air. Aldehydes such as acrolein and acetaldehyde which are often present in houses (see Indoor Pollutants, rational Academy Press, Washington, D.C, 1981) are also removed by polyethylenimine or the ebove polymeric amines and hydrazines.

Example 3.
A one storey bungalow (with basement) which had urea formaldehyde foam insulation had levels of formaldehyde where were from 0.085 to 0.120 ppm. When a fiber glass filter ~16" x 20" x 1") was treated with polyethylenimine, 150 mL of 5% PEI in water (6.2 g on filter) the level OI formaldehyde dropped to 0.015 ppm within a week but after an additional 10 days rose to 0.095 ppm. When a similar filter was treated with 150 mL of a 5~ polyethylenimine solution of glycerol/water, 30/70 by volume, the level of formaldehyde remained below 0.040 ppm for one month.

The use of plasticizers in paint is not desirable but other elastomers or softening agents such as latex can be used to facilitate diffusion within the coating and thereby extend the useful life of the paint as a trap for pollutants.
Since various modifications can be made in my invention as herein above described, and many apparently widely different embodiments of same made within the spirit and scope of the claims without departing from such spirit and scope, it is intended that all matter contained in the accompanying specification shall be interpreted as illustrative only and not in a limiting sense.

Claims (10)

I. Claim:
1. A method of reducing the indoor air concentration of aldehyde vapour by coating a porous support filter with water soluble polymeric amine to which a water soluble low-volatile liquid plasticizer is added to render the coating soft and flexible and passing the indoor air through said support filter.
2. A method according to Claim 1, in which the polymeric amine has primary amino functional groups (?NH2).
3. A method according to claim 1 in which the polymeric amine is selected from the group consisting of polyethyleneimine and polyvinylamine.
4. A method according to Claim 1 in which the aldehyde is selected from the group consisting of formaldehyde, acetaldehyde and acrolein.
5. A method according to Claim 1 in which the low volatile liquid plasticizer is glycerol, ethylene glycol, diethylene glycol and propylene glycol or mixtures of these.
6. A method of reducing the indoor air concentration of aldehydes by coating a porous support filter with a water soluble polymeric hydrazine to which a water soluble low-volatile plasticizer is added to render the coating soft and flexible and passing the indoor air through said support filter.
7. A method according to Claim 6 in which the aldehyde is selected from the group consisting of formaldehyde, acetaldehye and acrolein.
8. A method according to Claim 6 in which the low volatile plasticizer is selected from the group consisting of glycerol, ethylene glycol, diethylene glycol, and propylene glycol or mixtures of these.
9. A method of reducing the indoor air concentration of aldehydes by allowing the air containing the aldehyde to come into contact with polymers having primary amino (-NH2) or hydrazine (-NH-NH2, and -N-NH2) functional groups to which a water soluble low volatile liquid plasticizer is added.
10. A method according to Claim 9 in which the polymer is water insoluble and incorporated into a paint which is applied to the indoor walls and ceilings of a house or building.
CA000472473A 1985-01-21 1985-01-21 Abatement of indoor formaldehyde vapour and other indoor gaseous pollutants Expired CA1241524A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
CA000472473A CA1241524A (en) 1985-01-21 1985-01-21 Abatement of indoor formaldehyde vapour and other indoor gaseous pollutants
US07/235,493 US4892719A (en) 1985-01-21 1988-08-24 Removal of aldehydes and acidic gases from indoor air

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CA000472473A CA1241524A (en) 1985-01-21 1985-01-21 Abatement of indoor formaldehyde vapour and other indoor gaseous pollutants

Publications (1)

Publication Number Publication Date
CA1241524A true CA1241524A (en) 1988-09-06

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Country Link
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CA (1) CA1241524A (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4892719A (en) * 1985-01-21 1990-01-09 Gesser Hyman D Removal of aldehydes and acidic gases from indoor air

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Publication number Priority date Publication date Assignee Title
US4892719A (en) * 1985-01-21 1990-01-09 Gesser Hyman D Removal of aldehydes and acidic gases from indoor air

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