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emissions. Secondary formation of formaldehyde occurs in the atmosphere through the photochemical oxidation of natural and anthropogenic volatile organic compounds (VOCs) in the air.
Formaldehyde is used predominantly in the synthesis of resins, with urea-formaldehyde resins, phenolic-formaldehyde resins, pentaerythritol, and other resins accounting for the major use of Canadian consumption. They are used to manufacture building materials and numerous household products such as plastics, adhesives, paints, varnishes, dyes and fertilizers etc... Because formaldehyde is also a product of combustion, fuel-burning devices like woodstoves, fireplaces, gas stove or kerosene space heaters can also be potential sources.
Some common indoor sources of formaldehyde:
| • |
Tobacco smoke: cigarettes, cigars |
| • |
Heating devices: woodstove, fireplaces, kerosene heaters, gas stoves |
| • |
Pressed wood products: particle boards, medium density fibreboards and plywood that use adhesives containing formaldehyde |
| • |
Furniture, cabinetry and floor products that used pressed wood products and/or acid-catalyzed urea-formaldehyde type finishes |
| • |
Household products: wallpaper, paint, coatings, cardboard and other paper products |
| • |
Some carpets and textile fabric finishes |
| • |
Vehicle emissions: from attached garages or outdoors
|
Ozone can also cause the formation of formaldehyde through chemical reaction with some building materials such as plaster, plywood and carpet etc. Office equipments (photocopiers and laser printers) have been found to release formaldehyde possibly through oxidation reaction of ozone with aliphatic hydrocarbons from these equipments.
Exposure Guidelines
Residential indoor air quality guidelines for formaldehyde (Health Canada 2006).
|
Exposure period
|
Concentration
|
Critical effect |
| µg/m3 |
ppb |
| 1 hour |
123 |
100 |
Eye irritation |
| 8 hours |
50 |
40 |
Respiratory symptoms in children |
Average exposure concentrations to formaldehyde and contribution of various atmospheric environments to average exposure to formaldehyde.
| Sources |
Concentration
(mg/m3) |
Exposure
(mg/day) |
| Ambient air (10% of time; 2 m3/day) |
0.001 0.02 |
0.002 0.04 |
Indoor air
Home (65% of time; 10 m3/day) |
| conventional |
0.03 0.06 |
0.3 0.6 |
| mobile home |
0.1 |
1.0 |
| environmental tobacco smoke |
0.050.35 |
0.5 3.5 |
| Workplace (25% of time; 8 m3/day) |
|
|
| without occupational exposurea |
0.03 0.06 |
0.2 0.5 |
| with occupational exposure |
1.0 |
8.0 |
| environmental tobacco smoke |
0.05 0.35 |
0.4 2.8 |
| Smoking (20 cigarettes/day) |
60 130 |
0.9 2.0b |
a Assuming the normal formaldehyde concentration in conventional buildings.
b Total amount of formaldehyde in smoke from 20 cigarettes.
Source: WHO Regional Office for Europe (4).
|
Analytical Methods for Formaldehyde
A number of analytical methods have been employed to determine the airborne concentration of formaldehyde. Active and passive sampling techniques have been used, both have their advantages in different applications. For example, passive samplers are useful in the absence of the sampling pumps, or in situations where longer time sampling is required. They are also small, light and easy to wear or deploy which is important for personal exposure and indoor measurement. The most sensitive method is through the use of high performance liquid chromatography, which has detection limits of low parts per billion (ppb) levels. The methods for the determination of formaldehyde in air are shown in the following table:
| •Sample Preparation |
Assay Procedure |
Limit of Detection |
| Draw air through impinger containing aqueous pararosaniline; treat with acidic pararosaniline and sodium sulfite |
Spectrometry |
0.01 |
| Draw air through polytetrafluorethylene filter and impingers, each treated with sodium bisulfite solution; develop colour with chromotropic acid and sulfuric acid; read absorbance at 580 nm |
Spectrometry |
0.03 |
| Draw air through solid sorbent tube treated with 10% 2-(hydroxymethyl) piperidine on XAD-2; desorb with toluene |
Gas chromatography/ flame ionization detection |
0.02 |
| Draw air through impinger containing hydrochloric acid/2,4-dinitrophenyl hydrazine reagent and isooctane; extract with hexane/dichloromethane |
High performance liquid chromatography/UV detection |
0.002 |
| Draw air through silica gel coated with acidified 2,4-dinitrophenylhydrazine reagent |
High performance liquid chromatography/UV detection |
0.002 |
| Expose passive monitor (Du Pont Pro-Tek® Formaldehyde Badge) for at least 2 ppm-h; analyse according to manufacturer’s specifications |
Chromotropic
acid test |
0.1 |
| Source: International Agency for Research on Cancer (6). |
CASSEN’s Analytical Performance
In addition to sensitivity, CASSEN demonstrates excellent data quality through participation in the only international proficiency program for formaldehyde offered by the United Kingdom Health and Safety Laboratory (HSL), a laboratory of UK’s Health and Safety Executive (HSE) - Workplace Analysis Scheme for Proficiency (WASP) Program. The program provides independent verification of the analytical competence and accuracy of a laboratory giving analysts confidence that the services which they provide will withstand scrutiny. A recent round of formaldehyde proficiency results is shown here and indicates the consistent accuracy and excellent data quality of CASSEN’s performance.
References
|
1.
|
Proposed residential indoor air quality guideline for formaldehyde,
Health Canada 2005 |
| 2. |
The Inside Story: A Guide to Indoor Air Quality,
U.S. Environmental Protection Agency Publication 402-K-93-007 |
| 3. |
Toxicological Profile for Formaldehyde, Agency for Toxic Substances and Disease Registry, US Department of Health and Human Services; 1999
|
| 4. |
Formaldehyde. Geneva, World Health Organization, 1989 (Environmental Health Criteria, No. 89). |
| 5. |
Agency for Toxic Substances and Disease Registry. Managing Hazardous Materials Incidents, Medical Management Guidelines for Acute Chemical Exposures, Formaldehyde.
Atlanta: US Department of Health and Human Services; 2001. |
| 6. |
Formaldehyde. In: Wood dust and formaldehyde, International Agency for Research on Cancer, 1995, pp. 217362 (IARC Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Humans, Vol. 62). |
| 7. |
Residential Indoor Air Quality Guideline: Formaldehyde,
Health Canada 2006 |
| 8. |
Formaldehyde Sampling of FEMA Temporary-Housing Trailers,
U.S. Department of Health and Human Services, Public Health Service, Agency for Toxic Substances and Disease Registry, 2007 |
| 9. |
Indoor Air Quality Guideline, “Formaldehyde in the Home”
California Air Resources Board, 2004 |
| 10. |
Air Quality Guidelines - Second Edition,
WHO Regional Office for Europe, Copenhagen, Denmark, 2001
|
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