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Causes of Variation in Indoor Mold or Particle Levels MoldAPedia © Enter your search terms Submit search form   Search This Website - InspectAPedia.com

• What are the sources of variation in the mold level that air tests can detect?
• Just how accurate and valid is air sampling for toxic mold testing?
• What is the range of variation in air test samples for mold and what does that say about the accuracy of air tests used to state mold exposure?
• How should an environment be inspected and tested to get a reliable estimate of toxic mold levels or mold exposure levels?

Conditions that Cause High Variation in Indoor Airborne Particle Levels This document is a brief tutorial which provides information about tests for the level of allergenic and toxic mold in residential buildings: Are spore counts valid? Are cultures and swab tests valid? These critical questions are discussed in this paper. Readers should also see Mold Spore Counts: are indoor fungal spore counts valid?, and for a more in-depth critique of popular mold testing methods than this tutorial see Mold Sampling Methods in the Indoor Environment © Copyright 2008 Daniel Friedman, All Rights Reserved. Information Accuracy & Bias Pledge is at below-left. Use links at the left of each page to navigate this document or to view other topics at this website. Green links show where you are in our document or website.

Conditions that Cause High Variation in Indoor Airborne Particle Levels

Some of the site conditions that cause this wide variation in the level of airborne particles in a building are listed below. After reviewing indoor air quality reports produced by many investigators, we conclude that almost never does the IAQ investigator or "mold test expert" document much less control these building conditions. When we have no documentation of building conditions we cannot easily interpret the meaning of spore counts or airborne particle level counts in a building. The sources of variation in the level of indoor airborne mold spores or other particles are arranged very roughly in order of increasing effect on mold test results.

1. Empty rooms where no windows are open, no fans are operating, and no occupants are present will tend to produce lower airborne particle counts than when the same rooms are in normal use.
2. Culture plates or air samples using settlement plates are inaccurate both by species (only a small percent of molds will grow on culture media so we miss up to 90% of genera/species with this method) and also by quantity (large spores and other particles settle out of air faster than small spores or other particles. For more detail see Air sampling by culture plate, mold swab, or surface testing by swab are questionable
3. Outdoor mold counts are tricky to compare with indoor mold spore counts because the same genera counted by a lab, say Pen/Asp may both be the same genera (say Aspergillus but the species may be completely different, making comparison of these two numbers meaningless. Yet most mold labs cannot or do not speciate to this level of detail. Further, even a low indoor Pen/Asp mold spore count could be significant if the spores occurred in spore chains rather than individual spores - indicating that a growing mold source reservoir is nearby. For more detail see Indoor airborne particle counts vs. outdoor counts and also review Concentration Bursts of Mold Spores
4. A room with one individual sitting at a desk quietly reading will produce higher particle counts than an empty room but lower than the conditions listed next.
5. The genera/species or "type" of mold contamination makes a big difference in what is detected in indoor air: for example, Stachybotrys chartarum is a large (so not easily airborne) mold spore which is sticky (not easily airborne) which evolved to be spread by sticking to a cow's foot as she walked through moldy straw. These spores are not normally found in indoor air even if a large mold reservoir is present, unless the Stachybotrys chartarum is being disturbed, say by incompetent demolition and cleaning, or by carrying moldy cardboard boxes out of a wet moldy basement. By contrast, Aspergillus sp. are usually much smaller mold spores, are often easily made airborne by simple air currents (varying depending on growth stage of the mold and indoor humidity and temperature levels). Air tests tend to find particles that are naturally more easily airborne.
6. A carpeted room with someone walking across the carpeting will produce a higher particle count than an un-carpeted room, other conditions being equal.
7. An air sample collected at floor height may vary considerably from a sample collected on a table depending on where mold is growing there could be surprises. For more detail see Variation in Airborne Particle Levels due to Placement Height of Air Sampling Device
8. The aggressiveness of air sampling methods for mold makes an enormous difference in the level of airborne particles. Waving a notebook at local tabletops, rapping on a hot air duct, and similar acts produce much higher counts than very gentle passive (and unrealistic) mold sampling methods. For more detail see Variation in Airborne Particle Levels in Heating and Air Conditioning Ducts
9. A room occupied by several people walking about or a bedroom with a child bouncing on a bed will produce higher airborne particle counts than the conditions listed above.
10. A room with in-use portable heaters, air cleaners, or other devices which stir indoor air may produce higher particle levels than the conditions listed above.
11. A room located close to a large airborne-type problem mold reservoir will usually show higher spore counts than if the reservoir is more distant. However the simple act of opening or closing building interior doors can completely change this picture. In a mold investigation of a home with a large airborne-type mold reservoir in its basement and crawl space, we found very low indoor airborne mold spore counts in the building's first floor over these mold reservoirs when the basement door was kept shut. But within minutes of opening the basement door we observed a significant rise in the level of indoor mold spores at the same test location. For more detail see Variation in Airborne Particle Levels as Windows or Doors are Open or Closed
12. A room with windows open in a tall building will have considerably more air movement (due to convection currents in the building) and may have considerably higher airborne particle counts than when the window is shut. For more detail see Variation in Airborne Particle Levels as Windows or Doors are Open or Closed
13. A room where central air conditioning or hot air heat is operating will produce substantially higher airborne particle levels than the same room when that equipment or its blowers are off.
14. A room where a ceiling fan or other fans are in use will produce among the highest levels of airborne particle counts, other conditions being equal.

Effects of Overall Dust or Mold Level on Mold or Dust Particle Count Variation

What is remarkable about all of these observations is that a large amount of variation in airborne particle level will occur as these conations vary regardless of whether the room is relatively clean or relatively dusty. The absolute numbers will of course be higher in a dusty environment, but the relative numbers will still vary by several orders of magnitude even in a less dusty area.

Use links just below or at the left of each page to navigate this document or to view other topics at this website. Green links show where you are in our document or website.

ACCURACY OF VARIOUS MOLD TEST METHODS
  Causes of Variation in Airborne Particle Levels
  Indoor vs. Outdoor Spore Counts
  Extent of Variation of Airborne Particle Counts
  Particle Levels vs Sampler Height
  Particle Levels vs Windows/Doors
  Particle Levels in Ducts
  Concentration Bursts of Mold Spores
  False Negative Results in Mold Tests
  Mold Culture Plate Test Errors
  Why Use Airborne Mold/Particle Sampling?
  Visual Inspection and History for Mold

Technical Reviewers & References

Particular thanks are due to experts and also consumers who read these articles and suggest corrections, changes, and additions to the material.

• Thanks to Susan Flappan, Flappan Consulting, moldetect.com, Overland Park KS, 913-402-1131, for contributing comments and some suggested text from ACGIH Bioaerosols: Assessment and Remediation 12/2006.
• Daniel Friedman - principal author/editor of the InspectAPedia ^TM Website
• Technical reviewers are invited to comment or ask questions - contact us

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