Notes
Slide Show
Outline
1
IAQ & Mold “Testing”
  • Examining the Validity of Current Indoor Mold Sampling Techniques
2

About this presentation:
  • Opinions based on observations of
    • Field investigations 1978-2005
    • Sample contents 1986-2005
    • By same person making field investigation and lab analysis
    • Influenced by academics in aerobiology, mycology, IH, engineering, sciences
3
Agenda - Shortcomings and Errors of Popular IAQ Tools
  • Air sampling
    • counts (spores/M3 of air) are inaccurate
    • causes of particle level variation
  • Tape samples – surface selection errors
  • Vacuum samples
    • surface vs. cavity vs. insulation
  • Cultures
    • not so great for screening
4
Why Investigators Look at Air
5
Collecting Airborne Particles


6
Measuring Airborne Particle Levels
  • Scan a whole trace at low X
  • Count >= 25% of trace at 480x or 720x (ID & count important particles)
  • Calculate Spores/M3 of air for that trace (i.e. for that 6 minute interval)
  • Spores/M3 = (raw count/%of trace)x(1000/trace vol)


  • Example 17,840 Aspergillus niger spores/M3 of air – BUT how accurate is this procedure?
7
Particle Trace Variation
Successive 90L Samples
6 min. on, 6 min off
8
Particle Trace Variation Among Two successive 90L samples
6 minutes apart
9
Counting Spores/M3 of Air
  • Problem: extreme variation in airborne particle levels occur over very short intervals


  • Fallacy: interpreting specific “counts” i.e. “air tests,” as “exposure” without other building diagnosis, may be unreliable
10
How Far Off ?
  • It depends …
  • A precise count
  •  -- 11,543 spores/M3
  • may be highly inaccurate, off by a factor of
  • 10 -- 115,430 spores/M3
  • 100 -- 1,154,300 spores/M3


  • This means at least 1-2 orders of magnitude of error, misrepresenting the actual longer term exposure level. Precise doesn’t mean accurate.
11
Some Causes of Short Term Airborne Particle Level Variation
Spatial Variation
e.g. 1 room, two close locations
12
Passive/Aggressive Sampling Procedural Variation
  • Passive in Plenum
13
Convection Airflow Variation
  • Building stack effects
  • Building ventilation – passive (windows, temperatures)


14
"Mechanicals operation Variation -"
  • Mechanicals operation Variation - A/C or heat on/off
15
More Causes of short term variation in indoor air particle levels
  • Human/animal presence, even if “sitting still”
  • Mechanical disturbance – walk on carpet
  • Ceiling fans
  • Local environment changes affect spore release (wind on bldg, rain, RH, temp. season, etc.)
16
Counts without diagnostic inspections?
  • The absolute number is “wrong”
  • The count interpretation based on building conditions is more important than the absolute number.
  • Cannot interpret a count if there was
    • no diagnostic inspection
    • no recording of test conditions
17
 
18
Comments on the
Spores/M3 Table
  • High spore counts may not correlate with high physical activity
  • A previous event may produce high levels of moldy dust in an apparently clean area
  • A large hidden mold reservoir may be present outside the remediation area
  • Relative counts were important
    in this case
  • Further investigation is needed
19
What do “Spore Counts” Mean
when obtained as a simple
“air test”
  • It Depends.
  • High (>10k problem spores/M3) = contaminated (somewhere)
  • Medium = ambiguous
  • Low = ambiguous (look at species and chains)
  • Zero = ambiguous (Was the basement door shut?)
20
Diagnostic inspection + invasive measures + physical samples, e.g. tape, was very important here where the spore count was low
21
Air Sampling Conclusions
  • Short duration indoor airborne particle counts of spores/M3 of air are
    • Subject to extreme variation minute to minute for many reasons
    • Not repeatable
    • Precise does not mean accurate
    • And
    • Building conditions affecting the sample need to be documented
    • Counts should be interpreted in light of a careful diagnostic inspection
22
Adhesive Tape Surface Samples
  • Collect visible mold
  • Exposed surfaces or by cavity invasion
  • Collect settled dust
  • Collect HVAC inlet, supply, filter debris
  • Inexpensive, rapid, often definitive
    • Spores, Conidiophores, Fungal hyphae
    • Other diagnostic particles
    • Examine non-viable or culture (maybe)
23
Tape Sampling Limitation
 Spatial Variation of Mold Genera
24
Tape Sampling Limitation
 Spatial Variation of Mold Genera
25
Tape Sampling Limitation
Selection Error: Take Easy-to-See Mold
26
Tape Sampling Limitation
Selection Error: Skip Hard-to-See Mold
27
Vacuum Samples
(Air-O-Cel ™ or MCE Cassette)
Some Good Uses Include
  • Multiple surfaces – dust screening
  • Carpet, furniture, soft-goods
  • Support both viable and non-viable qualitative analysis
28
Important Vacuum Sample
  • Building insulation – the under-estimated common large mold reservoir in buildings can be pinpointed


29
Vacuum Sample Limitations
  • Surface vacuums leave important mold structures on the surface (use tape)
  • Vacuums do not collect sticky and non-sticky spores with equal success (use tape)
  • Small-bore wall cavity vacuums are unreliable (compared with test cut)
    • Not enough air movement in cavity
    • Short Air-O-Cel™ easily overloaded
    • Long MCE samples, too few or too costly

30
Cultures to "Test for Mold"
  • Settlement plates – “Home Test Kits”
  • Rely on gravity, large spores fall faster
31
Cultures to "Test for Mold"
  • Settlement plates
  • False negative results (Chaetom. & S. chart.)
  • Possible false positive results


32
More Culture Limitations
  • Only 10% of all molds will grow on any culture
  • Cultures as screens may be 90% wrong
  • What grows in the culture is what likes it
  • What does not grow may be what was important


33
Moldy Tea Results
  • MEA grew Cladosporium
  • DG-18 grew Aspergillus niger, A. flavus, A. glaucus and Penicillium sp.
34
Mold cultures
  • Great to try to coax out and ID an unknown – if culturable
  • Great for photographs – if culturable
  • Great for detailed speciation studies – if culturable
  • May identify a problem in a building, if culturable - else maybe not:
    10% vs. 90%!
35
Polymerase Chain Reaction
  • Works by amplification of nucleic acids (DNA cloning)
  • Highly accurate identification to species
  • Limited data base (being expanded)
  • Ideal to look for a specific mold
  • May not be useful as a broad screen –have to look for specific targets
36
Some Lab Limitations
  • Expertise at fungal spore identification PAACB - the only fungal spore identification certification exam www.paacb.org
  • EMLAP/Culture ID/Lab Procedures - AIHA
  • Workload – who’s really examining the sample?
  • Expertise in microscopy and slide preparation
37
Lab Limitation: Particle Level Variation Due To Microscope Adjustment
38
Conclusions: Mold-IAQ Investigation objectives should include
  • Detect evidence of a hidden problem sufficient to …
  • Justify (or not) invasive measures to …
  • Find and Map Large Mold Reservoirs
  • Permit writing a remediation plan
  • And also Provide baseline comparison samples for follow-up
39
Conclusions: About Sampling Methods, Every tool is useful, but with limitations
  • Air Samples: Spores/M3 of air may be precise but inaccurate
  • Tape samples: collection points are critical
  • Vacuums surfaces & insulation-yes, but wall vacs-doubtful
  • Cultures: 10% chance (maybe more)
  • Investigators should document building conditions affecting sample (simple “air tests” are ???)


40
"Fulltext version of this paper"
  • Fulltext version of this paper:
  • InspectAPedia.com/mold/Mold_Test_Method_Validity.php
  • Both full-text and this Power Point version (illustrated) are © 2005 Daniel Friedman all rights reserved


  • Contact: Daniel Friedman at InspectAPedia.com/Contact.htm


41