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ENVIRONMENTAL HAZARDS - INSPECT, TEST, REMEDY
MOLD: A COMPLETE GUIDE to TEST CLEAN PREVENT
ACTIVITY of MOLD in BUILDINGS
AGE of MOLD, HOW OLD
AIR CLEANER PURIFIER TYPES
AIR FILTERS for HVAC SYSTEMS
AIR TEST SAMPLING CASSETTE STUDY
AIRBORNE MOLD COUNT NUMBER GUIDE
AIRBORNE PARTICLE ANALYSIS METHODS
ALLERGEN TESTS for BUILDINGS
BROWN HAIRY BATHROOM MOLD
BIBLIOGAPHY for ENVIRONMENTAL HEALTH, MOLD, IAQ
BLACK MOLD, HARMLESS COSMETIC
BLACK MOLD, TOXIC & ALLERGENIC
BLEACHING MOLD, Advice about
BOOK MOLD, Moldy Book Cleaning
BOOKSTORE - ENVIRONMENTAL
CACTUS FUNGI / MOLD
CAR MOLD CONTAMINATION
CARPET DUST IDENTIFICATION
CARPET PADDING ASBESTOS, MOLD, ODORS
CARPET FUNGICIDAL SPRAY
CARPET STAIN DIAGNOSIS
CARPET & other STAIN TESTS
CARPET TEST PROCEDURE
CARPETING & INDOOR AIR QUALITY
CHAIN OF CUSTODY - TEST SAMPLE
CLEARANCE INSPECTIONS - MOLD CLEANUP
DIRECTORY of MOLD / ENVIRONMENTAL EXPERTS
DIRT FLOOR MOLD CONTAMINATION
DISINFECTANTS & SANITIZERS, SOURCES
DISINFECTING BUILDINGS with BLEACH
DO-IT-YOURSELF MOLD CLEANUP WARNINGS
DUST ANALYSIS for FIBERGLASS
DUST, HVAC CONTAMINATION STUDY
EFFLORESCENCE SALTS & WHITE DEPOSITS
FEAR of MOLD - MYCOPHOBIA
FIBERBOARD INSULATION SHEATHING MOLD
FIBERGLASS INSULATION MOLD
FIND MOLD, ESSENTIAL STEPS
MOLD in BUILDINGS
FIRE DAMAGE vs MOLD DAMAGE
FLOODS in BUILDINGS, MOLD PREVENTION
FOXING STAINS on books & papers
FUNGICIDAL SPRAY & SEALANT USE GUIDE
GAS DETECTION INSTRUMENTS
GAS EXPOSURE EFFECTS, TOXIC
GAS EXPOSURE LIMITS & STANDARDS
GAS TEST PROCEDURES
HOUSE DUST ANALYSIS
HOUSE DUST COMPONENTS
HUMIDITY CONTROL & TARGETS INDOORS
LAB PROCEDURES MICROSCOPE TECHNIQUES
LIGHT, GUIDE to FORENSIC USE
MEDIA BLASTING for MOLD REMOVAL
METHANE GAS SOURCES
MICROSCOPE DIGITAL PHOTOGRAPHY
MEDIA BLASTING for MOLD REMOVAL
METHANE GAS SOURCES
MICROSCOPE DIGITAL PHOTOGRAPHY
MILDEW ERRORS, IT's MOLD
MILDEW REMOVAL & PREVENTION
MOISTURE CONTROL in BUILDINGS
MOLD: A COMPLETE GUIDE TO MOLD
MOLD EXPERT, WHEN TO HIRE
MVOCs & MOLDY MUSTY ODORS
MYCOPHOBIA, STAINS MISTAKEN for MOLD
MYCOTOXIN EFFECTS of MOLD EXPOSURE
ODORS GASES SMELLS, DIAGNOSIS & CURE
RENTERS GUIDE TO MOLD & IAQ
ROBIGUS & Wheat Rust Fungus
SMELL PATCH TEST to Track Down Odors
STAINS on & in BUILDINGS, CAUSES & CURES
THERMAL IMAGING MOLD SCANS
TRAPPED MOLD BETWEEN WOOD SURFACES
UV LIGHT BLACK LIGHT USES
VAPOR BARRIERS & CONDENSATION
VENTILATION in BUILDINGS
VOCs VOLATILE ORGANIC COMPOUNDS
WATER ENTRY in buildings
How much variation do we see when using Air Sampling to test for Mold Exposure or Contamination Levels in Buildings?Here we demonstrate that indoor airborne mold or other particle counts vary enormously from minute to minute, providing highly inaccurate (though precise) numbers of spores per cubic meter of air. Here we answer these key questions about mold testing:
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This is a brief tutorial which provides information about the accuracy of 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 series of articles.
There is normally very high variation in the level of airborne particles in indoor air from moment to moment in buildings.
Actual field data easily demonstrates that particle presence in indoor air varies by orders of magnitude from minute to minute.
Sampling identical quantities of air indoors just a few minutes apart regularly shows up in our data as enormous differences in particle density from interval to interval, as you can see in this photograph of parallel traces of airborne particles captured by an air sampler which collected these samples just minutes apart in the same location in a building.
We always see this phenomenon in buildings, since unless we are measuring airborne particles released at a fixed rate in a controlled test chamber there are quite a few site conditions that agitate airborne debris.
A simple visual examination of the five traces of airborne particles captured on this microscope slide make clear that the variation in particle level is significant.
Further examples of wide variation of airborne spore counts indoors are provided at Particle Levels vs Sampler Height where you can see microphotographs of traces such as the ones above.
At Causes of Variation in Airborne Particle Levels we discuss the causes of this high level of airborne particle variability.
Readers should also see MOLD LEVEL IN AIR, VALIDITY, and for a more in-depth critique of popular mold testing methods than this tutorial
Don't Confuse Precision and Accuracy in Airborne Mold Spore Counts?
Some people are confused about the difference between precision and accuracy.
An airborne mold spore count obtained from a spore trap or similar air sampling device can be processed in an aerobiology lab or mold test lab by several methods of varying accuracy depending on not only the site variables (which dominate the airborne particle count, but also depending on the skill and experience of the lab technician, the quality of the microscope and slide preparation, and the percentage of the particle trace that is examined.
In the hands of a skilled microscopist who uses the best practices and who examines 100% of the particle trace, the resulting lab report can give mold spore count that is very precise - for example, citing 5,731 Aspergillus niger spores per M3 (cubic meter) of air.
But what the mold test field investigator and laboratory technician may not be able to report is that the variability from minute to minute in the airborne particle level was enormous, easily by a factor of 100.
If the mold test field investigator had collected her or his sample in the very next five minute interval using exactly the same equipment and methods and processing the sample in exactly the same lab with the same technician may produce a very precise count of 573,124 airborne mold spore count of Aspergillus niger spores per M3 of air.
The two counts are very precise (5,731 and 573,124), but the airborne mold spore count produced by this spore trap method is completely inaccurate: 573,124 mold spores per cubic meter of air is 100 times more mold spores per cubic meter of air than 5,731.
If your airborne mold spore count can easily vary by a factor of 100 from minute to minute it may be precise, but it is inaccurate, and therefore in many cases, especially in cases of low counts that appear to be below the threshold of concern in many mold standards, such counts are completely unreliable.
Just try waving a note book across a table before counting mold spores in air and check the difference in airborne spore levels.
Then review mold inspection and mold test reports to notice whether or not the field investigator has noticed and recorded building conditions that affect air current activity in a building: fans on or off, space occupied or unoccupied, heat on or off, air conditioning on or off, etc. Any one of these completely changes the airborne particle level indoors.
The realization that airborne mold spore counts or counts of any indoor airborne particle are inaccurate is a reason to perform a thoughtful visual inspection of and history taking of a building that is under investigation for air quality problems. But such investigations, properly performed, may be costly and often are unnecessary and should not be performed at all.
Continue reading at MOLD CLEANUP GUIDE- HOW TO GET RID OF MOLD or select a topic from the More Reading links shown below.
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Technical Reviewers & References
Mold Contamination Testing, Cleanup, Prevention: references & products
OTHER IAQ ISSUES: How To Find and Address Other Indoor Air or Indoor Environment Contaminants Besides Mold
Mold or allergens may not be the only or even the main indoor environmental contaminant. Don't let media attention to mold cause so much enviro-scare fear that other, possibly more urgent hazards go un-addressed.