- •Air sampling and industrial hygiene engineering. Martha j. Boss & Dennis w. Day
- •4.1 Definitions
- •4.2 Example—outline of bulk sampling qa/qc procedure
- •4.3 Example—outline of the niosh 7400 qa procedure
- •4.3.1 Precision: Laboratory Uses a Precision of 0.45
- •4.3.2 Precision: Laboratory Uses a Precision sr that is Better Than 0.45
- •4.3.3 Records to Be Kept in a qa/qc System
- •4.3.4 Field Monitoring Procedures—Air Sample
- •4.3.5 Calibration
- •4.4 Sampling and analytical errors
- •95% Confident That the Employer Is in Compliance
- •95% Confident That the Employer Is not in Compliance
- •4.5 Sampling methods
- •4.5.1 Full-Period, Continuous Single Sampling
- •4.5.2 Full-Period, Consecutive Sampling
- •4.5.3 Grab Sampling
- •4.6 Calculations
- •4.6.1 Calculation Method for a Full-Period, Continuous Single Sample
- •4.6.2 Sample Calculation for a Full-Period, Continuous Single Sample
- •4.6.3 Calculation Method for a Full-Period Consecutive Sampling
- •4.7 Grab sampling
- •4.8 Saes—exposure to chemical mixtures
- •5.1 Baseline risk assessment
- •5.2 Conceptual site model
- •5.2.1 Source Areas
- •5.2.2 Possible Receptors
- •5.3 Chemicals of potential concern
- •5.4 Human health blra criteria
- •5.5 Toxicity assessment
- •5.6 Toxicological profiles
- •5.7 Uncertainties related to toxicity information
- •5.8 Potentially exposed populations
- •5.8.1 Exposure Pathways
- •5.8.2 Sources
- •5.9 Environmental fate and transport of copCs
- •5.10 Exposure points and exposure routes
- •5.11 Complete exposure pathways evaluated
- •5.12 Ecological risk assessment
- •5.13 Data evaluation and data gaps
- •5.14 Uncertainties
- •5.14.1 Uncertainties Related to Toxicity Information
- •5.14.2 Uncertainties in the Exposure Assessment
- •5.15 Risk characterization
- •5.16 Headspace monitoring—volatiles
- •5.18 Industrial monitoring—process safety management
- •5.19 Bulk samples
- •6.1 Fungi, molds, and risk
- •6.1.1 What Is the Difference between Molds, Fungi, and Yeasts?
- •6.1.2 How Would I Become Exposed to Fungi That Would Create a Health Effect?
- •6.1.3 What Types of Molds Are Commonly Found Indoors?
- •6.1.4 Are Mold Counts Helpful?
- •6.1.5 What Can Happen with Mold-Caused Health Disorders?
- •6.2 Biological agents and fungi types
- •6.2.1 Alternaria
- •6.3 Aspergillus
- •6.4 Penicillium
- •6.5 Fungi and disease
- •6.6 Fungi control
- •6.6.1 Ubiquitous Fungi
- •6.6.2 Infection
- •6.6.3 Immediate Worker Protection
- •6.6.4 Decontamination
- •6.6.5 Fungi and voCs
- •6.6.6 Controlling Fungi
- •6.7 Abatement
- •Indoor Air Quality and Environments
- •7.1 Ventilation design guide
- •7.2 Example design conditions guidance
- •7.2.1 Outside Design Conditions
- •7.2.2 Inside Design Conditions
- •7.3 Mechanical room layout requirements
- •7.4 Electrical equipment/panel coordination
- •7.5 General piping requirements
- •7.6 Roof-mounted equipment
- •7.7 Vibration isolation/equipment pads
- •7.8 Instrumentation
- •7.9 Redundancy
- •7.10 Exterior heat distribution system
- •7.10.1 Determination of Existing Heat Distribution Systems
- •7.10.2 Selection of Heat Distribution Systems
- •7.10.2.1 Ag Systems
- •7.10.2.2 Cst Systems
- •7.10.2.3 Buried Conduit (preapproved type)
- •7.10.2.4 Buried Conduit (not preapproved type)
- •7.11 Thermal insulation of mechanical systems
- •7.12 Plumbing system
- •7.12.1 Piping Run
- •7.13 Compressed air system
- •7.13.1 Compressor Selection and Analysis
- •7.13.2 Compressor Capacity
- •7.13.3 Compressor Location and Foundations
- •7.13.4 Makeup Air
- •7.13.5 Compressed Air Outlets
- •7.13.6 Refrigerated Dryer
- •7.14.5 Outdoor Air Intakes
- •7.14.6 Filtration
- •7.14 Air supply and distribution system
- •7.14.1 Basic Design Principles
- •7.14.2 Temperature Settings
- •7.14.3 Air-Conditioning Loads
- •7.14.4 Infiltration
- •7.14.7 Economizer Cycle
- •7.15 Ductwork design
- •7.15.3 Evaporative Cooling
- •7.16 Ventilation and exhaust systems
- •7.16.1 Supply and Exhaust Fans
- •7.17 Testing, adjusting, and balancing of hvac systems
- •7.18 Ventilation adequacy
- •7.19 Laboratory fume hood performance criteria
- •7.20 Flow hoods
- •7.21 Thermoanemometers
- •7.22 Other velometers
4.2 Example—outline of bulk sampling qa/qc procedure
Bulk sample analysis procedures are defined in the NIOSH method for PLM and the NIOSH 7402 method for ТЕМ. Because bulk sample analysis is done by an independent laboratory off-site, this QA/QC document will not address bulk sampling as a field-verified procedure. The NVLAP is currently used to ascertain laboratory effectiveness. The contractor must provide proof that NVLAP certification is current for the laboratory designated to receive both the initial bulk samples and the 10% bulk sample duplicates.
The optical properties and ID of fibers are as follows:
Determine 13 specific items for asbestos.
ID other fibers with some optical data.
ID matrix components.
In addition record
Special procedures or solvents
Sampling of layers
Deviations from EPA test procedure
The 10% bulk sample duplicates are provided by physically dividing 10% of the samples collected. This division should occur concurrently with the collection of field samples. The rationale for splitting the samples at a time and location removed from the field collection site must be provided.
All field collection procedures, sample labeling, and transport and disposal procedures must be addressed in the QA/QC document. Provide the rationale for the classification and remediation of errors. The following is a sample of error classification:
Major Error
False positive
False negative (asbestos actually >1%)
Incorrect asbestos type classification
Analysis quantification in error by 25%
Minor Error
Incorrect ID of tremolite or actinolite as another type of asbestos
False negative (asbestos actually >1% or trace)
Analysis quantification in error by 15%
Incomplete lab data sheets (repeated omissions may equal major error)
Corrective Steps—Major Errors
• Take immediate action.
Review documents for transcription errors.
Review sample, especially matrix description.
Reanalyze sample; submit to other labs for analysis.
Check environment for contamination and out of calibration equipment.
For misidentification of asbestos species review literature and reference samples.
Corrective Steps—Minor Errors
One to two weeks or after monthly summaries
Steps 1 through 4 above.
Review to determine if error is systematic estimation bias, then retrain on esti mation techniques and/or sample preparation techniques.
Completed data sheets are required; frequent omissions should be considered a major error.
Review sampling and stereomicroscope sample preparation procedures.
To recalibrate estimation techniques, reanalyze known samples; review literature on estimation training.
Review; retrain on reference samples, especially in problem matrix mixtures. Review specific problems like tremolite or crocidolite samples.
Review lab's special sample preparations for Vinyl Asbestos Tile (VAT) or tar matrix materials. Practice on known materials including blanks.
