
- •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 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
- •7.14.5 Outdoor Air Intakes
- •7.14.6 Filtration
- •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
4.4 Sampling and analytical errors
When an employee's personal exposure or the area exposure is sampled and the results analyzed, the measured exposure will rarely be the same as the true exposure. This variation is due to sampling and analytical errors or SAEs. The total error depends on the combined effects of the contributing errors inherent in sampling, analysis, and pump flow.
Error factors determined by statistical methods shall be incorporated into the sample results to obtain:
The lowest value that the true exposure could be (with a given degree of confidence)
The highest value the true exposure could be (also with some degree of confidence)
The lower value is called the lower confidence limit (LCL), and the upper value is the UCL. These confidence limits are one sided, since the only concern is with being confident that the true exposure is on one side of the Permissible Exposure Limit (PEL).
4.4.1 Determining SAEs
SAEs that provide a 95% confidence limit have been developed and are listed on the OSHA-91B report form (most current SAEs). If there is no SAE listed in the OSHA-91B for a specific substance, call the laboratory. If using detector tubes or direct-reading instruments, use the SAEs provided by the manufacturer.
4.4.2 Environmental Variables
Environmental variables generally far exceed SAE. Samples taken on a given day are used by OSHA to determine compliance with PELs. However, where samples are taken over a period of time (as is the practice of some employers), the industrial hygienist should review the long-term pattern and compare it with the results. When OSHA's samples fit the long-term pattern, it helps to support the compliance determination. When OSHA's results differ substantially from the historical pattern, the industrial hygienist should investigate the cause of this difference and perhaps conduct additional sampling.
4.4.3 Confidence Limits
One-sided confidence limits can be used by OSHA to classify the measured exposure into the following categories.
95% Confident That the Employer Is in Compliance
Measured exposure results do not exceed the PEL.
UCL of that exposure does not exceed the PEL.
95% Confident That the Employer Is not in Compliance
Measured exposure results do exceed the PEL.
LCL of that exposure does exceed the PEL.
95% Confident That the Employer Is in Compliance = Possible Overexposure
Measured exposure results do not exceed the PEL.
UCL of that exposure does exceed the PEL.
NOT 95% Confident That the Employer Is NOT in Compliance = Possible Overexposure
Measured exposure results do exceed the PEL.
LCL of that exposure does not exceed the PEL.
A violation is not established if the measured exposure is in the "possible over-exposure" region. It should be noted that the closer the LCL comes to exceeding the PEL, the more probable it becomes that the employer is in noncompliance.
If measured results are in this region, the industrial hygienist should consider further sampling, taking into consideration the seriousness of the hazard, pending citations, and how close the LCL is to exceeding the PEL.
If further sampling is not conducted, or if additional measured exposures still fall into the "possible overexposure" region, the industrial hygienist should carefully explain to the employer and employee that the exposed employee(s) may be overexposed, but that there were insufficient data to document noncompliance. The employer should be encouraged to voluntarily reduce the exposure and/or to conduct further sampling to assure that exposures are not in excess of the standard.