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Monitoring Requirements
A. The monitoring and sample analysis will be conducted by competent
personnel and closely supervised by an experienced individual certified
with NIOSH 582 course training or equivalent.
B. Air monitoring samples will be collected.
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They may be perimeter and/or area monitoring samples.
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They are to be representative samples of the emissions downwind of
the work activities.
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They may be obtained at any on-site, downwind location, up to and
including the point demarcating public areas.
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They will be analyzed by the NIOSH 7400 method.
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Confirmatory transmission electron microscopy (TEM) may be
used as an option.
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Overloaded air monitoring sample filters that can not be analyzed
by the NIOSH 7400 method will be archived. A qualitative report as
to the presence or absence of fibers along with a reason for the
inability to analyze the filters will be included in the Project
Report.
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NOTE: Overloaded samples will be considered an
indication of excessive fugitive dust resulting from inadequate
dust control.
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C. Project Reports of the perimeter, area, and personal monitoring
results will be submitted to this office.
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Reports will be submitted in a timely fashion.
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Reports concerning violations to Directive 1 will be submitted
immediately upon discovery.
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Project Report Requirements.
A. A written description of the work activities.
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Methods used to investigate for the presence and forms of
actinolite/tremolite minerals at the site.
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Work activities with the potential to generate fugitive dust
emissions.
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Evaluation of the site to identify potential problem areas
including such features as areas of high emission potential, areas
likely to produce maximum off site impacts, etc.
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Daily weather and soil conditions at the construction project, to
include but not limited to wind direction, wind speed,
precipitation, and approximate soil moisture.
B. Diagram of the Construction Project.
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The diagram is at least an 8 by 11 inch copy of the project site
drawings.
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Label diagram to include perimeters.
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Identify the work activities.
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Label the air monitors.
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Indicate wind direction during air monitoring.
C. Air Monitoring Results.
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Sample date.
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Monitor location.
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Date of last calibrations for samplers.
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Interpretations of data and exposure potential.
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Explanation of voided samples to include the possible cause, and a
qualitative report as to the presence or absence of fibers
(Non-NIOSH 7400 methods allowed).
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Sample results
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Asbestos concentration in fibers per cubic centimeter of air,
reported to two decimal places.
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Duration of sample in minutes.
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Rate of sample flow in liters/minute.
D. Violations to DIRECTIVE 1 detected by air monitoring.
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Suspected cause for each violation.
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Best estimate of duration and magnitude of fiber release, areas
exposed, and supporting rationale.
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Actions taken to prevent similar violations in the future.
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The 24-hour average standard is calculated by:
(W X S) + (2 X MDC) + {[24 Hrs. - (W + 2 Hrs.)] X 0.005
F/CC}
24 Hrs.
Where: W= Work Day in Hours.
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S= Sample results in Fibers per
Cubic Centimeter.
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MDC= Mean Decay Period Concentration
(Concentration decays to
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background levels during the two hours following the
end of the workday).
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MCD= (Start Concentration + End Concentration)/2
= (S + 0.005)/2
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NOTE: Since 2 X MDC = 2 X (S + 0.005)/2= S + (0.005)/2
» S
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S may be substituted for 2 X MDC as a simplification.
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0.005 F/CC is the approximate background concentration.