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ARCHIVED REPORTS_2008_18
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ARCHIVED REPORTS_2008_18
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Last modified
7/17/2020 3:53:27 PM
Creation date
7/3/2020 10:53:31 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2008_18
RECORD_ID
PR0440005
PE
4433
FACILITY_ID
FA0004516
FACILITY_NAME
FORWARD DISPOSAL SITE
STREET_NUMBER
9999
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
20106001-3, 5
CURRENT_STATUS
01
SITE_LOCATION
9999 AUSTIN RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2008_18.tif
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EHD - Public
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ASBESTOS by TEM: METHOD 7402, Issue 2, dated 15 August 1994 - Page 4 of 7 <br /> Cut a V-notch on the edge of the foam and filter paper. Use the V-notch as a reservoir for <br /> adding solvent- <br /> NOTE: The wicking substrate should be thin enough to fit into the petri dish without touching <br /> the lid. <br /> 12. Place the TEM grid on the filter or lens paper. Label the grids by marking with a pencil on the <br /> filter paper or by putting registration marks on the petri dish halves and marking with a <br /> waterproof marker on the dish lid. In a fume hood, fill the dish with acetone until the wicking <br /> substrate is saturated. <br /> NOTE: The level of acetone should be just high enough to saturate the filter paper without <br /> creating puddles. <br /> 13. Remove about a quarter section of the carbon-coated filter from the glass slide using a surgical <br /> knife and tweezers. Carefully place the excised filter, carbon side down, on the <br /> appropriately-labeled grid in the acetone-saturated Petri dish. When all filter sections have been <br /> transferred, slowly add more solvent to the wedge-shaped trough to raise the acetone level as <br /> high as possible without disturbing the sample preparations. Cover the petri dish. Elevate one <br /> side of the petri dish by placing a slide under it(allowing drops of condensed acetone to form <br /> near the edge rather than in the center where they would drip onto the grid preparation). <br /> CALIBRATION AND QUALITY CONTROL: <br /> 14. Determine the TEM magnification on the fluorescent screen: <br /> a. Define a field of view on the fluorescent screen either by markings or physical boundaries. <br /> NOTE: The field of view must be measurable or previously inscribed with a scale or <br /> concentric circles (all scales should be metric) [71- <br /> b- Insert a diffraction grating replica into the specimen holder and place into the microscope. <br /> Orient the replica so that the grating lines fall perpendicular to the scale on the TEM <br /> fluorescent screen. Ensure that goniometer stage tilt is zero. <br /> c. Adjust microscope magnification to 10,000X. Measure the distance (mm) between the same <br /> relative positions (e.g., between left edges) of two widely-separated lines on the grating <br /> replica. Count the number of spaces between the lines. <br /> NOTE: On most microscopes the magnification is substantially constant only within the <br /> central 8- to 10-cm diameter region of the fluorescent screen. <br /> d. Calculate the true magnification (M) on the fluorescent screen: <br /> M = X G <br /> Y <br /> where: X total distance (mm) between the two grating lines; <br /> G = calibration constant of the grating replica ((ines/mm); <br /> Y = number of grating replica spaces counted <br /> e. After calibration, note the apparent sizes of 025 and 5.0 pm on the fluorescent screen. <br /> (These dimensions are the boundary limits for counting asbestos fibers by phase contrast <br /> microscopy_) <br /> 15. Measure 20 grid openings at random on a 200-mesh copper grid by placing a grid on a glass <br /> slide and examining it under the PCM_ Use the Walton-Beckett graticule to measure the grid <br /> opening dimensions. Calculate an average graticule field dimension from the data and use this <br /> number to calculate the graticule field area for an average grid opening. <br /> NOTE: A grid opening is considered as one graticule field. <br /> 16. Obtain reference selected area electron diffraction (SAED) or microdiffraction patterns from <br /> standard asbestos materials prepared for TEM analysis. <br /> NOTE: This is a visual reference technique. No quantitative SAED analysis is required [71. <br /> Microdiffraction may produce clearer patterns on very small fibers or fibers partially <br /> s obscured by other material. <br /> a. Set the specimen holder at zero tilt. <br /> NiOSH Manual of Analytical Methods NMAM Fourth Edition 8/15/94 <br /> t ). <br />
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