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Pacific Southwest, Region 9

Serving: Arizona, California, Hawaii, Nevada, Pacific Islands, Tribal Nations

Naturally Occurring Asbestos

El Dorado Hills

Multimedia Exposure Assessment
Preliminary Assessment and Site Inspection Report Interim Final

El Dorado Hills Quick Finder
El Dorado Assessment Home 1.0 Introduction 2.0 Apparent Problem 3.0 Site Location, Description & History 4.0 Regulatory Involvement 5.0 Summary of Investigative Efforts 6.0 Hazard Ranking System Factors 7.0 Emergency Response Considerations 8.0 Summary Appendices References Acronyms Definitions Appendices & References

5.0 Summary of Investigative Efforts (cont'd)

5.4 Air Sampling

The START conducted activity-based air sampling according to the El Dorado Hills Naturally Occurring Asbestos Multimedia Exposure Assessment, El Dorado Hills, California, Activity-Based Outdoor Air Sampling of Community Park and Schools Field Sampling Plan and the El Dorado Hills Naturally Occurring Asbestos Multimedia Exposure Assessment, El Dorado Hills, California, Activity-Based Outdoor Air Sampling of Community Park Children’s Playground Field Sampling Plan. The types of activities the START conducted during activity-based outdoor air sampling included simulating work and play on baseball fields, soccer fields, basketball courts, playgrounds, and a hiking trail. Changes to these plans, if any, are noted in the discussion below.

The START conducted activity-based outdoor air sample collection at the following locations during 19 different activity-based sampling events or scenarios. These areas are illustrated on Figure 5-3 (Scenarios Location Map):

  • The New York Creek Nature Trail;
  • The New York Creek baseball playing field at the Community Park;
  • The north baseball playing field at the Community Park;
  • The south baseball playing field at the Community Park;
  • The (lower) soccer playing field between the north and south baseball playing fields at the Community Park;
  • The children’s playground at the Community Park;
  • The baseball playing field at Silva Valley Elementary School;
  • The basketball court area at Rolling Hills Middle School;
  • The soccer playing field at Rolling Hills Middle School;
  • Playing fields and paved play areas at Jackson Elementary School; and
  • The garden and outdoor classroom at Jackson Elementary School.

Members of the sampling team wore personal air monitoring pumps and Level C personal protective equipment while con­ducting activities within scripted scenarios to collect samples on air collection filter cassettes. The majority of the scenarios were designed to simulate primarily the activities of children, with simulation of adult activities as a small component. Some of the scenarios included simulation of only child activities, and some scenarios included simulation of only adult activities. Air collection filter cassettes were placed at a height of about 3 feet above ground surface to represent the breathing height of a child and about 5 feet above ground surface to represent the breathing height of an adult.

At each of the areas of concern the sampling team conducted the scenarios for the duration of the event, engaging in dust generation activities that could disturb asbestos fibers and release them into the air. The level of activity ranged from minimal to aggressive dust generation. Except as noted, the sampling team conducted each scenario for 2 hours. For all baseball and soccer scenarios, members of the sampling team who participated as players wore baseball cleats.

Table 5-4
New York Creek Nature Trail Perimeter Monitoring Air Sample Summary Results
Sample ID Location Location Description Date PCME Structures (s/cc) AHERA-like Total
Structures
(s/cc)
Sensitivity (s/cc)
CC2-H8-1CT-100304 CC2-1CT trail position #1CT hi-vol 10/03/04 0.000883 0.00353 0.000294
CC2-H8-2CT-100304 CC2-2CT trail position #2CT hi-vol 10/03/04 0.000583 0.00321 0.000291
CC2-H8-3CT-100304 CC2-3CT trail position #3CT hi-vol 10/03/04 <0.000892 0.00328 0.000298
CC2-H8-4CT-100304 CC2-4CT trail position #4CT hi-vol 10/03/04 0.000830 0.00277 0.000277
CC2-H8-5CT-100304 CC2-5CT trail position #5CT hi-vol 10/03/04 0.000955 0.00573 0.000955
TRA-H8-1TR-100904 TRA-1TRA trail position #TRA1 hi-vol 10/09/04 0.000294 0.00118 0.000294
TRA-H8-11TR-100904 TRA-1TRA duplicate of trail position #TRA1 hi-vol 10/09/04 <0.000867 <0.000867 0.000290
TRA-H8-2TR-100904 TRA-2TRA trail position #TRA2 hi-vol 10/09/04 0.000286 0.000286 0.000286
TRA-H8-3TR-100904 TRA-3TRA trail position #TRA3 hi-vol 10/09/04 <0.000881 <0.000881 0.000295
TRA-H8-4TR-100904 TRA-4TRA trail position #TRA4 hi-vol 10/09/04 <0.000879 0.000879 0.000294
TRA-H8-5TR-100904 TRA-5TRA trail position #TRA5 hi-vol 10/09/04 <0.000875 <0.000875 0.000293
TRA-H2-1ZP-100904 performance evaluation performance evaluation 10/09/04 0.0380 0.313 0.00316
TRA-L2-1ZP-100904 performance evaluation performance evaluation 10/09/04 0.252 1.21 0.0126

PCME fibers = fibers longer than 5 microns with a width between 0.25 and 3 microns, and an aspect ratio (length to width) greater than 3:1

AHERA-like total structures = structures longer than 0.5 microns with an aspect ratio greater than 3:1 (Note this differs somewhat from the strict AHERA structure definition)

Sensitivity = the sample-specific lowest concentration of asbestos the laboratory can reliably detect

s/cc = structures per cubic centimeter

 

Figure 5-3
Scenarios Location Map
(click image for larger version)
photo of:

Activities within each scenario area were conducted by a specific number of people (either five, six, or seven, depending on the activity). When a member of the sampling team took a break from the activity, another member of the sampling team took his or her place in the scenario so that the number of people conducting scenario activities remained constant. The sample pumps and dust monitors were carried in removable work belts to facilitate the exchange of sampling team members as needed.

In addition to the personal air sample pumps worn by members of the sampling team, and except as noted, the START positioned several stationary air sample pumps within each scenario activity and upwind and downwind of scenario activity. For activity-based sampling scenarios conducted at the baseball playing fields at the Community Park, the START also positioned stationary sampling pumps at the Children’s Playground at the Community Park. The intakes for the air collection filter cassettes of the stationary sample pumps were set at a height of about 3 feet, except as noted.

Field conditions required the START to make several changes to the FSPs, most of which are related to the sampling schedule. Table 5-5 (Final Schedule of Field Work) shows the final sampling schedule as conducted.

Table 5-5
Final Schedule of Field Work
Date Scenario 1 Scenario 2 Scenario 3 Reference Sample Areas
9/27/2005   Ambient Air Monitoring Station (AAMS)
9/28/2005   AAMS
9/29/2005   AAMS
9/30/2005   AAMS
10/1/2005 Rehearsal All Day and Press Availability 1:00 pm to 3:00 pm AAMS, Southern Reference Area
10/2/2005 Silva Valley Baseball Field Maintenance Silva Valley Baseball (A)   AAMS, Southern Reference Area
10/3/2005 Silva Valley Baseball (B) Rolling Hills Soccer Rolling Hills Basketball AAMS, Southern Reference Area
New York Creek Nature Trail 8-Hour Perimeter Sampling (CC2-#CT)
10/4/2005 Community Park Children's Playground - Typical Scenario Community Park Children's Playground - Aggressive Scenario   AAMS, Southern Reference Area
10/5/2005 New York Creek Nature Trail Biking Community Park Baseball North Field Community Park Baseball South Field (A) AAMS, Southern Reference Area
10/6/2005 New York Creek Nature Trail Jogging (A) Community Park Baseball South Field (B) Community Park Baseball South Field B without maintenance (C) AAMS, Southern Reference Area
10/7/2005 New York Creek Nature Trail Jogging (B) Community Park Baseball New York Creek Field Community Park Soccer Lower Field AAMS, Southern Reference Area
10/8/2005 Soil Sampling - Community Park, New York Creek Nature Trail AAMS, Southern Reference Area
10/9/2005 Soil Sampling - Silva Valley Elementary School, Rolling Hills Middle School AAMS, Northern Reference Area
New York Creek Nature Trail 8-Hour Perimeter Sampling (TRA-#TR)
10/10/2005 Jackson School Garden and Outdoor Classroom Jackson School Soccer Jackson School Basketball and Kindergarten Play Area AAMS, Northern Reference Area
10/11/2005 Soil Sampling - Dirt Parking Area AAMS, Northern Reference Area
10/12/2005   AAMS

Go to Air Sampling section 5.4.2.1

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