HomeMy WebLinkAbout3955; Survey Report Pajama Drive Reservior; Survey Report Pajama Drive Reservior; 2007-06-293^155
c/> PRE-DEMOLITION ASBESTOS SURVEY &
^ LEAD TESTING REPORT
o
Project Site:
Pajama Drive Reservoir
End of Pajama Drive
Oceanside, California 92054
Prepared For:
Dale A. Schuck
City of Carlsbad, California
405 Oak Avenue
Carlsbad, California 92008
RECEIVED
JUL09200?
ENGINEERING
DEPARTMENT
Prepared By:
WINZLER & KELLY CONSULTING ENGINEERS
4180 Ruffm Road, Suite 115
San Diego, California 92123
(858) 244-0440
& Kelly Project .77010
June 29, 2007
CONSULTING ENGINEERS
TABLE OF CONTENTS -
PRE-DEMOLITION ASBESTOS SURVEY
AND LEAD TESTING REPORT
SECTION 1 - EXECUTIVE SUMMARY
SECTION 2 - MAIN BODY OF REPORT
APPENDIX A - CERTIFICATIONS
APPENDIX B - ASBESTOS SAMPLE LOCATION/LEAD TESTING
ORIENTATION MAP
APPENDIX C - ASBESTOS ANALYTICAL DATA (LABORATORY
REPORT)
APPENDIX D - XRF LEAD DATA TABLE
SECTION 1
EXECUTIVE SUMMARY
CONSULTING ENGINEERS
CONSULTING ENGINEERS
EXECUTIVE SUMMARY
At the request of the City of Carlsbad, Winzler & Kelly Consulting Engineers (Winzler & Kelly)
performed a Pre-demolition Asbestos Survey and Lead Testing Services of the Pajama Drive Reservoir
located at the end of Pajama Drive in the City of Oceanside, County of San Diego, California (site). The
survey and testing was conducted at the Control Building and the aboveground storage tank of the Pajama
Drive Reservoir for the purposes of demolition.
The survey was conducted to identify and sample suspect asbestos-containing materials (ACMs) and
asbestos-containing construction materials (ACCMs) and to sample representative building components
for the presence of lead-containing surface coatings, lead-based paints, and lead-bearing substances
(LCSCs, LBPs, and LBSs).
The results of the survey and testing indicate that hazardous building materials are present at the subject
site. The following table lists the hazardous materials within the subject site, including the location and
the estimated total quantity of the hazardous materials.
PAJAMA DRIVE RESERVOIR
MATERIAL/COMPONENT
DESCRIPTION
Asbestos-containing
Joint Compound
Asbestos-containing
Window Putty
Asbestos-containing
Roof Mastic
Asbestos-containing
Gasket
Asbestos-containing (<1%)
Concrete Seal
Lead-Based Paints
(Color/Substrate):
Green/Wood
Green/Wood
Green/Wood
Green/Metal
Green/Metal
Green/Metal
LOCATION
Interior Walls, Ceiling and Floor
Exterior Windows
Roof at Penetrations
Piping at Flanges
Inlet, Outlet and Overflow Pipe
Doors
Door Jambs
Door Frames
Tank Exterior
Doors of Chlorine Meter
Overflow Pipe
CONDITION
Damaged
Damaged
Good
Good
Good
Intact
Intact
Intact
Intact
Intact
Intact
ESTIMATED TOTAL
QUANTITY
(SF/LF/EA)
500 SF
100SF
4SF
15 EA
15 SF
SEA
3EA
SEA
1,600SF
6SF
25 LF
Notes:
SF = square feet
LF = linear feet
EA = each
NA = not applicable
Asbestos -containing = 1% or greater of asbestos by Polarized Light Microscopy (PLM), as defined by USEPA
Asbestos-containing (<1%1 = 0.1% or greater but less than 1% of asbestos by Polarized Light Microscopy (PLM), as defined by Cal/OSHA
as asbestos-containing construction materials (ACCMs)
Lead-Based Paint = 1 .00 milligrams per square centimeter (mg/cm2) of lead or greater is present, as defined by 1 7 California Code of
Regulations (CCR) 35001-36100
Lead-Containing Surface Coatings = 0.10 to 0.99 mg/cm2 of lead present (8 California Code of Regulations [CCR] 1532.1). Refer to the XRF
Lead Data Table (Appendix D) for building components and surface coatings considered LCSCs at the subject site.
Survey Report - Executive Summary
Pajama Drive Reservoir
June 29, 2007
Page 1
CONSULTING ENGINEERS
At no time should the identified ACMs or ACCMs be drilled, cut, sanded, scraped or otherwise disturbed
by untrained personnel. These materials should be removed prior to any activities which will impact these
materials.
Asbestos disturbance and/or removal operations must be conducted by a Cal/OSHA-registered and State
licensed asbestos removal contractor. Disturbance and/or abatement operations should be performed
under the direct observation of a California Certified Asbestos Consultant or Certified Site Surveillance
Technician.
Construction activities involving the potential for impacting ACMs should be conducted in accordance
with the requirements of Title 8 of the California Code of Regulations, Section 1529 (8 CCR 1529).
For abatement activities which will involve the removal of at least 160 square feet, 260 linear feet, or 35
cubic feet of identified friable ACMs and/or regulated ACMs, notification must be made to the San Diego
Air Pollution Control District (SDAPCD). Notification to the SDAPCD must be accomplished ten
working days prior to the initiation of such activities.
For abatement activities which will involve asbestos-related work of at least 100 square or linear feet,
written notification must be made to the Cal/OSHA. Notification to the Cal/OSHA must be accomplished
24 hours prior to the initiation of such activities.
Notification to employees and contractors working within the building should be made in accordance with
the California Health and Safety Code, Section 25915 et.seq. and Proposition 65.
At present there is no state or federal regulation requiring mandatory lead removal or abatement prior to
disturbance or demolition of structures with identified lead materials. However, there are applicable
Cal/OSHA worker protection and training requirements; Cal/EPA waste disposal requirements, Cal/DHS
requirements for public and residential buildings, and SB 460 lead hazard regulations that apply to lead-
related construction activities, abatement activities and their associated wastes. The following is a brief
discussion and summary of applicable regulatory requirements:
4 Cal/OSHA: Title 8, California Code of Regulation (CCR), Section 1532.1 (8 CCR 1532.1)
governs occupational exposure to lead. This regulation requires that prior to initiation of certain
activities, referred to as "trigger tasks", workers must be trained, medically evaluated, and
properly fitted with respiratory protection, and protective clothing until statistically reliable
personal eight-hour time weighted average (TWA) results indicate lead exposure levels below
the Personal Exposure Limit (PEL) for each unique task which disturbs lead-based and lead-
containing coatings. This process is known as a Negative Exposure Assessment or NEA. If the
result of the exposure assessment is above the Action Level (AL) additional monitoring is
required and if the result is above the PEL additional exposure monitoring, worker protection
(including respirator protection and PPE), training and medical requirements apply. However
even where the NEA criteria is met, certain hazard communication training and work practice
controls still apply where lead is disturbed.
"Trigger tasks" are tasks that are assumed to exceed the PEL pending an exposure assessment and
they encompass the majority of construction activities that disturb surface coatings. Examples of
"trigger" tasks range from manual paint scraping as a lower expected exposure up to hot work
and abrasive blasting as the highest expected exposures, and include any non-listed task that the
employer determines may potentially expose employees to lead levels above the AL.
Survey Report - Executive Summary June 29, 2007
Pajama Drive Reservoir Page 2
CONSULTING ENGINEERS
NOTE - "OSHA does not consider any method that relies solely on the analysis of bulk
materials or surface content of lead (or other toxic material) to be acceptable for safely
predicting employee exposure to airborne contaminates. Without air monitoring results or
without the benefit of historical or objective data (including air sampling which clearly
demonstrates that the employee can not be exposed above the action level during any
process, operation, or activity) the analysis of bulk or surface samples can not be used to
determine employee exposure." OSHA Standard Interpretation 5/8/2000.
Furthermore, OSHA states that these rules apply to "any detectable concentration of lead"
without a specified detection level. Due to the Consumer Product Safety Commission currently
allowing paint to contain up to 600 parts per million (ppm) of lead, the variation of lead content
due to aging and weathering, and the variation of detection limits associated with both paint chip
and XKF analysis, it is recommended that all painted or coated surfaces be treated as potentially
containing lead. Clearly, positive analytical results by either method can be used to indicate that
detectable lead is present but negative results cannot be interpreted as conclusively demonstrating
the absence of lead. Analytical data of bulk paint/coating materials or surface content (by XRF)
of lead can be helpful in evaluation of lead-related environmental risks in general but cannot be
used to calculate worker exposures and are not a substitute for employee exposure monitoring.
As a result of the above, any employee that works around potential lead-based or lead-containing
coatings must have HAZCOM training and personal exposure air monitoring is additionally
required for employees that disturb such coatings. Significant additional certification,
notification, and work practices are required for materials found to be "lead-based".
* Any welding, cutting or heating of metal surfaces containing surface coatings should be
conducted in accordance with 29 CFR 1926.354 and 8 CCR 1537. These regulations require
surfaces covered with toxic preservatives, and in enclosed areas, be stripped of all toxic coatings
for a distance of at least 4 inches, in all directions, from the area of heat application prior to the
initiation of such heat application.
» Cal/EPA through the Division of Toxic Substance Control (DTSC) regulates disposal of lead
hazardous waste (22 CCR Division 4, Chapter 30, Minimum Standards for Management of
Hazardous and Extremely Hazardous Wastes). DTSC has issued guidance indicating that
architectural debris with intact lead paint is normally expected to be handled as general
construction waste. However, waste stream segregation and analysis is still required for all paint
or coatirig debris regardless of if the paint or coating is intact on a building component or not.
The resulting wastes may be hazardous under California and federal RCRA standards for lead and
therefore require proper handling, packaging, labeling, and transportation under a proper manifest
to a permitted hazardous waste storage, treatment and disposal facility.
* Cal DHS: The Department of Health Services (DHS) has specific requirements (Title 17
Sections 35001 thru 36100 et. al.) for hazard assessment and work in public or residential
structures. These regulations require special certifications, work practices, and notification for
such activities.
* Senate Bill 460 (SB 460): An act to amend Section 1941.1 of the Civil Code, and to amend
Sections 17961, 17980, and 124130 of, and to add Sections 17920.10, 105251, 105252, 105253,
105254, 105255, 105256, and 105257 to, the Health and Safety Code, relating to lead abatement.
This bill allows for fines and criminal penalties to be levied on any person who is found to have
Survey Report - Executive Summary June 29,2007
Pajama Drive Reservoir Page 3
CONSULTING ENGINEERS
performed lead abatement without containment or created a measurable lead hazard based upon
current DHS standards. The testing for this determination can be initiated by any local or state
building inspector, health department inspector, or other designated state or local official. A
determination of a lead hazard is not solely based upon the lead content of the paint or coating
and can be the result of the disturbance of such materials with low concentrations of lead.
Written notification to Cal/OSHA must be accomplished should LBP activities involve more than 100
square or 100 linear feet of removal in accordance with the requirements of 8 CCR 1532.1. Proper
written notification to Cal/DHS may be required, depending upon the nature of the abatement activity.
It is the contractor's responsibly to confirm the hazardous material quantities present prior to initiating
renovation or demolition activities at the subject building. Should materials similar to those identified in
this report, or other forms of suspect hazardous materials be present or identified, maintenance
personnel/contractors should be instructed to immediately cease work activities which may initiate a fiber
release episode, and notify the appropriate management personnel.
Report prepared for City of Carlsbad by:
teve G.Pitts
Environmental Field Engineer
Certified Asbestos Consultant #05-3852
DHS Lead Inspector/Assessor #15644
Jerry R.gljefman
Hazardous Material Division Manager
Certified Asbestos Consultant #97-2324
DHS Lead Inspector/Assessor #5809
Survey Report - Executive Summary
Pajama Drive Reservoir
June 29, 2007
Page 4
SECTION 2
MAIN BODY OF REPORT
CONSULTING ENGINEERS
CONSULTING ENGINEERS
INTRODUCTION
At the request of the City of Carlsbad, Winzler & Kelly Consulting Engineers (Winzler & Kelly) performed a
Pre-demolition Asbestos Survey and Lead Testing Services of the Pajama Drive Reservoir located at the end of
Pajama Drive in the City of Oceanside, County of San Diego, California (site). The survey and testing was
conducted at the Control Building and the aboveground storage tank of the Pajama Drive Reservoir for the
purposes of demolition.
The survey was conducted to identify and sample suspect asbestos-containing materials (ACMs) and asbestos-
containing construction materials (ACCMs) and to sample representative building components for the presence
of lead-containing surface coatings, lead-based paints, and lead-bearing substances (LCSCs, LBPs, and LBSs).
The survey and testing was conducted on June 13,2007, by Mr. Steve Pitts and Mr. Jerry Sherman. Mr. Jerry
Sherman performed report preparation and Mr. Steve Reese performed report review. Mr. Sherman, Mr. Reese
and Mr. Pitts, are California Occupational Safety and Health Administration (Cal/OSHA)-Certified Asbestos
Consultants and California Department of Health Services (Cal/DHS)-Certified Lead-Related
Inspector/Assessors. All members of the survey team are employees of Winzler & Kelly, and have received
Hazardous Waste Operations and Emergency Response (HAZWOPER) training in accordance with Title 8
California Code of Regulations (CCR) 5194. Copies of certifications can be found in Appendix A of this
document.
Building Description
The survey and testing was conducted at the Pajama Drive Reservoir located at the end of Pajama Drive in the
City of Oceanside, California. The Pre-demolition Asbestos Survey and Lead Testing was conducted at the
Control Building and the aboveground storage tank of the Pajama Drive Reservoir for purposes of demolition.
Samples were collected from suspect materials that may be impacted during the demolition.
METHODOLOGY
Asbestos - Survey Methodology
Suspect ACMs and ACCMs visual identification was performed by entering representative areas and assessing
accessible structural, architectural, and mechanical components for the presence of suspect ACMs or ACCMs.
Each suspect ACM or ACCM identified was sampled in accordance with sampling guidelines established by
the United States Environmental Protection Agency (USEPA) and 8 CCR 1529. The following summarizes the
sampling procedures utilized:
1. The location and total quantity of each ACM, ACCM, and presumed ACM (PACM) was tabulated.
2. These materials were then categorized into homogeneous materials. A homogeneous material is defined as
being uniform in texture, color, and date of application.
3. A sampling scheme was developed based upon the location and quantity of the various homogeneous
materials.
Survey Report - Section 2 June 29, 2007
Pajama Drive Reservoir Page 1
CONSULTING ENGINEERS
4. Bulk samples were collected by trained personnel using an appropriate sampling tool and a leak-tight
container.
5. Decontamination of bulk sampling tools to prevent the spread of secondary contamination to subsequent
bulk samples.
6. Each bulk sample was individually numbered and recorded on a Bulk Sample Log.
7. A Chain-of-Custody Record was maintained and submitted with the samples to the laboratory.
A representative drawing showing asbestos sample locations can be found in Appendix B of this document.
Asbestos - Analytical Methodology
All bulk samples were analyzed by AmeriSci of Los Angeles, California. AmeriSci is accredited by the
National Voluntary Laboratory Accreditation Program (NVLAP), the National Institute of Standards and
Technology (NIST) and is a successful participant in the Proficiency Analytical Testing (PAT) Program.
Polarized Light Microscopy (PLM)
All bulk samples were analyzed by Polarized Light Microscopy (PLM) utilizing dispersion staining techniques
in accordance with the USEPA Method: "Method for the Determination of Asbestos in Bulk Building
Materials U. S. EPA/600/R-93/116" dated July 1993, and adopted by the NVLAP, NVLAP Test Method Code
18/A01, as affiliated with the NIST. Each sample was subjected to two microscopy examinations.
The first examination was performed at 20X magnification using a stereo microscope equipped with an
external illuminator. Each sample was examined for layering, homogeneity, and the presence of fibrous and
non-fibrous materials. An estimate of the percentage for each sample component, relative to the entire sample
volume, was made. When discrete strata are identified as a separate material, fibers are first identified and
quantified by layer and then the results are combined to yield an estimate of total percent asbestos present.
The second examination was performed at a range from of 100X to 400X magnification using a Polarized
Light Microscope equipped with two polarizing filters to observe specific optical characteristics. The use of
polarized light allows the determination of refractive indices along specific crystallographic axes. Morphology
and color were also observed. A retardation plate was placed at a 45 degree angle between the cross polars to
determine the sign of elongation using orthoscopic illumination.
Orientation of the two filters such that their vibration planes were perpendicular allowed observation of the
birefringence and extinction characteristics of anisotropic particles.
Lead-Containing Surface Coatings, Lead-Based Paints, and Lead-Bearing Substances (LCSCs, LBPs, and
LBSs) - Testing and Analytical Methodology
Potential LCSCs, LBPs, and LBSs were identified via visual identification. The representative, suspect surface
coatings were then measured on-site through the use of a NITON XL x-ray fluorescence (XRF) spectrum
analyzer, in accordance with the requirements of the manufacturer's performance characteristics sheet (PCS)
Survey Report - Section 2 June 29, 2007
Pajama Drive Reservoir Page 2
CONSULTING ENGINEERS
for this instrument.
For purposes of this survey, and in accordance with Title 8 of the California Code of Regulations, Section
1532.1 (8 CCR 1532.1) and Title 17 of the California Code of Regulations, Section 35001 et. seq., the XRF
measurement data results were interpreted as follows:
1. Positive results (LBPs/LBSs present) were determined when analytical results revealed a lead
concentration of 1.00 milligrams per square centimeter (mg/cm2) or greater, equivalent to 5,000 parts per
million (ppm) or greater.
2. Positive results (LCSCs present) were determined when analytical results revealed a lead concentration of
0.10 mg/cm2 or greater, up to 1.00 mg/cm2.
3. Negative results (LCSCs not present) were determined when analytical results revealed a lead
concentration of less than 0.10 mg/cm2, which is below the analytical sensitivity of the XRF measurement
methodology.
RESULTS
Pre-Demolition Asbestos Survey
A total of 23 bulk samples for the determination of asbestos content were collected from the subject site on
June 13, 2007. Based on the results of the pre-demolition asbestos survey of the subject property and
laboratory analytical results, the following materials are considered to be ACMs, as defined by USEPA, and
found to contain detectable concentrations of 1% OR GREATER OF ASBESTOS (locations, conditions, and
estimated total quantity of materials are found in the Executive Summary):
Pajama Drive Reservoir
1. Joint Compound
2. Window Putty
3. Roof Mastic
4. Gaskets
Based on the results of the limited asbestos survey of the subject building, the following materials are
considered to be 'ACCMs, as defined by Cal/OSHA, and found to contain detectable concentrations of
0.1% OR GREATER, BUT LESS THAN 1% OF ASBESTOS (locations, conditions, and estimated total
quantity of materials are found in the Executive Summary):
Pajama Drive Reservoir
1. Concrete Seal
The individual bulk sampling results and the materials suspected to be asbestos and determined not to contain
detectable concentrations of asbestos can be found in the AmeriSci laboratory reports, which are located within
Appendix C of this document.
Survey Report - Section 2 June 29, 2007
Pajama Drive Reservoir Page 3
CONSULTING ENGINEERS
Lead Testing Services
A total of 39 XRF measurements for the determination of lead content were collected from the subject site on
June 13, 2007. The analytical results for this testing indicate that the components and respective surface
coatings did have lead concentrations defining them as LBPs, in accordance with Title 17 of the California
Code of Regulations, Section 35001 et. Seq (locations, conditions, and estimated total quantity of materials are
found in the Executive Summary):
Pa jama Drive Reservoir
1. Green/Wood Doors
2. Green/Wood Door Jambs
3. Green/Wood Door Frames
4. Green/Metal Tank Exterior
5. Green/Metal Doors of Chlorine Meter
6. Green/Metal Overflow Pipe
A lead testing orientation map can be found in Appendix B of this document. Individual XRF measurement
results and LCSCs can be found in Appendix D of this document.
CONCLUSIONS/RECOMMENDATIONS
Pre-Demolition Asbestos Survey
The results of the pre-demolition asbestos survey indicate that ACMs and ACCMs are present at the Pajama
Drive Reservoir, which may be impacted by the impending demolition activities.
At no time should the identified ACMs or ACCMs be drilled, cut, sanded, scraped or otherwise disturbed by
untrained personnel. These materials should be removed prior to any activities which will impact these
materials.
Asbestos disturbance and/or removal operations must be conducted by a Cal/OSHA-registered and State
licensed asbestos removal contractor. Disturbance and/or abatement operations should be performed under the
direct observation of a California Certified Asbestos Consultant or Certified Site Surveillance Technician.
Construction activities involving the potential for impacting ACMs should be conducted in accordance with
the requirements of Title 8 of the California Code of Regulations, Section 1529 (8 CCR 1529).
For abatement activities which will involve the removal of at least 160 square feet, 260 linear feet, or 35 cubic
feet of identified friable ACMs and/or regulated ACMs, notification must be made to the San Diego Air
Pollution Control District (SDAPCD). Notification to the SDAPCD must be accomplished ten working days
prior to the initiation of such activities.
For abatement activities which will involve asbestos-related work of at least 100 square or linear feet, written
notification must be made to the Cal/OSHA. Notification to the Cal/OSHA must be accomplished 24 hours
prior to the initiation of such activities.
Survey Report - Section 2 June 29, 2007
Pajama Drive Reservoir Page 4
CONSULTING ENGINEERS
Notification to employees and contractors working within the building should be made in accordance with the
California Health and Safety Code, Section 25915 et.seq. and Proposition 65.
It is the contractor's responsibly to confirm the ACM and ACCM quantities present prior to initiating
renovation or demolition activities at the subject building. Should materials similar to those identified in this
report, or other forms of suspect ACMs or ACCMs be present or identified, maintenance personnel/contractors
should be instructed to immediately cease work activities which may initiate a fiber release episode, and notify
the appropriate management personnel.
Lead Testing Services
The lead testing services revealed that building components with coatings defining them as LBPs and LCSCs
are present at the Pajama Drive Reservoir, which may be impacted by the impending demolition activities.
At present there is no state or federal regulation requiring mandatory lead removal or abatement prior to
disturbance or demolition of structures with identified lead materials. However, there are applicable Cal/OSHA
worker protection and training requirements; Cal/EPA waste disposal requirements, Cal/DHS requirements for
public and residential buildings, and SB 460 lead hazard regulations that apply to lead-related construction
activities, abatement activities and their associated wastes. The following is a brief discussion and summary of
applicable regulatory requirements:
* Cal/OSHA: Title 8, California Code of Regulation (CCR), Section 1532.1 (8 CCR 1532.1) governs
occupational exposure to lead. This regulation requires that prior to initiation of certain activities,
referred to as "trigger tasks", workers must be trained, medically evaluated, and properly fitted with
respiratory protection, and protective clothing until statistically reliable personal eight-hour time
weighted average (TWA) results indicate lead exposure levels below the Personal Exposure Limit
(PEL) for each unique task which disturbs lead-based and lead-containing coatings. This process is
known as a Negative Exposure Assessment or NEA. If the result of the exposure assessment is above
the Action Level (AL) additional monitoring is required and if the result is above the PEL additional
exposure monitoring, worker protection (including respirator protection and PPE), training and
medical requirements apply. However even where the NEA criteria is met, certain hazard
communication training and work practice controls still apply where lead is disturbed.
"Trigger tasks" are tasks that are assumed to exceed the PEL pending an exposure assessment and they
encompass the majority of construction activities that disturb surface coatings. Examples of "trigger"
tasks range from manual paint scraping as a lower expected exposure up to hot work and abrasive
blasting as the highest expected exposures, and include any non-listed task that the employer
determines may potentially expose employees to lead levels above the AL.
NOTE - "OSHA does not consider any method that relies solely on the analysis of bulk
materials or surface content of lead (or other toxic material) to be acceptable for safely
predicting employee exposure to airborne contaminates. Without air monitoring results or
without the benefit of historical or objective data (including air sampling which clearly
demonstrates that the employee can not be exposed above the action level during any process,
operation, or activity) the analysis of bulk or surface samples can not be used to determine
employee exposure." OSHA Standard Interpretation 5/8/2000.
Survey Report - Section 2 June 29, 2007
Pajama Drive Reservoir Page 5
CONSULTING ENGINEERS
Furthermore, OSHA states that these rules apply to "any detectable concentration of lead" without a
specified detection level. Due to the Consumer Product Safety Commission currently allowing paint
to contain up to 600 parts per million (ppm) of lead, the variation of lead content due to aging and
weathering, and the variation of detection limits associated with both paint chip and XRF analysis, it is
recommended that all painted or coated surfaces be treated as potentially containing lead. Clearly,
positive analytical results by either method can be used to indicate that detectable lead is present but
negative results cannot be interpreted as conclusively demonstrating the absence of lead. Analytical
data of bulk paint/coating materials or surface content (by XRF) of lead can be helpful in evaluation of
lead-related environmental risks in general but cannot be used to calculate worker exposures and are
not a substitute for employee exposure monitoring.
As a result of the above, any employee that works around potential lead-based or lead-containing
coatings must have HAZCOM training and personal exposure air monitoring is additionally required
for employees that disturb such coatings. Significant additional certification, notification, and work
practices are required for materials found to be "lead-based".
Any welding, cutting or heating of metal surfaces containing surface coatings should be conducted in
accordance with 29 CFR 1926.354 and 8 CCR 1537. These regulations require surfaces covered with
toxic preservatives, and in enclosed areas, be stripped of all toxic coatings for a distance of at least 4
inches, in all directions, from the area of heat application prior to the initiation of such heat
application.
Cal/EPA through the Division of Toxic Substance Control (DTSC) regulates disposal of lead
hazardous waste (22 CCR Division 4, Chapter 30, Minimum Standards for Management of Hazardous
and Extremely Hazardous Wastes). DTSC has issued guidance indicating that architectural debris with
intact lead paint is normally expected to be handled as general construction waste. However, waste
stream segregation and analysis is still required for all paint or coating debris regardless of if the paint
or coating is intact on a building component or not. The resulting wastes may be hazardous under
California and federal RCRA standards for lead and therefore require proper handling, packaging,
labeling, and transportation under a proper manifest to a permitted hazardous waste storage, treatment
and disposal facility.
Cal DHS: The Department of Health Services (DHS) has specific requirements (Title 17 Sections
35001 thru 36100 et. al.) for hazard assessment and work in public or residential structures. These
regulations require special certifications, work practices, and notification for such activities.
Senate Bill 460 (SB 460): An act to amend Section 1941.1 of the Civil Code, and to amend Sections
17961, 17980, and 124130 of, and to add Sections 17920.10, 105251, 105252, 105253, 105254,
105255, 105256, and 105257 to, the Health and Safety Code, relating to lead abatement. This bill
allows for fines and criminal penalties to be levied on any person who is found to have performed lead
abatement without containment or created a measurable lead hazard based upon current DHS
standards. The testing for this determination can be initiated by any local or state building inspector,
health department inspector, or other designated state or local official. A determination of a lead
hazard is not solely based upon the lead content of the paint or coating and can be the result of the
disturbance of such materials with low concentrations of lead.
Survey Report - Section 2 June 29, 2007
Pajama Drive Reservoir Page 6
CONSULTING ENGINEERS
Written notification to Cal/OSHA must be accomplished should LBP activities involve more than 100 square
or 100 linear feet of removal in accordance with the requirements of 8 CCR 1532.1. Proper written
notification to Cal/DHS may be required, depending upon the nature of the abatement activity
It is the contractor's responsibly to confirm the hazardous material quantities present prior to initiating
renovation or demolition activities at the subject building. Should materials similar to those identified in this
report, or other forms of suspect hazardous materials be present or identified, maintenance
personnel/contractors should be instructed to immediately cease work activities which may initiate a fiber
release episode, and notify the appropriate management personnel.
Survey Report - Section 2 June 29, 2007
Pajama Drive Reservoir Page 7
APPENDIX A
CERTIFICATIONS
CONSULTING ENGINEER
State of California
Division of Occupational Safety and Health
Certified Asbestos Consultant
Jerry Robert Sherman
Name
-. .... .. . 97-2324Certification No
02/06/08
^
State of California Department of Health Services
Lead-Related Certificate Expiration
Construction Type
Certificate
STATE OF CALIFORNIA Arnold Schwarzenegger, Governor
DEPARTMENT OF INDUSTRIAL RELATIONS
DIVISION OF OCCUPATIONAL SAFETY AND HEALTH
ASBESTOS CONSULTANT and TRAINER APPROVAL UNIT
2211 Park Towne Circle, Suite 1
Sacramento, CA 95825
Tel: (916) 574-2993 Fax: (916) 483-0572
508173852C
Steve G Pitts
1131 Moana Dr
San Diego
282
CA 92107
July 31, 2006
Dear Certified Asbestos Consultant or Technician:
Enclosed is your certification card. To maintain your certification, please abide
by the rules printed on the back of the certification card.
Your certification is valid for a period of one year. If you wish to renew your
certification, you must apply for renewal at least 60 days before the expiration
date shown on your card. [8 CCR 341.15(h)(1)].
Please hold and do not send copies of your required AHERA refresher renewal
certificates to our office until you apply for renewal of your certification.
Please inform our office at the above address, fax number or actu@dir.ca.gov of
any changes in your contact/mailing information within 15 days of the change.
Sincerely,
Jeff Ferrell
Senior Industrial Hygienist
JF/ms
Attachment: Certification Card
cc: File
(Renewal - Card Attached Revised 10/13/05)
State of California
Division of Occupational Safety and Health
Certified Asbestos Consultant
Steve GPJtfs
Name
Certification No.
Expires
This certification was issued by Ihe Division ol
MAY /
Mr. Steve G. Pitts
Winzler & Kelly Consulting Engineers
4180RuffmRoad,#115
San Diego, California 92123
State of California Department of Health Services
Lead-Related Certificate Expiration.Construction Type pajeCertificate
Inspector/Assessor 05/12/2008
STATE OF CALIFORNIA Arnold Schwarzenegger, Governor
DEPARTMENT OF INDUSTRIAL RELATIONS
DIVISION OF OCCUPATIONAL SAFETY AND HEALTH
ASBESTOS CONSULTANT and f RAINER APPROVAL UNIT
2211 Park Towne Circle, Suite 1 i
Sacramento, CA 95825
Tel: (916)574-2993 Fax:(916)483-0572
508173853C
Stephen S Reese
4123 Twilight Ridge
San Diego
282
July 31, 2006
CA 92130
Dear Certified Asbestos Consultant or Technician:
Enclosed is your certification card. To maintain your certification, please abide
by the rules printed on the back of the certification card.
Your certification is valid for a period of one year. If you wish to renew your
certification, you must apply for renewal at least 60 days before the expiration
date shown on your card. [8 CCR 341.15(h)(1)].
Please hold and do not send copies of your required AHERA refresher renewal
certificates to our office until you apply for renewal of your certification.
Please inform our office at the above address, fax number or actu@dir.ca.gov of
any changes in your contact/mailing information within 15 days of the change.
Jeff Ferrell
Senior Industrial Hygienist
JF/ms
Attachment: Certification Card
cc: File
(Renewal - Card Attached Revised 10/13/05)
State of California
Division of Occupational Safety and Health
Certified Asbestos Consultant
Stephen S Reese
Name
Certification No..
Expires on
05-3853
09/22/07
Ttiis certification was issued by the Division ol
Occupational Safely and Health as authorized by
Sections 7180 el seq. ol the Business and
Professions Code
Mr. Stephen S. Reese
Winzler & Kelly Consulting Engineers
4180RuffmRoad,#115
San Diego, California 92123
State of California Department of Health Services
Lead-Related Certificate Expiration
Construction Type Date
Certificate inspector/Assessor 11/25/2007
Sject Monitor 11/25/2007
ID J: 13938
APPENDIX B
ASBESTOS SAMPLE LOCATION/LEAD TESTING ORIENTATION MAP
CONSULTING ENGINEER
CONSULTI N G ENGI NEERS
BY: PITTS/SHERMAN REPORT DATE: 06/29/07 CLIENT: CITY OF CARLSBAD
4180 RUFFIN ROAD SUITE 115
SAN DIEGO, CALIFORNIA 92123
PH (858) 244-0440
FAX (858) 244-0441
SUBJECT: ASBESTOS SAMPLE LOCATION / LEAD TESTING ORIENTATION MAP
LOCATION: PAJAMA DRIVE RESERVOIR
JOB No. 1038207006.77010
SHEET No. 1 of 1
A-6
DO
LU
Q
CO
LOCATIONS AND DIRECTIONS ARE APPROXIMATE
A . APPROXIMATE LOCATION OF ASBESTOS ROOF SAMPLE
• - APPROXIMATE LOCATION OF SAMPLE ANALYZED FOR ASBESTOSXXX
SIDE A- APPROXIMATE LOCATION OF SAMPLE ANALYZED FOR ASBESTOS
NOT TO SCALE
SIDE C
APPENDIX C
ASBESTOS ANALYTICAL DATA (LABORATORY REPORT)
CONSULTING ENGINEERS
AmeriSci Los Angeles
yi r> 24416 SOUTH MAIN STREET • SUITE 308
r\ MERI O C/ CARSON, CA 90745
TEL: (310) 834-4868 • FAX (310) 834-4772
June 20.2007
Winzler & Kelly Consulting Engineers / San Oi
Attn: Steve Reese
4180 Ruffin Road
Suite 115
San Diego, CA92123
RE: Winzler & Kelly Consulting Engineers / San Di
Job Number 907061365
P.O. #1038207006.77010
1038207006.77010; City Carlsbad; Pajama Dr. Reservoir (Report Amended 6/20/2007)
Dear Steve Reese:
Enclosed are the results for polarized light microscopy analysis (PLM) of the following Winzler & Kelly Consulting Engineers /
San Di samples received at AmeriSci on Thursday, June 14, 2007, for a 24 hour turnaround:
A-1. A-2, A-3, A-4. A-5, A-6, A-7, A-8, A-9, A-10, A-11, A-12, A-13, A-14, A-15. A-16. A-17, A-18. A-19, A-20, A-21. A-22, A-23
The 23 samples contained in Ziplock Bags were shipped to AmeriSci via Federal Express. These samples were prepared and
analyzed according to the EPA Interim Method (EPA 600/M4-82-020 per 40 CFR 763, subpt F, App. A). The samples were
evaluated for homogeneity by low power stereomicroscopy. Asbestos fibers were identified by PLM and dispersion staining
through the determination of the required optical properties including: morphology, color, pleochroism, refractive indices,
birefringence, extinction and sign of elongation. The required analytical information, analysis results, analyst signature and
laboratory identification is contained in the Analyst's Report.
This report relates ONLY to the sample analysis expressed as percent asbestos. The CV for this analysis is expected to range
from 0.3 to 1.2, depending on the quantity of analyte present. AmeriSci assumes no responsibility for customer supplied data
such as "sample type", "location", or "area sampled". This report must not be used to claim product endorsement by AmeriSci,
NVLAP or any agency of the U. S. Government. The National Institute of Standards and Technology Accreditation
requirements mandate that this report must not be reproduced, except in full without the written approval of the laboratory. This
report may contain specific data not covered by NVLAP or ELAP accreditations respectively, if so identified in relevant
footnotes.
AmeriSci appreciates this opportunity to serve your organization. Please contact us for any further assistance or with any
questions.
/lary S. David
' Client Services Manager"
Boston * Los Angeles • New York • Richmond
AMERlSd
AmeriSci Los Angeles
24416 S. Main Street, Ste 308
Carson. California 90745
TEL: (310) 834-4868 • FAX: (310) 834-4772
PLM Bulk Asbestos Report
Winzler & Kelly Consulting
Engineers / San Di
Attn: Steve Reese
4180 Ruffin Road
Suite 115
San Diego, CA92123
Date Received 06/14/07
Date Examined 06/15/07
AmeriSci Job No. 907061365
P.O.* 1038207006.77010
Page 1 of 5
RE 1038207006.77010; City Carlsbad; Pajama Dr.
Reservoir (Report Amended 6/20/2007)
Client No. / HGA Lab No. Asbestos Present
A-1 907061365-01.1 No
A Location: Control Bldg. (Debris) / Drywall / Joint Compound /White
Description: White/Brown, Heterogeneous, Fibrous, Drywall / Tape
Asbestos Types:
Other Material: Cellulose 15 %, Non-fibrous 85 %
A-1
A
907061365-01.2 Yes
Location: Control Bldg. (Debris) / Drywall / Joint Compound / White
Description: Beige, Heterogeneous, Fibrous, Joint Compound
Asbestos Types: Chrysotile 6.0 %
Other Material: Non-fibrous 94 %
Total % Asbestos
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
6%
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-2
A
907061365-02.1 No
Location: Control Bldg. (Debris) / Drywall / Joint Compound / White
Description: White/Brown, Heterogeneous, Fibrous, Drywall / Tape
Asbestos Types:
Other Material: Cellulose 20 %, Non-fibrous 80 %
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-2
A
907061365-02.2
Location: Control Bldg. (Debris) / Drywall / Joint Compound / White
Description: Beige, Heterogeneous, Fibrous, Joint Compound
Asbestos Types: Chrysotile 6.0 %
Other Material: Non-fibrous 94 %
6%
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-3
A
907061365-03.1 No
Location: Control Bldg. (Ceiling) / Drywall / Joint Compound / White
Description: White/Brown, Heterogeneous, Fibrous, Drywall / Tape
Asbestos Types:
Other Material: Cellulose 10 %, Non-fibrous 90 %
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
See Reporting notes on last page
AmeriSciJob*: 907061365
Client Name: Winzler & Kelly Consulting Engineers / San Di
Page 2 of
PLM Bulk Asbestos Report
1038207006.77010; City Carlsbad; Pajama Dr.
Reservoir (Report Amended 6/20/2007)
Client No. / HGA Lab No. Asbestos Present
A-3 907061365-03.2 Yes
A Location: Control Bldg. (Ceiling) / Drywall / Joint Compound / White
Description: Beige, Heterogeneous, Fibrous, Joint Compound
Asbestos Types: Chrysotile 5.0 %
Other Material: Non-fibrous 95 %
A-4
B
907061365-04 Yes
Location: Control Bldg. Window / Window Putty / Gray
Description: Grey, Heterogeneous, Non-Fibrous, Cementitious, Bulk Material
Asbestos Types: Chrysotile 2.0 %
Other Material: Non-fibrous 98 %
A-5
B
907061365-05 Yes
Location: Control Bldg. Window / Window Putty / Gray
Description: Grey, Heterogeneous, Non-Fibrous, Cementitious, Bulk Material
Asbestos Types: Chrysotile 2.0 %
Other Material: Non-fibrous 98 %
A-6
B
907061365-06 Vies
Location: Control Bldg. Window / Window Putty / Gray
Description: Grey, Heterogeneous, Non-Fibrous, Cementitious, Bulk Material
Asbestos Types: Chrysotile 2.0 %
Other Material: Non-fibrous 98 %
A-7
C
907061365-07
Location: Control Bldg. Scale / Silver Paint / Silver
Description: Silver, Homogeneous, Non-Fibrous, Bulk Material
Asbestos Types:
Other Material: Non-fibrous 100 %
Total % Asbestos
5%
(by CVES)
by Olga K. Katsuk
on 06/15/07
2%
(by CVES)
by Olga K. Katsuk
on 06/15/07
2%
(by CVES)
by Olga K. Katsuk
on 06/15/07
2%
(by CVES)
by Olga K. Katsuk
on 06/15/07
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-8
C
907061365-08 No
Location: Control Bldg. Valve / Silver Paint / Silver
Description: Silver/Grey, Homogeneous, Non-Fibrous, Bulk Material
Asbestos Types:
Other Material: Non-fibrous 100 %
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
See Reporting notes on last page
AmeriSci Job #: 907061365
Client Name: Winzler & Kelly Consulting Engineers / San Di
Page 3 of
PLM Bulk Asbestos Report
1038207006.77010; City Carlsbad; Pajama Dr.
Reservoir {Report Amended 6/20/2007)
Client No. / HGA Lab No. Asbestos Present
A-9 907061365-09 No
C Location: Control Bldg. Scale / Silver Paint / Silver
Description: Silver, Homogeneous, Non-Fibrous, Bulk Material
Asbestos Types:
Other Material: Non-fibrous 100 %
A-10
D
907061365-10 Wo
Location: Control Bldg. Roof / Built Up Roof Mat'l / Blk
Description: Black, Heterogeneous, Fibrous, Bulk Material
Asbestos Types:
Other Material: Cellulose 10 %, Non-fibrous 90 %
Total % Asbestos
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-11
D
907061365-11
Location: Control Bldg. Roof/ Built Up Roof Mat'l / Blk
Description: Black, Heterogeneous, Fibrous, Bulk Material
Asbestos Types:
Other Material: Cellulose 10 %, Non-fibrous 90 %
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-12
D
907061365-12 Wo
Location: Control Bldg. Roof / Built Up Roof Mat'l / Blk
Description: Black, Heterogeneous, Fibrous, Bulk Material
Asbestos Types:
Other Material: Cellulose 15 %, Non-fibrous 85 %
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-13
E
907061365-13 Vies
Location: Control Bldg. Roof / Roofing Mastic / Gray
Description: Grey, Heterogeneous, Fibrous, Bulk Material
Asbestos Types: Chrysotile 6.0 %
Other Material: Non-fibrous 94 %
6%
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-14
F
907061365-14
Location: Tank Inside / Tank Lining / Blk
Description: Black, Homogeneous, Non-Fibrous, Bulk Material
Asbestos Types:
Other Material: Non-fibrous 100 %
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
See Reporting notes on last page
AmeriSci Job #: 907061365
Client Name: Winzler & Kelly Consulting Engineers / San Di
Page 4 of
PLM Bulk Asbestos Report
1038207006.77010; City Carlsbad; Pajama Dr.
Reservoir (Report Amended 6/20/2007)
Client No. / HGA
A-15
F
Lab No. Asbestos Present
907061365-15 No
Location: Tank Inside / Tank Lining / Blk
Description: Black, Homogeneous, Non-Fibrous, Bulk Material
Asbestos Types:
Other Material: Non-fibrous 100 %
Total % Asbestos
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-16
F
907061365-16
Location: Tank Inside / Tank Lining / Blk
Description: Black, Homogeneous, Non-Fibrous, Bulk Material
Asbestos Types:
Other Material: Non-fibrous 100 %
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-17
G
907061365-17
Location: Base Of Tank / Tank Gasket / Brn
Description: Brown, Homogeneous, Non-Fibrous, Bulk Material
Asbestos Types:
Other Material: Non-fibrous 100 %
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-18
G
907061365-18
Location: Base Of Tank / Tank Gasket / Brn
No
Description: Brown, Homogeneous, Non-Fibrous, Bulk Material
Asbestos Types:
Other Material: Non-fibrous 100 %
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-19
G
907061365-19
Location: Base Of Tank / Tank Gasket / Brn
Description: Brown, Homogeneous, Non-Fibrous, Bulk Material
Asbestos Types:
Other Material: Non-fibrous 100 %
NAD
(by CVES)
by Olga K. Katsuk
on 06/15/07
A-20
H
907061365-20
Location: Tank Piping / Flange Gasket / Gray
yes
Description: Blue, Heterogeneous, Non-Fibrous, Cementitious, Bulk Material
Asbestos Types: Chrysotile 40.0 %
Other Material: Non-fibrous 60 %
40%
(by CVES)
by Olga K. Katsuk
on 06/15/07
See Reporting notes on last page
AmeriSciJob#: 907061365
Client Name: Winzler & Kelly Consulting Engineers / San Di
Page 5 of
PLM Bulk Asbestos Report
1038207006.77010; City Carlsbad; Pajama Dr.
Reservoir (Report Amended 6/20/2007)
Client No. / HGA Lab No. Asbestos Present
A-21 907061365-21 Yes
I Location: Tank Inlet Pipe / Concrete Seal / Gray
Description: Beige/Grey, Heterogeneous, Non-Fibrous, Cementitious, Bulk Material
Asbestos Types: Chrysotile <1. %
Other Material: Non-fibrous 100 %
A-22
I
907061365-22
Location: Tank Outlet Pipe / Concrete
Ves
Description: Beige/Grey, Heterogeneous, Non-Fibrous, Cementitious, Bulk Material
Asbestos Types: Chrysotile <1. %
Other Material: Non-fibrous 100 %
A-23 907061365-23
Location: Tank Over Flow Pipe / Concrete Seal / Gray
Description: Beige/Grey, Heterogeneous. Non-Fibrous, Cementitious, Bulk Material
Asbestos Types: Chrysotile <1. %
Other Material: Non-fibrous 100 %
Reporting Notes:
Total % Asbestos
Trace (<1 %)
(by CVES)
by Oiga K. Katsuk
on 06/15/07
Trace (<1 %)
(by CVES)
by Olga K. Katsuk
on 06/15/07
Trace (<1 %)
(by CVES)
by Olga K. Katsuk
on 06/15/07
; Date Analyzed: 6/15/2007Analyzed By: Olga K. Katsuk.
*NAD = no asbestos detected; Defefctioh Limit <1%; Reporting Limits: CVES = 1%, 400 PtCt = 0.25%, 1000 Pt Ct = 0.1%; NA =
not analyzed; NA/PS = not analyze! I / positive stop; PLM (polarized light microscopy) Bulk Asbestos Analysis by EPA
600/M4-82-020 per 40 CFR 763 (N.VLAP Lab #200346-0, CA ELAP lab #2322); Note: PLM is not consistently reliable in detecting
asbestos in floor coverings and similar NOB materia[sr-\TEM is currently the only method that can be used to determine if this
material can be considered or treatet las non-asbastos-pontaining in New York State (also see EPA Advisory for floor tile, PR 59,
146,38970,8/1/94). NIST
approval of the laboratory.
Reviewed By:
bn requirements/mandate that this report must not be reproduced except in full with the
NLY to the items tested.
Asbestbs Bulk Sample Log W1NZLER& KELLY
CONSULTING ENGINEERS
4180 Ruffln Road. Suite 115
San Diego, CA 92123
Phone: (858) 244-0440
Fax: (858)244-0441
Client:Date:: (J//1/0 7
Vf'Project Number:>.-7?*/.f
Collected Bv:
Co
V
W
Vf
Analytical Method: X PLM V Turnaround Time: SameJDay
Sample Receiver: Winzler'STKEIIyConsulting Engineers - 4780 Ruffin fld, #775, San D/ego, CA 92723
CHAIN OF CUSTODY:
3 day
1.
(/Title
Signature Title
Inclusive Dates
Inclusive 0afes
3.
Signature Title Inclusive Dales
Page of
Asbestos Bulk Sample Log
7081365
WINZLER& KELLY
CONSULTING ENGINEERS
4180 Ruffin Road. Suite 215
San Diego, CA 92123
Phone:(858)244-0440
Fax: (858)244-0441
Client:Date:
Location.
Collected Bv:
Project Number:
or SST No:
A-tf
Con-fr^l
r&o£
0-4-
I
•in
Analytical Method: (PLM^X Turnaround Time: Same Day X34hr? 3 day
Sample Keceiver: Winzler & Kelly Consulting Engineers -4180 Ruffin Rd., #115, San Diego, CA 92123
CHAIN QE£JJSTODY:
Signature
Inclusive Dates
Title I inclusive i/i
w>Inclusive D;
3.
Signature Title Inclusive Dates
Asbestos Bulk Sample Log WINZLER& KELLY
CONSULTING ENGINEERS
4180 Ruffin Road, Suite 115
San Diego, CA 92123
Phone:(858)244-0440
Fax: (858) 244-044J
Date:
Location:
Collected By:_
Project Number:_
^D'
Analytical Method: (: PjAy Turnaround Time: Same Day / 24hjX 3 day
^-'
Sample Receiver: Winzler & Kelly Consulting Engineers - 4780 Ruffin Rd., #115, San Diego, CA 92123
CHAIN OF CUSTODY:
ffitle Inclusive Dates
Title Inclusive Dates
Signature Title Inclusive Dates
Page of.
APPENDIX D
XRF LEAD DATA TABLE
CONSULTING ENGINEERS
WINZLER AND KELLY
CONSULTING ENGINEERS XRF LEAD DATA TABLE
CITY OF CARLSBAD - PAJAMA DRIVE
mm
2
3
4
5
6
7
a
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
32
33
34
35
36
37
38
39
" SHUTTER_CAL
CALIBRATE
CALIBRATE
WALL
DOOR
DOOR
DOORFRAME
DOOR JAMB
WINDOW
WINDOW
WALL
valve
chlorine meter
chlorine meter
chart recorder
turf meter
PIPE
FLOOR
WALL
WALL
WALL
water tank
water tank
water tank
water tank
water tank
water tank
water tank
water tank
OVERFLOW PIPE
ladder
PIPE
PIPE
PIPE
TRIM UPPER
TRIM UPPER
TRIM UPPER
TRIM UPPER
CONCRETE
WOOD
WOOD
WOOD
WOOD
METAL
METAL
CONCRETE
METAL
METAL
METAL
METAL
METAL
METAL
CONCRETE
CONCRETE
CONCRETE
CONCRETE
METAL
METAL
METAL
METAL
METAL
METAL
METAL
METAL
METAL
METAL
METAL
METAL
METAL
METAL
METAL
METAL
METAL
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
POOR
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
INTACT
CALIBRATE
A
A
A
A
A
B
B
B
c
A
A
A
B
C
A
A
C
C
D
B
B
B
D
CALIBRATE
CALIBRATE
CALIBRATE
WHITE
GREEN
GREEN
GREEN
GREEN
GRAY
GRAY
WHITE
SILVER
GREEN
GREEN
GRAY
GREEN
WHITE
GREEN
WHITE
WHITE
WHITE
GREEN
GREEN
GREEN
GREEN
GREEN
GREEN
GREEN
GREEN
GREEN
GREEN
GREEN
GREEN
GREEN
GREEN
GREEN
GREEN
GREEN
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
control bldg.
reservoir
reservoir
reservoir
reservoir
reservoir
reservoir
reservoir
reservoir
reservoir
reservoir
reservoir
reservoir
reservoir
control bldg
control bldg
control bldg
control bldg
east
east
ext.
east
east
east
cntr
cntr
cntr
cntr
cntr
east
east
east
east
ext.
ext.
ext.
inside lid
outside lid
top roof
top roof
top roof
sides
sides
sides
sides
sides
sides
sides
sides
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
Positive
Positive
Positive
Negative
LBP
LBP
LBP
LBP
Negative
LCSC
Negative
Negative
LCSC
LBP
LCSC
LCSC
Negative
LCSC
Negative
Negative
LCSC
Negative
LBP
LBP
LBP
LBP
LBP
LCSC
LCSC
LBP
LCSC
LCSC
LCSC
LCSC
LCSC
Positive
Positive
Positive
6
1.2
1.2
1.1
0.02
2.2
2.6
3.4
3
0.06
0.15
0.01
0
0.17
7
0.15
0.19
0.03
0.16
0.08
0.05
0.1
0.02
2.6
1.1
1.1
1.5
1
0.9
0.8
1
0.1
0.26
0.4
0.3
0.4
1.1
1.1
1.1
Notes:
XRF - X-ray fluorescence spectrum analyzer
mg/cm2 -milligrams per square centimeter
LCSC - Lead-Containing Surface Coating (8 CCR
LBP - Lead-Based Paint (17 CCR 35001 et. seq.),
1532.1) lead present from 0.10 to 0.99 mg/cm2
lead is present at 1 .00 mg/cm2 or greater