&EPA
United States
Environmental Protection
Agency
Quality Assurance Project Plan for the
Federal Lead (Pb) Performance Evaluation
Program
U.S. Environmental Protection Agency
Office of Air Quality Planning and Standards
Research Triangle Park, NC
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EPA-457/B-14-001a
September 2014
Quality Assurance Project Plan for the
Federal Lead (Pb) Performance Evaluation Program
By:
Gregory W. Noah
U.S. Environmental Protection Agency
Research Triangle Park, North Carolina
U.S. Environmental Protection Agency
Office of Air Quality Planning and Standards
Air Quality Assessment Division
Ambient Air Monitoring Group
Research Triangle Park, North Carolina
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Project: Pb-PEP QAPP
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Foreword
U.S. Environmental Protection Agency (EPA) policy requires that all projects involving the
generation, acquisition, and use of environmental data be planned and documented and have an
Agency-approved Quality Assurance Project Plan (QAPP) before the start of data collection. The
primary purpose of the QAPP is to provide a project overview, describe the need for the
measurements, and define quality assurance/quality control (QA/QC) activities to be applied to
the project, all within a single document.
This document represents the QAPP for the environmental data operations involved in EPA's
Lead (Pb) Monitoring Network Performance Evaluation Program. This QAPP was generated
using the following EPA monitoring and QA regulations and guidance:
• 40 Code of Federal Regulations (CFR) Part 50 Appendix G
• 40 CFR Part 58 Appendices A and C
• EPA QA/R-5, EPA Requirements for Quality Assurance Project Plans
• EPAQA/G-5, Guidance for Quality Assurance Project Plans.
All pertinent elements of the QAPP regulations and guidance are addressed in this QAPP.
This document has been reviewed by EPA Regional Work Assignment Managers responsible for
implementing the performance evaluation program (PEP) in their respective regions and is
considered acceptable (see the following approval page).
Mention of corporation names, trade names, or commercial products does not constitute
endorsement or recommendation for use.
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A cknowledgments
This QAPP is the product of the combined efforts of the EPA's Office of Air Quality Planning
and Standards (OAQPS); and EPA Regional Offices. The review of the material in this
document was accomplished through the activities of the Pb QA Workgroup. The following
individuals are acknowledged for their contributions.
EPA Regions
Region
1 Mary Jane Cuzzupe
2 Mark Winter
3 Loretta Hyden and Kia Hence
4 Richard Guillot, Mike Crowe
5 Basim Dihu, Scott Hamilton, Anthony Ross, Bilal Qazzaz
6 John Lay
7 Thien Bui and James Regehr
8 Joshua Rickard
9 Mathew Plate, Richard Bauer, Gwen Yoshimura
10 Christopher Hall
RTI International (RTI)
Jennifer Lloyd, Jeff Nichol, Ed Rickman, Cynthia Salmons, Emaly Simone
Battelle Memorial Institute
Thomas Kelly, Elizabeth Hanft
Office of Air Quality Planning and Standards
Dennis Grumpier, Greg Noah
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Acronyms and Abbreviations
AAMG Ambient Air Monitoring Group
ACS American Chemical Society
ADQ audit of data quality
AFC Agency File Code
AMTIC Ambient Monitoring Technology Information Center
ANOVA analysis of variance
ANSI American National Standards Institute
APTI Air Pollution Training Institute
AQAD Air Quality Assessment Division
AQS Air Quality System
ASTM American Society for Testing and Materials
AWMA Air and Waste Management Association
CAA Clean Air Act
CAS Chemical Abstracts Service
CB calibration blank
CCV Continuing Calibration Verification
CFR Code of Federal Regulations
CMD C ontracts Managem ent Di vi si on
CO Contracting Officer
COC chain of custody
CV coefficient of variation
DOCOR Delivery Order Contracting Officer Representative
DOPO Delivery Order Project Manager
DQA data quality assessment
DQO data quality obj ective
EDD electronic data deliverable
EDO environmental data operation
ESAT Environmental Services Assistance Team
EPA Environmental Protection Agency
FB field blank
FCS failed collocated sample
FDS field data sheet
FEM Federal equivalent method
FRM Federal reference method
FS field scientist
GLP good laboratory practice
ICP-MS inductively coupled plasma mass spectrometry
ICV initial calibration verification
ID identification
LA laboratory analyst
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Acronyms and Abbreviations (continued)
LCS laboratory control standard
LIMS laboratory information management system
MB method blank
MD matrix duplicate
MDL minimum detection limit
MQO measurement quality obj ective
MS matrix spike
MSR management system review
NAAQS National Ambient Air Quality Standards
NCore National core monitoring network
NERL National Exposure Research Laboratory
NIST National Institute of Standards and Technology
NRMRL National Risk Management Research Laboratory
OAQPS Office of Air Quality Planning and Standards
OAR Office of Air and Radiation
ORD Office of Research and Development
OSRTI Office of Superfund Remediation and Technology Innovation
P&A precision and accuracy
PAMS Photochemical Assessment Monitoring Station
Pb lead
PE performance evaluation
PEP performance evaluation program
PM2.5 particulate matter < 2.5 microns aerodynamic diameter
PMio parti culate matter < 10 microns aerodynamic diameter
PMio-2.5 coarse particulate matter (aerodynamic diameter >2.5 and <10 microns)
POC parameter occurrence code
PQAO primary quality assurance organization
PTFE polytetrafluoroethylene
Qa sampler flow rate at ambient (actual) conditions of temperature and pressure.
Qs sampler flow rate adjusted to standard conditions (latm and 25° C)
QA/QC quality assurance/quality control
QA quality assurance
QAM Quality Assurance Manager
QAPP Quality Assurance Proj ect Plan
QL quantitation limit
QLS Quantitation Limit Standard
RPD relative percent difference
RPO Regional Proj ect Officer
RTF Research Triangle Park
SCV Source Calibration Verification
SIP State Implementation Plan
SLAMS state and local monitoring stations
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Acronyms and Abbreviations (continued)
SLT state/local/tribal
SOP standard operating procedure
SOW scope of work
SPMS special purpose monitoring stations
STAG State and Tribal Assistance Grant
Ta temperature, ambient or actual
TB trip blank
TOCOR Task Order Contracting Officer Representative
TOPO Task Order Proj ect Officer
TSA technical system audit
TSP total suspended particulate
Va air volume, at ambient or actual conditions
WACOR Work Assignment Contracting Officer Representative
WAM Work Assignment Manager
XRF x-ray fluorescence
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1.0 QA Project Plan Identification and Approval
Title: Quality Assurance Project Plan- Federal Lead (Pb) Performance Evaluation Program
QAPP Category - 1
The attached Quality Assurance Project Plan (QAPP) for the Federal Pb Performance Evaluation
Program (PEP) is hereby recommended for approval and commits the participants of the
program to follow the elements described within.
Signature:
OAQPS QA Manager Office fti" Air (Duality Planning and Standards
Signature:
OAQPS Pl^Pwioi'mance Evaluation Program QA~Lead '
Signature:
Region I
Signature:
Signature:
Region 3
Signature:
Region 4
Signature:
Region 5
Signature:
Region 6
Signature:
Region 7
Signature:
Region 8
Date:
Date:
Date:
Date
Date: - / ' /
Dale: ^ ' '< 1 f
Date:
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Signature:
Region 9
Signature:
Region 10
Date: /
Date:
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2.0 Table of Contents
Element No. - Page
Foreword ii
Acknowledgments iii
Acronyms and Abbreviations iv
1.0 QA Project Plan Identification and Approval 7
2.0 Table of Contents 9
3.0 Distribution 14
4.0 Project/Task Organization 16
4.1 The PEP Workgroup 16
4.2 EPA Office of Air Quality Planning and Standards 16
4.3 ESAT Organization 17
4.4 EPA Regional Offices 19
4.5 ESAT Contractors 20
4.6 State, Local, and Tribal Agencies 21
4.7 Other Affected Entities 24
5.0 Problem Definition/Background 26
5.1 Problem Statement and Background 26
6.0 Project/Task Description 31
6.1 Description of Work to be Performed 31
6.2 Field Activities 33
6.3 Laboratory Activities 39
6.4 Schedule of Activities 41
6.5 Project Assessment Techniques 49
6.6 Project Records 49
7.0 Data Quality Objectives and Criteria for Measurement 51
7.1 Data Quality Objectives 51
7.2 Pb-PEP Measurement Quality Objectives 53
8.0 Special Training Requirements/Certification 57
8.1 OAQPS Training Facilities 57
8.2 Training Program 58
8.3 Field Training 58
8.4 Laboratory Training 59
8.5 Certification 59
8.6 Additional Pb-PEP Field and Laboratory Training 60
8.7 Additional Ambient Air Monitoring Training 60
9.0 Documentation and Records 62
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9.1 Information Included in the Reporting Package 62
9.2 Reports to Management 67
9.3 Data Reporting Package Archiving and Retrieval 68
10.0 Sampling Design 69
10.1 Scheduled Project Activities, Including Measurement Activities 69
10.2 Rationale for the Design 69
10.3 Design Assumptions 69
10.4 Procedure for Locating and Selecting Environmental Samples 70
10.5 Classification of Measurements as Critical/Noncritical 71
10.6 Validation of Any Non-Standard Measurements 72
11.0 Sampling Methods Requirements 73
11.1 Sample Collection and Preparation 73
11.2 Support Facilities for Sampling Methods 74
11.3 Sampling/Measurement System Corrective Action Process 75
11.4 Sampling Equipment, Preservation, and Holding Time Requirements 79
12.0 Sample Handling and Custody 81
13.0 Analytical Methods Requirements 82
13.1 Inductively Coupled Plasma Mass Spectrometry Analysis 82
13.2 X-Ray Fluorescence Analysis 83
13.3 Internal QC and Corrective Action for Measurement System 84
13.4 Filter Sample Contamination Prevention 85
14.0 Quality Control Requirements 86
14.1 QC Procedures 86
14.2 Sample Batching—QC Sample Distribution 95
15.0 Instrument/Equipment Testing, Inspection, and Maintenance Requirements 97
15.1 Testing 97
15.2 Inspection 98
15.3 Maintenance 99
16.0 Instrument Calibration and Frequency 102
16.1 Instrumentation Requiring Calibration 102
16.2 Calibration Method That Will Be Used for Each Instrument 104
16.3 Calibration Standard Materials and Apparatus 104
16.4 Calibration Frequency 105
16.5 Standards Recertifications 106
17.0 Inspection/Acceptance for Supplies and Consumables 107
17.1 Purpose 107
17.2 Critical Supplies and Consumables 107
17.3 Acceptance Criteria Ill
17.4 Tracking and Quality Verification of Supplies and Consumables 112
18.0 Data Acquisition Requirements 115
18.1 Acquisition of Non-Direct Measurement Data 115
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19.0 Data Management 117
19.1 Background and Overview 117
19.2 Information Management Flow 118
19.3 Data Recording 120
19.4 Performance Evaluation Data Transfer and Archiving 121
19.5 Data Validation 121
19.6 Data Transformation 123
19.7 Data Transmittal 124
19.8 Data Reduction and Data Integrity 126
19.9 Data Analysis 126
19.10 Data Flagging -Sample Qualifiers 127
19.11 Data Tracking 128
19.12 Data Storage and Retrieval 128
19.13 Information Management Security 129
20.0 Assessments and Response Actions 130
20.1 Assessment Activities and Project Planning 130
20.2 Documentation of Assessments 137
21.0 Reports to Management 138
21.1 Communication 138
21.2 Reports 141
22.0 Data Review, Validation, and Verification Requirements 147
22.1 Sampling Design 147
22.2 Sample Collection Procedures 148
22.3 Sample Handling 148
22.4 Analytical Procedures 149
22.5 Quality Control 150
22.6 Calibration 150
22.7 Data Reduction and Processing 151
23.0 Validation and Verification Methods 152
23.1 Process for Validating and Verifying Data 152
24.0 Reconciliation with Data Quality Objectives 156
24.1 Preliminary Review of Available Data 156
24.2 Evaluation of Data Collected While All Pb-PEP Samplers Collocated—Regional
Level 156
24.3 Evaluation of Data Collected While All Pb-PEP Samplers Collocated—National
Level 157
APPENDICES
1. Glossary
2. Training Certification Evaluation Forms
3. Data Qualifiers/Flags
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Tables
Element No. - Page
Table 6-1. Design/Performance Specifications 35
Table 6-2. Field Measurement Requirements 38
Table 6-3. Laboratory Performance Specifications 40
Table 6-4. Implementation Summary 46
Table 6-5. Data Reporting Schedule for AQS 47
Table 6-6. Assessment Schedule 49
Table 6-7. Critical Documents and Records 50
Table 7-1. Pb Performance Evaluation Program Field Measurement Quality Objectives 54
Table 7-2. ICP-MS Laboratory Measurement Quality Objectives 55
Table 7-3. XRF Laboratory Measurement Quality Objectives 56
Table 9-1. Pb-PEP Reporting Package Information 63
Table 11-1. Field Corrective Action 77
Table 13-1. Filter Preparation and Analysis Checks 85
Table 14-1 QC Sample Distribution 96
Table 15-1. Inspections in the Laboratory 98
Table 15-2. Inspection of Field Items 99
Table 15-3. Maintenance for ICP-MS Pb-PEP Laboratories 100
Table 15-4. Maintenance for XRF Pb-PEP Laboratories 100
Table 15-5. Preventive Maintenance of Field Items 101
Table 16-1. Calibration Standards and/or Apparatus for Pb Calibration 105
Table 17-1. Laboratory Equipment 108
Table 17-2. Field Equipment and Supplies 110
Table 19-1. PEP Data Management Structure 117
Table 19-2. List of Pb-PEP Data Processing Operations for Critical Values 121
Table 19-3 Data Transfer and Archiving 121
Table 19-4. Validation Check Summaries 123
Table 19-5. Raw Data Calculations 124
Table 19-6. Data Transfer Operations 125
Table 19-7. Data Reporting Schedule 125
Table 19-8. Report Equations 127
Table 19-9. Data Archive Policies 128
Table 20-1. Assessment Summary 137
Table 21-1. Communications Summary 139
Table 21-2. Control Charting Recommendations 145
Table 21-3. Report Summary 146
Table 23-l.AIRQA Critical Criteria Validation Template 154
Table 23-2. AIRQA Operational Evaluation Criteria Template 155
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Figures
Element No. - Page
Figure 4-1. Definition of an Independent Assessment 22
Figure 6-1. The Lead (Pb) PEP Overview 32
Figure 11-1. Illustration of ESAT Workgroup Quality Bulletin 76
Figure 17-1 Field/Laboratory Inventory Form (INV-01) 113
Figure 17-2 Field/Laboratory Procurement Log Form (PRO-01) 113
Figure 17-3. Field/Laboratory Equipment/Consumable Receiving Report Form (REC-01) 114
Figure 19-1. Pb-PEP Information/Sample Flow 118
Figure 20-1. Audit Activities 131
Figure 20-2. Assessment Finding Form 133
Figure 20-3. Assessment Fin ding Response Form 135
Figure 21-1. Lines of communication 138
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3.0 Distribution
A copy of this QAPP will be distributed to the Regional Work Assignment Managers (WAMs),
Task Order Project Officers (TOPOs), or Delivery Order Project Managers (DOPOs). Since there
is personnel turnover, the list of WAM/TOPOs/DOPOs that will receive a copy of this document,
as well as the document itself, will be posted on the Pb-PEP site on EPA's Ambient Monitoring
Technical Information Center (AMTIC)1. The AMTIC site will be updated annually. The
WAM/TOPOs/DOPOs will be responsible for distributing the QAPP to each Environmental
Services Assistance Team (ESAT) contractor participating in the environmental data operations
of the PEP. The Regional WAMs/TOPOs/DOPOs should also provide a copy of this QAPP to
their Regional Quality Assurance Managers (QAMs). Any monitoring organization self-
implementing the Pb-PEP will have access to this document on AMTIC.
http://www.epa.gov/ttn/amtic/pbpep.html
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4.0 Project/Task Organization
This element will provide the EPA and other involved parties with a clear understanding of the
role that each party plays in the Pb-PEP and will provide the lines of authority and reporting for
the project.
The degree of complexity and the number of agencies involved with the Pb monitoring program
and the subsequent Pb-PEP requires that the flow of information and associated communications
be structured to optimize the collective resources. The only realistic perspective on implementing
this program is one that recognizes that deployment and operation of this network is a shared
responsibility among all the involved organizations. The purpose of the following role
descriptions is to facilitate communications and to outline basic responsibilities.
4.1 The PEP Workgroup
The PEP Workgroup consists of the EPA Regional Work Assignment Contracting Officer
Representatives (WACORs), Task Order Contracting Officer Representatives (TOCORs),
Delivery Order Contracting Officer Representatives (DOCORs), for the ESAT contract, and
state/local/tribal (SLT) agencies that have opted to run at least the field operations component of
the PEP in their jurisdictions. The PEP ESAT field and laboratory personnel are invited to
participate in the conference calls. The PEP Workgroup, which is chaired by the Office of Air
Quality Planning and Standards (OAQPS) National PEP Project Leader, meets at least twice per
year and more often if needed. The PEP Workgroup serves in an advisory role and assists in the
review and revision of PEP guidance documents, such as the PEP field and laboratory standard
operating procedures (SOPs) and the PEP QAPP. Revisions to these documents, which may have
national implications or issues that are national in scope, are reviewed by the National Ambient
Monitoring QA Strategy Workgroup.
4.2 EPA Office of Air Quality Planning and Standards
OAQPS has the overall responsibility for ensuring the quality of the nation's ambient air
monitoring data. OAQPS has developed specific regulations for the development of a quality
system as found in 40 CFR Part 58, Appendix A. OAQPS has the following responsibilities to
ensure the development of this Pb-PEP Program:
• Provide a contractual vehicle for the manufacturing and distribution of the Pb-PEP portable
evaluation sampler.
• Develop and or continue the memorandum of understanding with the ESAT Office.
• Work with the EPA Regions to determine which monitoring organizations will utilize the
federally implemented Pb-PEP and to determine how many Pb-PEP audits are required per
PQAO.
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Receive and allocate the appropriate State and Tribal Assistance Grant (STAG) funds to
implement the federal Pb-PEP program.
Transfer the necessary funds to the EPA Regional ESAT Contracts Management Division
(CMD) to support the Pb-PEP and to the Region 9 office for laboratory equipment and
consumables.
Distribute filters to the regional field offices or Pb-PEP laboratories.
Develop and update the Pb-PEP Implementation Plan, the Pb-PEP QAPP, the ESAT Scope
of Work (SOW), and field SOPs.
Develop the field and laboratory personnel requirements.
Develop the field and laboratory training activities, participate in training, and provide
technical, support, and guidance to regional Pb-PEP contacts.
Develop a list of primary quality assurance organizations (PQAOs) which are monitoring Pb
at state and local air monitoring stations (SLAMS) and special purpose monitoring (SPM)
sites.
Develop field and laboratory information management systems.
Upload audit data to the air quality system (AQS) database.
Assess the Pb-PEP concentration information and completeness data entered into AQS.
Initiate and implement a communications network and act as a liaison to groups working on
the Pb-PEP.
• Interact with the monitoring organizations concerning the setup, operation, and data results of
the performance evaluations.
• Ensure the success of the program by performing various oversight activities such as
management system reviews and/or technical systems audits (TSAs).
Most budgetary and technical planning activities are coordinated through OAQPS. The Ambient
Air Monitoring Group (AAMG) within the Air Quality Assessment Division (AQAD) is
ultimately responsible for this QAPP, most technical components (with support from the EPA
Regional Offices and monitoring organizations), and the resource estimates underlying program
implementation. Various forms of resource guidance necessary for the STAG distribution are
coordinated through OAQPS. In addition, the OAQPS National Air Data Group is responsible
for the AQS data management system.
4.3 ESAT Organization
The ESAT contract is administered by the Office of Superfund Remediation and Technology
Innovation (OSRTI) Technology Innovation and Field Services Division Analytical Services
Branch. OAQPS has entered into a memorandum of understanding with this office in order for
the ESAT contract to provide the services necessary for the Pb-PEP. The ESAT contractor is
managed by contracting officers (COs) at the Headquarters office in Washington, D.C. and with
WACORs/TOCORs/DOCORs, and Regional Project Officers (RPOs) within each Region. RPOs
are necessary because each Region awards an ESAT contract to assist in the implementation and
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execution of the program. The AMTIC Web site2 provides the current ESAT contacts list. Since
the list may change, contact names will not be included in this document, but will be posted on
AMTIC and updated on an annual basis.
Some important aspects of the ESAT contract include:
• Only the WACOR/TOCOR/DOCOR, RPO, and COs are authorized to give instructions or
clarification (technical direction) to the ESAT contractor on the work to be performed. This
technical direction is provided in writing.
• The work assignments will be prepared by the TOCOR/DOCOR and are effective only upon
approval by the CO.
The EPA Contracts Manual describes the roles and responsibilities of COs, specialists, and
project officers; these need not be explained here. The important roles and responsibilities for the
Pb-PEP are described below.
Contracting Officers
• Work with OAQPS to secure, obligate, commit, and distribute funds for work performed
under the ESAT contract (or other contract vehicle as appropriate).
• Ensure work assignment activities fall within ESAT's SOW.
• Approve work assignments, task orders, and delivery orders.
Contracting Specialists
• Work with OAQPS or Regional ESAT WACOR/TOCOR/DOCORs to modify contracts or
track the use of funds for work performed under the ESAT contract (or other contract vehicle
as appropriate).
Headquarters Project Officers
• Serve as regional liaison between the RPO and the CO.
• Provide contract-wide administration.
• Develop a memorandum of understanding with OSRTI.
Regional Project Officers
• Provide overall management and oversee performance of respective regional ESAT
personnel.
• Review region-specific invoices with input from WACORs, TOCORs, and DOCORs.
• Prepare (with WACOR/TOCOR/DOCOR) Pb-PEP work assignments, task orders, and
delivery orders.
• Assist in developing ESAT work assignments, task orders, and delivery orders.
: http://www.epa.gov/ttn/amtic/pbpep.html
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• Ensure that there are qualified contractual personnel available to implement the Pb-PEP.
• Provide administrative and logistical support for the ESAT contract.
• Regularly communicate with program participants (OAQPS, Region, etc.).
Work Assignment, Task Order, and Delivery Order Contracting Officer Representatives
In most cases, the WACOR/TOCOR/DOCOR, as a technical resource from the regional air
monitoring branch/division, will be responsible for assisting in the technical implementation of
the program. Some of the WACOR/TOCOR/DOCOR's activities, as they relate to the ESAT
contract, are the following:
• Communicate with the National PEP Project Leader about the current status of funding for
the federally implemented Pb-PEP.
• Prepare (with RPO) Pb-PEP work assignments, task orders, and delivery orders.
• Set up a file system containing all relevant documentation, including notes of conversations
with the contractor and other items that will provide an audit trail of the contractor's actions
under the contract, as well as all technical information related to the Pb-PEP.
• Review the contractor's work plan and prepare findings on proposed tasks, labor hours, skill
mix, and materials and quantities.
• Monitor compliance with the work assignments.
• Track dollars and hours, provide technical direction (in accordance with the terms of the
contract), and review monthly technical and financial reports.
• Verify contractor representations of deliverables received and accepted, and/or progress
made.
• Communicate contractor performance, budgetary, and administrative/logistical issues to the
RPO and to the National PEP Project Leader.
• Review validation data and accept or rej ect Pb-PEP audits.
4.4 EPA Regional Offices
The EPA Regional Offices are the major communication link with monitoring organizations and
OAQPS. This role is absolutely necessary for the development of effective policies and
programs. For the Pb-PEP, the regional offices have the following specific responsibilities:
All Regions:
• Assist in the development of all pertinent Pb-PEP evaluation guidance documents.
• Review and approve the work plans submitted by the ESAT contractors.
• Identify WACORs/TOCORs/DOCORs to oversee the technical aspects of field activities that
are performed by the ESAT contractors.
• Train and certify ESAT field personnel and/or self-implementing agencies after initial
training.
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• Provide technical oversight of the field activities by performing annual TSAs of these
activities.
• Work with monitoring organizations in developing a yearly schedule of site audits and
provide this schedule to the ESAT contractors.
• Inform monitoring organizations of an upcoming performance evaluation.
• Evaluate the performance evaluation data and inform monitoring organizations of significant
differences.
• Participate in training activities, including national and regional conferences, EPA satellite
broadcasts, and other training vehicles.
• Attend conference calls and meetings on performance evaluation activities.
Region 9 (including items listed for all regions):
• Identify WAMs to oversee the technical aspects of laboratory activities related to high
volume total suspended particulate (TSP) and low volume PMio Pb analyses that are
performed by the ESAT contractors.
• Develop and operate the primary laboratory for the Pb analyses with respect to logistical,
technical, and analytical support, including necessary facilities to store and archive filters and
extracts.
• Maintain and certify proficiency of ESAT laboratory personnel after initial training.
• Provide technical oversight of the laboratory activities by performing TSAs of these
activities.
Region 4 (including items listed for all regions):
• Identify WAMs to oversee the technical aspects of laboratory activities related to low volume
Pb-PMio PEP filter preparation that are performed by the ESAT contractors.
• As a secondary role, identify WAMs to oversee the technical aspects of laboratory activities
related to low volume Pb-PMio PEP filter preparation that are performed by the state, local,
and tribal agencies.
• Develop the primary laboratory for the low volume Pb-PMio filter loading with respect to
logistical, technical, and analytical support, including necessary facilities to store, distribute,
and receive filters. The laboratory will also provide for the cleaning of cassettes.
• Train and certify ESAT laboratory personnel after initial training.
• Provide technical oversight of the laboratory activities by performing TSAs of these
activities.
4.5 ESAT Contractors
The ESAT contractors will perform the specific tasks associated with the Pb-PEP. Their
responsibilities will include the following:
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• Develop a work plan and cost estimates for each work assignment, task order, or delivery
order.
• Provide qualified staff to meet the contract requirements.
• Successfully implement the activities described in the work plan and work assignment, task
order, or delivery order.
• Receive training and certification(s) to perform field and laboratory Pb-PEP activities, as
appropriate.
• Understand government regulations as they relate to contracts and inherent government
functions.
4.6 State, Local, and Tribal Agencies
EPA could not effectively plan and execute this program without SLT organization participation.
The SLT agencies bear the heaviest responsibility for developing and implementing the national
Pb Monitoring Program, as well as for optimizing the data quality. Conversely, the Pb-PEP
provides an invaluable quality assurance/quality control (QA/QC) function on the overall
performance of the network and often identifies potentially serious sampler performance
problems, site problems, or laboratory issues. It is imperative that SLT organizations work with
the EPA regional offices to make every Pb-PEP audit event successful. They should identify
problems that will impede the mission of the Pb-PEP as early as possible and help find solutions.
The SLT organizations have the following specific responsibilities:
General monitoring site accommodations:
• Ensure that there is sufficient space for collocating an audit monitor and low volume Pb-
PMio monitor or high volume Pb-TSP monitor, while still meeting siting requirements listed
in 40 CFR Part 58, Appendix E and the Pb-PEP SOP.
• Ensure that each site is safely accessible for a Pb-PEP audit.
• Ensure that each site meets the applicable state or federal Occupational Safety and Health
Administration safety requirements (includes providing secured ladders and appropriate
safety rails and/or cages).
• Ensure that adequate power is available for the Pb-PEP samplers.
• If the above siting criteria cannot be met, the EPA Regional PEP leader must be consulted
before continuing with the Pb-PEP audit.
• SLT monitoring programs are required to supply to the PEP analytical support laboratory
either four or six samples annually from their collocated monitor at the collocated Pb
monitoring sites.
If an SLT chooses to implement the Pb-PEP:
• Implement a comparable or equivalent Pb-PEP at the frequency prescribed by the federal
regulations in 40 CFR Part 58, Appendix A.
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• Adhere to the definition of independent assessment (see Figure 4-1).
• Participate in consistent Pb-PEP specific training and certification activities.
• Procure necessary equipment and consumables.
Independent assessment—An assessment that is performed by a qualified individual, group,
or organization that is not part of the organization that is directly performing and accountable
for the work being assessed. This auditing organization must not be involved with generating
the routine ambient air monitoring data. An independent organization could be another unit of
the same agency, which is sufficiently separated in terms of organizational reporting and can
provide for independent filter weighing and performance evaluation (PE) auditing.
An organization can conduct the PEP if it can meet the above definition and has a
management structure that, at a minimum, will allow for the separation of its routine sampling
personnel from its auditing personnel by two levels of management. In addition, the audit
filters must be analyzed by separate laboratory facility using separate laboratory equipment.
Field and laboratory personnel would be required to meet the PEP field and laboratory training
and certification requirements. The SLT organizations are also asked to consider participating
in the centralized field and laboratory standards certification process.
Organization
3rd Level
Supervision
Organization
Personnel
CA Lab Analysis
Organization
Personnel
CA Field Sampling
Qganization
Personnel
Routine Lab Analysis
Organization
Personnel
Routine Field Samplingl
Organizations that are planning to implement the PEP must submit a plan that demonstrates
independence to the EPA regional office that is responsible for overseeing QA-related
activities for the Ambient Air Quality Monitoring Network.
Figure 4-1. Definition of an Independent Assessment
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• Develop the necessary SOPs and QA procedures into their respective QAPPs.
• Participate in annual collocation precision studies of the SLT and federally deployed Pb-PEP
samplers.
• If necessary, transmit data to the AQS according to the schedule outlined in the monitoring
QA regulations and procedures provided by EPA. (If an SLT chooses the federal Pb-PEP, or
chooses to use the PEP analytical support laboratory, the data are transmitted automatically.)
• Select the sites for evaluation.
• If using a third-party laboratory, require that laboratory to participate in an annual round-
robin PE if available. This is not required if the SLT uses EPA's Pb-PEP laboratory for its
filter analyses.
• Prepare a laboratory annual report in an EPA-specified format and submits it to EPA. This is
not required if the SLT uses EPA's Pb-PEP laboratory for its filter analyses.
• Submit to an annual TSA of their Pb-PEP activities by the EPA Regional PEP Leader or
QAM.
If using the federal PEP:
• Operates the routine Pb federal reference method (FRM)/FEM monitoring network according
to the established regulations and guidelines, including proper siting, operations, and QA
procedures.
• Creates an accurate list of SLAMS, SPMS or tribal sites with addresses, AQS identifications
(IDs), makes and models of routine sampling equipment, and sampling schedules.
• Assists, through PEP Workgroup activities, in the development of pertinent PEP guidance
documents.
• On a yearly basis, determines whether to continue using the federal implementation of the
PEP.
• Identifies the sites within the routine Pb FRM/FEM monitoring network for PEs and the
associated sampling schedules.
• Ensures that an Agency representative is aware of when the PEP Field Scientist (FS) arrives
and performs the evaluation. The evaluation includes communicating with the operator,
operating the routine monitor in the normal operating mode (including posting site results to
the AQS), and generally supporting the PEP.
• Conducts follow-up of the audit to ensure a valid routine concentration (for a routine PEP
pair) is collected for comparison. If a valid pair has not been collected, a "make-up audit" is
strongly encouraged).
• Ensures the program's success by performing various internal oversight activities of the SLT
monitoring networks, such as TSAs of field and laboratory activities.
• Participates in training activities, including multi-state conferences, EPA satellite broadcasts,
and other training vehicles.
• Reviews routine and PE data and works with the EPA Region on corrective actions.
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4.7 Other Affected Entities
EPA Office of Research and Development (ORD)
The ORD's primary role in the implementation of the Pb-PEP will be as a technical consultant,
advisor, and arbiter of technical issues. This action will be primarily through the National
Environmental Research Laboratory, which provides many of the applied research elements for
the program. ORD also has the overall responsibility for designating all air monitors as an FRM
or FEM. The FRM/FEM portable PMio low volume audit samplers must be designated by ORD
through its Federal Reference and Equivalency Program (40 CFR Part 53). The high volume
TSP samplers are not given FRM/FEM designation. The method is described in 40 CFR
Part 50, B as a specification that high volume TSP samplers must follow. The overall
responsibilities of ORD include the following:
• Designate PMio low volume Pb samplers as FRM/FEM and provide technical support.
• Provide technical support for the national monitor procurement contracts.
• Arbitrate Pb-PEP technical issues.
• Provide guidance for field and analytical activities.
In addition, the ORD National Risk Management Research Laboratory (NRMRL) Metrology
Laboratory will provide annual verification of the flow/pressure/temperature standards used for
the Pb-PEP.
EPA Contracts Management Division Responsibilities
The CMD, within the Office of Acquisition Management, is responsible for issuing contracts and
various national procurements. These contracts are developed in concert with OAQPS AQAD
technical staff. The CMD is responsible for all communications with vendors and extramural
contract organizations. The CMD's responsibilities include the following:
• Developing national contracts for the sampler purchases and filter purchases and working
with ORD and Office of Air and Radiation (OAR) contracts and technical staff to provide
these products.
• Providing support to COs and contract support staff for national procurements for federal
implementation of the Pb-PEP, major equipment repairs, and equipment upgrades.
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5.0 Problem Definition/Background
The background information provided in this element will place the problem in historical
perspective, giving readers of the QAPP a sense of the project's purpose and position relative to
the Ambient Air Monitoring Program.
5.1 Problem Statement and Background
In 1970, the Clean Air Act (CAA) was signed into law. Under the CAA, the ambient
concentrations of six criteria pollutants (particulate matter, sulfur dioxide, carbon monoxide,
nitrogen dioxide, ozone, and lead) are regulated. The CAA requires monitoring organizations to
monitor these criteria pollutants through the Ambient Air Quality Surveillance Program as
defined in 40 CFR Part 58.
On November 12, 2008, EPA substantially strengthened the national ambient air quality
standards (NAAQS) for Pb (see 73 FR 66934). EPA revised the level of the primary (health-
based) standard from 1.5 micrograms per cubic meter (|ig/m3) to 0.15 |ig/m3, measured as TSP,
and revised the secondary (welfare-based) standard to be identical in all respects to the primary
standard. In conjunction with strengthening the Pb NAAQS, EPA identified the need for states to
improve existing Pb monitoring networks by requiring monitors to be placed in areas with
sources that emit one half ton per year or more of Pb and in urban areas with more than 500,000
people. Depending on specific circumstances, states may have the option of using monitoring for
either Pb in TSP (Pb-TSP) or Pb in PMio (Pb-PMio) using approved FRMs or FEMs to
demonstrate compliance.
Due to the promulgation of the lower Pb NAAQS, EPA made some changes in the QA
requirements in 40 CFR Part 58 Appendix A. The following are the highlights of the changes
that occurred in 40 CFR Part 58 Appendix A:
• Data Quality Objective (DQO) Goals- Measurement uncertainty for precision will be 20%
for a 90% confidence limit coefficient of variation and an overall absolute bias upper bound
goal of 15%. Goals will be assessed on 3 years of data at the PQAO level of aggregation.
• Flow Rates-No changes occurred to flow rate. Flow rate verification will be implemented
monthly (PMio low volume) or quarterly (TSP high volume) and flow rate performance
evaluations will be implemented every 6 months.
• Collocated Monitoring-No changes occurred to the collocation requirements. Collocation
will continue to be required at 15% of each method designation within a PQAO at a l-in-12
day sampling frequency. EPA added language encouraging monitoring organizations to site
the first collocated sampler in each network at the highest concentration site. This will allow
the site to operate over the longest time period. Since it may be the site that affects the
NAAQS and it is allowable to substitute collocated data for missing data from the primary
monitor, this siting would be advantageous for improving data completeness at a very
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important site. Routine/collocated data pairs will be used when Pb concentrations of both
samples are greater than or equal to 0.02 |j,g/m3. Prior to 2008, this cutoff value was 0.15
Hg/m3.
• Pb Strip Audits-The requirement for the analysis of six Pb audit strips per quarter (three
strips at two concentration ranges) has not changed. However, the audit concentration ranges
have changed. The lower concentration range is 30 to 100% of the NAAQS and the higher
concentration range is 200 to 300% of the NAAQS. This activity does not affect the Pb-PEP;
however, the service lab for the PEP will participate in inter-laboratory comparative PEs.
• Pb-Performance Evaluation Program (Pb-PEP)-The implementation of an audit similar to
the PM2.5 PEP is a new requirement and it provides some assessment of overall bias. An
additional focus on the laboratory analysis and the local primary sampler operating
proficiency is included in the new Pb-PEP. The program as a whole will be a mix of one or
two conventional PEP-like independent audits with additional collocated sampling conducted
by the state or local agency using an independent analytical laboratory.
This QAPP focuses on one QA activity, the Pb-PEP, which is associated with Pb monitoring.
The background and rationale for the implementation of the Pb FRM/FEM monitoring network
can be found on the Office of Air and Radiation web site3.
With the end use of the air quality samples as a prime consideration, various networks can be
designed to meet one of the following six basic monitoring objectives:
• Determine the highest concentrations to occur in the area covered by the network
• Determine representative concentrations in areas of high population density
• Determine the impact on ambient pollution levels of significant source or source categories
• Determine general background concentration levels
• Determine the extent of regional pollutant transport among populated areas and in support of
secondary standards
• Determine the welfare-related impacts in more rural and remote areas.
The monitoring network consists of four major categories of monitoring stations that measure the
criteria pollutants. These stations are described below.
The SLAMS and Tribal Monitoring Network4 consists of-4,000 monitoring stations whose
size and distribution are largely determined by the needs of tribal, state and local air pollution
control agencies to meet their respective Tribal Implementation Plan and State Implementation
Plan (SIP) requirements.
3 http://www.epa.gov/air/lead/
4 http://www.epa.gov/ttn/amtic/slams.html
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The NCore Network5 is a multi-pollutant network that integrates several advanced
measurement systems for particulate matter, gaseous pollutants, and meteorology. The NCore
network is a relatively new network of approximately 80 sites that has been operating since
January 2011.
The Special Purpose Monitoring Stations (SPMS) network provides for special studies needed
by the monitoring organizations to support their SIPs and other air program activities. The SPMs
are not permanently established and, thus, can be easily adjusted to accommodate changing
needs and priorities. The SPMs are used to supplement the fixed monitoring network as
circumstances require and resources permit. If the data from SPMs are used for SIP purposes,
they must meet all QA and methodology requirements for SLAMS monitoring.
The Photochemical Assessment Monitoring Station6 (PAMS) network is required to measure
ozone precursors in each ozone non-attainment area that is designated as serious, severe, or
extreme. The required networks have from two to five sites, depending on the population of the
area. The current PAMS network has approximately 80 sites.
This QAPP only focuses on the QA activities of the SLAMS, Tribal, NCore, and 8PM
networks and the objectives of these networks, which include any Pb sampler used for
comparison to theNAAQS.
Throughout this document, the term "decision maker" will be used. This term represents the
individuals who are the ultimate users of ambient air monitoring data and, therefore, may be
responsible for activities such as setting and making comparisons to the NAAQS and evaluating
trends. Because there is more than one objective for these data and more than one decision
maker, the quality of the data will be based on the highest priority objective, which was
identified as the determination of attainment of the NAAQS.
Since the data for the monitoring networks can be used for NAAQS comparisons, the quality of
these data is very important. Therefore, a system has been developed to control and evaluate the
quality of data in order to make NAAQS determinations within an acceptable level of
confidence. During the development of the Pb NAAQS, the EPA used the DQO process to
determine the allowable measurement system imprecision and bias that would not significantly
affect a decision maker's ability to compare pollutant concentrations to the NAAQS. The
precision requirement (20% coefficient of variation [CV]) and bias requirement (±15%) are
based on total measurement uncertainty, which incorporates errors coming from all phases (e.g.,
field sampling, handling, analysis) of the measurement process. The collocated samples provide
adequate estimates of precision and bias. The Pb-PEP, if properly implemented, can provide the
bias estimate.
5 http://www.epa.gov/ttn/amtic/ncore/index.html
6 http://www.epa.gov/ttn/amtic/pamsmain.html
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Pb-PEP Description
A PE is defined as a type of audit in which the quantitative data generated in a measurement
system are obtained independently and compared with routinely obtained data to evaluate the
proficiency of the analyst or laboratory. In the case of the Pb-PEP, the goal is to evaluate total
measurement system bias, which includes measurement uncertainties from the field and the
laboratory activities. The pertinent regulations for this PE are found in 40 CFR Part 58,
Appendix A, section 3.3.4.4. The number of audits required is based on the number of routine
sites within a PQAO. The program will require the same number of audit samples as required
for PM2.5, however the responsibility for collecting the PEP samples may be shared between
EPA and the SLT monitoring agencies:
PQAOs with < 5 sites require five audits (one EPA or independent audit, four SLT site-
collocated audits)
PQAOs with > 5 sites require eight audits (two EPA or independent audits, six SLT site-
collocated audits)
The Pb PEP QAPP focuses on one QA activity, the Pb-PEP, which is associated with Pb
monitoring. The background and rationale for the implementation of the Pb FRM/FEM
monitoring network can be found on the Office of Air and Radiation Web site7.
The strategy is to collocate a portable Pb air sampling instrument with a routine SLAMS or
SPMS air monitoring instrument, operate both monitors in the same manner, and then compare
the results. In addition to this collocation with an independent portable audit sampler, four or six
filter samples (depending on number of total sites within a PQAO) as described above and in 40
CFR Part 58, Appendix A, Section 3.3.4.3 will be collected by SLTs from sites at which they
operated their own collocated samplers for precision. EPA expects that these collocated samples
would be collected and submitted as soon as possible to the EPA's PEP analytical support
laboratory.
The implementation of the Pb-PEP is a monitoring organization responsibility. However, similar
to the PM2.5 PEP program, EPA has developed and implemented a federal Pb-PEP to acquire the
independent PEP samples. Monitoring organizations have the option to self-implement the
independent collection of PEP samples or they may utilize the federally implemented program.
Self-implementation will require monitoring organizations to meet a level of independence and
adequacy. 40 CFR Part 58 Appendix A and a guidance document by OAQPS at
http://www.epa.gov/ttn/amtic/files/ambient/pm25/qa/pepadequacy.pdf provides the information
on adequacy and independence. Since this information may change over the years, the guidance
document will also be posted on AMTIC and will be reviewed annually and updated as
necessary.
7 http://www.epa.gov/air/lead/
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EPA will use the ESAT contract that is currently in place in each Region to provide the
necessary field and laboratory activities for the federally implemented program. Each EPA
Regional Office will implement the field component of this activity. The EPA Region 9
Laboratory located in Richmond, CA, will be responsible for the lab analysis of high volume
filters. An independent laboratory capable of performing X-ray fluorescence (XRF) analysis of
the low volume PMio Pb filters will be selected by OAQPS. In addition, the EPA NRMRL
Metrology Laboratory will function as a field standards verification facility. The EPA Region 4
laboratory will provide back-up capabilities for the high volume filter analysis if the Region 9
laboratory requires assistance. OAQPS's technical support contractor will provide data
management support including development and maintenance of web-enabled data entry forms,
web reporting utilities, and posting final results to AQS. Note that some Agencies can assume
the full responsibility of conducting the independent audits in their jurisdiction if they can meet
the independence and adequacy requirements.
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6.0 Project/Task Description
The purpose of this element is to provide the participants with a background understanding of the
project and the types of activities to be conducted, including the measurements that will be taken
and the associated QA/QC goals, procedures, and timetables for collecting the measurements.
6.1 Description of Work to be Performed
In general, the measurement goal of the Pb-PEP is to estimate the bias of routine Pb FRM/FEM
national network, aggregated at various levels. These levels of aggregation are: local, tribal and
state; PQAO; regional; and national levels. This is accomplished by: collocating a Pb-PEP
sampler with a routine state, local or tribal Pb sampler; collecting a 24-hour sample; and
comparing the two concentrations in units of micrograms per cubic meter (//g/m3) measured at
local conditions. The applicable regulations for this activity can be found in 40 CFR Part 58,
Appendix A, Section 3.3.4.4.
The following sections describe the measurements required for the routine field and laboratory
activities for the network. Independent field measurements will be performed by EPA's
Regional ESAT contractors or by independent SLT PEP auditors. The SLT agencies will also
provide four or six sample filters from at least one collocated site in each PQAO's network.
High volume TSP samples will be analyzed with inductively coupled plasma mass spectrometry
(ICP-MS) and low volume PMio filters will be analyzed using XRF spectroscopy.
The following information provides a brief description of these activities. Detailed SOPs have
been developed for all field and laboratory activities and have been distributed to all field,
laboratory, and regional contacts identified on the distribution list described in Element 3.0,
Distribution. These SOPs can be found on the AirQA Web site
(https://www.sdas.battelle.org/AirOA/) under Pb PEP, Documentation, and on the AMTIC Web
site (http://www.epa.gov/ttnamtil/). Figure 6-1 provides a basic description of the Pb-PEP.
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Regions 1-10
Field Work
Field
Pb-PEP and Collocated
Samples
Hi-Vol filter analysis
New Filter^ J[ \ Lab or Lo-Vol filter
analysis Lab
IT Contractor
Data
Management
Figure 6-1. The Lead (Pb) PEP Overview
EPA procures 8 inch x 10 inch high volume glass fiber filters and 47 mm
polytetrafluoroethylene (PTFE) filters for the Pb high volume TSP and low volume PMio
samplers, respectively, operating in the national network for the calendar year.
EPA subjects the production lot of these filters to acceptance testing that is required by the
applicable FRM (see 40 CFR Part 50 Appendices B, G and L). SLTs generally receive glass
fiber and 47 mm filters by ordering from OAQPS for their monitoring programs.
Consequently, the SLTs may use their own supply of filters for their collocated PEP samples
if the filters originate with the production lots purchased and tested by OAQPS under the
national contract.
EPA will distribute high volume filters directly to EPA Regions where they will be
inventoried, inspected, and prepared for the field. Low volume filters for the Federal
independent audits will be loaded into cassettes and shipped upon request to the requestor by
EPA's designated handler, which is currently the EPA Region 4 Filter Weighing Lab.
The auditor will initiate the electronic chain of custody (COC)/field data sheet (FDS) form on
the AirQA Web site and print a hard copy to carry to the field. The SLT-collocated PEP
sample COCs will be initiated by the operator or auditor designated by the SLT in the same
manner.
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• The auditor or SLT collocated sampler operator will take the filters and COC/FDS form to
the field and operate the collocated Pb audit sampler (TSP or low volume PMio).
• The auditor will collect and send high volume filters and signed copies of the COC/FDS
forms to the Region 9 Pb-PEP Laboratory. Low volume filters will be collected and sent to
EPA's designated XRF laboratory along with signed copies of the COC/FDS forms. A copy
of the field data, instrument download data, and associated sampling records for all audits
will be kept at the auditor's field office.
• The auditor or SLT collocated sampler operator will electronically enter the data from the
COC/FDS form and upload the raw sampler data files on OAQPS's Pb-PEP data
management Web site, AirQA, which is hosted and maintained by the technical support
contractor.
• The Region 9 Pb-PEP Laboratory will receive, inspect, and analyze the high volume filters.
EPA's designated XRF laboratory will receive, inspect, and analyze the low volume filters.
Each support lab will validate their analytical results and submit analytical results along with
electronic copies of the signed COC/FDS forms to OAQPS's technical support contractor via
the AirQA Web site. The low volume cassettes will be shipped back to the EPA Region 4
Filter Weighing Lab to be washed and prepared for re-distribution.
• OAQPS's technical support contractor will process the electronic data submitted by the field
and lab, associate the related data elements in the Pb-PEP database, perform automated data
validation checks against the Pb-PEP acceptance criteria, and submit data for EPA's final
review and approval.
• Each Region's Pb-PEP Lead (or designated QA Officers) will review the automated Pb-PEP
validation results, indicate approval or rejection, and initiate investigation of any
questionable data.
• OAQPS's technical support contractor will prepare and upload the approved data to EPA's
AQS.
• The OAQPS program lead will assess the data calculating the bias statistic to determine bias
within the Pb monitoring network.
6.2 Field Activities
There are two types of field operations of the Pb-PEP: independent Pb-PEP collocated audits and
additional SLT collocated sampling runs. The independent Pb-PEP audits are conducted by the
ESAT contractor or approved organization that performs a completely independent sampling
event once if the PQAO contains five monitoring sites or less or twice if the PQAO contains
more than five monitoring sites. Additional SLT collocated audits are conducted by the SLT at
an existing collocated site at a rate of four or six samples according to the criteria above. These
samples are separate from the normal collocated runs prescribed by the monitoring collocation
requirements. In other words, these samples cannot be counted as a normal collocated run and
Pb-PEP audit sample. This process is repeated for both high volume sampling and low volume
sampling. Both high volume and low volume sampling methods must be audited. Individual
methods within the high volume and low volume groups should be grouped together as one for
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the aggregate count to determine the number of audits necessary. All sampling must be
conducted in conformance to the prescribed FRM. General instructions are found in this Pb-PEP
QAPP and specific instructions are detailed in the Pb-PEP high volume and low volume field
SOPs.
The following general requirements must be observed to ensure the quality of the data:
• Samples must be collected and handled in a manner that adheres to the specifications in this
QAPP and the SOPs for field activities.
• The samplers must be operated in adherence to the manufacturers' operating manuals, which
discuss the sampler's proper transport, assembly, calibration, verifications, operation, and
maintenance. All deviations must be identified in the PEP or SLT's SOP for that sampler
and the applicable QAPP. Changes to the procedures of the independent audits will be vetted
among and approved by the PEP work group.
• Siting criteria and operating schedules must adhere to specific site requirements defined in 40
CFR Part 58 Appendices D and E for the identified sites. An exception may be where a
sampler is not properly sited according to 40 CFR Part 58, but the monitoring organization
has an approved waiver from the EPA Regional ambient air monitoring program.
• Personnel who perform the Federal and SLT independent PEP audits must complete the
required initial training and then participate in recertification training at least every 2 years.
This training may be provided by qualified PEP trainers in the 10 EPA regional offices or
OAQPS.
• For SLT collocated audits, agencies that have personnel other than independent auditors to
set up these sampling events and collect the filter samples should ensure that the operators
have been fully trained on the applicable requirements of the Pb monitoring network
"Implementation Plan". The SLT auditors should be independent from the routine operators
and preferably part of the QA staff.
The performance requirements of the Pb-PEP air sampler are specified in 40 CFR Part 50,
Appendix B for TSP high-volume samplers and Appendix Q for PM10 low volume samplers.
Appendix Q refers to the technical specifications for the low-volume samplers as stated in
Appendix L; the only difference in the two methods is the absence of the PIVb.s separator.
Required recovery times and shipping schedule are provided in Section 6.4.4. Table 6-1
summarizes some of the more critical performance requirements.
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Table 6-1. Design/Performance Specifications
Equipment
Acceptance Criteria
Reference
Pb-TSP Filter Design Specifications (Certified by Vendor)
Size
Exposed Area
Medium
Collection efficiency
Maximum pressure drop
pH
Integrity
Tear Strength
20.3 ±0.2x25.4 ±0.2 cm
406.5 cm2
Glass Fiber
99%
42-54 mm Hg at 1.5 std m3/min
6-10
2.4 mg maximum weight loss
500g min for 20mm strip in
weakest dimension
40 CFR Part 50, Appendix B, Section
7.1.1
40 CFR Part 50, Appendix B, Section
7.1.2
40 CFR Part 50, Appendix B, Section
7.1.3
40 CFR Part 50, Appendix B, Section
7.1.4
40 CFR Part 50, Appendix B, Section
7.1.5
40 CFR Part 50, Appendix B, Section
7.1.6
40 CFR Part 50, Appendix B, Section
7.1.7
40 CFR Part 50, Appendix B, Section
7.1.9
Pb-TSP Sampler Performance Specifications
Min/Max sampler flow rate
at actual conditions
Flow regulation
Flow rate sensor
Ambient temperature
sensor
Barometric pressure
Clock/timer
1.1 to 1.7m3/min
1.000±5%m3/hr
Readable to nearest 0.02 m3/min
-30°C-45°C
O.PC res. ±1.0°C accuracy
500-800 mm Hg
± 5 mm res
± 5 minutes/24-h sample
40 CFR Part 50, Appendix B, Section
7.2.2 and 7.2.3
40 CFR Part 50, Appendix L, Section 7.4
40 CFR Part 50, Appendix B, Section
7.4.2
Volume II-MS. 2.12
40 CFR Part 50, Appendix B, Section 7.5
40 CFR Part 50, Appendix B, Section
7.6. land 7.6.2
No Reference
Pb-PMw Filter Design Specifications (Certified by Vendor)
Size
Medium
Support ring
Pore size
Filter thickness
Maximum pressure drop
Maximum moisture pickup
Collection efficiency
46.2-mm diameter ± 0.25 mm
Polytetrafluoroethylene
Polymethylpentene or
equivalent inert material
0.38-± 0.04 mm thick
46.2 ± 0.25 mm outer diameter
3.68 (± 0.00 mm, -0.51 mm)
width
2 um
30-50 um
30cmH2Oatl6.67LPM
10-ug increase in 24 hr
99.7%
40 CFR Part 50, Appendix L, Section 6. 1
40 CFR Part 50, Appendix L, Section 6.2
40 CFR Part 50, Appendix L, Section 6.3
40 CFR Part 50, Appendix L, Section 6.4
40 CFR Part 50, Appendix L, Section 6.5
40 CFR Part 50, Appendix L, Section 6.6
40 CFR Part 50, Appendix L, Section 6.7
40 CFR Part 50, Appendix L, Section 6.8
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Equipment
Filter weight stability
Alkalinity
Acceptance Criteria
<20ug
<25.0 microequivalents/g
Reference
40 CFR Part 50, Appendix L, Sections
6.9. land 6.9.2
40 CFR Part 50, Appendix L, Section
6.10
Pb-PMw Sampler Performance Specifications
Sample flow rate
Flow regulation
Flow rate precision
Flow rate accuracy
External leakage
Internal leakage
Ambient temperature
sensor
Filter temperature sensor
Barometric pressure
Clock/timer
1.000m3/hr
1.000±5%m3/hr
2% CV
±2%
<80 mL/min
<80 mL/min
-30°C to 45°C
O.PC resolution and ± 2°C
accuracy
-30°C-45°C
0. PC resolution and ± 1.0°C
accuracy
600 mm Hg to 800 mm Hg
5-mm resolution and ± 10-mm
accuracy
Date/time
1 min resolution and ± 1
min/mo accuracy
40 CFR Part 50, Appendix L, Section 7.4
40 CFR Part 50, Appendix L, Section 7.4
40 CFR Part 50, Appendix L, Section 7.4
40 CFR Part 50, Appendix L, Section 7.4
40 CFR Part 50, Appendix L, Section 7.4
40 CFR Part 50, Appendix L, Section 7.4
Volume II-MS. 2.12
40 CFR Part 50, Appendix L, Section 7.4
Volume II-MS. 2.12
40 CFR Part 50, Appendix L, Section 7.4
Volume II-MS. 2.12
40 CFR Part 50, Appendix L, Section 7.4
Volume II-MS. 2.12
40 CFR Part 50, Appendix L, Section 7.4
The independent air samplers used by ESAT contractors will be purchased and distributed by
EPA OAQPS. The samplers procured must be designated as FRM or meet FRM specifications
in 40 CFR Part 50,
B (high volume) and Appendix L (low volume). SLT agencies that conduct independent audits
must also use independent FRM samplers for their sampling events. The FRM-compliant
sampling instruments should be intrinsically capable of accurately sampling for TSP- or PMio-
borne Pb. Nevertheless, the Pb-PEP auditors are responsible for verifying the performance
parameters of the audit Pb samplers after assuming custody of the samplers. Quarterly internal
audits of the samplers and annual verifications of calibrators are performed thereafter. Element
15.0, Instrument/Equipment Testing, Inspection, and Maintenance Requirements, lists all the
primary operational equipment requirements for the Pb-PEP data collection operations. All
additional support equipment will be listed in the Pb-PEP high volume and low volume field
SOPs.
6.2.1 Independent PEP Sampling Events
The independent PEP sampling events are covered in detail in the Pb-PEP field SOPs for audits
conducted by Federal ESAT contractors and SLT auditors. A summary of events is included in
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this QAPP in Section 6.4.3.
6.2.2 SLT Collocated Site PEP sampling events
These events are performed at sites with collocated samplers that are owned and operated by
SLT agencies. The samplers are routinely used to collect samples for precision measurements of
the SLT's network to which the site belongs. SLT agencies will follow their own SOPs for
sample collection while adhering to the provisions regarding sample shipping, data upload to the
AIRQA database and audit validation prescribed in the Pb-PEP SOP and Pb-PEP QAPP.
6.2.3 Critical "Field Data" Measurements
The most critical measurement is the total amount of air drawn through the filter during a
sampling event. The mass of Pb that has been deposited on the filter is divided by this value to
determine the 24-hour average concentration of Pb during the sampling event. The PMio is also
dependent on the flow rate of the sampler, which determines how precisely the particulate matter
separator at the inlet eliminates particles larger than PMio from the filtrate. Table 6-2 lists the
measurements that are made by the air sampler (or possibly other instruments) and are stored in
the instrument for downloading during sample recovery.
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Table 6-2. Field Measurement Requirements
Information to be Provided
Availability
Anytime"
End of
Periodb
Visual
Display0
Data
Outputd
Format
Digital Reading6
Units
Pb-TSP Samplers
Flow rate, average for the sample period
Sample volume, total
Temperature, ambient, minimum, maximum, average for the
sample period
Barometric pressure, ambient, minimum, maximum, average
for the sample period
Date and time
Sample start and stop time settings
Sample period start time
Elapsed sample time
Elapsed sample time out of specificationf
User-entered information, such as sampler and site
identification
*
*
*
*
•/
•/
—
*
—
•/
•/
•/
•/
•/
—
•/
•/
•/
•/
•/
*
•/
•/
•/
•/
•/
•/
•/
•/
•/
•/
•/
^
't
—
•/
•/
•/
•/
•/
xx.x
xx.x
xx.x
XXX
YY/MM/DD HH:mm
YY/MM/DD HH:mm
YYYY/MM/DD
HH:mm
HH:mm
On/off
As entered
m3/min
m3
°C
mmHg
Yr/mo/day hr min
Yr/mo/day hr min
Yr/mo/day hr min
Hr min
Pb-PMw Samplers
Flow rate, 30-second maximum interval
Flow rate, average for the sample period
Flow rate, coefficient of variation for the sample period
Flow rate, 5-minute average out of specificationf
Sample volume, total
Temperature, ambient,
30-second interval
Temperature, ambient, minimum, maximum, average for the
sample period
Barometric pressure, ambient, 30-second interval
Barometric pressure, ambient, minimum, maximum, average
for the sample period
Filter temperature, 30-second interval
Filter temperature, differential, 30 -minute interval, out of
specificationf
Filter temperature, maximum differential from ambient, date,
time of occurrence
Date and time
Sample start and stop time settings
Sample period start time
Elapsed sample time
Elapsed sample time out of specification
Power interruptions >1 min, start time of first 10 power
interruptions
User-entered information, such as sampler and site
identification
•/
*
*
•/
*
•/
*
•/
*
^
*
*
•/
•/
—
*
—
*
•/
—
•/
•/
•/
•/
—
•/
—
^
—
^
*
—
•/
•/
•/
•/
•/
•/
•/
*
*
•/
•/
•/
•/
•/
•/
•/
•/
*
•/
•/
•/
•/
•/
*
•/
*
•/
•/
•/
•/
—
•/
—
^
—
^ •
*
—
•/
S •
S •
s •
•/
s •
XX.X
XX.X
XX.X
On/off
XX.X
XX.X
XX.X
XXX
XXX
xx.x
On/off
X.X, YY/MM/DD
HH:mm
YY/MM/DD HH:mm
YY/MM/DD HH:mm
YYYY/MM/DD
HH:mm
HH:mm
On/off
lHH:mm, 2HH:mm,
etc.
As entered
L/min
L/min
%CV
m3
°C
°C
mmHg
mmHg
°C
°C, Yr/mo/day hr
min
Yr/mo/day hr min
Yr/mo/day hr min
Yr/mo/day hr min
Hr min
Hr min
S Provision of this information is required.
f Legacy high volume samplers, if they use volumetric flow control, do not provide ambient temperature and barometric pressure. These values are necessary,
however, to convert the flow rate recorded at standard conditions to flow rate at local conditions. The FRM allows a 24-hour average value supplied by the
nearest National Weather Service reporting facility to be used if the ambient temperature and barometric pressure are not measured directly at the site. These
measurements may also be made at the site with National Institute of Standards and Technology (NIST) Traceable instruments that have been certified to
perform within acceptable accuracy within a year of the sampling event.
— Not applicable.
* Legacy high volume samplers do not provide very much real-time data. Provision of this information is optional. If information related to the entire sample
period is optionally provided before the end of the sample period, the value provided should be the value calculated for the portion of the sample period
completed up to the time the information is provided.
a Information must be available to the independent PEP auditor at any time the sampler is operating, whether it is sampling or not.
b Information relates to the entire sample period and must be provided following the end of the sample period until the auditor manually resets the sampler or
the sampler automatically resets itself upon the start of a new sample period.
0 Information shall be available to the auditor visually.
d Information will be available as digital data at the sampler's data output port following the end of the sample period until the auditor manually resets the
sampler or the sampler automatically resets itself upon the start of a new sample period.
e Digital readings, both visual and data output, shall have no less than the number of significant digits and resolution specified.
f Flag warnings may be displayed to the auditor by a single-flag indicator or each flag may be displayed individually. Only a set (on) flag warning must be
indicated; an unset (off) flag may be indicated by the absence of a flag warning. Sampler users should refer to Section 10.12 of Appendix L about the validity
of samples for which the sampler provided an associated flag warning.
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In addition to the measurements collected in Table 6-2, supporting field data will also be
collected. These additional parameters are identified in the Pb-PEP high volume and low volume
field SOPs and help to identify the samples, ensure proper COC, holding times, and data quality.
The information may also be important for validating data that appear to be unusual or
unexpected. This information is recorded on the COC/FDS Form.
6.3 Laboratory Activities
The Pb-PEP requires two separate analyses depending on the size range of the Pb particulate, the
samplers which collect it, and the filter media on which it is collected.
ICP-MS Analysis for Glass Fiber Filters (High Volume TSP Sampling)
The primary activities and steps are:
• Preparation of extraction fluids and check standards for the ICP-MS
• Calibration and verification of ICP-MS
• Receipt of filter samples from the Federal and SLT independent auditors, and from the
collocated sampler operators or auditors
• Recording COC data into the laboratory information management system (LEVIS)
• Filter handling,
• Sample extraction
• Analysis of extracts with ICP-MS instrument
• Resulting data entry and validation
• Sample filter and extract retention and archival, and
• Transmittal of the results and validation data to the AIRQA Web site.
EPA Region 9 operates the Pb-PEP laboratory for the high volume Pb-TSP samples. Specific
detailed instructions will be available in the laboratory SOPs. They are attached as Appendix 3.
XRF Analysis for PTFE 47 mm Filters (Low-Volume PMio Sampling)
The primary activities and steps are:
• Receipt of filter samples from the Federal and SLT independent auditors, and from the
collocated sampler operators
• Recording COC data into the LEVIS
• Filter handling
• Analyze check standards with the XRF instrument
• Load Filters into XRF sample holders
• Subject Filters and blanks to XRF analysis
• Resulting data entry/management,
• Sample filter and extract retention and archival
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• Transmittal of the results and validation data to the AIRQA Web site.
• Returning filter cassettes to the designated originator of the filters, presumably EPA Region 4
PEP support laboratory in Athens, GA.
EPA OAQPS will secure the Pb-PEP analytical XRF laboratory services for the low volume Pb-
PMio samples. Since this will be a commercial vendor, specific detailed instructions will be
found in the laboratory SOPs. They are attached as Appendix 4.
The participating analytical support laboratories will implement an internal QA/QC program that
incorporates the pertinent elements of good laboratory practices (GLPs). The GLP will include
the following:
• Establishing specific QA goals and implementing procedures for the particular analyses
performed in support of the PEP.
• Adherence to the vendor's operations manual for the proper operation of the extraction
and/or analytical equipment (TCP-MS and XRF spectroscopy).
• Adherence to the SOPs for the program.
• Adherence to the standards, principles, and practices outlined in the Pb-PEP QAPP.
• Special attention must also be given to any activity involving filter handling. This area
contains the greatest potential for introducing measurement uncertainty, and care must be
given to the proper handling of both TSP and PMio filters.
Table 6-3 provides the performance specifications of the laboratory environment and equipment.
Table 6-3. Laboratory Performance Specifications
Equipment
Acceptance Criteria
Pb-TSP Analyses
Inductively Coupled Plasma
Mass Spectrometer
Reagent Water
Nitric Acid (HNO3)
Argon gas supply
MDL
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6.3.1 Critical Laboratory Measurements
For generating a concentration, the critical lab measurement of high-volume TSP samples is the
Pb concentration in (j,g/filter strip. This value is used to calculate the Pb concentration on the full
TSP filter that, when divided by the air volume in cubic meters (m3) pulled through the filter,
provides a final concentration (|j,g/m3). With respect to the XRF analysis, the resulting value is
expressed as ng/cm2. This value is multiplied by a specified exposed area for the 46.2 mm (4.62
cm) PTFE PMio filter. Then it can be divided by the 24-hour volume of air sampled through it
for the average concentration. In addition to these critical measurements, supporting laboratory
data will also be collected to help identify the samples, ensure proper COC, holding times, and
data quality. These additional parameters are described in more detail in SectionlS.0 Analytical
Methods Requirements and in the laboratory SOPs.
6.4 Schedule of Activities
The Pb-PEP consists of laboratory and field activities that must be coordinated and completed in
a timely and efficient manner for the program to be successful. This includes activities such as
acquiring equipment and supplies, developing sampling and analytical schedules, initiating the
COC/FDS forms, conducting the setup and sampling event at the site, extracting and analyzing
filters, performing QC checks and data validation, and uploading to the AQS database. The
sections below describe some of the time-critical components of conducting Pb-PEP audits.
Additional detail is provided in the Pb-PEP SOPs.
6.4.1 Pb-PEP Audit Frequency
The sampling design has been codified in 40 CFR Part 58, Appendix A, Section 3.3.4.4, as:
"Each year, one performance evaluation audit, as described in section 3.2.7 of this appendix,
must be performed at one Pb site in each primary quality assurance organization that has less
than or equal to five sites and two audits at primary quality assurance organizations with
greater than five sites. In addition, each year, four collocated samples from primary quality
assurance organizations with less than or equal to 5 sites and six collocated samples at primary
quality assurance organizations with greater than 5 sites must be sent to an independent
laboratory, the same laboratory as the performance evaluation audit, for analysis. "
In addition to the required criteria above, the Pb-PEP will audit all SLAMs and SPM Pb
monitoring sites per PQAO over a 6-year period.
Pb sampling in the NAAQS and NCore network may be conducted using either the high volume
or low volume sampling method. In determining how many Pb-PEP audits are required for a
PQAO, all Pb monitoring sites, regardless of sampling method, must be added together to
determine the correct audit frequency. The one exception will be that low volume PMio sites in
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the NCore network are treated as one PQAO. In this situation, each primary NCore PMio Pb
sampler will be audited once per year.
6.4.1.1 Pb-PEP at NCore
The NCore network is treated as its own PQAO when planning low volume PMio Pb-PEP audits.
Every primary, low volume PMio Pb sampler at an NCore site will receive one Pb-PEP audit
annually. The reason this frequency of audits was instituted was because that the NCore network
contains only 20 sites with PMio Pb samplers. 15% of these would provide an insufficient
number of audits to calculate bias with any degree of confidence. If a PQAO has agreed to self-
implement their Pb-PEP, they will be responsible to conduct an audit of each primary NCore
PMio Pb sampler in their jurisdiction.
There are approximately five NCore sites that have collocated PMio Pb samplers. EPA is
requesting that each of these collocated sites provide four SLT collocated sampler samples to the
PEP analytical support laboratory during the course of a calendar year.
To sum up for the Pb-PEP, TSP samplers at NCore sites are to be treated like any other Pb
samplers in the individual monitoring organization PQAOs. In other words such samplers go
into the 6-year cycle, for one or two independent PEP audits, depending on the total number of
Pb monitoring sites (which might include any non-NCore, low volume PM-10 Pb sites) in the
PQAO.
6.4.2 Pb-PEP Sampling Schedule
On or before December 1, EPA Regions will work with monitoring organizations to select and
develop a list of sites for the evaluations to be conducted for the next calendar year. The
Regional WAM/TOPO/DOPOs, with the assistance of the ESAT contractors, will attempt to
determine the most efficient site visit schedule. This schedule should be based upon the
following:
• CFR requirements for audit frequency
• Network audit completeness (all sites audited in 6 years; all NCore PMio Pb low volume
samplers each year)
• Meeting the same monitoring schedule as the monitoring agency's routine samplers to be
evaluated
• Site proximity (the sites that are closest in proximity to each other may be visited within the
same day or week)
• Coordination with other audit programs (PM2.5 and PMio-2.5 PEP, and NPAP) if possible.
PEP audits should be conducted on normal sampling days so that the evaluation does not create
additional work for the monitoring organizations. However, if the monitoring organization is
amenable to perform a PE on a day other than a routine sampling day and is willing to post the
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result to AQS, the Pb-PEP visit can be scheduled for that day.
SLT Collocated Sampling Events
SLTs have been instructed through the Pb monitoring QA Implementation Guidance to provide
the collocated site samples from sampling events that are on different days than the precision
sampling events. They are supposed to be seasonably distributed; however, if a make-up is
needed the seasonality can be disregarded.
6.4.3 General Sequence of Pb-PEP Activities
6.4.3.1 "Independent"_FRMPb-PEP audit
Below is a list of activities, in general chronological order, that are performed by Pb-PEP field
personnel (auditors) and the laboratory to conduct an "Independent" FRM Pb-PEP audit:
EPA, ESAT staff and independent SLT auditors who participate in the Pb-PEP are certified
through hands-on exercises and a written examination in the operation, conduct, and
management of the Pb-PEP activities. This activity is coordinated by the EPA OAQPS PEP
program lead if the training event is conducted at the national level or by the EPA Regional PEP
lead if conducted at the regional level.
1. The EPA WAM/TOPO/DOPO selects the Pb sites to be audited for the current calendar
year by the Pb-PEP.
2. The WAM/TOPO/DOPO, auditor, and monitoring organization coordinate scheduling
site visits if needed.
3. The auditor and site operators coordinate the details of the audit. EPA distributes boxes
of glass fiber filters for the high volume TSP sampling to each EPA regional office and
each SLT independent auditing group. EPA or its designated handler ships the PMio
filters to the auditor.
4. Each high volume filter recipient pulls a randomly chosen filter from the box and ships to
the ICP-MS laboratory for lot blank analysis. PMio filter blanks are supplied to the XRF
laboratory by OAQPS or the designated handler.
5. The auditor transports the audit sampler to the site and evaluates the site for safety prior
to setup.
6. The auditor assembles the sampler and sets the date/time, then performs leak checks,
barometric pressure verifications, temperature (ambient and filter) verifications, and flow
rate verifications.
7. The auditor performs the field blank exercise, if needed, and installs the sampling filter.
8. The auditor programs the sampler to run during a 24-hour sampling event (midnight to
midnight).
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9. The sampler pulls ambient air through a filter over a 24-hour time period on the
scheduled date/time.
10. The auditor recovers the filter and downloads recorded sampling event summary data
11. The auditor disassembles the sampler.
12. The auditor packages the recovered filter and ships it along with the COC/ FDS forms to
the analytical laboratory.
13. The auditor will enter the data from the COC/ FDS form(s) and upload the raw sampler
data files to the OAQPS Pb-PEP data management Web site.
14. The Pb-PEP laboratory receives filters, logs them in as appropriate, and performs
extraction and/or analysis.
15. The Pb-PEP laboratory reviews and validates the laboratory data.
16. EPA's technical support contractor will process the electronic field and laboratory data,
associate related elements in the database, perform manual and automated data validation
checks, and make the data available for review and approval.
17. The Regional Pb-PEP Leads (or designated QA Officers) approve data that are to be
loaded into the AQS.
18. The OAQPS National Pb-PEP Lead ensures the Pb-PEP data are being validated on a
timely basis and are acceptable and complete for AQS upload.
19. EPA's technical support contractor loads data into the AQS.
20. The OAQPS National Pb-PEP Lead uses the data to calculate the annual bias estimate.
6.4.3.2 SL T-owned Collocated site PEP samples
1. The SLT collocated sites from which samples are collected will be selected by the SLT.
If the resulting data suggest there may be an operational issue, the use of that site in
subsequent years will be determined in consultation with the associated EPA regional
office.
2. The EPA regional office Pb-PEP contact and monitoring organization coordinate
scheduling site visits if needed.
3. The SLT's site operators (and auditor(s), if utilized) coordinate the details of the
sampling event used to collect the samples for the PEP.
4. If the SLT requests a separate supply of filters for PEP use, EPA OAQPS will ship the
glass fiber filters or PMio filters to the contact supplied by the SLT. A random sample of
the glass fiber filters is taken from the box and supplied to the ICP-MS laboratory for a
lot/lab blank. Each year EPA will be supplying a supply of 10 unused 47 mm PTFE
filters to the XRF lab for background analysis. If the SLT uses a separate box of filters
supplied by EPA and it is used for more than one year, the SLT should send one filter
from the box in every year it is used beyond the first year.
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5. If the SLT uses their own stock of filters, the person preparing the audit cassettes should
send at least one randomly selected filter from the originating box of filters, whether
glass fiber or 47 mm PTFE, to the appropriate ICP-MS lab or XRF laboratory.
6. The SLT operator or independent operator should note any parameter of the monitoring
site that does not comply with the applicable regulations for Pb sampling. This
information should be entered on the COC/FDS in the comment section. If a waiver has
been issued for the site to be exempted for one or more requirements, the waiver should
be noted also in the comments.
7. The SLT operator (or auditor) completes as much information as possible on the web-
enabled COC/FDS at the AIRQA Web site.
8. The SLT's collocated sampler is typically permanently installed at the monitoring site;
therefore transport and setup will not be necessary. The SLT operator (or auditor)
performs leak checks, barometric pressure verifications, temperature (ambient and filter)
verifications, and flow rate verifications.
9. The SLT operator (or auditor) should perform at least one field blank exercise per year
per site from which PEP samples are derived.
10. The SLT operator (or auditor) installs the sampling filter.
11. The SLT operator (or auditor) programs the sampler to run during a 24-hour sampling
event (midnight to midnight) that coincides with a routine sampling event of the site's
primary sampler, but that is on a different day than a normal precision measuring event.
12. The sampler pulls ambient air through a filter over a 24-hour time period on the
scheduled date/time.
13. The SLT operator (or auditor) recovers the filter and downloads recorded sampling event
summary data. Post-sampling verification checks may be requested dependent on the
make and model of the audit sampler, or if pre-sampling verification checks were outside
of expected operating parameters
14. The SLT operator (or auditor) packages the recovered filter and ships it with the COC/
FDS forms to the analytical laboratory. EPA will supply prepaid shipping labels if the
SLT requests it.
15. The SLT operator (or auditor) will complete the data entry on the web-enabled COC/
FDS form(s) and upload the raw sampler data files to the OAQPS Pb-PEP data
management Web site.
16. The Pb-PEP laboratory receives filters, logs them in as appropriate, and performs either
the extraction and ICP-MS analysis or the XRF analysis.
17. The Pb-PEP laboratory reviews and validates the analytical data and transfers it to the
web-enabled QA Web site.
18. EPA's technical support contractor ensures the electronic field and laboratory data
successfully merge, and the automated data validation checks occur. They make the data
available for review and approval.
19. The Regional Pb-PEP Leads (or designated QA Officers and Independent SLT-PEP
auditors) approve data that are to be loaded into the AQS.
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20. The OAQPS National Pb-PEP Lead ensures the Pb-PEP data are being validated on a
timely basis and are acceptable and complete for AQS upload.
21. EPA's technical support contractor loads data into the AQS.
6.4.4 Implementation Time Lines
There are some other important benchmarks that must be met during implementation activities.
They involve both field and laboratory activities.
6.4.4.1 Field Activities
For best practice, the independent PEP and SLT-PEP auditor should retrieve the filters within 24
hours of the end of the sample exposure period. For independent PEP audits additional time
should be minimized. A passive blank could be collected to determine potential passive
contamination during long periods when the sampler is not running. Another way to avoid this
potential contamination is to arrange to retrieve the filter at or near the same time that the SLT
agency retrieves the routine primary filter for that site's sampling event. Additional studies may
be conducted to determine the potential impact of passive contamination over several days
between the conclusion of the sampling event and retrieval. The SLT collocated site operator
should retrieve the PEP sample at the same time the primary routine Pb filter sample is retrieved.
Ideally, the independent PEP and SLT-PEP auditor or SLT collocated site operator should ship
PEP samples on the day of retrieval to the appropriate laboratory. However, the retrieval
schedules for multi-site audit trips or long distances from offices may necessitate a need for more
flexibility. The independent PEP auditor or SLT collocated site operator should ship the exposed
filters within 48 hours of the end of the sampling period. Downloaded data from the portable
sampler and COC/FDS data will be uploaded to the AIRQA Web site for Pb-PEP upon arrival
back to the field office. Table 6-4 provides a summary of the key activities discussed above.
6.4.4.2 Laboratory Activities
Because Pb is very stable once deposited on a filter, the expedited analysis of individual samples
is not critical. It is more practical and economically desirable to accumulate a number of filters
for batch processing. The batch holding time for all filters is set at a maximum of 30 calendar
days from receipt by the laboratory until analysis is performed. Validation and transmittal of the
laboratory results to the QA Web site should be complete within 15 days.
Table 6-4. Implementation Summary
Activity
AUDITOR arrives on site
and loads filter in the sampler
Filter exposure
Filter collection3
Holding Time
NA
24 hours
< 24 hours
From
AUDITOR Office
Midnight (-12:00 a.m.) of
prescribed sampling day
End of sampling period
To
Mounting in sampler
Midnight (-12:00 a.m.)
following the sampling day
Recovery
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Sampler data collection
Shipped to laboratory
(best practice)
Transmittal of sampler run
data, FDS, and COC
Laboratory analysis
Data Validation and Web
Transmittal
NA
< 48 hours
24 hours
< 30 days
15 days
Recovery
End of sampling period
Upon arrival at field office
Sample Delivery Date at lab
Completion of analysis
Site exit
Shipment
QA Web site
Analysis
Upload to AIRQA Web site
6.4.5 Assessment Time Lines
6.4.5.1 Data Availability
The Pb-PEP laboratories should complete data validation and transmit/upload it to the QA Web
site within 15 days of the conclusion of the analysis of that batch. This data is immediately
available to the PEP auditors, the SLT operators of the collocated site samplers, and Regional
PEP leads. The Regional PEP leads are to review and approve or disapprove the recorded and
posted results by the end of each month. This is so that additional audits may be scheduled in the
event that a result has been invalidated due to circumstances associated with the conduct of the
audit. Note that an ambient concentration below the validation threshold does not by itself
constitute a reason for repeating an audit.
Each Pb-PEP audit result is posted to AQS as a conjugate to the monitoring site's value as
derived from the primary, routine sampler. In order for the Pb-PEP data to post in AQS, the
site's measured value must be already posted in AQS. SLT agencies are required to post
SLAMS data to AQS within 90 days after the end of the quarter as shown in Table 6-5.
The PEP technical support contractor will attempt to post available PEP data on or about the 15th
of every month. PEP data that do not post will be placed back in the queue until the next posting
date, at which time another attempt will be made to post it. Consequently, for SLT site data that
are submitted after the quarterly due date, the PEP data will post at the next opportunity. If an
SLT site's data have been posted and they do not see PEP data within 45 days after the last
posted sampling event, they should contact the Regional PEP contact to investigate the status of
the PEP data.
Table 6-5. Data Reporting Schedule for AQS
Reporting Period
January 1 -March 3 1
April 1-June 30
July 1 -September 30
October 1-December 3 1
Due Date
June 30
September 30
December 3 1
March 3 1
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6.4.5.2 Data Assessments
The Regional ESAT contractors are tasked to provide initial reviews and assessments of the Pb-
PEP field data. The Region 9 ESAT contractor and the Pb XRF analytical lab are tasked to
provide full validation and assessments of the Pb-PEP laboratory data. The Regional EPA
contacts are tasked to provide a final assessment of the Pb-PEP audit before it can be uploaded to
AQS. Following the monitoring organization's submittals of quarterly Pb FRM/FEM data,
OAQPS (via the support contractor) will load the Pb-PEP data into the AQS. The Pb-PEP
Laboratory Managers and the OAQPS technical support contractor(s) will review the Pb-PEP
data. They will report to the ESAT Workgroup and QA Workgroup any significant Pb-PEP
operations issues that are reflected by the data. Once both routine data and PE data for a site are
in the AQS database, OAQPS, EPA regions, and monitoring organizations can use the AQS data
evaluation programs, based on data quality assessment techniques, to assess this information.
National bias is determined based on statistical equations given in 40 CFR Part 58, Appendix A,
Section 4.
6.4.6 OAQPS Reporting Time Lines
6.4.6.1 QA Reports
OAQPS will issue an Annual QA Summary Report through the use of the AQS AMP 255
Report. Additional data will be available to the Regional PEP lead and participating SLT
agencies through the QA Web site. It will include:
• Basic statistics of the data including completeness;
• Pb-PEP audit results vs. routine SLAMS results;
• Results of collocation studies for precision of Pb-PEP samplers;
• QC charts for the laboratory;
• Pb-PEP sampler performance vs. acceptance criteria; and
• Results of blank analyses.
From the statistical analyses and results, Pb-PEP TSA findings, and a summary of the annual
standard certifications, all collected over the course of each calendar year, a more comprehensive
report will be generated. The Annual QA Report should be completed 6 months from the end of
December of the calendar year which it represents. Every third annual report will be superseded
by and incorporated into an interpretive 3-year QA Report drafted in the year following the third
year in the evaluation period. In other words, this report is a composite of the third year's data
and information and two previous annual reports, but with a more narrative interpretation and
evaluation of longer term trends with respect to Pb-PEP sampler and operational performance.
The first three-year report for the Pb-PEP will be drafted in 2014 and cover years 2011-2013.
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6.4.6.2 Assessment Reports
OAQPS will perform a QA assessment of the Pb-PEP ESAT contractors and SLT organizations
that have assumed some or all of the independent Pb-PEP activities as specified in Table 6-6.
Initial assessment findings will be documented and reported back to the audited organization
within 15 working days after the assessments. Final assessment reports, including responses to
findings and follow-up activities, will be submitted to the National Pb-PEP Project Leader at
OAQPS by the end of the first quarter of the following year to have the results summarized in the
Annual QA Summary and 3-year QA Reports.
6.5 Project Assessment Techniques
An assessment is an evaluation process used to measure the performance or effectiveness of a
system and its elements. As used here, "assessment" is an all-inclusive term used to denote any
of the following: audit, PE, management systems review (MSR), peer review, inspection, or
surveillance. Definitions for each of these activities can be found in the glossary (Appendix A).
Section 20.0, Assessments and Response Actions, presents the details of the assessments.
Table 6-6 provides information on the organizations implementing the assessment and the
frequency of these assessments.
Table 6-6. Assessment Schedule
Assessment Type
TSA of auditor and field
operations
Surveillance of auditor's
operations
Performance test of supporting
Analytical Laboratories
TSA of the laboratory operations
Data quality assessment
Assessment Agency
EPA Regional office
OAQPS at annual recertification of
auditors or by the EPA Regional
office as needed
NAREL and OAQPS
OAQPS or NAREL
OAQPS
Frequency
One per year
One per year unless there is a need
for additional Regional surveillance
One per year
One every 3 years
Every year
6.6 Project Records
The field and laboratory programs will establish and maintain procedures for the timely
preparation, review, approval, issuance, use, control, revision, and maintenance of documents
and records. Table 6-7 represents the categories and types of records and documents that are
applicable to document control for Pb-PEP information. Information on key documents in each
category is explained in more detail in Element 9.0, Documentation and Records.
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Table 6-7. Critical Documents and Records
Categories
Record/Document Types
Management and
organization
Reporting agency information
Organizational structure
Personnel qualifications and training
Training certification
Quality management plan
Document control plan
EPA directives
Grant allocations
Support contract
Site information
Network description
Site characterization file
Site maps
Site pictures
Environmental data
operations
Quality Assurance Project Plans
Standard operating procedures
Field and laboratory notebooks
Sample handling/custody records
Inspection/maintenance records
Raw data
Any original data (routine and quality control
data) including data entry forms
Data reporting
Air Quality Index Report
Annual state and local monitoring stations' air
quality information
Data/summary reports
Journal articles/papers/presentations
Data management
Data algorithms
Data management plans/flowcharts
Data management systems
Quality assurance (QA)
Good laboratory practices
Network reviews
Control charts
Data quality assessments
QA reports
System audits
Response/corrective action reports
Site audits
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7.0 Data Quality Objectives and Criteria for Measurement
The purpose of this element is to document the DQOs of the project and to establish performance
criteria for the environmental data operation (EDO) that will be used in generating the data.
7.1 Data Quality Objectives
DQOs are qualitative and quantitative statements derived from the DQO process that clarify the
monitoring objectives, define the appropriate type of data, and specify the tolerable levels of
decision errors for the monitoring program. By applying the DQO process to the development of
a quality system for Pb, EPA guards against committing resources to data collection efforts that
do not support a defensible decision.
During the process of revising the Pb NAAQS, the monitoring requirements for Pb were
reviewed and included monitoring options such as:
• Change in averaging time of the indicator from the fixed quarterly average to either a rolling
quarterly or monthly average; and a
• Option in monitoring device from the current FRM, the high volume TSP sampler, to use the
low volume PMio sampler in some circumstances.
Using the DQO process, EPA explored how changes in design value averaging times, sampling
frequency, data completeness, precision, and bias affect one's ability to compare Pb estimates to
a NAAQS value. A report on the DQO process can be found on the EPA AMTIC Web site8.
Based on this evaluation, EPA identified a measurement quality objective (MQO) for precision
of 20% for a 90% confidence limit CV and an overall absolute bias upper bound goal of 15%.
The Pb-PEP provides the measurements upon which the bias component of the national network
DQO is evaluated. In many environmental measurements, bias can be measured and evaluated
by simply introducing standard reference material into a measurement phase and evaluating the
results. Because there is no accurate way of introducing a known concentration of Pb particles
into a Pb sampler, the Pb-PEP was developed to serve, as closely as possible, as a reference
standard by which a relative network bias can be determined.
This value will be generated by the combined data from the independently acquired PEP filter
samples and samples from SLT collocated samplers that are submitted to and analyzed by the
PEP laboratory. The dataset will also include similarly acquired data from the low volume PMio
samplers at NCore and other sites. Goals will be assessed on 3 years of data at the PQAO level
of aggregation. While not mandated by the regulations, the bias for the different types of
samplers and origin of the filters will also be determined from the dataset.
: http://www.epa.gov/ttn/naaqs/standards/pb/data/20080929DQO.pdf
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7.1.1 Proposed Measurement Quality Objectives for Precision and Bias Data Quality
Indicators
Once a DQO is established, the quality of the data must be evaluated and controlled to ensure
that it is maintained within the established acceptance criteria. MQOs are designed to evaluate
and control various phases (e.g., sampling, preparation, analysis) of the measurement process to
ensure that total measurement uncertainty is within the range recommended by the DQOs. The
MQOs can be defined in terms of the following data quality indicators:
Accuracy - A term that is frequently used to represent closeness to "truth" and includes a
combination of precision and bias error components. The term "accuracy" has been used
throughout the CFR and in some of the elements of this document. It is quite difficult if not
impossible to make accurate real-time measurements of airborne Pb-containing particulate
matter, therefore the accuracy of filter based measurements must be apportioned into
measurement of precision and bias.
Precision - A measure of mutual agreement among individual measurements of the same
property usually under prescribed similar conditions. This is the random component of error.
Bias - The systematic or persistent distortion of a measurement process, which causes error
in one direction. Bias is determined by estimating the positive and negative deviations from
the true or reference value as a percentage of the true or reference value.
Representativeness—A measure of the degree in which data accurately and precisely
represent a characteristic of a population, parameter variations at a sampling point, a process
condition, or an environmental condition.
Detectability—The determination of the low-range critical value of a characteristic that a
method-specific procedure can reliably discern.
Completeness—A measure of the amount of valid data obtained from a measurement system
compared to the amount that was expected to be obtained under correct, normal conditions.
Data completeness requirements are included in the reference methods (40 CFR Part 50).
Comparability—A measure of confidence with which one dataset can be compared to
another. Since the PEP data are generated in the same manner, with the small exception that
PEP MQOs may be slightly tighter, comparability is not an issue at any level of aggregation.
The PEP's collocation events for precision will also provide an indication of the
comparability of the data produced from independent PEP audits and the results of analyzing
the filters from SLT-owned collocated samplers.
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7.2 Pb-PEP Measurement Quality Objectives
The Pb-PEP is, in essence, a small monitoring program. However, because it has the added
importance of being the program used to estimate bias at the PQAO level, it must have a greater
level of data quality than the national ambient air monitoring program. Tables 7-1, 7-2 and 7-3
list the MQOs for the field and laboratory activities of the Pb-PEP. Acceptance criteria have
been developed for each of these MQO attributes. In theory, if these MQOs are met,
measurement uncertainty should be controlled to the levels that will provide high confidence that
the values can be compared to the DQO.
Some MQOs for Pb-PEP are more stringent than routine Pb measurement quality objectives of
the national network. More detailed descriptions of these MQOs and how they will be used to
control and assess measurement uncertainty will be described in other elements of this QAPP
and in the SOPs.
The new Pb NAAQS requires that concentrations be reported at local or actual conditions. New
samplers include temperature and pressure sensors in the sampling unit to record the flow rate at
local conditions. Older model samplers without this capability may be used; however they
require a conversion using a 24-hour average ambient temperature and pressure measurement.
These data may be collected from other calibrated samplers that are at the monitoring site, or
they may deploy separate NIST traceable instruments to take these measurements over the 24-
hour run period.
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Table 7-2. ICP-MS Laboratory Measurement Quality Objectives
Parameter
Initial Calibration
Instrument Calibration Verification
Continuing Calibration Verification
Calibration Blank
Second Source Calibration Verification
Quantitation Limit Standard
Method Blank
Lab Control Standard
LCS Duplicate, Precision
Matrix Duplicate, Precision
Matrix Spike, Accuracy
Internal Standard
Audit Strips
Reagents (HNO3 and HCL)
Pb nitrate Pb (NO3)2
Code
ICAL
ICV
CCV
CB
scv
QLS
MB
LCS
LCS-D
MD
MS
IS
Frequency
Each day or every sample batch
After ICAL
Every 10 Samples
After each ICV/CCV
Each batch
After ICAL & after every 40
analytical samples
Each Batch
Each Batch
Each Batch (PM lOOnly)
Every 20 samples (TSP Only)
Every 20 samples
(TSP Only)
Every analysis
1 /quarter
NA
NA
Criteria
> 0.995 Correlation
Coefficient
90-110%
90-110%
< % QL
90-110%
60-140%
<%QL
85-115%
<20RPD
<20RPD
70-130%
60-125% of initial
CB
90-110%
ACS reagent grade
ACS reagent grade
(99.0% purity)
Corrective Action Upon Criteria Failure
No analysis until acceptable results
No analysis until acceptable results
No analysis until acceptable results
Stop analysis, recalibration and analysis of samples bracketed
by unacceptable result
No analysis until acceptable results
Determine the cause and re-analyze.
If sample results are non-detects or > 5 times MB accept
results
If sample results detectable and < 5 times MB rerun extract or
prepare new strips
Re-analyze once to verify. If the recovery is still
unacceptable
(1) For PMio filter, all associated results are reported and
qualified
(2) For TSP filter strip, the MB, LCS, and all associated
samples must be re-prepared and re-analyzed if there is
enough sample to work with.
Re-analyze once to verify. If exceeded again flag
Re-analyze sample and duplicate once. If exceeded again flag
If the MS does not meet these criteria, examine other QC
results to determine if a matrix problem exists. If laboratory
performance is in control, the poor MS accuracy is likely to
be matrix-related
If the intensities of the internal standards for the ICV, CCV,
or CB are out-of-control, recalibrate and re-analyze the
samples affected
If the intensities of the internal standards for the ICV, CCV,
and CB are within control limits but sample internal
standards are out-of-control, rerun the sample or rerun at an
appropriate dilution.
Re-analyze extract. If failure extract/run another set.
Flag
NF
NF
NF
NF
NF
NF
J
J
J
J
J
J
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Table 7-3. XRF Laboratory Measurement Quality Objectives
Parameter
Filter Visual Defect Check
(unexposed)
Pb blank filter Acceptance
Testing
Pre Sampling Filter Holding
Time
Analysis Audits
Lab Filter Blank
Thin Film Standards (standard
reference materials)
Run time quality control
standards,
checking peak areas,
background
areas, centroid and FWHM
XRF analyzer calibration
(at least two thin film standards
per element)
XRF detector digital signal
processor calibration
Code
FDC
N/A
HTE
FAA
LFB
TFS
RTS
XAC
XSP
Frequency
all filters
~ 20 test filters per lot
all filters
6 filters/quarter, 3 at each
concentration range
I/ sample run
Beginning and end of each
analytical run
Beginning and end of each
analytical run
I/year or when significant
repairs or changes occur or
QC limits exceeded
1 per week
Criteria
Correct type, size, no
pinholes, defects or
contamination
90% of filters < 4. 8 ng
Pb/cm2
< 30 days before
sampling
10% (percent
difference)
<003 ng/m3
XRF cone. + 3x the 1
sigma uncertainty
overlaps the NIST
certified conc.+ Ix its
reported uncertainty
Target value + 3 SD
XRF cone. + 3x the 1
sigma uncertainty
overlaps the NIST
certified cone. + Ix its
reported uncertainty.
Within manufacturer
specifications
Corrective Action Upon Criteria Failure
Discard filter and replace with filter meeting specifications.
Reject lot, request new filters from vendor.
Required only if filters will be used for PMio mass as well
as Pb. If only used for Pb then 30 day
pre- sampling holding time not required. Reweigh filters
that exceed pre holding time criteria.
Troubleshoot XRF unit and re-run samples.
Investigate areas for contamination including XRF unit,
work area, petri slides, and background Pb in filter.
Investigate filter handling procedures.
Troubleshoot and/or service the XRF unit. Recalibrate and
rerun samples. Recertify thin film standards if necessary.
Troubleshoot and/or service the XRF unit. Recalibrate and
rerun samples.
Troubleshoot and recalibrate the XRF unit. Rerun samples.
Troubleshoot and recalibrate the XRF unit. Rerun samples.
Flag
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8.0 Special Training Requirements/Certification
The purpose of this element is to ensure that any specialized or unusual training requirements to
conduct the Pb-PEP are implemented. Within this element, the procedures are described in
sufficient detail to ensure that specific training skills can be verified, documented, and updated as
necessary.
OAQPS has developed a two-fold Pb-PEP training program. The first aspect of the training
program is to ensure all monitoring personnel have a baseline level of knowledge about the
Ambient Air Monitoring Network, the principles and operation of the Pb-PEP, and the QA
procedures. This phase of training is ongoing and includes the following:
• National-level conferences and training workshops
• An air training facility for hands-on experience
• National- and Regional-level conference calls
• Individual sessions upon request
• All documentation of SOPs and current materials used in Pb-PEP training are posted on the
AMTIC website at http://www.epa.gov/ttnamtil/pbpep.html and on the AIRQA Web site at
https://www. sdas.battelle.org/AirO A/
Focused training for the Pb-PEP includes the following, and is required at least once every two
years for staff who conduct Pb-PEP audits.
• Specific, extensive hands-on field and laboratory training sessions, which are sponsored and
developed by OAQPS, and involve the ESAT contractors, regional personnel, and
monitoring organization personnel.
• A certification program to "certify" the ESAT field and laboratory personnel. This
certification will involve a written test, as well as a performance test. Failure of either of
these tests will result in retraining until the personnel achieve successful certification.
8.1 OAQPS Training Facilities
EPA, through its regional laboratories and OAQPS, has multiple training facilities, which
provide the capacity to:
• Develop internal expertise in Pb monitoring and analysis
• Have monitoring equipment readily accessible to EPA staff for questions and concerns
• Perform field and laboratory training for personnel at EPA, regional, monitoring
organizations, and ESAT
• Perform special studies (study monitor performance, evaluate measurement uncertainty)
• Perform research studies for future monitoring activities.
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8.2 Training Program
The field and laboratory Pb-PEP training program will involve the following four phases:
Classroom lecture. This will include an overall review of the Pb program and the
consequential importance of the Pb-PEP. Classroom lectures will also be implemented
for each training module. Revisions to the training modules and SOPs are made based on
suggestions from Pb-PEP field scientists and a subsequent annual evaluation and
consensus of the EPA Pb-PEP WAM/TOPO/DOPOs and the QA Workgroup.
Hands-on activities. After a classroom lecture, personnel will be taken to the training area
where the field/laboratory activities will be demonstrated, and then the trainees will
perform the same activity under instruction.
Certification-written exam. A written test will be administered to trainees to cover the
information and activities of importance in each of the training modules.
Certification-performance exam. This is a review of the actual field implementation
activities by the trainer/evaluator. Appendix B contains PE forms for this review.
Trainers will include OAQPS personnel from the AAMG QA Team, as well as regional Pb-PEP
QA staff and contractors who are certified by OAQPS to conduct Pb-PEP field and laboratory
audits.
8.3 Field Training
All personnel, which include EPA Regional WAM/TOPO/DOPOs and ESAT contractors, will
be trained before performing Pb-PEP field data collection activities. Representatives of
monitoring organizations are welcome to attend this training to satisfy the training requirement
for their implementation of the Pb-PEP.
Field training/recertification will be conducted at a facility designated by OAQPS. One full
certification course (if needed) and one recertification course will be conducted at least every
two years. Additional training may be arranged at the discretion of OAQPS.
Field training for full certification may last up to two full days. Trainers are usually required to
be available after the training for any individual trainees requiring more instruction.
Field training will include the following topics:
• Introduction to the Pb-PEP
• Planning and preparation
• Filter receipt, storage, and handling
• Sampler transport, placement, and assembly
• System checks
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• Programming the run
• Filter exposure and concluding the sampling event
• coc
• UseofFDS
• Use of the online FDS entry forms and the OAQPS data management Web site
• Data verification via the AIRQA Web site
• QA/QC and information retention
• Troubleshooting in the field: When to perform multipoint verifications and calibrations (not
typically performed in the field).
8.4 Laboratory Training
Region 9 performs Pb analysis on a routine basis for the Region 9 facilities. Consequently the
Region 9 laboratory is required to have an established training program for ESAT contractors
and will not need a separate specific Pb-PEP training related to filter extraction and analysis.
However, personnel at the XRF contract laboratory are required to have their own training
program. At both laboratories, personnel specifically used for the Pb-PEP filter analysis will be
provided additional training related to the following topics that may be more ambient air related:
• Communications
• Filter handling
• COC and use of FDS
• Data entry and data transfer.
These topics could be covered through web-based training, attending the field certification
training, or by EPA personnel.
8.5 Certification
Certification is required by EPA and will help ensure that field and laboratory personnel are
sufficiently trained to perform the necessary Pb-PEP activities at a level that does not
compromise data quality and also inspires confidence in the Pb-PEP by the monitoring
organizations. This certification is required at least once every two years for EPA regional leads,
SLT staff, and ESAT contractors who are involved in the Pb-PEP.
Both the written exam and the performance review are considered part of the certification
requirements. The written exam is gauged to review the more critical aspects of the Pb-PEP and
to identify where the individual requires additional training. The written test will be generated by
OAQPS. A score of 90% is required for passing the written exam. The PE is focused on
ensuring that the individual understands and follows the SOPs. The trainer(s) will evaluate the
trainees' implementation of the topics identified in the field and laboratory sections above.
Appendix B provides the qualitative check forms that will be used during the evaluation of field
and laboratory performance.
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The intent of the certification activities is not to fail individuals, but to determine where
additional training is required to ensure that the Pb-PEP is implemented consistently across the
nation. By testing and evaluating each module, the trainer(s) will be able to identify the areas
where individuals will require additional training. If many individuals fail a particular
component, this may indicate that the classroom or hands-on training is not adequate. In any
case, failure by individuals of parts of either the written or hands-on PE will indicate that more
training is required. Trainees will be required to attend additional training on these components.
Trainers will be available for an additional day of field/laboratory training and will ensure that
personnel are certified by the end of the training session.
If the certification or recertification activities identify individuals who appear to be incapable of
properly performing the field/laboratory activities, the ESAT WAM/TOPO/DOPOs and RPOs
will be notified to initiate remedial action.
8.6 Additional Pb-PEP Field and Laboratory Training
Annual certifications and recertifications will be arranged and conducted by OAQPS. Personnel
turnover is expected among Pb-PEP contractors and monitoring organizations. Occasionally, the
Pb-PEP contracts will be awarded to new contractors. This situation will dictate that a second
full training course needs to be conducted in the same year. The WAM/TOPO/DOPOs will
contact OAQPS as soon as possible when training is required. The following two options are
available for training in these circumstances:
• Because WAM/TOPO/DOPOs will be trained and certified along with ESAT contractors, the
WAM/TOPO/DOPOs are certified to train additional ESAT personnel.
• Individual training arranged at the discretion of OAQPS at its Research Triangle Park (RTF)
air training facility.
OAQPS will work with the regional Pb-PEP leaders and the WAM/TOPO/DOPOs to determine
the need for training and what method is logistically the most efficient for all involved.
8.7 Additional Ambient Air Monitoring Training
Appropriate training will be available to personnel supporting the Ambient Air Monitoring
Program, commensurate with their duties. Such training may consist of classroom lectures,
workshops, teleconferences, and on-the-job training. Over the years, many courses have been
developed for personnel involved in ambient air monitoring and QA aspects. Formal QA/QC
training is offered through the following organizations:
• EPA, OAQPS, AQAD (http://www.epa.gov/air/oaqps/organization/aqad/io.html)
• Air & Waste Management Association (AWMA) (http://www.awma.org)
• EPA Air Pollution Training Institute (APTI) (http://www.epa.gov/apti)
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• EPA Office of Environmental Information (http://www.epa.gov/quality/trcourse.html)
• EPA regional offices
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9.0 Documentation and Records
The purpose of this element is to define the records critical to the project, the information to be
included in reports, the data reporting format, and the document control procedures to be used.
A document, from a records management perspective, is a volume that contains information and
describes, defines, specifies, reports, certifies, or provides data or results pertaining to
environmental programs. As defined in the Federal Records Act of 1950 and the Paperwork
Reduction Act of 1995 (now 44 U.S.C. 3101-3107), records are: "...books, papers, maps,
photographs, machine readable materials, or other documentary materials, regardless of physical
form or characteristics, made or received by an agency of the U.S. Government under Federal
Law or in connection with the transaction of public business and preserved or appropriate for
preservation by that agency or its legitimate successor as evidence of the organization, functions,
policies, decisions, procedures, operations, or other activities of the Government or because of
the informational value of data in them..."
The following information describes the document and records procedures for the Pb-PEP. In
EPA's QAPP regulation and guidance, EPA uses the term "reporting package," which will be
defined as all of the information required to support the concentration data reported to EPA. This
information includes all data required to be collected, as well as data deemed important by the
Pb-PEP.
9.1 Information Included in the Reporting Package
9.1.1 Data Reporting Package Format and Document Control
The Pb-PEP has structured its records management system according to EPA's File Plan Guide
(see http://www.epa.gov/records/tools/toolkits/filecode). A file plan lists office records and
describes how they are organized and maintained. A good file plan is one of the essential
components of a recordkeeping system and is key to a successful records management program,
and can help complete the following:
• Document activities effectively
• Identify records consistently
• Retrieve records quickly
• Determine disposition of records no longer needed
• Meet statutory and regulatory requirements.
The Pb-PEP records management system uses the Agency File Codes (AFCs) to facilitate easy
retrieval of information during EPA TSAs and reviews. The Pb-PEP records management also
follows EPA records schedules, which constitute EPA's official policy on how long to keep
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Agency records (retention) and what to do with them afterwards (disposition). More information
on EPA records schedules can be found at the EPA Web site9.
Table 9-1 includes the documents and records that will be filed according to the statute of
limitations discussed in Section 9.3, Data Reporting Package Archiving and Retrieval. To
archive the information as a cohesive unit, all the Pb-PEP information will be filed under the
major code "Pb-PEP," followed by the AFC function code and schedule numbers listed in Table
9-1. For example, Pb-PEP project plans would be filed under the heading "Pb-PEP/301-093-
006. 1," and COC forms would be filed under "Pb-PEP/301-093-006.3." Each field and
laboratory SOP provides instruction on the proper filing of data collected during the particular
procedure.
Table 9-1. Pb-PEP Reporting Package Information
Agency File Code
Function
301-093
No.
006
006.1
006.2
006.3
006.4
Category
Record/Document Types
Program Management Files
Management
and organization
Monitoring site
information
Field operations and data
acquisition (by EPA
Regional staff or
contractors on behalf of
EPA)
Communications
(contractor technical
project activity)
Organizational structure for the U.S. Environmental
Protection Agency (EPA) and how the Regions and
Environmental Services Assistance Team (ESAT)
contractors fit into running the Pb-PEP Performance
Evaluation Program (Pb-PEP)
Organizational structure for the support contractors
Pb-PEP project plans and subsequent revisions
Quality Management Plan
Site characterization file (site data sheets)
Site maps
Site pictures
Monitoring Organization site contact information
Quality Assurance Project Plans (QAPPs)
Standard operating procedures (SOPs)
Field logbooks and communications
Sample handling/Chain-of-Custody (COC) Forms
Documentation of instrument inspection
and maintenance
Field testing of Pb-PEP equipment
Telephone record and e-mail between ESAT contractor
and monitoring organizations
Telephone record and e-mail between ESAT contractor
and the Contract Officer's Representative (COR)
'http://www.epa.gov/records/policv/schedule
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Table 9-1. Pb-PEP Reporting Package Information (Continued)
Agency File Code
Function
301-093
405
404-142-01
404-142-01
No.
006.5
006.6
202
202.1
179
179.1
173
173.1
Category
Communications (EPA
project activity)
Equipment and instruments
used by contractors in the
Pb-PEP (records about
charged time to the support
of the program would
reference AFC 405-202)
Record/Document Types
Telephone record and e-mail between EPA Regional or
headquarters staff and monitoring organizations and
vice versa
Telephone record and e-mail between EPA Regional
and other EPA personnel (headquarters to Regions
and vice versa)
Procurement logs
Inventories of capital equipment, operating supplies,
and consumables
Repair and maintenance (e.g., vendor service records,
calibration records)
Retirement or scrapping
Contract Management Records
Contract administration
Work assignments, task orders, delivery orders, and
work plans
Contractor monthly reports
Technical directives from the COR to the contractor
Invoices for consumables
Requisite qualifications of field scientists (FSs) and
laboratory analysts (LA) for Pb-PEP-related,
contractor-implemented activities
Training records and certificates of ESAT contractors
conducted and issued by the EPA Regional ESAT
COR
Special Purpose Programs
Data administration
and integration
Data management plans/flowcharts
Raw data: any original data (routine and quality control
[QC] data), including data entry forms
Data algorithms
Documentation of Pb-PEP database (FED)
PM2 5 FED data
Field Data Sheets and COC Forms
Data Files Consisting of Summarized Information
Data summaries, special
reports, and progress
reports
Data/summary/monthly field activity reports
Journal articles/papers/presentations
Data validation summaries
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Table 9-1. Pb-PEP Reporting Package Information (Continued)
Agency File Code
Function
108-025-01-
01
405
403-256
No.
237
237.1
036
036.1
122
122.1
Category
Record/Document Types
State and Local Agency Air Monitoring Files
QA/QC Reports
3 -year Pb-PEP QA reports
Pb-PEP data quality assessments
QA reports
Response/corrective action reports
Site audits
Routine Procurement
Acquisition of capital
equipment and supplies by
EPA (either headquarters
or Regional office)
Needs assessments and reports
Program copies of purchase requests
Requests for bids or proposals
Proposals, bids, or quotations
Bills of lading
Warranties and certificates of performance
Evaluations of proposals, bids, quotations, or trial
installations
Supervisors' Personnel Files and Duplicate Official Personnel Folder
Documentation
Personnel qualifications,
training, and certifications
COR training certifications
Certification as a Pb-PEP FS and/or LA
Certification as a Pb-PEP FS trainer and/or LA trainer
9.1.2 Notebooks
The following types of notebooks will be required of field and laboratory personnel.
Field/Laboratory Notebooks. The Pb-PEP will require each FS and Laboratory Analyst (LA)
to keep a notebook. Each notebook will be uniquely numbered and associated with the
individual and the Pb-PEP. Although data entry forms are associated with all routine
environmental data operations, the notebooks can be used to record additional information about
these operations. In the laboratory, notebooks may also be associated with the temperature and
humidity recording instruments, the refrigerator, calibration equipment/standards, and the
analytical balances used for this program.
Field/Laboratory Binders. Three-ring binders may be used by each FS and will contain the
appropriate data forms for routine operations, as well as inspection and maintenance forms and
SOPs. Laboratories may keep records in their own LEVIS.
Sample Shipping/Receipt Notebook. The sample shipping notebook will be kept by the FS and
include information pertaining to sample shipments to the laboratories. The notebook will be
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uniquely numbered and associated with the Pb-PEP program. It will include standard forms and
areas for free-form notes. The laboratories may keep these records as a part of their own LIMS.
Field/Laboratory Communications Notebook. One communications notebook will be issued
to each FS and LA to record communications. Element 21.0, Reports to Management provides
more information about this activity.
9.1.3 Electronic Data Collection
All raw data required for calculating Pb concentrations, including QA/QC data, are collected
electronically or on the data forms that are included in the field and laboratory SOPs. Field
measurements listed in Element 6.0, Table 6-2 will be collected. Both the primary field and
laboratory data will be collected electronically and primary data will be used to electronically
calculate a final concentration. More details about this process can be found in Element 18.0,
Data Acquisition Requirements, and Element 19.0, Data Management.
Various hard copies are created from electronic systems, such as database reports and
spreadsheets used by the FS and others. Hard copies that are determined to be permanent record
(e.g., data that lead to significant findings or conclusions) should be filed as a data reporting
package to ensure that all Pb-PEP data are properly archived.
It is anticipated that other instruments will provide an automated means for collecting the
information that would otherwise be recorded on data entry forms. Information on these systems
is detailed in Element 18.0, Data Acquisition Requirements, and Element 19.0, Data
Management. To reduce the potential for data entry errors, automated systems will be used
where appropriate and will record the same information that is found on data entry forms. To
provide a backup, a hard copy of automated data collection information will be stored as
specified by EPA records schedules in project files.
9.1.4 Hand-Entered Data
Some data forms will be entered by hand. These forms can be found at the end of each field and
laboratory SOP. All hard copy information will be completed in indelible ink. Corrections will
be made by inserting one line through the incorrect entry, initialing and dating this correction,
and placing the correct entry alongside the incorrect entry, if this can be accomplished legibly, or
by providing the information on a new line.
9.1.5 E-mail and Attachments
EPA and ESAT contractors should use their own in-house e-mail and archiving protocols. All
Pb-PEP e-mails should be saved or backed up routinely on a network server. Any e-mails or
attachments that provide documentation noteworthy to the program such as data validation
investigations, site observations, or official inquiries should be printed and stored in the
Field/Laboratory Communications Notebook.
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9.2 Reports to Management
In addition to the reporting package, various reports will be required by the Pb-PEP.
9.2.1 Laboratory Monthly Report
The laboratories will provide the oversight designee (TOPO/WACOR/DOCOR) with a written
progress report at the end of each month. ESAT staffed laboratories will maintain a complete
record of laboratory monthly progress reports or equivalent as required by the contract. Contract
laboratories will adhere to the reporting stipulations in the current contract. The
WACOR/TOCOR/DOCOR may request more information to be included in the monthly reports
if he/she deems that it is necessary.
9.2.2 Field Monthly Report
The FS will provide the WAM/TOPO/DOPO with a written progress report at the end of each
month (the deadline is the 15th calendar day of the following month unless otherwise specified by
the WAM/TOPO/DOPO). See the Pb-PEP Field SOPs for the details of this report. This monthly
report will be filed according to the schedule outlined in Table 9-1. If the FS also conducts
PM2.5 PEP audits, the Pb-PEP and PIVh.s PEP reports may be merged together to avoid
duplicating work.
The Monthly Progress Report (Form COM-2 from Pb-PEP Hi-Vol Field SOP and Pb-PEP Lo-
Vol SOP) will convey the following information:
• Reporting date—The beginning and end date that the report covers
• Reporter—The person who is writing the reports
• Progress—Progress on field activities
- Evaluations scheduled within the reporting date
- Evaluations conducted within the reporting date
• Issues
- Old issues—Issues reported in earlier reports that have not been resolved
- New issues—Issues that arise within the reporting date
• Actions—The action necessary to resolve issues, including the person(s) responsible for
resolving them and the anticipated dates when they will be resolved.
The WAMs/TOPOs/DOPOs may request more information to be included in the monthly reports
if they deem that it is necessary.
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9.3 Data Reporting Package Archiving and Retrieval
The information listed in Table 9-1 will be retained by the ESAT contractor for 4 years, and it is
based on a calendar year (i.e., all data from calendar year 2009 will be archived until December
31, 2013). Upon reaching the 4-year archival date, the ESAT contractor will inform OAQPS and
the regional Pb-PEP lead that the material has met the archive limit and will ask for a decision
whether further archiving or disposal should be conducted.
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10.0 Sampling Design
The purpose of this element is to describe all of the relevant components of the Pb-PEP sampling
design, the key parameters to be estimated, the number and types of samples to be expected, and
how the samples are to be collected.
10.1 Scheduled Project Activities, Including Measurement Activities
Element 6.0, Project/Task Description, Section 6.4 details the critical time lines and activities for
the Pb-PEP.
10.2 Rationale for the Design
This QAPP reflects the EDOs for a QA activity, not a routine monitoring activity. The sampling
design has been codified in 40 CFR Part 58, Appendix A, Section 3.3.4.4, as described below.
Each year, one performance evaluation audit, as described in section 3.2.7 of this appendix must
be performed at one Pb site in each primary quality assurance organization that has less than or
equal to 5 sites and two audits at primary quality assurance organizations with greater than 5
sites. In addition, each year, four collocated samples from PQAOs with less than or equal to 5
sites and six collocated samples at primary quality assurance organizations with greater than 5
sites must be sent to an independent laboratory, the same laboratory as the performance
evaluation audit, for analysis.
On or before December 1, the regional WAM/TOPO/DOPOs will select the sites that meet the
above criteria and compile a list of sites to be audited during the next calendar year. The
Regional WAM/TOPO/DOPOs, with the assistance of the ESAT contractors, will determine the
most efficient site visit schedule. This schedule will be based on
• CFR requirements for audit frequency
• Meeting the same monitoring schedule as the routine sampler being evaluated (this prevents
the site from having to run and post an additional sample for the PE audit to AQS)
• Site proximity (the sites that are closest in proximity to each other can be visited within the
same day or week).
10.3 Design Assumptions
The intent of the sampling design is to determine that the total measurement bias is within the
DQOs described in Element 7.0, Data Quality Objectives and Criteria for Measurement. The
sampling design will allow the Pb-PEP data to be statistically evaluated at various levels of
aggregation to determine whether the DQOs have been attained. Data quality assessments will
be aggregated at the following four levels:
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Monitor Type. Monitor/method designation.
PQAO. All monitors within a PQAO.
Region. All contained within an EPA region
National. All monitors and possibly aggregated by method designation.
OAQPS believes it is important to stratify monitors by method designation to assist in the
determination of instrument-specific bias (i.e., a particular make and model).
The statistical calculations for the assessments are found in 40 CFR Part 58, Appendix A. Once
both the routine and PE data are in the AQS database, these calculations will be performed on the
data and will allow for the generation of reports at the levels specified above.
The DQO for the Pb-PEP is based on how the NAAQS for Pb is determined. Attainment of the
NAAQS for Pb is based on a rolling 3 month average from data collected from individual
monitors; therefore, it is important to assess the PE data against the DQO at the same frequency
and level of aggregation. The Pb-PEP data have limited use at the unique monitor level of
aggregation. At the PQAO and national levels of aggregation, a sufficient amount of Pb-PEP
data will be available to evaluate bias. The uncertainty of the Pb-PEP data will be controlled and
evaluated by using various QA/QC samples described in Element 7.0, Data Quality Objectives
and Criteria for Measurement, and Element 14.0, Quality Control Requirements. For example,
the aggregation of the collocated samplers over the 3-year period will determine the precision of
the program. Use of various blanks, verification checks, and inter-laboratory comparison studies
can help to determine bias.
10.3.1 Representativeness
Representativeness is a measure of the degree to which data accurately and precisely represent a
characteristic of a population, parameter variations at a sampling point, a process condition, or an
environmental condition. The Pb-PEP design attempts to represent parameter variations at a
sampling point by locating a high volume Pb-PEP sampler within 2 to 4 meters of the primary
routine sampler and by operating the Pb-PEP sampler on the same sampling schedule as the
routine sampler. In the same way, the low volume Pb-PEP sampler will be placed within 1 to 4
meters of the primary routine sampler and by operating the Pb-PEP sampler on the same
sampling schedule as the routine sampler. The assumption is that the air within these areas is
homogenous; therefore, both monitors will sample the same Pb load.
10.4 Procedure for Locating and Selecting Environmental Samples
The physical location of the routine monitor is the responsibility of the monitoring organizations
and does not affect the intent of the PE. Site location information is entered by the monitoring
organization into the AQS database. The critical piece of information is the AQS site ID (state,
county, unit, parameter occurrence code), which must be entered into AQS for primary data to be
loaded into the database. The ESAT FS will have access to this information.
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For each site, the ESAT contractor will complete a Site Data Sheet (Form SD-01) that contains
the following information:
• AQS site ID
• Monitor parameter occurrence code (POC)
• Method designation
• Monitor make and model
• Site coordinates
• Network type (SLAMS/Ncore)
• Reporting organization
• Reporting organization contact
• Street address
• Directions to the site (from the Regional office)
• Directions to the site from a major thoroughfare
• Safety concerns
• Additional equipment needed (ropes, ladders)
• Closest hospital (address)
• Closest express mail facility
• Closest hardware store
• Recommended hotel (address/phone)
• Important free-form notes
• Closest Pb site
• Closest PM2.5 site
The information listed above will be kept in a site file (filed by AQS site ID) and included in a
site notebook for each FS. In addition, maps for each state and city where a monitor is located
will be acquired. Sites can be placed on these maps along with the site IDs.
Sites will not be visited and samplers will not be set up in conditions that are deemed unsafe.
Unsafe conditions may include bad weather or monitoring platforms where the FS feels that
he/she cannot transport or set up the monitor without jeopardizing his/her personnel safety. The
FS will document the occurrence of any unsafe conditions so that mechanisms can be instituted
to address the issue. This information will be conveyed to the WAM/TOPO/DOPO.
10.5 Classification of Measurements as Critical/Noncritical
Sections 6.2.2 and 6.3.1 classify the critical field and laboratory measurements for the Pb-PEP.
Although the field and laboratory SOPs contain many additional measurements, they are
considered noncritical.
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10.6 Validation of Any Non-Standard Measurements
Because the Pb-PEP is deploying only FRM and FEM samplers and will be operating these
samplers according to the established SOPs, there will not be any non-standard measurements.
Also, because the Pb-PEP will be sending its filters to a certified laboratory using an FEM
method for analysis, there will not be any non-standard measurements from the analysis of the
filters.
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11.0 Sampling Methods Requirements
The Pb-PEP provides for measurement of the mass concentration of Pb in ambient air over a
24-hour period. Two sets of SOPs for field sampling (Field Standard Operating Procedures for
the Federal Lead (Pb) Performance Evaluation Program:Hi-Vol Pb-TSP Audits and Field
Standard Operating Procedures for the Federal Lead (Pb) Performance Evaluation
Program:Lo-Vol Pb-PMw Audits) have been developed for the Pb-PEP and are to be used in all
sampling activities under this QAPP. The following section will provide summaries of some of
the more detailed information in the field SOPs. These summaries do not replace the SOPs.
11.1 Sample Collection and Preparation
The use of one portable FRM monitor is required for collecting Pb samples for the Pb-PEP.
Because the goal is to provide comparable results across the nation, using one make and model
of portable monitor to evaluate all of the routine monitors is advantageous. Using a single
sampler model reduces the chances that bias and imprecision among different portable
instrument models will confound the routine monitor comparisons.
11.1.1 Preparation
Before conducting an evaluation excursion for the week, the sampling equipment and
consumables will be inspected to ensure proper operation and adequate supplies are available
based upon the number of sites to be visited. Filters will be requested and stored per SOPs for
transport to the sites. The filter COC/FDS will be initiated using the AIRQA Web site. Site data
sheets, which contain information on characteristics for each site, will be available. For initial
visits, some of the information on the site data sheets may be blank and must be completed
during the first visit. The Pb-PEP FS will review the site schedule to be sure that they
understand which tasks will be implemented at the sites they are visiting in a particular audit trip.
11.1.2 Field Sample Collection
The FS will travel to the monitoring sites to conduct the audits. Access to the monitoring site
may be granted to the FS via meeting on site or another pre-arrangement. It is recommended,
but not required, that the site operator be present during the audit. The portable high volume
FRM monitors will be transported to within 2 to 4 meters of the routine monitor, assembled, and
systems verified per the Pb-PEP field SOPs. The portable low volume FRM monitors will be
transported to within 1 to 4 meters of the routine monitor, assembled, and systems verified per
the Pb-PEP field SOPs. The filters will be installed and the monitor will be set to run on a
midnight-to-midnight local standard time schedule. The FS will then either perform additional
tasks as required at this site or proceed to another site for sampling. If there are any delays in the
sampling schedule, the ESAT FS will contact the affected monitoring organizations and will also
notify the Regional WAM/TOPO/DOPO.
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Upon completion of sampling, the FS will return to the site(s), remove the sampling filter,
visually inspect the filter, store it appropriately for transport to the laboratory, and download the
data per the field SOPs. Each FS will have a laptop and digital data storage media to download
and store sampler data. The FS should also contact the site operator to determine if the site
sampler completed its run. If the run was not completed, the site should be re-audited at some
point during the year.
11.1.3 Filter Transportation
It is important that the filters be properly stored and transported to the laboratory as soon as
possible. Ideally, filters will be shipped the same day that they are removed from the monitors
via next-day delivery. Filters and COC/FDSs will be included in the shipment. The FS will
keep a copy of the FDS/COC Form (to file under Pb-PEP/301-093-006.3) and will record the
number of filters shipped and the air bill number in the field notebook. On the day of shipping,
the FS will contact the laboratory via email or phone to make its personnel aware of the shipment
and to provide the laboratory with the number of filters shipped and the air bill number.
11.1.4 Return to Station
Upon completing a sampling excursion, the FS will return to the regional office and enter the
FDS/COC data into the electronic form on the Web site. A second copy of the audit's field
data will be stored at the field office and provided to the EPA Regional WAM/TOPO/DOPO.
The WAM/TOPO/DOPO will use the COC/FDS form to QC the FS's data entry on the Web site.
The WAM/TOPO/DOPO will mark the audit run as "Approved" if it passes the automated
critical QC checks. The FS will also ensure that all equipment and consumables are properly
stored and determine if ordering supplies or performing equipment maintenance are required.
Vehicles will be serviced as required. The FS will debrief the WAM/TOPO/DOPO on the field
excursion and will include information about whether the site visits remain on schedule.
11.1.5 Field Maintenance
A maintenance list will be developed by the Pb-PEP field personnel for all sensitive capital
equipment. The list will contain columns for item, maintenance schedule, and date that will be
filled in when maintenance (scheduled or unscheduled) is performed. See Element 15.0,
Instrument/Equipment Testing, Inspection, and Maintenance Requirements, for this information.
11.2 Support Facilities for Sampling Methods
The analytical support facilities for the federally implemented Pb-PEP will be provided by the
Region 9 laboratory in Richmond, CA for the high volume filters and by a contract laboratory
selected by OAQPS for the low volume filters. These laboratories have been shown to meet the
MQOs described in Tables 7-2 and 7-3, respectively.
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11.3 Sampling/Measurement System Corrective Action Process
11.3.1 Corrections to the SOPs
The ESAT contractors are responsible for implementing this QAPP and the field SOPs and are
responsible for the quality of the data. All methods will be reviewed and implemented by the
ESAT contractors. If changes or corrections are required to the methods or QAPP, the ESAT
contractor will notify the Regional WAM/TOPO/DOPO in writing. The Regional WAM/TOPO/
DOPO will then convey the issue to the Pb ESAT Workgroup, which will review the change and
attempt to classify it according to the effect that the change would have on the data. The classes
follow:
• Class 1—The change improves the data and the new procedure replaces the current
procedure. If the change is found to be acceptable by the ESAT Workgroup, a new SOP
section will be issued that can be inserted into the compendium. The document control
information in the heading will contain a new revision number and date. A Quality Bulletin
will be completed to describe the change, and it will be distributed to all Regional
WAMs/TOPOs/DOPOs and ESAT personnel.
• Class 2—The change provides for an alternate method that does not affect the quality of the
data but may provide for efficiencies in some circumstances or be more cost effective. If the
change is found to be acceptable by the Pb-PEP community, the original SOP will not be
altered, but an addendum to the procedure will be initiated by EPA OAQPS that describes the
modification and provides an alternate method.
• Class 3—The change is grammatical in nature and does not reflect a change in the procedure.
The changes will be highlighted and modified during a Class 1 change (where appropriate) or
will be corrected during the development of a full revision to the document.
Upon agreement by the ESAT Workgroup to institute a change, hard copies of Class 1 and 2
changes will be distributed using the Quality Bulletin illustrated in Figure 11-1.
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Quality Bulletin
Subject:
Number
Date
Page of_
Supersedes No.
Dated
Replace and Discard Original
Add Material to Document
Notes:
Pb QA Coordinator
Retain this bulletin until further notice D
Discard this bulletin after noting contents D
This bulletin will be invalid after (Date) D
This bulletin will be incorporated into quality D
Procedure No. by (Date) D
Figure 11-1. Illustration of ESAT Workgroup Quality Bulletin.
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11.3.2 Data Operations
Corrective action measures in the Pb-PEP will be taken to ensure that the DQOs are attained.
There is the potential for many types of sampling and measurement system corrective actions.
Table 11-1 lists some of the expected problems and corrective actions needed for a well-run Pb-
PEP. Some corrective actions can be addressed in the field while others are better addressed in a
clean laboratory. This table does not attempt to dictate the appropriate location for repairs or
troubleshooting but rather gives examples of potential issues and solutions.
Table 11-1. Field Corrective Action
Item
Problem
Action
Notification
Pre-Sampling Event Activities
Filter
inspection
Pinhole(s) or
tear(s)
1) Additional filters will be brought to the
site; use one of them. Void filters with
pinholes or tears
1) Document on the FDS
Leak test
Leak outside
acceptable
tolerance
(Table 7-1)
1) Completely remove the flow rate
measurement adapter, reconnect it, and
perform the leak test again
2) Inspect all seals and O-rings, replace
them as necessary, and perform the leak
test again
3) Check sampler with different leak test
device
4) Use back-up sampler
1) Document in a log book
2) Document in a log book;
notify the Regional WAM/
TOPO/DOPO; flag the
data since the last
successful leak test
3) Document in a log book;
notify the Regional
WAM/TOPO/DOPO
Ambient
pressure
verification
Out of
specification
(Table 7-1)
1) Make sure pressure sensors are exposed
to the ambient air and are not in direct
sunlight
2) Call the local airport or other source of
ambient pressure data and compare that
pressure to pressure data from the
monitor's sensor. Pressure correction
may be required
3) Connect a new pressure sensor
1) Document on the FDS
2) Document on the FDS
3) Document on the FDS;
notify Regional
WAM/TOPO/DOPO
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Table 11-1. Field Corrective Action (Continued)
Item
Ambient
temperature
verification.
Sample flow
rate
verification
Sample flow
rate
Problem
Out of
specification
(Table 7-1)
Out of
specification
(Table 7-1)
Consistently low
flows are
documented during
the sample run.
Action
1) Make sure that thermocouples are
immersed in the same liquid at same
point without touching the sides or
bottom of the container
2) Use ice bath or warm water bath to
check a different temperature. If the
temperature is acceptable, perform the
ambient temperature verification again
3) Connect a new thermocouple
4) Check the ambient temperature with
another National Institute of Standards
and Technology -traceable thermometer
1) Completely remove the flow rate
measurement adapter, reconnect it, and
perform the flow rate check again
2) Perform the leak test
3) Recalibrate the flow rate
4) Verify it again; flow rate must be within
±5% of limits of linearity
1) Check programming of the sampler
flow rate
2) Check the flow with a flow rate
verification filter and determine if the
actual flow is low
Notification
1) Document on the FDS
2) Document on the FDS
3) Document on the FDS;
notify the Regional WAM/
TOPO/DOPO
4) Document on the FDS;
notify the Regional
WAM/TOPO/DOPO
1) Document on the FDS
2) Document on the FDS
3) Document on the FDS;
notify the Regional
WAM/TOPO/DOPO
4) Document on the FDS
1) Document in the log book
2) Document in the log book
Post-Sampling Event Activities
Elapsed
sample time
Elapsed
sample time
Out of
specification
(Table 7-1)
Sample did not run
Check programming; verify power outages
1) Check programming
2) Try programming the sample run to
start while the operator is at the site
Notify the Regional WAM/
TOPO/DOPO
1) Document on the FDS;
notify the Regional
WAM/TOPO/DOPO
2) Document in the log book;
notify the Regional
WAM/TOPO/DOPO
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Table 11-1. Field Corrective Action (Continued)
Item
Power
Power
Filter
inspection
Data
downloading
Problem
Power
interruptions
Liquid crystal
display (LCD)
panel is on, but the
sampler is not
working
Torn filter or
otherwise suspect
paniculate matter
on the filter
Data will not
transfer to laptop
computer
Action
Check line voltage
Check the circuit breaker
1) Inspect area downstream of where filter
rests in the sampler and determine if
paniculate matter has been bypassing
filter
Document key information on the sample
data sheet; make sure the problem is
resolved before data are written over in the
sampler microprocessor
Notification
Notify the Regional WAM/
TOPO/DOPO
Document in the log book
1) Document on the FDS
Notify the Regional WAM/
TOPO/DOPO
11.4 Sampling Equipment, Preservation, and Holding Time Requirements
This section details the requirements needed to prevent sample contamination, the volume of air
to be sampled, temperature preservation requirements, and the permissible holding times to
ensure against degradation of sample integrity. In addition, Element 15.0, Instrument/Equipment
Testing, Inspection, and Maintenance Requirements, provides information on sampler
maintenance to reduce the potential of contamination or the collection of samples that do not
represent the population of interest.
11.4.1 Sample Contamination Prevention
The Pb-PEP has rigid requirements for preventing sample contamination. Powder-free, antistatic
gloves are worn while handling filters in the laboratory and the field. Filters should remain in
protective boxes or a container where a few can be taken in the field but remain protected. Upon
removal of filters from the sampler, they are folded in half lengthwise, placed in a glassine
envelope and then into a shipping envelope for filter shipping to the laboratory.
11.4.2 Sample Volume
High volume Pb-PEP audit samplers operate at a rate of 1.1 m3/min to 1.7 m3/min to collect
approximately 1750 m3 of ambient air over a 24 hour period. Low volume Pb-PEP audit
samplers operate at 16.67 liters per minute to collect approximately 24 m3 of ambient air over a
24-hour period. Sampling time is expected to be 24 hours (midnight to midnight). The sample
period must not be less than 23 hours or greater than 25 hours. If this occurs, the sample will be
flagged, the Regional WAM/TOPO/DOPO will be notified, and the audit will not be approved.
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11.4.3 Temperature Preservation Requirements
The glass fiber and Teflon® Pb-PEP filters have no temperature preservation requirements. The
best practice would be to avoid placing the filters in extreme heat or cold.
11.4.4 Permissible Holding Times
The glass fiber and Teflon® filters used for the Pb-PEP have no specified holding time
requirements for the laboratory. The general rule is for the filters to be analyzed within the
month they are received so they may be validated and posted to the AIRQA Web site at the end
of the month. In the field, there is no holding time to use the filters, but the 46.2 mm Teflon®
filters should be used within 30 days. After recovery, all filters should be shipped to the
laboratory as soon as possible to allow the laboratory enough time to analyze the filters by the
end of the month for validation and posting.
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12.0 Sample Handling and Custody
Due to the potential use of the Pb-PEP data for comparison to the NAAQS and the requirement
for care in handling the sample collection filters, sample COC procedures will be followed. The
laboratory SOPs and the field SOPs provide detailed instruction on filter-handling and COC
procedures, which will not be included in this section.
Due to the amount of PM that is expected on these filters, improper filter handling can be a
major source of error. Care must be taken when handling both exposed and unexposed filters.
Filters should be handled in a manner to prevent them from being damaged or contaminated.
Similarly, rough handling of exposed filters should be avoided because this may dislodge
collected PM on the filters.
COC forms are used to ensure that
• Filters are processed, transferred, stored, and analyzed by authorized personnel.
• Sample integrity is maintained during all laboratory phases of sample handling and analyses.
• An accurate written record is maintained of sample handling and treatment from the time of
receipt from EPA, through laboratory procedures, to disposal.
Proper sample custody minimizes accidents by assigning responsibility at each stage of sample
handling and ensures that problems will be detected and documented if they occur. A sample is
in custody if it is in actual physical possession of authorized personnel or if it is in a secured area
that is restricted to authorized personnel. As illustrated in Figure 6-1, which appears in Element
6.0, Project/Task Description, the FDS/ COC form is printed from the AIRQA Web site and
follows the filter into the field. The FDS/COC is completed at the end of the audit and is sent to
the laboratory with the filter. Prior to shipping, the FDS/COC information is entered into the
AIRQA Web site and the Pb-PEP laboratory's sample tracking system, where electronic records
will be kept. In addition, the ESAT auditor will retain a copy of the COC in the field office as a
record.
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13.0 Analytical Methods Requirements
The analytical methods described below provide for the analysis of either TSP glass fiber filters
or 46.2 mm Teflon® filters in the Pb-PEP. High volume TSP samplers will be used to audit TSP
monitoring sites and these samplers will use the glass fiber filters. Low volume PMio samplers
will be used at low volume PMio monitoring sites and these samplers will use the 46.2 mm
Teflon® filters. The Region 9 laboratory will receive and analyze the glass fiber filters using
ICP/MS, and an OAQPS contract laboratory will receive and analyze the 46.2 mm Teflon® filters
using XRF.
The Region 9 laboratory provides routine analysis of environmental samples for a number of
media (air/water/soil) for Region 9. It maintains a compendium of methods for the specific
analytical technique but also support activities such as glassware cleaning, waste management,
sample archive etc. The primary analytical methods for the high volume Pb-PEP are the
extraction technique Standard Operating Procedure 409 Digestion for Lead on Filters and the
analysis technique Standard Operating Procedure 509 Determination of Lead on Filters by
ICP/MS. The following sections summarize methods 409 and 509. The 409 and 509 methods
listed above have passed EPA equivalency testing defined in 40 CFR Part 53 Section 33 and
been deemed FEMs in accordance with the FRM for high volume sampling listed in 40 CFR Part
50 Appendix G and the FRM for low volume sampling listed in 40 CFR Part 50 Appendix Q.
The OAQPS contract laboratory will be selected through the EPA contract laboratory
mechanism. The contract laboratory selected will be required to use an approved FEM for the
XRF analysis of the 46.2 mm Teflon® filters. The contract laboratory will provide a QAPP and
an SOP to EPA, and the national Pb-PEP lead will review the documentation. In addition, the
laboratory will be given audit filters to analyze to verify the laboratory's precision and minimum
detection limit (MDL) to ensure that they can provide acceptable precision and quantification.
The laboratory must be able to demonstrate precision on the test filters to 10% and an MDL of at
least 0.02 jig/m3. If the method, audit, and documentation are acceptable, EPA will enlist the
laboratory's services.
13.1 Inductively Coupled Plasma Mass Spectrometry Analysis
13.1.1 Extraction of TSP Filters for ICP-MS Analysis (SOP 409)
The Region 9 SOP 409 provides sample preparation procedures for the determination of lead on
PMio filters or TSP filters by ICP-MS. This SOP is based on 40 CFR Part 50, Appendix G—
Reference Method for the Determination of Lead in Suspended? articulate Matter Collected
from Ambient Air. This SOP extends the scope of the procedure to the digestion of PMio filters
and makes further modifications to utilize disposable labware to minimize contamination.
Deviations from the reference method are described in Appendix A of 409 and the analyte and
Chemical Abstracts Service (CAS) number are listed in Appendix B of 409.
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In this method, nitric acid is dispensed into a digestion tube containing a PMio filter or a 3/4 inch
x 8 inch TSP filter strip. Lead in the filter paper is digested by covering the tube with a watch
glass and refluxing the sample via a hot block in the dilute acid mixture for 60 minutes. After
digestion, the tube is allowed to cool. The digestate is then brought up to a final volume of 50
mL with reagent water, is capped, and shaken thoroughly. The digestate is set aside (with the
filter in the digestion tube) for at least 30 minutes to allow the nitric acid trapped in the filter to
diffuse into the digestate. The digestate is shaken thoroughly and allowed to settle for at least an
hour. The sample is then ready for analysis by ICP-MS using SOP 509 Determination of Lead
on Filters.
13.1.2 Analysis of TSP Filters Using ICP-MS Analysis (SOP 509)
SOP 509 provides procedures for the determination of lead in PMio filter or TSP filter strip by
ICP-MS. This SOP is based on procedures in EPA Method 200.8, Determination of Trace
Elements in Waters and Wastes by ICP-MS, Rev. 5.4, May 1994. Deviations from the reference
method are described in Appendix A of Method 509 and the analyte, CAS number, and
quantitation limit (QL) are listed in Appendix B of Method 509.
This SOP describes the determination of lead on filter samples by ICP-MS after digestion with
nitric acid or nitric acid/hydrochloric acid solution. Sample solutions are introduced by
pneumatic nebulization into a plasma, in which desolvation, atomization, and ionization occurs.
Ions are extracted from the plasma through a differentially pumped vacuum interface and
separated on the basis of their mass-to-charge ratio by a quadrupole mass spectrometer. The ions
transmitted through the quadrupole are detected by an electron multiplier. Ion intensities at each
mass are recorded and compared to those obtained from external calibration standards to
generate concentration values for the samples. Results are corrected for instrument drift and
matrix effects using certified internal quality control standards. Additional corrections are
applied as necessary to correct for isobaric and polyatomic elemental interferences.
13.1.3 Analytical Equipment and Method
A complete listing of the analytical equipment is found in laboratory SOP 509.
13.2 X-Ray Fluorescence Analysis
XRF analysis is based on energy dispersive X-ray fluorescence of elemental components in a
thin film sample. The emissions of X-ray photons from the sample are integrated over time and
yield quantitative measurements of elements ranging from aluminum (Al) through uranium (U)
and semi-quantitative measurements of sodium (Na) and magnesium (Mg). A spectrum of X-ray
counts versus photon energy is acquired and displayed during analysis, with individual peak
energies corresponding to each element and peak areas corresponding to elemental
concentrations.
As an example, the PANalytical Epsilon 5 XRF analyzer utilizes a side window dual anode X-
ray tube with both scandium (Sc) and tungsten (W) anodes. X-rays are focused on one of 11
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secondary targets, which in turn emit polarized X-rays used to excite a sample. X-rays from a
secondary target or the tube are absorbed by the sample, exciting electrons to high level orbitals.
As the electrons return to their ground state, photons are emitted which are characteristic of the
quantum level jumps made by the electron; the energy of the emitted photons are, therefore,
characteristic of the elements contained in the sample. The fluoresced photons are detected in a
solid state germanium X-ray detector. Each photon that enters the detector generates an electrical
charge whose magnitude is proportional to the photon's energy. The electrical signals from the
detector are sorted into energy channels, counted, and displayed. A sample spectrum consists of
characteristic peaks superimposed on a background caused by the scatter of X-rays from the tube
into the detector.
13.3 Internal QC and Corrective Action for Measurement System
13.3.1 Corrections to the SOPs
The Region 9 methods are reviewed and approved by Region 9 EPA personnel including the
Region 9 Laboratory Team Lead, the Region 9 Laboratory QAM, and the Region 9 Laboratory
Director. The ESAT contractors are responsible for implementing this QAPP and the laboratory
SOPs, and they are responsible for the quality of the data. All methods will be reviewed and
implemented by the ESAT contractors. If changes or corrections are required to the laboratory
SOPs or QAPP, the ESAT contractor will notify the Regional WAM/TOPO/DOPO and the
Laboratory Team Lead in writing. The WAM/TOPO/DOPO will then convey the issue(s) to the
Pb ESAT Workgroup, which will review the changes and attempt to classify them according to
the effect the changes would have on the data.
The contract laboratory methods are reviewed and approved by the contract laboratory as
needed. New revisions to the SOP will be forwarded to the National Pb-PEP lead at OAQPS.
The contract laboratory will monitor and assess the changes in the SOP to ensure proper
implementation.
13.3.2 Data Operations
A QC notebook or database (with electronic backups) will be maintained and will contain QC
data and entry forms, calibration and maintenance information, and routine internal QC checks.
Control charts will be maintained for a number of important QC components. These charts may
allow for the discovery of excess drift that could signal an instrument malfunction. Corrective
action measures in the Pb-PEP will be taken to ensure data of adequate quality. The laboratory's
SOPs and Section 14 will provide additional information on these activities. Table 13-1 lists
several filter preparation and analysis QC checks.
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Table 13-1. Filter Preparation and Analysis Checks
Activity
Post- sampling
inspection,
documentation, and
verification
Filter handling
Filter integrity
check
Filter identification
Internal QC
Method and Frequency
Examine the filter and Field Data
Sheets (FDSs) and COC for correct
and complete entries.
Observe handling procedures
Visually inspect each filter
Ensure filter number of filter and
FDS/COC are the same.
See Section 14 and analytical SOPs
Requirements
No damage to filter; FDS/COC
complete; sampler operated properly
Use powder-free and antistatic
gloves and smooth forceps
(Teflon®).
No pinholes, separation, chaff, loose
material, discoloration, or filter
non-uniformity
Make sure the numbers are written
legibly and compare
Pass requirements
Action If the
Requirements Are Not
Met
Notify the Pb-PEP
Laboratory Manager; flag
filters in LIMS
Flag any mishandled filter
in the LIMS
Flag any defective filter
in the LIMS
Flag any mislabeled
sample in the LIMS and
check with field
personnel.
May require repeat
analysis on extracts or
second extraction and
analysis
13.4 Filter Sample Contamination Prevention
The analytical support component of the Pb-PEP has requirements for preventing sample
contamination. Powder-free and antistatic gloves are worn while handling 46.2 mm Teflon®
filters, and TSP filters are only handled on unexposed edges. The 46.2 mm Teflon® filters are
only handled with smooth non-serrated Teflon® forceps on the outer reinforcing support ring.
Laboratory "Best Practices" should be employed while handling filters of any kind.
In the field component of the Pb-PEP, glass fiber filters are handled only on the edges, and the
filters should be loaded in the transport cassette/carrier in a clean area in the office. The transport
cassette should have a snap cover that should be in place during handling until the sample is
loaded onto the high volume sampler. Each glass fiber filter should be packed for shipping in
individual envelopes, and shipped in a protective envelope. The 46.2 mm Teflon® filters are
shipped with a plastic lid covering the filter. The Teflon® filters should stay covered and in their
cassettes to avoid contamination from the field. 46.2 mm Teflon® filters are covered with the
plastic cap and kept in individual antistatic bags for shipping. Organizations outside the ESAT
operated Pb-PEP may choose to remove the 46.2 mm Teflon® filters from the cassettes if
facilities exist where this can be done without risk of contamination.
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14.0 Quality Control Requirements
To assure the quality of data from air monitoring measurements, two distinct and important
interrelated functions must be performed. One function is the control of the measurement process
through broad QA activities, such as establishing policies and procedures, developing DQOs,
assigning roles and responsibilities, conducting oversight and reviews, and implementing
corrective actions. The other function is the control of the measurement process through the
implementation of specific QC procedures, such as audits, calibrations, checks, replicates, and
routine self-assessments. In general, the greater the control that can be achieved of a given
system, the better the resulting quality of the monitoring data.
QC is the overall system of technical activities that measures the attributes and performance of a
process, item, or service against defined standards to verify that the stated requirements
established by the customer are met. In the case of the Ambient Air Quality Monitoring
Network, QC activities are used to ensure that measurement uncertainty, as discussed in Element
7.0, Quality Objectives and Criteria for Measurement Data, is maintained within acceptance
criteria for the attainment of the DQO.
14.1 QC Procedures
Day-to-day QC is implemented through various check samples or instruments that are used for
comparison. The MQO tables (Tables 7-1 to 7-3) in Element 7.0, Quality Objectives and
Criteria for Measurement Data, contains a complete listing of these QC samples, as well as other
requirements for the Pb-PEP. The procedures for implementing the QC samples are included in
the field and laboratory SOPs, respectively. The following information provides some additional
descriptions of these QC activities, how they will be used in the evaluation process, and what
corrective actions will be taken when they do not meet acceptance criteria.
14.1.1 Calibrations
Calibration is the comparison of a measurement standard or instrument with another standard or
instrument to report, or eliminate by adjustment, any variation (deviation) in the accuracy of the
item being compared. The purpose of calibration is to minimize bias.
For the Pb-PEP, calibration activities follow a two-step process:
• Step 1. Certifying the calibration standard and/or transfer standard against an authoritative
standard.
• Step 2. Comparing the calibration standard and/or transfer standard against the routine
sampling/analytical instruments.
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Calibration requirements for the critical field and laboratory equipment are found in Tables 7-1
through 7-3; the details of the calibration methods are included in the calibration section (Section
16.0, Instrument Calibration and Frequency) and in the field and laboratory SOPs.
14.1.1.1 Field Calibration Evaluation
Field equipment calibrations will be evaluated using independent NIST traceable standards.
Accuracy of field verification/calibration checks — Single check (quarterly) basis (
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M
%R= —x 100
where
%R = percent recovery of the standard
M= measured concentration of the analyte, |ig/L
T= true concentration of the analyte in the ICV/CCV, |ig/L
14.1.1.3 Second Source Calibration Verification
Analyze a second source calibration verification (SCV) daily to verify the calibration standards
and acceptable instrument performance. If the measured concentration is not within + 10% of
the true value, the method performance is unacceptable. The source of the problem must be
identified and corrected before proceeding with analyses.
The recovery of the analyte in the SCV is calculated as:
M
%R=—x 100
where
%R = percent recovery of the standard
M= measured concentration of the analyte, |ig/L
T= true concentration of the analyte in the SCV, |ig/L
14.1.2 Blanks
Blank samples are used to determine contamination arising principally from the following four
sources: the environment from which the sample was collected/analyzed, the reagents used in the
analysis, the apparatus used, and the operator/analyst who performed the data operation. The
following five types of blanks will be implemented in the Pb-PEP:
Field Blank - These provide an estimate of total measurement system contamination. By
comparing information from laboratory blanks against the field blanks, the contamination from
field activities can be assessed. Details about using field blanks can be found in the Field SOP.
The acceptance goal for field blanks is for the blanks concentration to be less than the laboratory
method detection limit.
Trip Blank - These are used to measure possible contamination to filters during transportation to
and from sampling locations. They provide a frame of reference in case field blanks exhibit mass
gain higher than the acceptance levels. Trip blanks shall represent approximately 10% of all Pb-
PEP filters. Trip blanks should be used in conjunction with field blanks but not at the same
frequency. Details about using the trip blanks can be found in field SOPs. The acceptance goal
for trip blanks is for the blanks concentration to be less than the laboratory method detection
limit.
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Laboratory Blank -These provide an estimate of contamination occurring at the analytical
facility. Details about using the laboratory blanks can be found in lab SOP 509.
Calibration Blank - The stability of the baseline must be monitored by analyzing a CB
immediately after every ICV/CCV standard. If the value of the CB result is less than one half
the QL, the result is acceptable. If the value of the CB result equals or exceeds one-half the QL,
the analysis may not continue. The cause of the high CB result must be determined and the
problem corrected. The instrument must be re-calibrated and all samples not bracketed by
acceptable CB results must be re-analyzed.
Method Blank - Analyze at least one MB with each batch of 20 or fewer field samples in an
SDG. MB values > l/2 the QL indicate potential laboratory or reagent contamination. Use the
following guidelines to determine when samples must be re-prepared, re-analyzed, and flagged
as estimated:
• If the MB analyte value is > 1A the QL and the sample result is less than five times the MB
analyte amount, rerun the MB once to verify and if still unacceptable: (1) For PMio filter, all
associated results are to be reported and qualified as estimated "J", (2) For TSP filter strip,
the MB and all associated samples must be re-prepared and re-analyzed if there is enough
sample to work with. The associated sample results can also be reported but will be qualified
as estimated "J".
• If the MB analyte value is > l/2 the QL and the sample result is non-detected or is greater than
five times the MB analyte concentration, report sample results without qualification.
14.1.3 Precision Checks
Precision is the measure of mutual agreement among individual measurements of the same
property, usually under prescribed similar conditions. To meet the DQOs for precision, the Pb-
PEP must ensure the entire measurement process is within statistical control. The following two
types of precision measurements will be made in the Pb Program:
• Collocated monitoring (see Section 14.1.3.1.)
• Filter duplicates (see Section 14.1.3.2.).
14.1.3.1 Collocated Monitoring
To evaluate the total measurement precision of the Pb-PEP fleet of samplers, collocated
monitoring study will be implemented. Twice a year, the FS will complete a collocation study.
One collocation study is defined as setting up and operating an extra Pb-PEP sampler at a routine
monitoring site; repeating the process in a 6 month period until all Pb-PEP samplers have been
compared. The data from the two Pb-PEP samplers and the SLT sampler will be compared. If
the Pb-PEP samplers differ by more than 10% using Equation 10 below, the FS will troubleshoot
the sampler that has the highest percent difference from the SLT sampler. The SLT will be used
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as a "referee" if there is a difference between the Pb-PEP samplers. This process will be
completed twice per year. This study will assess bias among the Pb-PEP sampler fleet.
Evaluation of collocated data. Collocated measurement pairs are selected for use in the
precision calculations only when both measurements are above 0.02 ug/m3. The following
algorithms will be used to evaluate collocated data.
Percent difference for a single check (
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Corrective action: Collocated Study. Samplers in a collocation study that measure a CV >10%
require corrective action. The FS will troubleshoot the sampler that has the highest percent
difference from the SLT sampler. If the CV remains between 10 and 20%, the regional contact
will be alerted to the problem. Paired CVs and percent differences will be control charted to
determine trends. Problems and solutions will be reported as soon as possible to the EPA
Regional WACOR/TOCOR/DOCOR and appropriately filed under response and corrective
action reports (Pb-PEP/108-025-01-01-237.1, see Element 9.0, Documentation and Records).
14.1.3.2 Duplicate Laboratory Measurement
Matrix Duplicate (For TSP Filter Strip Only)
One matrix duplicate (MD) must be analyzed for every 20 or fewer field samples. Treat the MD
as a routine sample.
Calculate the relative percent difference (RPD) using the following equation:
RPD= \Cmd~C\ •
where
RPD = relative percent difference
Cmd= measured concentration in the MD, corrected for sample preparation and any dilutions
C = measured concentration in the routine sample, corrected for sample preparation and any
dilutions
Apply precision criteria in Section 7, Table 7.2 for samples with analyte levels > QL. If control
limits are exceeded, re-analyze the sample and duplicate once. If the control limits are exceeded
again, flag the associated sample result as estimated (J).
Laboratory Control Standard Duplicate (For PMio Filter Only)
Analyze one laboratory control standard (LCS) duplicate with each batch of 20 or fewer samples
in an SDG. Recovery of analytes in the LCS is calculated as:
M
%R=—x WOxD
where
%R = percent recovery of the standard
M= measured concentration of the analyte, |ig/L
T= true concentration of the analyte in the LCS, |ig/L
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If the recovery of the LCS does not meet the recovery criteria in Section 7, Table 7.2, re-analyze
once to verify. If the recovery is still unacceptable, the analyte is judged to be out- of-control
and the source of the problem must be identified and resolved. All samples associated with the
out-of-control LCS are to be reported and qualified as estimated "J".
14.1.4 Accuracy or Bias Checks
Accuracy is defined as the degree of agreement between an observed value and an accepted
reference value and includes a combination of random error (precision) and systematic error
(bias). The following three accuracy checks are implemented in the Pb-PEP Program:
• Field QC
o Flow, Barometric Pressure, Temperature
• Laboratory QC
o Quantitation Limit Standard, Lab Control Standard, Matrix Spike, Sample QC
1.4.1.4.1 Field Bias/Accuracy Quality Checks
Flow Rate
The Pb-PEP FS will implement a flow rate verification with each setup. Details of the
implementation aspects of the audit are included in Field SOP Pb-PEPF-5. The verification is
implemented by measuring the analyzer's normal operating flow rate using a certified flow rate
transfer standard. The audit (actual) flow rate and the corresponding flow rate indicated or
assumed by the sampler are reported. The procedures used to calculate measurement uncertainty
are described below.
Accuracy of a single sampler — single check (quarterly) basis (
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ensure that temperature and pressure are within acceptable ranges, and run the verification
procedure a second time. If the verification result is still unacceptable, a multipoint verification
should be performed by the FS. If the multi-point verification indicates that the sampler is
operating outside of the acceptance criteria found in Table 7-1, a flow rate calibration is required.
Then the single-point flow rate verification will be repeated. If the sampler fails to meet the
acceptance requirement after calibration, or a flow rate calibration in the field is not possible, a
back-up sampler will be used (assuming it meets the acceptance criteria) while the affected
instrument is being evaluated/repaired.
Barometric Pressure
The TSP sampler has a built-in atmospheric pressure sensor. The sensor's output is processed to
allow control of the sampling flow rate to the design value under actual ambient conditions of
temperature and pressure.
To perform a routine verification, the barometric pressure sensor reading is verified at ambient
pressure through comparison with the reading from an external standard of known accuracy. If a
pressure difference of more than 10 mmHg is observed, a multipoint verification/calibration of
the pressure-sensing and display system is required before the sampler may be used to perform
an evaluation.
Temperature
The TSP sampler has a built-in atmospheric temperature sensor. The ambient temperature sensor
is verified at a single point using an external temperature standard of known, NIST-traceable
accuracy. If a temperature difference of more than 2°C is observed, a multipoint
verification/calibration of the temperature sensor is required before the sampler may be used to
perform an evaluation.
14.1.4.2 Laboratory Bias/Accuracy Checks
Quantitation Limit Standard
To verify the ability to detect target analytes near the QL, a QL standard (QLS) must be analyzed
at the beginning of the analytical run and after each 40 analytical samples. The recovery of
analyte in the QLS is calculated as:
M
%R =— xlOO
where
%R = percent recovery of the standard
M= measured concentration of the analyte, |ig/L
T= true concentration of the analyte in the QLS, |ig/L
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If the QLS recovery does not meet the criteria in Section 7, Table 7.2, determine the cause, take
corrective action, and re-analyze the QLS.
Laboratory Control Standard
Analyze one LCS with each batch of 20 or fewer samples in an SDG. Recovery of analytes in
the LCS is calculated as:
M
%R =—XlQQ
where
%R = percent recovery of the standard
M= measured concentration of the analyte, |ig/L
T= true concentration of the analyte in the LCS, |ig/L
If the recovery of the LCS does not meet the recovery criteria in Section 7, Table 7.2, re-analyze
once to verify. If the recovery is still unacceptable, the analyte is judged to be out- of-control
and the source of the problem must be identified and resolved. (1) For PMio filter, all associated
results are to be reported and qualified as estimated "J", (2) For TSP filter strip, the MB, LCS,
and all associated samples must be re-prepared and re-analyzed if there is enough sample to
work with. The associated sample results can also be reported but will be qualified as estimated
"J".
Matrix Spike (For TSP Filter Strip Only)
The matrix spike (MS) is designed to provide information about the effect of sample matrix on
the measurement system. One MS sample must be prepared for every 20 field samples in an
SDG. Spike a filter strip with lead prior to any sample preparation. The spiking level must be
the same as that used for the LCS.
Samples identified as field blanks cannot be used for MS sample analysis. MS recovery is
calculated as:
where
%R = percent recovery
Cms = measured concentration of analyte in the MS, corrected for sample preparation and any
dilutions
C = measured concentration of analyte in the routine sample corrected for sample preparation
and any dilutions
s = expected spiked analyte concentration in the MS, corrected for sample preparation and any
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dilutions
If the value of C is less than four times the value of s, apply accuracy and precision criteria in 40
CFR Part 58 Section 4.4. If the value of C is greater than four times the value of s, %R is not
calculated. If the MS does not meet these criteria, examine other QC results to determine if a
matrix problem exists. If laboratory performance is in control, the poor MS accuracy is likely to
be matrix-related. Flag any out-of-control results as estimated "J".
Sample QC
Internal Standard Response - Monitor the signal intensity for the internal standard masses
throughout the analytical run. This information is useful in detecting instrument drift, sensitivity
shift; dissolved solids content, and inherent internal standard (i.e., a natural constituent in a
sample). The absolute intensity of the internal standard must not deviate more than 60 to 125%
from its original intensity in the calibration blank. If deviations greater than these are observed,
examine the internal standard intensities with the following actions:
• If the intensities of the internal standards for the ICV, CCV, or CB are out of control,
recalibrate and re-analyze the samples affected by the out-of-control internal standards.
• If the intensities of the internal standards for the ICV, CCV, and CB are within control limits
but sample internal standards are out-of-control, rerun the sample or rerun at an appropriate
dilution.
• Report results from the original, undiluted, or least diluted sample where the internal
standards are within the acceptance limits.
14.2 Sample Batching—QC Sample Distribution
To ensure that the Pb-PEP includes all types of QC samples within an analysis session, the Pb-
PEP will use the concept of sample batches. A batch of samples will consist of the samples
indicated in Table 14-1. QC samples will be interspersed within the batch to provide data quality
information throughout the analytical session. The definition for each QC sample and how they
are developed can be found in the field SOP for the field and trip blanks (FB, TB) and in the
Laboratory SOP-509 for the laboratory QC checks.
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Table 14-1 QC Sample Distribution
Seq.
1
2
3
4
5
6
7
8
9
10
11
12
13
14
Description1
CB
Cal Std 1
Cal Std 2
Cal Std 3
Cal Std 4
ICV
CB
SCV
QLS
MB
LCS
SI
Sl-MD
Sl-MSorLCS-D
Seq.
15
16
17
18
19
20
21
22
23
24
25
26
27
28
Description
S2
S3
S4
ccv
CB
S5
S6
FB
S8
S9
S10
Sll
S12
S13
Seq.
29
30
31
32
33
34
35
36
37
38
39
40
41
42
Description
S14
CCV
CB
S15
TB
S17
S18
S19
S20
CCV
CB
QLS*
*- See Table 7-2 for QC Codes.
NOTE: * Analyze another QLS if more than 40 analytical samples are to be analyzed.
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75.0 Instrument/Equipment Testing, Inspection,
and Maintenance Requirements
The purpose of this element in the Pb-PEP QAPP is to discuss the procedures used to verify that
all instruments and equipment are maintained in sound operating condition and are capable of
operating at acceptable performance levels. All instrument inspection and maintenance activities
are documented and filed under Pb-PEP/301-093-006.3. See Element 9.0, Documentation and
Records, for document filing and record details.
15.1 Testing
All TSP samplers used in the Pb-PEP will be designated FRM monitors that have been certified
as such by EPA; therefore, the samplers are assumed to be of sufficient quality for the data
collection operation. Testing of such equipment is accomplished by EPA through the procedures
described in 40 CFR Part 53. Annually, prior to deployment, the FSs within each region will
assemble and run all the samplers at the regional site (full collocation). The FSs will perform
temperature, time, date, pressure, and flow rate single-point verification checks every day of PE
audit sampling. If any of these checks are out of specification (see Tables 7-1 and 7-2), the FS or
WAM/TOPO/DOPO will initiate troubleshooting procedures, which may include multipoint
verification checks and calibration. If the problem cannot be located and the sampler continues
to fail the verification checks, the sampler cannot be used for the PE. The FS should use an
alternate sampler and return the sampler to the laboratory for maintenance. If the sampling
instrument meets the acceptance criteria, it will be assumed to be operating properly. If a new
sampler is acquired for use in the Pb-PEP, it should be subject to a collocation with a sampler
shown to be performing satisfactorily in a prior collocation. The results should comply with
acceptance criteria for a routine collocation study. If new upgraded FRM sampler hardware is
introduced, the same type of testing will be conducted. These tests will be properly documented
and filed under Pb-PEP/301-093-006.3.
The Pb-PEP laboratories will use ICP-MS for analyzing the glass fiber filters, and XRF for
analyzing the 46.2 mm Teflon® filters for Pb in PMio. The ICP-MS method contains two general
stages of operation; sample extraction and sample analysis. At the sample extraction stage,
testing will include the analysis of reagents to ensure they are not contaminated. These tests
occur in every sample batch. Also, the hot block equipment will be tested during each extraction
with the use of a NIST traceable thermometer to ensure proper extraction temperatures. Prior to
sample analysis, the laboratory will run a number of calibration checks to ensure proper
operation of the analyzer. In addition the QC samples described in Table 7-2 can help to
determine proper operation of the ICP-MS analyzer. The XRF method generally involves a
sample analysis without extraction. Prior to sample analysis, the laboratory will run a number of
calibration checks to ensure proper operation of the analyzer. In the same manner, the QC
checks described in Table 7-3 can help to determine the proper operation of the XRF analyzer.
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15.2 Inspection
Inspection of various equipment and components can be subdivided into the laboratory and field
activities.
15.2.1 Inspection in the Laboratory
There are several items that need routine inspection in the laboratory. Table 15-1 details the
items to inspect and summarizes how to appropriately document the inspection.
Table 15-1. Inspections in the Laboratory
Analysis
Method
ICP-MS
XRF
Item
Pipettes,
glassware
Standards
and reagents
Hot block
ICP-MS
Auto-
sampler
XRF
Analyzer
Thin film
standards
Inspection
Frequency
Weekly
Monthly
Before and
during
digestion
Before each
run
Before each
run
Weekly
Inspection
Parameter
Certification
status, physical
condition
Certification
status
Achieves proper
temperature
Physical
operation,
cleanliness
Physical operation
cleanliness
Dents, scratches,
discoloration
Action If Item
Fails Inspection
Recertify or
replace
glassware
Recertify or
discontinue use
Discontinue use
and service hot
block
Clean and/or
service unit
Clean and/or
service unit
Verify film,
replace if
necessary
Documentation
Requirement
Document in log
book or bench sheet
Document in log
book or bench sheet
Document in log
book or bench sheet
Document in log
book or bench sheet
Document in log
book or bench sheet
Document in log
book or bench sheet
15.2.2 Inspection of Field Items
There are several FRM sampler parts to inspect in the field operation's maintenance area and in
the field before and after a Pb sample has been taken. Checks specific to high volume or low
volume sampler are denoted by footnotes. Table 15-2 details these inspections.
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Table 15-2. Inspection of Field Items
Item
Sampler unit
Gasket
inspection a
Sample
downtube b
O-ringsb
Calibration and
working
standards
Filter
shipments
Filters
Inspection
Frequency
Prior to each
sampling run
Before and after
assembly
Before each
sampling event
Before each
sampling event
Before each
sampling event
After each
shipment
receipt, before
leaving on audit
Prior to each
sampling event
Inspection
Parameter
Contamination,
particulate matter
Not broken, seats
correctly, no damage
Visible particulate
Not broken, seats
correctly, no damage
Cleanliness, damage
Correct number and
COCs are present
No contamination,
pinholes,
discoloration
Action If Item Fails
Inspection
Clean with
laboratory wipe and
water
Replace with new
gasket
Clean with a dry
cloth
Replace o-rings
Clean the standard
and verify
calibration/ ship to
vendor for repair
Contact laboratory to
reconcile
discrepancy
Void filters and
return to laboratory
Documentation
Requirement
Document in the log
book
Document in the log
book
Document in the log
book
Document in log
book
Document in log
book and complete
REC-01,REC-02
forms (Pb-PEP SOP
Section 2)
Document in log
book or COM- 1
(Pb-PEP SOP
Section 2)
Document in log
book
Applies to high volume sampler only
b Applies to low volume sampler only
15.3 Maintenance
There are many items that need maintenance attention in the Pb-PEP. This section describes
those items according to whether they are laboratory or field activities.
15.3.1 Laboratory Maintenance Items
The successful execution of a maintenance program for the Pb-PEP laboratories is essential to
the success of the Pb-PEP. Table 15-3 and 15-4 provide information on laboratory preventive
maintenance. Maintenance is completed through the laboratory supervisor or the analyzer
vendor.
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Table 15-3. Maintenance for ICP-MS Pb-PEP Laboratories
Item
Auto-sampler Rinse
Station Reservoir
Pump Tubing
Cones
Torch Tip
Argon Dewar
Autodiluter
Auto-sampler and
Peristaltic Pump
Nebulizer Spray
Glassware
Glassware & Cone
alignment
Air filters
Chiller Coolant
Vacuum Oil
Frequency
As needed
Daily
Daily
Weekly
Daily
Daily
Daily
Weekly
Weekly
Weekly
Weekly
Monthly
Monthly
Monthly
Comments
Fillwith2%HN03
Check for fatigue and wear. Replace as needed.
Inspect for sample residues. Wipe clean or replace
with clean cone as needed.
Remove and inspect condition of cones. Replace if
needed.
Check for sample residues. Replace with clean
glassware if needed.
Check for sufficient amount and pressure. Order as
needed.
Rinse thoroughly with reagent water after each use.
Wipe spills or residues.
Check, unclog or replace if needed.
Inspect and clean if needed.
Perform X-Y alignment, if needed.
Clean or replace as needed.
Check level and top off as needed.
Check level and color, replace with fresh one if
needed.
Table 15-4. Maintenance for XRF Pb-PEP Laboratories
Item
Liquid nitrogen dewar
X-ray tube cooling water
vessel
Vacuum pump oil
Frequency
Weekly
Weekly
Weekly
Comments
Check level and top off as needed, calibrate nitrogen
level
Check level and top off as needed per vendor direction
Check level and top off as needed per vendor direction
A LIMS should be used to manage raw data from the analyzers. These LIMS systems should be
backed up weekly to a central server to guard against data loss. A monthly backup of the
network file shares used to store and operate the AIRQA database will be performed by EPA
contractor(s) according to policies established by EPA Office of Administration and Resource
Management.
15.3.2 Field Maintenance Items
There are many items associated with appropriate preventive maintenance of a successful field
program. The Pb-PEP field SOPs (high volume and low volume methods) provide procedures
for cleaning important components of field equipment. These SOPs can be found on the AIRQA
Web site under Pb-PEP, Documentation. Table 15-5 details the appropriate maintenance checks
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of the Pb-PEP samplers and their frequency. Footnotes identify elements specific to the high
volume or low volume samplers.
Table 15-5. Preventive Maintenance of Field Items
Frequency
Maintenance item
Every visit
1. Inspect sampler and verification/calibration equipment for damage
2. Inspect filter holder frame and rubber gasket for damage a
3. Inspect o-rings b
4. Inspect downtube b
Quarterly (every 3 months)
1. Clean sampler inlet surfaces
2. Clean interior of sampler unit
3. Check condition of sample transport containers
4. Inspect vacuum tubing, tube fittings, and other connections to pump and
electrical components; service if necessary
5. Clean downtube b
" Applies to high volume sampler only
b Applies to low volume sampler only
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16.0 Instrument Calibration and Frequency
This element of the Pb-PEP QAPP concerns the calibration procedures that will be used for
instruments involved in the environmental measurements. Tables 7-1 through 7-3 indicate the
instruments that require verification and calibration, the required frequencies of these activities,
and the acceptance criteria for these activities. All calibration activities/procedures are described
in more detail in the Field and Laboratory SOPs.
Calibrations that involve instrument adjustments should only be accomplished when it is obvious
that calibration is required; therefore, the Pb-PEP uses a three-phase approach to calibration,
which involves the following:
• One-point verification—These verifications ensure that the calibration is within acceptance
limits by performing frequent one-point verifications that do not include instrument
adjustments.
• Multipoint verification—Similar to one-point verifications, these occur at established
frequencies, as well as when there is a failure of a one-point verification. These multipoint
verifications do not include instrument adjustments.
• Calibration—This occurs when there is a failure of a verification. Instrument adjustment
occurs at this point and is followed by a one-point verification.
16.1 Instrumentation Requiring Calibration
16.1.1 Laboratory Equipment
ICP-MS
The Region 9 ICP-MS analyzer will require calibration. The lab will perform an initial
calibration daily or for every analytical batch, whichever is more frequent and a continuing
calibration verification. These calibrations are described in Section 14. Refer to Table 7-2 for
frequency, acceptance criteria, and corrective action requirements.
XRF
XRF analyzers typically will require two calibrations; a detector calibration and an analyzer
calibration. The detector contains a digital signal processor that is calibrated by repeatedly
measuring the beam stop inside the unit. The detector calibration will be completed on a weekly
basis. The analyzer is calibrated by analyzing thin film standards. Using at least two standards
for each element, the unit calculates a linear regression line. A full analyzer calibration is
completed if the daily quality control standard falls outside acceptable limits or when significant
repair or maintenance is conducted on the unit. Refer to Table 7-3 for frequency, acceptance
criteria, and corrective action requirements.
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16.1.2 Field Equipment
TSP Portable Sampler
Upon receipt of a new portable sampler, multipoint verifications will be performed. Multipoint
verifications and calibrations typically occur at the field office or laboratory. Refer to Table 7-1
for frequency, acceptance criteria, and corrective action requirements.
The following verifications are routinely performed in the field:
• Verification of the sampler's temperature probes against the working temperature standard
• Verification of the sampler's barometric pressure against the working pressure standard
• Verification of the sampler's volumetric flow rate against the working flow standard
• Verification of the sampler's internal clock against a known time standard.
Temperature Probes
The portable sampler contains an ambient temperature probe. At every sampling event, the FS
will perform a one-point field verification of the sensor using a digital NIST-traceable
temperature probe (e.g., BGI HiVolCal Model HC-2). A different NIST-traceable calibration
device will be used in the field office as a primary standard to perform multipoint temperature
verifications once a year or after there has been a one-point verification failure. If the multipoint
verification fails to meet the acceptance criteria, a temperature calibration will be performed.
Following a calibration where an adjustment is necessary, the working standard will be used to
verify the calibration.
Barometric Pressure
A NIST-traceable calibration device (e.g., BGI HiVolCal Model HC-2) will be used in the field
for one-point verifications of the portable sampler's pressure sensor during each sampling event.
A different NIST-traceable calibration device will be used in the field office as a primary
standard to perform multipoint pressure verifications once a year or after there has been a one-
point verification failure. If the multipoint verification fails to meet the acceptance criteria, a
barometric pressure calibration will be performed. Following a calibration where an adjustment
is necessary, the working standard will be used to verify the calibration.
Time Standard
The FS will check the time standard's time and date using the atomic clock, which can be found
on the Internet at http://www.time.gov or through a known time standard (e.g., cell phone).
Times can be checked each day before heading to the field, particularly where there is no cell
phone service at the sampler location(s) Samplers should be set up based on the local
standard time
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Flow Rate
Before every sampling event, after leak checks, temperature, and pressure verifications are
performed, a one-point flow rate verification will be performed using a NIST-traceable
calibration device (e.g., BGI HiVolCal Model HC-2). It is essential that the flow check be
performed after the other verifications because the total flow volume is calculated using the
ambient temperature and pressure. A different NIST-traceable calibration device will be used in
the field office as a primary standard to perform multipoint pressure verifications once a year or
after there has been a one-point verification failure. If the multipoint verification fails to meet
the acceptance criteria, a flow rate calibration will be performed. Following a calibration where
an adjustment is necessary, the working standard will be used to verify the calibration.
16.2 Calibration Method That Will Be Used for Each Instrument
The calibration methods are described in detail in the field and laboratory SOPs.
16.3 Calibration Standard Materials and Apparatus
Table 16-1 presents a summary of the specific standard materials and apparatus used in
calibrating measurement systems for parameters necessary to generate the quality Pb data
required. All of the standards meet the acceptance requirements for Tables 7-1 through 7-3 and
will be NIST-traceable.
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Table 16-1. Calibration Standards and/or Apparatus for Pb Calibration
Parameter
Standard (S)
Apparatus (A)
Description
Accuracy
or Resolution
Manufacturer's
Name
Model Number
Field
Equipment
Temperature
Pressure
Flow Rate
A
A
A
Multi-parameter
calibrator
Multi-parameter
calibrator
Multi-parameter
calibrator
Accuracy ±0.2°C
Resolution 0.1 °C
Accuracy ±0.1%
Resolution 0.01 psig
Accuracy 0.75% of
reading
Resolution
O.lmL/min
BGI HiVolCal
BGI HiVolCal
BGI HiVolCal
HC-2
HC-2
HC-2
Lab Standards
Pipettes &
Volumetric
flasks
Reagents
HNO3
Stock Standards
Argon gas
supply,
Film standards
A
S
S
S
S
Class Aa
trace metals grade or
betterb
NIST Traceable0
high-purity
grade,99.99%
50 ug/cm2 thickness
standards certified to
±5%
Baker Instra-
Analyzed
Spex or Inorganic
Ventures
Micromatter
a Class A Pipettes meet all the requirements of American Society for Testing and Materials (ASTM) E 969-95. Compliance with
the Class A Pipette requirements and other laboratory certifying groups is indicated by the letter "A" near the top of each pipette.
All pipettes are calibrated in accordance with ASTM E 542 and meet the accuracy requirements of ASTM E 969; borosilicate
glass meets ASTM E 438 for Type I, Class A requirements.
Only materials that conform to the American Chemical Society (ACS) specifications such as reagent grade or better will be
used.
°ICP & ICP-MS standards are assayed by validated ICP and wet chemical procedures to obtain the certified value. Every standard
is traceable to a specified NIST SRM. The NIST-traceable density is available on the certificate.
16.4 Calibration Frequency
See Tables 7-1 through 7-3 for a summary of calibration frequencies.
All calibration events, as well as sampler and calibration equipment maintenance, will be
documented in field/lab data records and notebooks as indicated in the field and laboratory
SOPs. The records will normally be controlled by the ESAT FSs or LAs and located in the
laboratory or field offices when in use. Eventually, all calibration records will be appropriately
filed under Pb-PEP/301-093-006.6 (see Element 9.0, Documentation and Records).
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16.5 Standards Recertifications
16.5.1 Field Standards
All primary/calibration and working standards will be certified every year as NIST-traceable
using the EPA Metrology laboratory in RTF, NC. OAQPS will work with the regional offices to
find an appropriate time frame to conduct re-certifications on the field instruments.
16.5.2 Lab Standards
All glassware will be calibrated in accordance with ASTM E 542 and meet the accuracy
requirements of ASTM E 969; borosilicate glass meets ASTM E 438 for Type I, Class A
requirements. TCP and ICP-MS standards are assayed by validated TCP and wet chemical
procedures to obtain the certified value. Every standard is traceable to a specified NIST SRM.
XRF thin film standards will be replaced when the stated manufacturer's tolerances are outside
of control limits.
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7 7.0 Inspection/Acceptance for Supplies and Consumables
17.1 Purpose
The purpose of this element is to establish and document a system for inspecting and accepting
all supplies and consumables that may directly or indirectly affect the quality of the Pb-PEP data.
The Pb-PEP relies on various supplies and consumables that are critical to its operation. By
having documented inspection and acceptance criteria, consistency of the supplies can be
assured. This element details the supplies/consumables, their acceptance criteria, and the
required documentation for tracking this process.
If the Pb-PEP program is being operated in conjunction with the PIVb.s PEP, the acceptance and
testing of equipment, supplies and consumables may be inspected and documented with the
PM2.5 PEP supplies using the requirements located in Section 17 of the PIVb.s QAPP. In the
same way, equipment common to both programs should be shared. This practice will reduce the
duplication of effort that could result by implementing the programs separately.
A number of forms will be discussed in the following sections. These forms are found in the
Field and Laboratory SOPs, but examples of them are placed at the end of this section. They are:
• Field/Laboratory Inventory Form (INV-01) (Figure 17-1)
• Field/Laboratory Procurement Log Form (PRO-01) (Figure 17-2)
• Field/Laboratory Equipment/Consumable Receiving Report Form (REC-01)
(Figure 17-3).
17.2 Critical Supplies and Consumables
This section attempts to describe the needed supplies for the Pb-PEP and includes items for the
laboratory and the field. Generally, critical field and laboratory equipment has been selected by
the Pb-PEP organizers based on the required performance specifications of resolution, accuracy,
and ease of use.
17.2.1 Laboratory Supplies
Table 17-1 is a list of the laboratory equipment required for the ICP-MS analysis of glass fiber
filters conducted by the Region 9 laboratory. Equipment that is not deemed critical (affecting
data quality) has been left to the Laboratory Manager to select. To maintain consistency in the
PE program, all consumables/equipment with a model number (as shown in Table 17-1) will be
purchased using the same model number when supplies run low. The LA is required to keep an
inventory of all equipment using Field/ Laboratory Inventory Form (INV-01), which is shown in
Figure 17-1. A general list of equipment and consumables for the XRF analysis of the 46.2mm
Teflon® filters is provided; however, the details may change according to vendor.
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Table 17-1. Laboratory Equipment
ICP-MS
Activity Description
Details
Preparation Logbook
Hot Block Digestion System
Pipettors
Pipettes
Nitric Acid (HNOs), concentrated
Gloves
Tweezers
Polypropylene Digestion Vessels
Ribbed Watch Glass,
Polycarbonate Transfer Racks
Paper cutter or scissors
Plastic or Teflon wash bottles
Glass Fiber Filter
Teflon Filters
Stock Standards
Bound with numbered pages
Environmental Express or equivalent
Variable volume for dispensing reagents and acids
Calibrated fixed volume and digital variable volume with
appropriate plastic tips
ACS Reagent Grade or better, suitable for trace metals analysis.
Powder-free gloves
Teflon non-serrated
Environmental Express P/N SC505 or equivalent
Environmental Express P/N SC505 or equivalent
Environmental Express P/N SC200 or equivalent
Any house wares vendor
Capable of dispensing reagent for cleaning
EPA National Filter Procurement
EPA National Filter Procurement
Spex or Inorganic Ventures
Analysis ICP-MS
Autosampler
Autodilutor
Peristaltic Pump
Refrigerated Circulator
Argon gas supply
Auto-sampler tubes
Volumetric flasks,
Volumetric pipettes
Storage bottles
Automatic pipettes
Disposable pipette tips
Perkin Elmer Elan DRC Plus
Cetac Autosampler, or equivalent
Cetac Autodilutor, or equivalent
Gilson MinipulsS Peristaltic Pump, or equivalent
Polyscience 6105 - Refrigerated Circulator, or equivalent
High-purity grade, 99.99%
Class A graduated cylinders, and funnels (glass and/or metal-
free plastic)
Class A
Narrow-mouth with screw closure, 125-mLto 1-L capacities
Capable of delivering volumes of 10 to 1,000 uL
Metal-free
XRF
Activity Description
Details
Preparation
Logbook
Methanol
Squeeze bottle
Stainless Steel Tweezers
Kimwipes
Mylar sheets
Vacuum oil
Bound with numbered pages, may include bench sheets
ACS Reagent Grade or better
Capable of dispensing reagent for cleaning
Millipore flat tipped tweezers P/N 62-000067 or equivalent
Large and small P/N 34255 and P/N 34155 or equivalent
2" x 2" precut squares
Analyzer specific
Analysis X-ray Fluorescence
Liquid Nitrogen
PANalytical Epsilon 5 EDXRF or equivalent
Detector cooling
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As consumables run low or when new equipment purchases are necessary, the LA will be
responsible for assisting in the procurement of these items following the policy and requirements
described in the ESAT scope of work. The LA should continue purchasing consumable
equipment with the same model numbers as the equipment initially procured unless the Pb-PEP
Laboratory Manager suggests a different item due to improved quality, reduction in
contamination, improved ease of use, or lower cost (without sacrificing quality). Such changes
should be coordinated with the WACOR/TOCOR/DOCOR. The Pb-PEP Laboratory Manager
will also present any such proposed equipment changes to the National Pb-PEP Project Lead for
approval. The following procedures will be performed by the LA:
• Develop procurement requests as per EPA requirements.
• Upon order, add items to the Field/Laboratory Procurement Log Form (PRO-01).
• Once a month, provide a copy of the PRO-01 to the Pb-PEP Laboratory Manager and the
laboratory services ESAT WACOR/TOCOR/DOCOR.
• File PRO-01 under Agency file code "Pb-PEP/301-093-006.6."
17.2.2 Field Equipment and Supplies
The field equipment and supplies are listed in Table 17-2. Quantities for some items in Table
17-2 are not shown because they will vary with the size of the field operation (number of
samplers and auditors). The FS is required to keep and inventory all equipment, which include
any warranty information.
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Table 17-2. Field Equipment and Supplies
Activity
Initial Set-up
Checks
Maintenance
Operation
Shipping
Data Transfer
Required Equipment
Knife
Tool kit (screw driver, pliers, etc.)
Transfer standards (1 per region)
Watch/clock check device
Cleaning solution
Soft bristle brush
Cotton swabs
Cleaning cloth
Distilled water
Isopropyl Rubbing Alcohol
FRM portable high volume audit sampler
Backup FRM portable high volume audit sampler
FRM portable low volume audit sampler
Backup FRM portable low volume audit sampler
Permanent marker
Sampler transport cassette(l set)
Ropes
Folding ladder
Gloves (powder free)
Laptop computer
Field data sheet (FDS)/ Chain of custody (COC)
TSP filters
Field blank filters
Glassine envelope for 8" x 10" high volume filters
Manila envelope for 8" x 10" high volume filters
Shipping Box for filters
Plastic ziplock bags for field and COC sheet
Pre-labeled shipping airbill
SD Memory Cards
SD Memory Card Reader
Web access to the AIRQA Web site
Identified Source
Available through PM2 5 PEP
Available through PM2 5 PEP
BGI Hi-Vol calibrator performs
flow/temp/pressure
Available through PM2 5 PEP
Available through PM2 5 PEP
Available through PM2 5 PEP
Available through PM2 5 PEP
Available through PM2 5 PEP
Available through PM2 5 PEP
Available through PM2 5 PEP
Tisch TE-5 170 or equivalent
Tisch TE-5 170 or equivalent
BGI PQ-200A or equivalent through
PM2 5 PEP
BGI PQ-200A or equivalent through
PM2 5 PEP
Sharpie
Available from sampler vendor
Available through PM2 5 PEP
Available through PM2 5 PEP
Fisher Scientific FB GLV LTX PF or
equivalent
Available through PM2 5 PEP
Begun electronically from AIRQA
Web site
EPA National Filter Procurement
EPA National Filter Procurement
www.clearbags.com 10 3/8 x 4 1/2
Glassine Open Side [G25] or
equivalent
www.officemax.com #12 Kraft
Business Envelope P/N 21642199 or
equivalent
www.uline.com 12 x 6 x 4" Long
Corrugated Box P/N S-4127 or
equivalent
General house wares vendor
EPA contract shipping vendor
Sandisk (1 GB minimum)
Initial quantities will be worked out with the WACOR/TOCOR/DOCOR in each region. As
consumables run low or when new equipment purchases are necessary, the FS will be
responsible for assisting in the procurement of these items following the policy and requirements
described in the ESAT scope of work. The FS should continue purchasing consumable
equipment with the same model numbers as the equipment that was initially procured unless the
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Regional WACOR/TOCOR/DOCOR suggests a different item due improved quality, reduction
in contamination, increased ease of use, or lower cost (without sacrificing quality). The
WACOR/TOCOR/DOCOR will report any equipment changes that could affect the results of
sampling events to the National Pb-PEP Project Leader. The following procedures will be
required:
• The FS will develop procurement requests as per EPA requirements.
• Upon order, add items to the Field/Laboratory Procurement Log Form (PRO-01).
• Monthly or upon request, provide a copy of the PRO-01 to the Regional
WACOR/TOCOR/DOCOR.
• File PRO-01 under Agency file code "Pb-PEP/301-093-006.6."
17.3 Acceptance Criteria
The major pieces of capital equipment are namely the following:
Laboratory Field
Perkin Elmer Elan DRC Plus ICP-MS Portable sampler
Hot Block digester Calibration equipment (see Section 16.0,
Cetac Autosampler, or equivalent Instrument Calibration and Frequency)
CetaAutodilutor, or equivalent Laptop computer
Gilson Minipuls 3 Peristaltic Pump, or
equivalent
Polyscience 6105 - Refrigerated
Circulator, or equivalent
PANalytical Epsilon 5 EDXRF or equivalent
The equipment and consumables have been selected based upon their advertised specifications
on accuracy and resolution, and the portable sampler has been built to FRM performance
specifications and has been accepted as such. Upon receipt of equipment, the equipment will be
inspected and tested using calibration standards (see Element 16.0, Instrument Calibration and
Frequency) to ensure they operate within the performance parameters. All equipment is under
warranty, and the equipment listed above will undergo yearly calibration and certification as
discussed in Element 16.0, Instrument Calibration and Frequency.
Both field and laboratory personnel will use procurement logs (PRO-01) (Figure 17-2) to record
the purchase of new equipment and consumables. These logs also indicate whether the items
were accepted or rejected. In addition, the laboratory and field personnel are required to keep a
Field/Laboratory Inventory Form (INV-01) (as shown in Figure 17-1), which lists each
equipment item and their warranty dates.
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17.4 Tracking and Quality Verification of Supplies and Consumables
Tracking and quality verification of supplies and consumables have two main components. The
first is the need of the end user of the supply or consumable to have an item of the required
quality. The second need is for the purchasing department to accurately track goods received so
that payment or credit of invoices can be approved. To address these two issues, the following
procedures outline the proper tracking and documentation process to follow by receiving
personnel:
1. Perform a rudimentary inspection of the packages as they are received from the courier or
shipping company and note any obvious problems with a receiving shipment, such as crushed
box or wet cardboard
2. Sign and date the appropriate purchase order for the incoming items from the files and send
to the purchaser.
3. Fill out a Field/Laboratory Equipment/Consumable Receiving Report Form (REC-01)
(Figure 17-3), comparing the items and quantity against the purchase order and inspecting the
condition of each item
4. If the items received match the purchase order and the condition of the equipment or
consumables is acceptable, signify this on the form and file under Agency file code "Pb-
PEP/301-093-006.6"
5. If the quantity, items, or condition are not acceptable, complete REC-01 with remarks and
send a copy of the form to the Regional WACOR/TOCOR/DOCOR
6. Call the vendor to report the problem with the package/contents
7. Add receipt information to the Field/Laboratory Procurement Log Form (PRO-01) and to the
Field/Laboratory Inventory Form (INV-01).
In addition, any conversations that field or laboratory personnel have with vendors will be
recorded on a phone communication form, which will also be filed.
Capital equipment will be verified for quality prior to implementation into the program to ensure
that they meet the minimum specifications for their intended use. This equipment will be tested
to ensure that it meets the specifications published by the manufacturer and the criteria described
in Section 7 of this QAPP. Ancillary equipment including consumables may also require testing
such as shipping media (glassine envelopes, petri-slides) and data logging devices. Assessments
of MQOs may assist in identifying these items. Filter media, both Teflon® low volume filters
and glass fiber high volume filters are subjected to EPA specific acceptance testing prior to
distribution to SLTs.
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Figure 17-1 Field/Laboratory Inventory Form (INV-01)
Field/Laboratory Inventory Form (INV-01)
Item
Vendor
Model
Number
Quantity
Purchase
Date
Warranty
Figure 17-2 Field/Laboratory Procurement Log Form (PRO-01)
Field/Laboratory Procurement Log Form (PRO-01)
Item
Model
Number
Quantity
PO#
Vendor
Date
Ordered
Received
Cost
Initials
Accept/
Reject
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Figure 17-3. Field/Laboratory Equipment/Consumable Receiving Report Form (REC-01)
Received From:
Shipped From: :
Shipped Via:
Shipping Charge
Prepaid
Purchase Order Number
Collect
Quantity
Freight Bill Number
Description of Item
Remarks: Accept Shipment
Problem
Condition
Notes:
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18.0 Data Acquisition Requirements
This element addresses data not obtained by direct measurement from the Pb-PEP. The majority
of data used in the Pb-PEP will be direct measurements acquired by the FSs and LAs working
for the Pb-PEP.
18.1 Acquisition of Non-Direct Measurement Data
The Pb-PEP relies on data that are generated through field and laboratory operations; however,
some data are obtained from sources outside the Pb-PEP. This element lists these data and
addresses quality issues related to the Pb-PEP.
18.1.1 Chemical and Physical Properties Data
Physical and chemical properties data and conversion constants are often required in the
processing of raw data into reporting units. This type of information, which has not already been
specified in the monitoring regulations, will be obtained from nationally and internationally
recognized sources. Other data sources may be used with approval from the National Pb-PEP
Project Leader. The following sources may be used in the Pb-PEP without prior approval:
• NIST
• International Organization for Standardization, International Union of Pure and Applied
Chemistry, American National Standards Institute (ANSI), and other widely recognized
national and international standards organizations
• EPA
• QA Handbook for Air Pollution Measurement Systems: "Volume II: Ambient Air Quality
Monitoring Program" EPA-454/B-13-003, May 2013 - Full Document and subsequent
revisions
18.1.2 Sampler Operation and Manufacturers' Literature
Manufacturers' literature, which includes operations manuals and users' manuals, are another
important source of information needed for sampler operation because they frequently provide
numerical information and equations pertaining to specific equipment. Pb-PEP personnel are
cautioned that such information is sometimes in error and appropriate cross-checks will be made
to verify the reasonableness of information in manuals. Whenever possible and especially during
acceptance testing, the FSs will compare physical and chemical constants in the operator's
manuals to those given in the sources listed above. If discrepancies are found, the FS may raise
these issues during Pb-PEP workgroup conference calls and during recertification training
sessions.
The following types of errors are commonly found in such manuals:
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• Insufficient precision
• Outdated values for physical constants
• Typographical errors
• Incorrectly specified units
• Inconsistent values within a manual
• Use of different reference conditions than those called for in EPA regulations.
18.1.3 Site Information
To determine the site and the monitor that the PE will be compared against, the FS must rely on
the site information provided to him/her by the EPA region or the SLT monitoring agency. This
information should be included in the site file and stored in the field office. This information
will include the following parameters:
• AQS site ID
• Monitor type
• Method designation (routine instrument)
• Parameter Occurrence Codes (POC)
• PQAO.
These values must be available in the AQS database and must be double-checked for
accuracy before proceeding to a site. Audit data are very difficult or impossible to load into
AQS if any of these parameters are recorded incorrectly during the audit.
18.1.4 External Monitoring Databases
It is the policy of the Pb-PEP that no data obtained from the Internet, computer bulletin boards,
or databases from outside organizations shall be used in creating reportable data or published
reports without approval from the National Pb-PEP Project Leader. Requests may be raised
during the Pb-PEP workgroup conference calls or on an individual basis. This policy is intended
to ensure the use of high-quality data in Pb-PEP publications.
Data from the EPA AQS database may be used in published reports with appropriate caution.
Care must be taken in reviewing/using any data that contain flags or data qualifiers. If data are
flagged, such data shall not be used unless it is clear that the data still meet critical QA/QC
requirements. It is impossible to assure that a database, such as AQS, is completely free from
errors, including outliers and biases, so caution and skepticism are called for in comparing
routine data from other reporting agencies as reported in the AQS. Users will review available
QA/QC information to assure that the external data are comparable with Pb-PEP measurements
and that the original data generator had an acceptable QA program in place.
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19.0 Data Management
19.1 Background and Overview
This element describes the data management operations, including data recording,
transformation, transmittal, reduction, validation, analysis, management, storage, and retrieval,
pertaining to Pb measurements for the Pb-PEP. This includes an overview of the mathematical
operations and analyses performed on raw ("as-collected") Pb data.
The Pb-PEP is dependent upon the collection of quality data which will come from several
different sources, such as the Pb-PEP field and laboratory activities as well as the field and
laboratory data collection activities for the routine sampling activities where a PE was
performed.
Each of the individual stakeholders is responsible for collecting quality data from their area of
influence and distributing the data to the appropriate participant. Table 19-1 represents the data
management structure for the Pb-PEP.
Table 19-1. PEP Data Management Structure
STAKEHOLDER
Regional Pb-PEP
Coordinator or Self-
Implementer Lead
Field Performance
Evaluation Operator
Monitoring organization
laboratory staff
Performance Evaluation
Laboratory Analyst
Performance Evaluation
Laboratory Manager
TYPE OF DATA
Sites to participate in the performance evaluation
for the year
AQS Site ID of the Primary Pb monitor, POC, and
Method Code of selected sites. Note: Method
Code can be determined if sampler make and
model are known
Data from the operation of the FRM portable audit
sampler including chain of custody information
for collocated sample.
Routine sample data
Pb Laboratory Data
Comprehensive Performance Evaluation Reports
DISTRIBUTION
To monitoring organizations
-To ESAT contractor
-To the ESAT field scientist conducting Pb-
PEP
-To Regional TOPO/DOPO
-To monitoring organization staff.
-To Region 9 laboratory
Use same distribution and validation
procedures as all other Pb data produced by
the monitoring organization, then uploaded
to AQS.
-To LIMS
-To AIRQA Web site
-To AQS via contractor
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19.2 Information Management Flow
Figure 19-1 provides a flow of the information management system for the Pb-PEP. In general,
hardcopy/electronic information will be collected at various stages of the field and laboratory
activities. The field information will be stored at both the Regional field office and in Region 9.
The required AQS fields, once verified and validated will be uploaded to AQS where it will be
compared with the routine data that has been uploaded from the monitoring organizations.
Field
Legend
Sample
Paper
Electronic
Data
Figure 19-1. Pb-PEP Information/Sample Flow
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19.2.1 Field Data
Information from the field will come from two sources: data from the Pb-PEP audit sampler and
data from the monitoring organization's primary or collocated sampler.
Pb Performance Evaluation Portable Audit Sampler Data
Before leaving for the audit, the FS will print a FDS/COC from the AIRQA Web site. Each type
of filter (routine, field blank, trip blank) requires different information, and the correct type must
be selected from the AIRQA Web site. Appropriate filter information should be filled in on the
form before the audit. The Pb portable audit sampler, once appropriately programmed, provides
all the required data that needs to be collected by the field scientist with the exception of the
filter ID and site identifying information. Data download will be accomplished by utilizing a
laptop computer immediately after recovery of the performance evaluation sample. Additional
information may be documented to supplement the information collected automatically. Once
the standard fields that will be automatically generated by the Pb portable sampler are
downloaded to the field laptop, the filter ID, and AQS site ID and any freeform notes about the
sampling activity will be input. The FS will use this information to complete the printed
FDS/COC form. Upon arrival back to the field office, the FS will input the information on the
hard copy FDS/COC to the online form in the AIRQA Web site. The original hard copy
FDS/COC form will be sent along with the filters. The field verifications and site related data,
although pertinent, does not need to be captured by the laboratory.
Pb Monitoring Organization Primary Sampler Data
The primary sampler will be operated in accordance with its normal operational schedule. The
data acquired by the routine field operator will follow its normal path as detailed in the
monitoring organizations QAPP and SOPs. The PEP data will be concatenated with the primary
sampler data in AQS where the data comparison will be made.
Pb Monitoring Organization Collocated Data
The monitoring organization will also perform four to six additional collocated samples at the
collocated site(s) representing the PQAO. The monitoring organization will be required to
submit the collocated sample with the COC and field data sheets to the Region 9 laboratory.
Since EPA does not dictate the type of sampler the monitoring organization will use (other than
the need for the sampler to have FRM/FEM status) the sampler may not be able to electronically
record the same type of information as the PEP audit sampler. Therefore, the lab will be
required to input information from either the monitoring organization's field data sheet or COC
form.
19.2.2 Laboratory Data
Similarly to field data, laboratory data come from the Region 9 ICP-MS laboratory, the
contracted XRF laboratory, and the monitoring organization laboratory.
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Region 9 ICP-MS Laboratory
The performance evaluation laboratory analyzing the glass fiber filters will be operated by ESAT
personnel according to the appropriate laboratory SOPs. The data acquired by the laboratory
will be collected and validated as detailed in the Pb-PEP SOPs. The data will be handled by a
LEVIS that acquires data both manually and automatically. The data will be electronically
delivered to the AIRQA Web site upon validation. The laboratory deliverables to the AIRQA
Web site are: chain of custody, analysis summary/report, and electronic data deliverable (EDD)
in Excel format.
XRF Contract Laboratory
The contract laboratory selected to analyze the 46.2 mm Teflon® filters will operate according to
the laboratory's current SOP. The data acquired by the laboratory will be collected and validated
as detailed in the SOP. The data should be handled by a LEVIS that acquires data both manually
and automatically. The data will be electronically delivered to the AIRQA Web site upon
validation. The laboratory deliverables to the AIRQA Web site are: chain of custody, analysis
summary/report, and EDD in Excel format.
Monitoring Organization Laboratory Data
The monitoring organization laboratory will be operated in accordance with its normal
operational procedures. The data acquired by the laboratory should follow its normal path as
detailed in the monitoring organizations QAPP and SOPs.
19.3 Data Recording
Each method that generates information in the Pb-PEP will have a data form available for hand
recording this information. These forms are found at the end of the particular Field or Laboratory
SOP that describes the data collection activity, as summarized in Table 19-2.
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Table 19-2. List of Pb-PEP Data Processing Operations for Critical Values
Reference
Pb-PEP Field SOP
Pb-PEP Field SOP and
Pb-PEP Laboratory SOP
AQS Manuals and
Guides Web site
AQS Manuals and
Guides Web site3
AQS Manuals and
Guides Web site3
Title
Filter Exposure and Concluding
the Sampling Event
COC Form and Field Data Sheet
User Guide -Air QA Reports
AQS Data Coding Manual (AQ2)
AQS User 's Guide
Description (Data Related)
Describes how to program the sampler to start
and end sampling for a 24 -hour period, as well as
the acquisition of data from the portable sampler
Describes the field procedure for completing the
field portions of the COC Form and Field Data
Sheet
Describes how to use the different reports within
the AIRQA Web site.
Describes the coding of air quality data
transactions; describes the various transactions
used to create, update, or delete data in the AQS
Describes the installation of AQS software,
accounts, data input (batch and online),
maintenance, and data retrievals (standard
reports)
N/A = Not applicable
a AQS reference documents can be found at http://www.epa.gov/ttn/airs/airsaqs/manuals/manuals.htm
19.4 Performance Evaluation Data Transfer and Archiving
Table 19-3 presents information such as where various data are produced, and how/when it will
be archived/transferred.
Table 19-3 Data Transfer and Archiving
Data Produced
Performance Evaluation Field
Sampler Data
Performance Evaluation
Laboratory
How to Archive
Download each FDS/COC form to
laptop computer or data link. Archive
data to second computer or flash
media at main field office.
Back-up of database occurs each
night as per laboratory computer
network storage procedures
When to Transfer
Transfer data to the AIRQA Web
site after each audit
Validated data paired to field data in
AIRQA once a month and upload to
AQS the following month
Concentration data will be uploaded to the AQS database using the most current AQS transaction
protocol.
19.5 Data Validation
Data validation is a combination of checking that data processing operations have been correctly
performed and of monitoring the quality of the field and laboratory operations. Data validation
can identify problems in either of these areas. Once problems are identified, the data can be
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corrected or invalidated, and corrective actions can be taken for field or laboratory operations.
Numerical data stored in the PB-PEP LEVIS are never internally overwritten by condition flags.
Flags denoting error conditions or QA status are saved as separate fields in the database, so that
it is possible to recover the original data.
The following validation functions are incorporated into the PB-PEP LEVIS to ensure the quality
of data entry and data processing operations:
• 100% data review. The FDS/COC forms are subjected to a 100% data review for accuracy
and completeness by the FS after each audit. The COC information on the FDS/COC form
and laboratory results/deliverables are subjected to a 100% data review by the LA monthly at
a minimum. All completed audit records on the AIRQA Web site must be reviewed and, if
acceptable, marked "APPROVED" once a month by regional Pb-PEP lead.
• Range checks. Simple range checks are performed by the PB-PEP LEVIS for almost all
monitored parameters. For example, valid times must be between 00:00 and 23:59.
Reasonableness checks may also be performed by the LA. For example, in most Regions the
summer temperatures should be between 10 and 50°C. Because these range limits for data
input are not regulatory requirements, the Pb-PEP Laboratory Manager may adjust them
from time to time to better meet quality goals.
• Completeness checks. When the data are processed, certain completeness criteria must be
met. For example, each sample event must have a start time, an end time, an average flow
rate, and operator and technician names. At a minimum, FDSs, COC forms, and pre- and
post-weighing data entry forms must be completely filled out.
• Internal consistency and other reasonableness checks. Several other internal consistency
checks are built into the PB-PEP LEVIS. For example, the end time of a filter must be greater
than the start time. Computed filter volume (integrated flow) must be approximately equal to
the exposure time multiplied by the nominal flow. Additional consistency and other checks
will be implemented as the result of problems encountered during data screening.
• Data retention. Raw data sheets are retained in the laboratory files for a minimum of four
calendar years and are readily available for audits and data verification activities. After 4
years, the FS or LA may request instructions from OAQPS on the disposition of hard copy
records and computer back-up media. Sample filters will be archived for 4 calendar years at
ambient temperature. At the end of the fourth calendar year, the LA may request instructions
from OAQPS on the disposition of archived sample filters. The time frame for retention and
disposition of Agency records is determined by EPA records schedules (see Element 9.0,
Documentation and Records); however records may need to be retained for longer periods
(e.g., for legal discovery). Therefore, approval from OAQPS is required before the
destruction of records.
• Statistical data checks. Errors found during statistical screening will be traced back to
original data entry files and to the raw data sheets, if necessary. These checks shall be
conducted on a monthly schedule and before any data are submitted to the AQS.
• Sample batch data validation. This is discussed in Element 23.0, Validation and
Verification Methods. Sample batch data validation associates flags, which are generated by
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QC values outside of acceptance criteria, with a sample batch. Batches containing too many
flags will be rerun and/or invalidated.
Table 19-4 summarizes the validation checks applicable to the Pb-PEP data.
Table 19-4. Validation Check Summaries
Type of Data Check
Data parity and transmission protocol checks
Data review
Date and time consistency
Completeness of required fields
Range checking
Statistical outlier checking
Manual inspection of charts and reports
Sample batch data validation
Electronic
Transmission
and Storage
/
Manual
Checks
/
/
/
/
Automated
Checks
/
/
/
/
/
/
Two key operational criteria for Pb sampling are bias and precision. As defined in 40 CFR Part
58, Appendix A, these are based on differences between collocated sampler results and FRM
PEs. The national Pb-PEP lead will evaluate these data as early in the process as possible, so
that potential operational problems can be addressed. An objective of the Pb-PEP will be to
optimize the performance of its Pb monitoring equipment. Initially, the results of collocated
operations were control charted (see Element 14.0, Quality Control Requirements) to establish
limits to flag potential problems. As the data results accumulate over time, EPA may reassess
data quality with higher confidence and adjust the control limits accordingly.
19.6 Data Transformation
Calculations for transforming raw data from measured units to final concentrations are relatively
straightforward and many are performed in the sampler data processing unit before being
recorded. The following relations in Table 19-5 pertain to Pb monitoring.
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Table 19-5. Raw Data Calculations
Parameter
Filter volume (Va)*
Mass on TSP filter
strip or 46.2 mm filter
TSP full filter mass
TSP Pb concentration
(Cpj)
PMioPb
Concentration (Cpj)
Units
m3
/*g
/*g
//g/m3
//g/m3
Type of Conversion
Calculated from average flow rate (Qave) in
L/min and total elapsed time (t) in min
multiplied by the unit conversion (m3/L)
Calculated from measured concentration
reported by instrument, in ug/L (M), the
volume of sample solution after sample
preparation, in mL (V/), the initial sample
mL (F,=either filter or strip) and the dilution
factor, performed after sample preparation
(D)
Calculated from the filter strip mass (jug)
multiplied by the number of strips (9) in a
TSP filter.
Calculated from the laboratory mass (PbTSp)
data and sampler total volume (Va)
Calculated from the laboratory mass (Pbw)
data and sampler total volume (Va)
Equation
ra=Qm.*tx\0-3
C= MX — x D
Vi
PbTSP = Cx9
Pbrsp
CPb y
r a
Pbw
CPb- y
a
* Federal Reference Method instruments will provide this value.
19.7 Data Transmittal
Data transmittal occurs when data are transferred from one person or location to another or when
data are copied from one form to another. Some examples of data transmittal are copying raw
data from a notebook onto a data entry form for keying into a computer file and electronic
transfer of data over a telephone or computer network. Table 19-6 summarizes data transfer
operations.
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Table 19-6. Data Transfer Operations
Description of Data
Transfer
Field data to AIRQA
Web site
Filter receiving, Chain-
of-Custody Forms, and
Field Data Sheets
Laboratory results to
AIRQA Web site
Audit data to AQS
Originator
Field Scientist
Field Scientist
Laboratory Analyst
Laboratory Analyst
Recipient
AIRQA Web
site
Laboratory
Analyst
AIRQA Web
site
AQS (EPA)
QA Measures Applied
Parity checking; transmission
protocols, check against field data
sheet information
Filter numbers are automatically
verified; reports indicate missing
filters and/or incorrect data entries;
FS checks data entry with 100%
review
Laboratory data is paired with field
data and a validation routine for all
pertinent QC checks is completed
Data transfer is checked by the
technical support contractor for AQS
The Pb-PEP will report all Pb ambient air quality data and information specified by the AQS
Data Coding Manual10 in the required format for AQS. Such air quality data and information
will be fully screened and validated and will be submitted directly to the AQS via electronic
transmission, in the format of AQS, and in accordance with the monthly schedule to the AQS
QA area since final Pb-PEP audit results are posted to the production AQS as data pairs. The
data pair consists of the Pb-PEP audit measured value and the site's measured (primary monitor)
value. SLAMS and NCore sites are required to post their site data to the AQS on the schedule
shown in Table 19-7. Because posting the Pb-PEP data requires first obtaining the site's
measured value from AQS, Pb-PEP data will not be posted to AQS production until after the due
dates in Table 19-7. In cases where the site data have been uploaded to AQS and validated on or
before the due date, the Pb-PEP audit data will also be uploaded.
Table 19-7. Data Reporting Schedule
Reporting Period
January 1 -March 3 1
April 1-June 30
July 1 -September 30
October 1-December 3 1
Due Date
June 30
September 30
December 3 1
March 3 1
'http://www.epa.gov/ttn/airs/airsaqs/manuals/manuals.htm
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19.8 Data Reduction and Data Integrity
Data-reduction processes involve aggregating and summarizing results so that they can be
understood and interpreted in different ways. The Pb monitoring regulations require certain
summary data to be computed and reported regularly to EPA. Examples of data summaries
include the following:
• Average Pb concentration
• Accuracy, bias, and precision statistics based on accumulated FRM/FEM data
• Data completeness reports based on numbers of valid samples collected during a specified
period.
The integrity of Pb-PEP data reduction can be verified by independent review of the data and
algorithms used. Verification of data integrity requires that Pb-PEP data be stored in a manner
that permits any data modification to be detected. Detection of data changes is facilitated by the
record keeping requirements of the Pb-PEP Laboratory SOPs, which require archiving of hard-
copy records for important data (such as analytical batch reports, sample COC forms, and FDSs).
These archived records enable EPA to trace raw data used in PEs to original documents, which
have been dated and signed by program personnel.
In addition, Pb-PEP Laboratory SOPs require that regular copies of the PB-PEP LEVIS data are
archived into read-only media (e.g., CD-ROM or back-up tape) and regularly stored at an off-site
location. These archival database copies may also be used to evaluate data integrity and to check
that data used in a particular PE match the data on hard-copy records.
19.9 Data Analysis
The Pb-PEP is currently implementing the data summary and analysis requirements contained in
40 CFR Part 58, Appendix A. It is anticipated that as the Pb Monitoring Program develops,
additional data analysis procedures may evolve. The following specific summary statistics will
be tracked and reported for the Pb-PEP:
• Single sampler bias or accuracy (based on flow rate performance audits and the collocation
study results)
• Single sampler precision (based on collocated data)
• Network-wide bias and precision (based on collocated data, flow rate performance audits)
• Data completeness.
Equations used for these reports are provided in the Table 19-8.
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Table 19-8. Report Equations
Criterion
Accuracy of single sampler flow - single
check (di) Xi is reference flow; Yi is
measured flow
Bias of a single sampler - annual basis
(Dj)- average of individual percent
differences between sampler and
reference value; nj is the number of
measurements over the period
Percent difference for a single check (di) -
Xi and Yi are concentrations from the
primary and duplicate samplers,
respectively.
Coefficient of variation (CVi) for a single
check
Pooled coefficient of variation, quarterly
basis (CVj,q) - CVi will only be used when
the two measurements are both greater
than 6 ug/m3
Completeness
Equation
Y y
H — ' ' -'i on
' x,
"'i't'-
Y Y
fi — ' ' -I on
(Yi+Xi)/2
<*'=*
cv -\ycv-'
"~V*»M
C'nmnlrfrnr w— valid 1-100
theoreticd
Reference
40 CFR 58, Appendix
A, Section 4. 1.1
40 CFR 58, Appendix
A, Section 4. 1.3
40 CFR 58, Appendix
A, Section 4. 2.1
Not referenced in
CFR
40 CFR 58, Appendix
A, Section 4. 3.2.1
Not referenced in
CFR
19.10 Data Flagging -Sample Qualifiers
A sample qualifier or a result qualifier consists of alphanumeric characters which indicate both
the fact and the reason why the data value:
• did not produce a numeric result,
• produced a valid numeric result, but it is qualified in some respect relating to the type or
validity of the result, or
• produced an invalid numeric result that is not to be reported outside the laboratory.
Qualifiers will be used in the field and the laboratory to signify data that may be suspect due to
contamination, special events, or failure of QC limits. Appendix C contains a complete list of
the data qualifiers for the field and laboratory activities. Qualifiers will be placed on field and
laboratory data forms with additional explanations in free-form notes areas. Flags may be
generated when sample batch information is entered into the Pb-LEVIS and the validation process
is run. During the sample validation process, which is discussed in Element 23.0, Validation and
Verification Methods, the flags will be used to decide on validating or invalidating individual
samples or batches of data.
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19.11 Data Tracking
The Pb-PEP LIMS contains the input functions and reports necessary to track and account for the
whereabouts of filters and the status of data processing operations for specific data. Information
about filter location is updated on distributed data entry terminals at the points of significant
operations. The following input data are used to track filter location and status:
• Laboratory package receipt (package is opened and filter IDs are logged in)
• Laboratory filter storage/archive (post-analysis)
• Laboratory data reporting (to AQS QA)
Tracking reports may be generated by any personnel with access to the PB-PEP LIMS. The
following tracking reports are available:
• List of all filters that have been received but have not been analyzed
• List of all filters analyzed
• List of all filters in the filter archive
• Ad hoc reports (as required by program)
The Pb-PEP Laboratory Manager or designee is responsible for tracking filter status at least once
a month and following up on anomalies such as excessive holding time in the laboratory before
reweighing.
19.12 Data Storage and Retrieval
Table 19-9 shows archival policies for the Pb data.
Table 19-9. Data Archive Policies
Data Type
Chain-of-Custody Forms
Field Data Sheets
Laboratory notebooks
Field notebooks
PB-PEP LIMS
(excluding audit trail
records)
PB-PEP LIMS audit trail
records
Medium
Hard copy
Hard copy
Hard copy
Electronic
(online)
Electronic
(back-up
tapes)
Location
Laboratory
Laboratory
Air Quality
Division
Air Quality
Division
Air Quality
Division
Retention Time
4 years
4 years
4 years
Indefinite
4 years
Final Disposition
Discarded, with
permission from OAQPS
N/A
Discarded, with
permission from OAQPS
Back-up media retained
indefinitely
Discarded, with
permission from OAQPS
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Filters
Filters
Laboratory
4 years at ambient
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Discarded, with
permission from OAQPS
The Pb data reside on a Microsoft® Windows-compatible computer in the Pb-PEP weighing
laboratory. The security of data in the Pb-PEP LIMS is ensured by using the following controls:
• Network security passwords for access to the project and database files
• Regular password changes (as specified by EPA network security)
• Independent password protection on all dial-in lines
• Logging of all incoming communication sessions, including the originating telephone
number, the user's ID, and connect times
• Storage of media, including back-up tapes in locked, restricted access areas.
19.13 Information Management Security
The Pb-PEP LIMS is maintained on the EPA OAQPS QA support contractor's server, and access
is restricted to authorized personnel. Data can only be released with the express permission of
the National Pb-PEP Project Leader. PE results should not be released for events that have not
been posted by the PQAO to AQS. Only validated, approved data are loaded into AQS, where
the information becomes public domain. In addition, hard copies of all weighing logs and
routine back-up copies of the Pb-PEP LIMS are archived. Comparison of the archived Pb-PEP
LIMS copies with current Pb-PEP LIMS permits the detection of unauthorized or altered entries
in the current Pb-PEP LIMS.
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20.0 Assessments and Response Actions
For the purposes of this QAPP, an assessment is defined as an evaluation process used to
measure the performance or effectiveness of the quality system and various measurement phases
of the data operation.
The results of assessments indicate whether the QC efforts are adequate or need to be improved.
Documentation of all QA and QC efforts implemented during the data collection, analysis, and
reporting phases are important to data users and decision makers who can then consider the
impact of these control efforts on the data quality (see Element 21.0, Reports to Management).
Both qualitative and quantitative assessments of the effectiveness of these control efforts will
identify those areas most likely to impact the data quality. Periodic assessments of Pb-PEP data
quality are required to be reported to EPA. However, the selection and extent of the QA and QC
activities used by the Pb-PEP depend on a number of local factors, such as the field and
laboratory conditions, the objectives for monitoring, the level of the data quality needed, the
expertise of assigned personnel, the cost of control procedures, and pollutant concentration
levels.
To ensure the adequate performance of the quality system, the Pb-PEP will perform the
following assessments:
- TSAs
• Audits of data quality (ADQs)
• Data quality assessments (DQAs)
• Peer review.
20.1 Assessment Activities and Project Planning
20.1.1 Technical Systems Assessment
A TSA is an evaluation of a data collection operation or organization to establish whether the
policies, practices, and procedures are adequate for ensuring that the type and quality of data
needed are obtained. TSAs are performed both for EPA Regions and monitoring organizations
that implement Pb-PEP activities. The Pb-PEP regional TSAs allow OAQPS to assess
consistency of operation among the Regions and to improve the quality system. TSAs will be
performed for field and laboratory activities.
TSAs of the Pb-PEP laboratories and data management operations will be conducted by EPA
(OAQPS, ORIA or a Region independent of Region 9) every two years and TSAs of the field
operations will be conducted by the Regional WAM/TOPO/ DOPOs annually. This will include
any monitoring organization-run Pb-PEP. It is possible that OAQPS would team with the
Region during the TSAs of monitoring organization-run Pb-PEPs. TSAs may be conducted as a
part of recertifying FSs, where appropriate.
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The TSA can be accomplished by a team or by an individual assessor. Key personnel to be
interviewed during the assessment are those who have responsibilities for planning, conducting
field operations, laboratory operations, QA/QC, data management, and reporting. The TSA will
review the following three activities:
• Field. Filter receipt, instrument setup, sampling, QA/QC, shipping and record keeping
• Laboratory. Sample receipt, sample preparation, analysis, archiving, QA/QC and record
keeping.
• Data management. Information collection, flagging, data review, security, and upload.
The assessment activities are illustrated in Figure 20-1. To increase uniformity of the TSA, an
assessment form will be used which can be found on the AIRQA website and the AMTIC Web
site.
Figure 20-1. Audit Activities
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idit Team Interview of Reporting Organization Director
—
Audit Group 1
Interview with Key Personnel
Interview Laboratory Manager |
I Visit Laboratory, Witness Operations [
Review Sample Receiving and Custody
]
Select Portion of Data, Initiate Audit Trail
Establish Data Audit Trail Through
Laboratory Operations to Data
A/TanaoF-mF-nt Tn'mnftinn
Meet to
Discuss
Findings
Interview Field
Vi:
Visit Audit and
Select Portion of I
Establish'
Oneration
Finalize Audit Trails and Complete Data Audit
Prepare Audit Result Summary of:
(a) Overall operations (b) data audit findings
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TSAs will usually focus on either the field or lab component but rarely both (with the exception
of Region 9). The TSA team will prepare a comprehensive written summary of findings
organized into the following areas: planning, field operations, laboratory operations, QA/QC,
data management, and reporting. Problems with specific areas will be discussed, and an attempt
will be made to rank them in order of their potential impact on data quality. For the more serious
of these problems, the TSA team will summarize assessment findings on the Assessment Finding
Form (Figure 20-2).
Figure 20-2. Assessment Finding Form
Assessment Finding
Assessment Title: Assessment #:
Finding #:
Finding:
Discussion:
QA Lead Signature: Date:
Assessed Agencies
Signature: Date:
By design, an Assessment Finding Form will be completed for each major deficiency that
requires formal corrective action. This form will include information such as the finding impact,
estimated time period of deficiency, site(s) affected, and reason for action. The Assessment
Finding Form will notify the laboratory or field office of serious problems that may compromise
the quality of the data and therefore require specific corrective actions. These forms are initiated
by the TSA team and discussed at the debriefing. If the assessed group is in agreement with the
finding, the form is signed by the ESAT organization during the debriefing. If a disagreement
occurs, the TSA team will record the opinions of the group assessed and set a time at some later
date to address the finding at issue. Assessment finding forms are filed under the AFC heading
"Pb-PEP/108-025-01-01-237.1" (see Element 9.0, Documentation and Records).
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20.1.1.1 Post-Assessment Activities
The major post-assessment activity is the preparation of the assessment report. The report will
include the following:
• Assessment title, number, and any other identifying information
• Assessment team leaders, assessment team participants, and assessed participants
• Background information about the project, purpose of the assessment, dates of the
assessment, particular measurement phase or parameters that were assessed, and a brief
description of the assessment process
• Summary and conclusions of the assessment and corrective action required
• Attachments or appendices that include all assessment evaluations and assessment finding
forms.
To prepare the report, the TSA team will meet and compare observations with collected
documents and results of interviews and discussions with key personnel. Expected QAPP
implementation is compared with observed accomplishments and deficiencies, and the
assessment findings are reviewed in detail. Within 30 calendar days of the completion of the
assessment, a draft assessment report will be prepared and submitted. The TSA report will be
submitted to the appropriate ESAT personnel and appropriately filed under the AFC heading
"Pb-PEP/108-025-01-01-237.1."
If the ESAT organization has written comments or questions about the TSA report, the TSA
team will review and incorporate them as appropriate and prepare and resubmit a report in final
form within 30 days of receiving the written comments. The report will include an agreed-upon
schedule for corrective action implementation.
20.1.2.2 Follow-up and Corrective Action Requirements
The Regional office and ESAT may work together to solve required corrective actions. As part
of corrective action and follow-up, an Assessment Finding Response Form (Figure 20-3) will be
generated by the assessed organization for each Assessment Finding Form submitted by the TSA
team. In addition, ESAT will include corrective action in its monthly progress reports. The
Assessment Finding Response Form will be signed by the assessed organization and will be sent
to the ESAT WAM/TOPO/DOPO, who reviews and accepts the corrective action. The
Assessment Finding Response Form will be completed by the assessed organization within 30
days of acceptance of the assessment report. Assessment Finding Response Forms are filed
under the AFC heading "Pb-PEP/108-025-01-01-237.1."
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Figure 20-3. Assessment Finding Response Form
Assessment Finding Response Form
Assessed Division:
Assessment Title: _
Finding #:
Assessment #:
Finding:
Cause of the problem:
Actions taken or planned for correction:
Responsibilities and timetable for the above actions:
Prepared by:
Signed by:
QA Division
Reviewed by:
Date: _
. Date:.
Date:
Remarks:
Is this assessment finding closed?
When?
File with official assessment records. Send copy to assessed organization.
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20.1.2 Audit of Data Quality
An ADQ reveals how the data are handled, what judgments were made, and whether uncorrected
mistakes were made. ADQs can often identify the means to correct systematic data reduction
errors. An ADQ will be performed annually by OAQPS as part of the TSA. Thus, sufficient
time and effort will be devoted to this activity so that the auditor or TSA team has a clear
understanding and complete documentation of data flow. Pertinent ADQ questions will appear
on the TSA check sheets to ensure that the data collected at each stage maintains its integrity.
The ADQ will serve as an effective framework for organizing the extensive amount of
information gathered during the audit of laboratory, field monitoring, and support functions
within the agency. The ADQ will have the same reporting/corrective action requirements as the
TSA.
20.1.3 Data Quality Assessments
A DQA is a statistical analysis of environmental data used to determine whether the quality of
data is adequate to support a decision based on the DQOs. Data are appropriate if the level of
uncertainty is acceptable for the decision based on the data. The DQA process is described in
detail in Guidance for the Data Quality Assessment Process (EPA QA/G-9) and is summarized
below.
• Review the DQOs and sampling design of the program. Review the DQOs and define
statistical hypothesis, tolerance limits, and/or confidence intervals
• Conduct preliminary data review. Review precision and accuracy (P&A) and other
available QA reports. Calculate summary statistics, plots, and graphs. Look for patterns,
relationships, and anomalies
• Select the statistical test. Select the best test for analysis based on the preliminary review
and identify underlying assumptions about the data for that test
• Verify test assumptions. Decide whether the underlying assumptions made by the selected
test hold true for the data and the consequences
• Perform the statistical test. Perform test and document inferences and evaluate the
performance for future use.
A DQA will be included in the Pb-PEP Annual QA Report. Details of these reports are discussed
in Element 21.0, Reports to Management.
Measurement uncertainty will be estimated. Terminology associated with measurement
uncertainty is found within 40 CFR Part 58 Appendix A and includes the following:
• Precision. A measurement of mutual agreement among individual measurements of the
same property usually under prescribed similar conditions, expressed generally in terms of
the standard deviation.
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• Accuracy. The degree of agreement between an observed value and an accepted reference
value; accuracy includes a combination of random error (precision) and systematic error
(bias) components, which are due to sampling and analytical operations
• Bias. The systematic or persistent distortion of a measurement process, which causes errors
in one direction; individual results of these tests for each method or analyzer shall be
reported to EPA.
Estimates of the data quality will be calculated on the basis of single monitors, PQAOs, regions,
laboratory and will be aggregated to all monitors.
20.1.4 Peer Review
Peer review is a documented critical review of work products. These reviews are conducted by
qualified individuals who are independent of those performing the work but are collectively
equivalent in technical expertise. OAQPS uses the peer-review process to assess its products and
guidance. Any guidance documents or reports developed during the implementation of this
program will be reviewed by EPA's QA Strategy Workgroup (facilitated by AAMG), which will
serve as a peer reviewer. OAQPS will document comments and responses received as part of the
peer-review process.
20.2 Documentation of Assessments
Table 20-1 summarizes each of the assessments discussed above.
Table 20-1. Assessment Summary
Assessment
Activity
TSAs
ADQs
DQAs
Frequency
1/yr
1/yr
1/yr
Personnel Responsible
OAQPS and Regional
Work Assignment
Manager/Task Order
Project Officer/ Delivery
Order Project Officer
(WAM/TOPO/DOPO
OAQPS (National Pb-PEP
Project Leader)
OAQPS and U.S.
Environmental Protection
Agency (EPA) Regions
Report
Completion
30 days after the
activity
30 days after the
activity
120 days after
the end of
calendar year
Resolution
Environmental Services
Assistance Team (ESAT) or
State, local, and Tribal
(monitoring organization)
WAM/TOPO/DOPOs
EPA Regions and
monitoring organization
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21.0 Reports to Management
This element describes the quality-related reports and communications to management necessary
to support the Pb-PEP.
Effective communication among all personnel is an integral part of a quality system. Regular,
planned quality reporting provides a means for tracking the following:
• Adherence to scheduled delivery of equipment, data, and reports
• Documentation of deviations from approved QA and SOPs and the impact of these
deviations on data quality
• Analysis of the potential uncertainties in decisions based on the data.
21.1 Communication
An organized communications framework facilitates the flow of information among the
participating organizations and other users of the information produced by the Pb network.
Figure 21-1 represents the principal communication pathways.
OAQPS
Support
Contractor
nAr
1 *• (QAWo
i
i
5PS
rkgroup)
State/local/ „ „ Region
Tribal
ESAT WAM/TOPO/DOPO
4 I
ESAT
Contracts Office
A
V
. Region
' ESAT PO
Technical —*•
Contractual >•
Figure 21-1. Lines of communication.
In general, ESAT contractors will be responsible for informing the Pb-PEP Laboratory Manager,
the ESAT WAM/TOPO/DOPO, and the POs about technical progress, issues, and contractual
obligations. On the technical side, the ESAT WAM/TOPO/DOPO(s) will be responsible for
communicating with monitoring organizations and for informing OAQPS about issues that
require technical attention. Contractual issues will be conveyed from the ESAT contractor
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through POs to the ESAT Contracts Office and, if necessary, to OAQPS. Table 21-1 lists key
EPA ESAT contacts.
The ESAT contractors will frequently communicate with the Pb-PEP Laboratory Manager and
the ESAT WAM/TOPO/DOPO on the progress of their activities and any problems/issues
associated with them. Resolution of these issues should take place in the Regions unless the
issue could affect the implementation of the Pb-PEP at a national level. In those cases, it can be
discussed and resolved through the ESAT Workgroup conference call.
Communications among various participants in the Pb-PEP will be critical to the success of the
program. The field and laboratory SOPs contain procedures for required communication and for
documenting this information.
Table 21-1. Communications Summary
Person
Performance Evaluation Program (Pb-
PEP) Laboratory Manager
Environmental Services Assistance
Team (ESAT) Work Assignment
Manager/Task Order Project
Officer/Delivery Order Project Officer
(WAM/TOPO/DOPO)
LA (ESAT or OAQPS Contractor)
FS
OAQPS or approved contractor
Communicates to
Office of Air Quality
Planning and Standards
(OAQPS)
Regional Project Officer
Laboratory Analyst (LA)
Field Scientist (FS)
OAQPS
Regional PO
Pb-PEP Laboratory Manager
and Laboratory ESAT
WAM/TOPO/DOPO
FS
OAQPS or approved
contractors)
LA
Pb-PEP Laboratory Manager
Communication Function
Funding and resource needs
National contract performance issues
Contract performance issues
Review of deliverables
Review of data
Corrective action
Schedule changes
Audit site selection and scheduling
Funding and resource needs
Contract performance issues
Laboratory progress
Problems and issues
Scheduling
Field equipment shipment
Filter shipment receipt from field
Field procedure issues
Database management and Air Quality
System (AQS) uploads
Filter shipment from field
Electronic mailing of field data
Filter/equipment requests
Schedule changes
Field data verification
Requests for Pb-PEP data
Data transfer to the AQS database
Data quality issues
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Person
National Pb-PEP Project Leader
Communicates to
ESAT WAM/TOPO/DOPO
Communication Function
Funding and resource needs
Contract performance issues
21.1.1 Field Communication
Field communications can take place by phone or by e-mail. Important phone messages or
conversations should be recorded using the Phone Communication Form (COM-1) in the field
communications notebook; however, it is understood that the FS may not be in a position where
this is feasible or the conversation is not noteworthy. Using the COM-1 form is most appropriate
in situations where important information is exchanged, problems are communicated, issues are
resolved or other activities that may support information reported in the monthly report. It is
highly encouraged notes will include the following:
• Date
• Time
• Personnel involved
• Issue(s)
• Decision(s)
• Follow-up action(s)
• Follow-up action responsibility
• Follow-up action completed by (date).
If follow-up action is required by the FS, these actions will be included in the monthly progress
reports (see Section 9.0, Documentation and Records, Section 9.2.2, Field Monthly Report). At
a minimum, the FS will keep the original hardcopy in the field communications notebook. The
FS may also choose to keep an electronic record of this information on a PC.
Field communication between the FS and the Regional WAM/TOPO/DOPO may be required.
Cellular phones have been provided to each FS for calls related to Pb-PEP activities. The
Regional WAM/TOPO/DOPOs should also identify alternates to receive field communications
when he or she is not in the office.
21.1.1.1 Equipment Shipment Receipt
Upon request, the laboratory will ship filter media and cassettes to the field offices. On the day
of receipt, the FS will contact the LA and will provide the following information to verify
receipt:
Date of shipment
Number of boxes in shipment
Tracking number.
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21.1.1.2 Pb-PEP Conference Calls
The FS may be asked to participate in Pb-PEP conference calls to discuss progress or resolution
of issues. The ESAT WAM/TOPO/DOPO will inform the FS of information that needs to be
prepared for the call at least 3 days before the call if possible. During the call, the FS may use
the Phone Communication Form (COM-1) to record issues and action items that pertain to his or
her activities. These items will be included in the next monthly progress report.
21.1.1.3 Communicating with Monitoring Organizations and Site Operators
Dates for the Pb-PEP audits should be coordinated with the site's normal operating schedule.
This coordination must be completed in advance so that the FS and the site operator have ample
advanced notice and time to prepare for the audit. The procedure for such communications
includes the following:
• The Regional WAM/TOPO/DOPO (or FS, as delegated by the Regional
WAM/TOPO/DOPO) will contact each site operator before the audit. Contact must be made
by phone if it is within 30 days of the audit, but e-mail is sufficient otherwise.
• About 1 week before the actual evaluation, the FS will call the site operator to confirm that
the audit remains on schedule and to confirm meeting arrangements.
21.1.2 Laboratory Communications
Laboratory personnel will use the Phone Communications Form (COM-1) in the same manner as
theFS, as described in Section 21.1.1.
21.1.2.1 Equipment Shipment
Once a month or as needed, the laboratory will ship filter media and cassettes to the Regional
offices via EPA's contract carrier. On the day of shipment, the LA will communicate with the
field contact and will provide the following information by e-mail:
• Date of shipment
• Number of boxes in shipment
• Tracking number.
21.2 Reports
The following section will discuss the various types of reports that will be generated in the Pb-
PEP. Table 21-3 provides a summary of this information.
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21.2.1 Progress Reports
Field Progress Reports
The FS will provide a written progress report to his or her Regional WAM/TOPO/DOPO at the
end of each month (Pb-PEPF-2). The deadline is the 15th calendar day of the following month,
unless otherwise specified by the Regional WAM/TOPO/DOPO. The Progress Report Form
(COM-2) will be used to convey the following information:
• Reporting date. Beginning and end date that is covered in the report
• Reporter. Person writing the reports
• Progress. Progress on field activities, including evaluations scheduled within reporting date
and evaluations conducted within reporting date
• Issues. Old issues reported in earlier reports that have not been resolved and new issues
arising within the reporting date
• Actions. Action necessary to resolve issues, the person(s) responsible for resolving them, and
the anticipated dates when they will be resolved.
Laboratory Progress Report
The LA will provide a written progress report to the Pb-PEP Laboratory Manager and the ESAT
WAM/TOPO/DOPO at the end of each month (Pb-PEPF-2). The deadline is the 15th calendar
day of the following month, unless otherwise specified by the Regional WAM/TOPO/DOPO.
Progress Report Form (COM-2) will be used to convey the following information:
• Reporting date. Beginning and end dates covered in the report
• Reporter. Person writing the reports
• Progress. Progress on field activities
- Receipt - Total number of filters received within a reporting date
- Analysis- Filters analyzed within a reporting date
- Data Submission - Valid data submitted to AQS
- Shipments- Shipments made to each Region within a reporting date
• Issues.
- Old issues. Issues reported in earlier reports that have not been resolved
- New issues. Issues arising within a reporting date
• Actions. Action necessary to resolve issues, including the person(s) responsible for resolving
them and the anticipated dates when they will be resolved.
The LA will maintain a complete record of the weekly progress reports in a three-ring binder.
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21.2.2 QA Reports
Various QA reports will be developed to document the quality of data for the Pb-PEP. For more
information about reporting time lines, please see Element 6.0, Project/Task Description, Section
6.4.6. The types of reports include the following:
DQA. This assessment is a scientific and statistical evaluation to determine if data are of the
right type, quality, and quantity to support their intended use. The Pb-PEP QA/QC data can be
statistically assessed at various levels of aggregation to determine its quality. Element 24.0,
Reconciliation with Data Quality Objectives, discusses the statistics to be used to evaluate the
data in relation to the DQOs. DQAs will primarily be the responsibility of the EPA Regions
(Regional assessments) and OAQPS (national assessments). A DQA will be performed
annually.
P&A Reports. These reports will be generated quarterly and annually and will evaluate the
precision, accuracy, and bias data against the acceptance criteria using the statistics documented
in 40 CFR Part 58. These reports will be generated through AQS and will be the responsibility of
OAQPS.
Assessment Reports. TSAs will be on file at the EPA Regional offices and OAQPS.
National QA Reports. A QA report provides an evaluation of QA/QC data for a given time
period to determine whether the DQOs were met. QA reports will be more evaluative in nature
than the P&A reports in that they will combine the various assessments and the QA data to report
on the overall quality system. OAQPS will generate Annual QA Summary Reports and 3-year
QA Reports on the Pb-PEP and its resultant data quality.
The Annual QA Summary Reports will include the following:
• Program overview and update
• Quality objectives for measurement data
• Implementation aspects
- Training and certifications
- Laboratory QA requirements (QC checks, TSAs, and data validation)
- Field QA requirements (QC checks, standards certifications, and TSAs)
• DQAs
- Laboratory and field controls
- Precision (based on collocated data)
- Accuracy and bias (based on collocated data, flow rate performance audits)
- Completeness (Pb-PEP results versus FRM/FEM results)
• Summary
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The 3-year QA Report is a composite of the annual reports, but with a more narrative
interpretation and evaluation of longer term trends with respect to Pb-PEP sampler and
operational performance.
21.2.3 Response/Corrective Action Reports
During TSAs, the response/corrective action reporting procedure will be followed whenever
there is a finding in which OAQPS and/or the Region determines may affect data quality. The
reporting procedure is designed as a closed-loop system. The Response/Corrective Action
Report Form identifies the originator (who reported and identified the problem), states the
problem, and may suggest a solution. The form also indicates the name of the person(s) assigned
to correct the problem. The assignment of personnel to address the problem and the schedule for
completion will be filled in by the appropriate supervisor. The reporting procedure closes the
loop by requiring that the recipient state on the form how the problem was resolved and the
effectiveness of the solution. Copies of the completed Response/Corrective Action Report Form
will be distributed twice: first when the problem has been identified and the action has been
scheduled; and second when the correction has been completed. The originator, the Regional
WAM/TOPO/DOPO, and the National Pb-PEP Project Leader will be included in both
distributions.
21.2.4 Control Charts with Summary
Control charts for field and laboratory instruments will be updated after every new calibration or
standardization as defined in the relevant Field and Laboratory SOPs. FSs and LAs are
responsible for reviewing each control chart immediately after it is updated and for taking
corrective actions whenever an out-of-control condition is observed. Control charts are to be
reviewed at least quarterly by the Pb-PEP Laboratory Manager (laboratory instruments) and the
ESAT WAM/TOPO/DOPO. Control charts are also subject to inspection during TSAs, and
laboratory personnel are responsible for maintaining a readily accessible file of control charts for
each instrument. Due to the relatively small number of audits completed, the frequencies may
need to be decreased for statistical significance. Minimally, the QC checks should in Table 21-2
should be control charted:
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Table 21-2. Control Charting Recommendations
Activity
Field Operations
Laboratory Analysis - ICP-MS
Laboratory Analysis - XRF
Quality Control Parameter
Average sampler flow rate for a
sampling run
Sampler flow rate verification
Sampler temperature verification
Sampler barometric pressure
verification
Collocation study results
Field and trip blank data
Initial calibration blank
Initial calibration verification
Lower level calibration verification
Continuing calibration blank
Continuing calibration verification
Thin film calibration
Digital signal processor calibration
(DSP)
Quality control filters
Frequency"
Quarterly
Quarterly
Quarterly
Quarterly
After each collocation
Quarterly
Monthly
Monthly
Monthly
Monthly
Monthly
Annually if necessary
Monthly
Monthly
a - Due to the relatively small number of audits completed, the frequencies may need to be decreased for statistical significance.
21.2.5 Data Reporting
The data reporting requirements of 40 CFR Part 58.35 apply to those stations designated as
SLAMS or NCore. Required accuracy and precision data are to be reported, at a minimum, on
the same schedule as quarterly routine monitoring data submittals; however, it is anticipated that
data will be reported to AQS no later than -45 days of receiving the filter from the field. The
required reporting periods and due dates for SLAMS and NCore sites are listed in Table 19-7.
Pb-PEP audit results are posted to AQS as paired data. The data pair comprises the Pb-PEP audit
measurement and the site sampler's routine measurement. The site measurement value is taken
from the site's posted AQS data for the date of the audit at the primary sampler. Because both
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measured values are needed to report Pb-PEP audits to the AQS, the Pb-PEP audit results will
not be available until the routine data is submitted.
In cases where the Pb-PEP audit results are available, but the routine measurements are not
available before the deadlines in Table 19-7, the Pb-PEP audit results will not be posted until the
next quarter's posting. For example, for a routine sample collected on March 31 and posted by
the state on or before June 30, the associated Pb-PEP audit results should be posted to AQS by
approximately July 31. If the same routine sample's result were not available in the AQS until
September 1, the Pb-PEP audit results would not be posted until approximately January 31.
Air quality data submitted for each reporting period will be edited, validated, and entered into the
AQS using the procedures described in the AQS User Guide and the AQS Data Coding
Manual11.
Table 21-3. Report Summary
Report Type
Field progress
Laboratory progress
Data Quality Assessment
(DQA)
Pb-PEP audit results
Pb-PEP precision and
accuracy (P&A)
(collocation study results)
TSAof monitoring
organization or ESAT Pb-
PEP
QA Report
OAQPS systems audit
Response/corrective action
Frequency
Monthly
Monthly
1/yr
Quarterly
2/yr
1/yr
1/3 years
1/yr
I/finding
Reporting Organization
Environmental Services
Assistance Team (ESAT)
contractor
ESAT contractor
Office of Air Quality Planning
and Standards (OAQPS) and
U.S. Environmental Protection
Agency (EPA) Regions
OAQPS and authorized
contractor
National Pb-PEP Project Leader
EPA Region
OAQPS and authorized
contractor
OAQPS
ESAT contractor
Distribution
Regional Work Assignment
Manager/Task Order Project
Officer/Delivery Order Project
Officer (WAM/TOPO/DOPO)
Performance Evaluation Program
(Pb-PEP) Laboratory Manager,
ESAT WAM/TOPO/DOPO
ESAT contractor, Regional
WAM/TOPO/DOPO, Ambient
Monitoring Technology
Information Center (AMTIC)
Air Quality System
Field Scientist, Regional
WAM/TOPO/DOPO, AMTIC
ESAT contractor, assessed
agency, National Pb-PEP Project
Leader
Internal/external organizations
through AMTIC
ESAT contractor, Regional
WAM/TOPO/DOPO
ESAT contractor, Regional
WAM/TOPO/DOPO, National
Pb-PEP Project Leader
11 http://www.epa.gov/ttn/airs/airsaqs/manuals/
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22.0 Data Review, Validation, and Verification Requirements
This element describes how the Pb-PEP will verify and validate the data collection operations
associated with the program. "Verification" can be defined as confirmation by examination and
provision of objective evidence that specified requirements have been fulfilled. "Validation" can
be defined as confirmation by examination and provision of objective evidence that the particular
requirements for a specific intended use are fulfilled. The major objective for the Pb-PEP is to
provide data of adequate quality to use in the comparison to routine data. This section will
describe the verification and validation activities that occur during a number of the important
data collection phases. Earlier elements of this QAPP and the Pb-PEP Field and Laboratory
SOPs describe how the activities in these data collection phases will be implemented to meet the
DQOs of the program. Review and approval of this QAPP provide initial agreement that the
processes described in the QAPP, if implemented, will provide data of adequate quality. To
verify and validate the phases of the data collection operation, the Pb-PEP will use various
qualitative assessments (e.g., technical systems assessments, network reviews) to verify that the
QAPP is being followed and will rely on the various QC samples, inserted at various phases of
the data collection operation, to validate that the data will meet the DQOs described in Element
7.0, Data Quality Objectives and Criteria for Measurement.
22.1 Sampling Design
Element 10.0, Sampling Design, describes the sampling design for the network established by the
Pb-PEP. It covers the number of PEs required for each PQAO, as well as the frequency of data
collection. These requirements have been described in the CFR; however, it is the responsibility
of Pb-PEP to ensure that the intent of the regulations are properly administered and performed.
22.1.1 Sampling Design Verification
Monitoring organizations will work with the EPA Regions to select and develop a list of sites for
the evaluations conducted in each calendar year on or before December 1 of the previous year.
The Regional WAM/TOPO/DOPOs, with the assistance of the ESAT contractors, will attempt to
determine the most efficient site visit schedule. This schedule should be based upon the
following:
• CFR requirements for audit frequency as discussed in Element 10.0, Sampling Design
• Meeting the same monitoring schedule as the routine sampler being evaluated (to prevent the
need for the site to run and post an additional sample for the evaluation)
• Site proximity (the sites that are closest in proximity to each other can be visited within the
same day or week).
The Pb-PEP implementation plan can then be reviewed and compared to the AQS data of active
SLAMS/Tribal and NCore sites aggregated by PQAO. This can ensure that the Pb-PEP design is
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being followed. The implementation plan will also be reviewed during OAQPS and Regional
TSAs.
22.2 Sample Collection Procedures
22.2.1 Sample Collection Verification
Sample collection procedures are described in Element 11.0, Sampling Methods Requirements,
and in detail in the Pb-PEP Field SOPs to ensure proper sampling and to maintain sample
integrity. The following processes will be used to verify the sampling collection activities:
• TSAs. Will be required by OAQPS and by the EPA Regions annually, as described in
Element 20.0, Assessments and Response Actions
• Surveillance. Will be conducted as required by the EPA Regions and will be used for
frequent monitoring of specific data collection phases if deemed necessary.
Both types of assessments will be used to verify that the sample collection activities are being
performed as described in this QAPP and in the field and laboratory SOPs. Deviations from the
sample collection activity will be noted in Assessment Finding Forms and will be corrected using
the procedures described in Element 20.0, Assessments and Response Actions.
22.2.2 Sample Collection Validation
The sample collection activity is just one phase of the measurement process. Using QC samples
throughout the measurement process can help validate the activities occurring at each phase.
The review of QC data (e.g., collocated sampling data, field/laboratory/trip blanks, and
sampling/ laboratory equipment verification checks) that are described in Element 14.0, Quality
Control Requirements, and Element 16.0, Instrument Calibration and Frequency, can be used to
validate the data collection activities. Any data that indicate unacceptable levels of bias or
precision or a tendency (trend on a control chart) will be flagged and investigated. This
investigation could lead to a discovery of inappropriate sampling activities.
22.3 Sample Handling
Element 11.0, Sampling Methods Requirements, and Element 12.0, Sample Handling and
Custody, detail the requirements for sampling handling; however, greater detail for both field and
laboratory sample handling procedures occur in the Field and Laboratory SOPs, including the
types of sample containers and the preservation methods used to ensure that they are appropriate
to the nature of the sample and the type of data generated from the sample. There are unique
handling concerns with both types of filters and the nature of the collected particles; therefore,
sample handling is one of the phases where inappropriate techniques can have a significant effect
on sample integrity and data quality.
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22.3.1 Verification of Sample Handling
As mentioned in the above section, TSAs and surveillance will be performed to ensure that the
specifications mentioned in the QAPP and SOPs are being followed. The assessments would
include checks on the identity of the sample (e.g., proper labeling and COC records), packaging
in the field, and proper storage conditions (e.g., COC and storage records) to ensure that the
sample continues to be representative of its native environment as it moves through the data
collection operation.
22.3.2 Validation of Sample Handling
Similar to the validation of sampling activities, the review of data from the collocated sampling
and field, trip, and laboratory blanks (described in Element 14.0, Quality Control Requirements,
and Element 16.0, Instrument Calibration and Frequency) and the use of control charts can be
used to validate the sample handling activities. Acceptable precision and bias in these samples
would lead one to believe that the sample handling activities are adequate. Any data that
indicates unacceptable levels of bias or precision or a tendency (trend on a control chart) will be
flagged and investigated. This investigation could lead to a discovery of inappropriate sampling
handling activities that would require corrective action.
22.4 Analytical Procedures
Element 13.0, Analytical Methods Requirements, details the requirements for the analytical
methods, while referent to the specific extraction and analysis SOPs. The methods include
acceptance criteria (Element 13.0, Analytical Methods Requirements, and Element 14.0, Quality
Control Requirements) for important components of the procedures, along with suitable codes
for characterizing and flagging a sample's deviation from the procedure.
22.4.1 Verification of Analytical Procedures
As mentioned in the above sections, both TSAs and surveillance will be performed to ensure that
the analytical method specifications mentioned in the QAPP and SOPs are being followed. The
assessments will include checks on the identity of the sample. Deviations from the analytical
procedures will be noted in Assessment Finding Forms and will be corrected using the
procedures described in Element 20.0, Assessments and Response Actions.
22.4.2 Validation of Analytical Procedures
Similar to the validation of sampling activities, the following can be used to validate the
analytical procedures: reviewing data from laboratory blanks, calibration checks, laboratory
duplicates, and other laboratory QC activities described in Element 14.0 (Quality Control
Requirements), Element 16.0 (Instrument Calibration and Frequency), and in the Pb-PEP
Laboratory SOPs. Acceptable precision and bias in these samples would lead one to believe that
the analytical procedures are adequate. Any data that indicate unacceptable levels of bias or
precision or a tendency (trend on a control chart) will be flagged and investigated as described in
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Element 14.0, Quality Control Requirements. This investigation could lead to a discovery of
inappropriate analytical procedures, requiring corrective action.
22.5 Quality Control
Element 14.0, Quality Control Requirements, and Element 16.0, Instrument Calibration and
Frequency of this QAPP specify the QC checks that are to be performed during sample
collection, handling, and analysis. These include analyses of check standards, blanks, and
duplicates, which indicate the quality of data being produced by specified components of the
measurement process. For each specified QC check, the procedure, acceptance criteria, and
corrective action are specified in field and laboratory SOPs.
22.5.1 Verification of Quality Control Procedures
As mentioned in the above sections, TSAs and surveillance will be performed to ensure that the
QC method specifications mentioned in the QAPP are being followed.
22.5.2 Validation of Quality Control Procedures
Validation activities of many of the other data collection phases mentioned in this subsection use
the QC data to validate the proper and adequate implementation of that phase. Therefore,
validation of QC procedures will require a review of the documentation of the corrective actions
that were taken when QC samples failed to meet the acceptance criteria and a review of the
potential effect of the corrective actions on the validity of the routine data. Element 14.0,
Quality Control Requirements, describes the techniques used to document QC review/corrective
action activities.
22.6 Calibration
Element 16.0, Instrument Calibration and Frequency, as well as the field (Element 11.0,
Sampling Methods Requirements) and the analytical (Element 13.0, Analytical Methods
Requirements) sections of this QAPP detail the calibration activities and requirements for the
critical pieces of equipment for the Pb-PEP. The Pb-PEP Field SOPs and the Pb-PEP Laboratory
SOPs provide detailed calibration techniques.
22.6.1 Verification of Calibration Procedures
As mentioned in the above sections, TSAs and surveillance will be performed to ensure the
calibration specifications and corrective actions mentioned in the QAPP are being followed.
Deviations from the calibration procedures will be noted in Assessment Finding Forms and will
be corrected using the procedures described in Element 20.0, Assessments and Response Actions.
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22.6.2 Validation of Calibration Procedures
Similar to the validation of sampling activities, the review of the calibration data described in
Element 14.0, Quality Control Requirements, and Element 16.0, Instrument Calibration and
Frequency can be used to validate calibration procedures. Calibration data within the acceptance
requirements would lead one to believe that the sample collection measurement devices are
operating properly. Any data that indicate unacceptable levels of bias or precision or a tendency
(trend on a control chart) will be flagged and investigated as described in Element 14.0, Quality
Control Requirements, and Element 16.0, Instrument Calibration and Frequency. This
investigation could lead to a discovery of inappropriate calibration procedures or equipment
problems requiring corrective action as detailed in the element. Validation would include the
review of the documentation to ensure that corrective action was taken as prescribed in the
QAPP.
22.7 Data Reduction and Processing
22.7.1 Verification of Data Reduction and Processing Procedures
As mentioned in the above sections, TSAs and surveillance will be performed to ensure that the
data reduction and processing activities mentioned in the QAPP are being followed.
22.7.2 Validation of Data Reduction and Processing Procedures
Data validation is initially completed by the Pb-PEP database on the AIRQA Web site. AIRQA
pairs the field data component with the laboratory analysis result to create the final concentration
for the sample. The AIRQA database also performs calculations for the required QC activities
across the lifetime of the sample. AIRQA completes and produces an automated "verified
dataset" that must then be validated by the regional and/or national Pb-PEP leads. This
validation is recorded in AIRQA creating a record of the validation. As part of the ADQ
discussed in Element 20.0, Assessments and Response Actions, the data used for these automated
checks will be reviewed to ensure that:
• All audit records conducted are present
• No blanks are in the dataset/records are complete
• QC parameters have been met
• Sampling periods are correct
• Site data is correct
• Sample analysis was performed
• Appropriate qualifiers/flags are properly assigned
• Audits are completed and documented by the regional Pb-PEP leads
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23.0 Validation and Verification Methods
Many of the processes for verifying and validating the measurement phases of the Pb-PEP data
collection operation have been discussed in Element 22.0, Data Review, Validation, and
Verification Requirements. If these processes, as written in the QAPP, are followed, the Pb-PEP
should obtain the necessary data quality to permit comparison of Pb-PEP with the routine
primary samplers. However, exceptional field events may occur and field and laboratory
activities may negatively affect the integrity of samples. In addition, it is expected that some of
the QC checks will fail to meet the acceptance criteria. Information on problems that affect the
integrity of data is identified in the form of flags (Appendix C). It is important to determine how
these failures affect the routine data. The review of this routine data and their associated QC
data will be verified and validated on a sample basis, on groups of samples, and on a sample
batch basis. Element 14.0, Quality Control Requirements, discusses the concept and use of
sample batching.
23.1 Process for Validating and Verifying Data
23.1.1 Verification of Samples/Audits
The FS initiates the COC for the Pb-PEP audits on the AIRQA Web site. After the audit, the FS
enters the field data into the AIRQA Web site. After each interaction with the AIRQA Web site,
the FS will review and verify that the information entered on the site is accurate and complete.
At the end of each month, a thorough review of the data will be conducted for completeness and
data entry accuracy by the laboratory analyst. Data used in the calculation of Pb concentrations
or used for evaluating critical validation criteria that are recorded on data sheets by hand will be
100% verified. After verification, these data will be reported electronically to the AIRQA Web
site for validation by the Regional Pb-PEP contacts.
23.1.2 Validation of Samples/Audits
Validation of measurement data will occur at two stages during the audit process; after the
laboratory analysis, and after the final pairing of the laboratory data with the field data in
AIRQA. At different points in the process, the laboratory analyst or FS or may observe instances
where the data quality may be affected, and they will document these events or observations in
the bench sheets, LEVIS or AIRQA Web site. In the case of the laboratory, the laboratory
manager will review the data against the laboratory Pb-PEP validation QC criteria listed in
Section 7, Tables 7-2 and 7-3 and notations made on the bench sheets and/or LEVIS and make a
decision regarding validation. In the same manner, the Regional Pb-PEP leads will review the
final audit data against the field Pb-PEP validation QC criteria and notations made by the FS
using the AIRQA Web site. The AIRQA Web site creates a report that shows the validation
criteria, the recorded data for those criteria, and an assessment on if the criteria passed the check.
These checks are classified into "critical criteria" and "operational evaluation criteria". The
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"critical criteria" and "operational evaluation criteria" are listed in Table 23-1 AIRQA Critical
Criteria Validation Template and Table 23-2 AIRQA Operational Evaluation Criteria Template.
As described above, validation will occur at the end of the analytical process and after the
analytical data has been uploaded to the AIRQA Web site and the automated validation routine
has been conducted. The laboratory manager, Regional Pb-PEP leads and National Pb-PEP lead
will have validation authority for Pb-PEP data. However, to avoid a waste of time and money,
the laboratory analyst and FS may request immediate invalidation of a sample in the event of a
significant failure or event. Some examples of a significant failure or event may be: malfunction
of laboratory analyzer resulting in a total shutdown, malfunction of field sampler, or
compromised filters (dropped, damaged, contaminated). Another important situation is a case
where an audit is conducted and the SLT sampler does not complete the sample run. In this case,
the FS will notify the Regional Pb-PEP lead and reschedule the audit.
23.1.3 Validation Acceptance and Reporting
The Pb-PEP Laboratory Manager will be responsible for determining that data have been
validated before submittal to the AIRQA Web site. A summary report documenting all data that
was validated and invalidated will be submitted to the Pb-PEP Laboratory Manager and National
Pb-PEP lead each month. The Regional Pb-PEP lead will be responsible for validating the final
audit concentration generated by the AIRQA Web site. All samples marked as "Approved" will
then be entered into AQS by the OAQPS support contractor. The Regional Pb-PEP leads will
follow the process described in Element 22 to approve and validate the audits. Audits that fail
critical criteria flags or do not meet the weight of evidence consideration will not be marked as
"Approved".
Audits that are not marked as "Approved" cannot be posted to the AQS because there is
currently no provision in the AQS precision data record format for adding null value codes or
data qualifiers.
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Table 23-1. AIRQA Critical Criteria Validation Template
Criteria
Void Sample/Visual Defect Check
Sampling Period
Average Flow Rate
One-point Flow Rate Verification
(High Volume TSP Sampling)
One-point Flow Rate Verification
(Low Volume Sampling)
Flow rate percent coefficient of
variance (low volume sampling
only)
Frequency
all filters
all filters
every 24 hours of op
During Set-up prior to every sample day
During Set-up prior to every sample day
Following each sampling run
Acceptable Range
Sample integrity protected during handling and transport (no
contamination, mishandling, etc.)
1440 minutes ± 60 minutes
midnight to midnight
1.1-1.70 m3/min (varies with instrument) in
actual condition
±7% from transfer standard
±4% from transfer standard ±4% from design set point
(16.67LPM)8
CV<2%
Reference
Part 50 App B sec 8.2
Part 50 App B sec 8. 15
Part 50 App B sec 8.8
Part 58 App A
Method 2.2 sec 2.6
40 CFR Part 50, App L, Sec 9.2.5 and
7.4.3.1 and 40 CFR Part 58, Appendix A
Sec 3.2.3 & 3.3.2
40 CFR Part 50, App L Sec 7.4.3.2
One-point flow rate verification is more stringent than the cited reference
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Project: PEP QAPP
Element No.: 23.0
Revision No.: 3
Date: 5/12/2014
Page 155 of 156
Table 23-2. AIRQA Operational Evaluation Criteria Template
Criteria
System Leak Check
Monitor Siting
Flow Rate Transfer Std.
Field Thermometer
Field Barometer
Clock/timer Verification
Flow Rate Verification
Barometric Pressure
Verification
Temperature Verification
Filter Check
Time Check
Frequency
During precalibration check
I/year
1/yr
1/yr
1/yr
1/3 mo.
Prior to each run
Prior to each run
Prior to each sampling run
After each sampling run
Prior to each sampling run
Acceptable Range
Visual and Auditory inspection with faceplate blocked
Meets siting criteria or waiver documented
Resolution 0.02 m3/min
+ 2% reproducibility
2° C resolution
+ 5 mm Hg resolution
+ 2 min/24-hour
< ± 4% of target flow rate
+ 10 mm Ha
+ 2°C
No contamination, pinholes. discoloration
+ 2min/24hours
Reference
1) Recommendation
1) 40 CFR Part 58 App E, sections 2-5
1) 40 CFR Part 50, App B sec 7.8
2) Method 2.2 section 2.5
1) 40 CFR Part 50, App B sec 7.5
1) 40 CFR Part 50, App B sec 7.6
1) Method 2.2. section 2.3
1) Part 50 App L Sec 7.4.3.1
1) 40 CFR Part 50, App L, Sec 9.3
2) Method 2.12 Table 6-1
1) 40 CFR Part 50, App L, Sec 9.3
2) Method 2.12 Table 6-1
1) Method 2.12 section 8
1) Method 2.2. section 2.3
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Project: PEP QAPP
Element No.: 24.0
Revision No.: 3
Date: 5/12/2014
Page 156 of 157
24.0 Reconciliation with Data Quality Objectives
The DQOs for the Pb-PEP are described in Element 7.0, Data Quality Objectives and Criteria
for Measurement. This element of the QAPP outlines the procedures that Pb-PEP will follow to
determine whether the monitors and laboratory analyses are producing data that are sufficiently
consistent to evaluate the bias of the National Pb network. For the data from the Pb-PEP to be
used for estimating the bias associated with the National Pb network, the data must be internally
consistent, meaning that the data should be precise and unbiased. The following outline is
conceptual, and it will be updated with formal statistical procedures once they have been
completely developed. For example, the amount of imprecision and bias that is tolerable in the
Pb-PEP, while maintaining confidence in the estimates of bias for the National Pb FRM/FEM
network, remains to be determined. An assessment of the quality of the data will be made at the
PQAO level. The Regional offices and the OAQPS have responsibilities in the DQA.
24.1 Preliminary Review of Available Data
Element 7.0, Data Quality Objectives and Criteria for Measurement, of this QAPP contains the
details for the development of the DQOs. Element 10.0, Sampling Design, of this QAPP
contains the details for the sampling design, including the rationale for the design, the design
assumptions, and the sampling locations and frequency. If changes in the DQOs or sampling
design occur, the potential effect should be considered throughout the entire DQA.
A preliminary data review should be performed to uncover potential limitations to using the data,
to reveal outliers, and generally to explore the basic structure of the data. The first step is to
review the QA reports. The second step is to calculate basic summary statistics, generate
graphical presentations of the data, and review these summary statistics and graphs. This review
will be completed by the National Pb-PEP Lead.
24.2 Evaluation of Data Collected While All Pb-PEP Samplers Collocated—
Regional Level
Twice per year (semi-annually), all of the Pb-PEP samplers used by a single FS, Region or a
number of Regions must be collocated and run at the same location over the same time period.
These are often referred to as "parking lot collocations."
The primary objective for collocating all of the samplers of the same method (high volume/low
volume) is to determine whether one of the samplers is biased relative to the average of all the
samplers and to estimate the repeatability of the instruments. An analysis of variance (ANOVA)
will be used to evaluate the first objective. Additionally, an output of the ANOVA is an estimate
of the repeatability. The conclusions from the ANOVA will allow EPA to determine whether
there is a Pb-PEP sampler that produces results sufficiently different from the average. If this is
the case, the instrument should not be used in the Pb-PEP. The estimate of the repeatability can
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Project: PEP QAPP
Element No.: 24.0
Revision No.: 3
Date: 5/12/2014
Page 157 of 157
be used to evaluate the certainty with which the bias of the routine program within the Region
can be estimated. Since there may be only two TSP Pb-PEP samplers in each Region, EPA may
ask Regions to work together to consolidate samplers at a common area equidistant from
Regional Headquarters but in an area with measurable Pb concentrations in order to run a more
robust evaluation.
24.3 Evaluation of Data Collected While All Pb-PEP Samplers Collocated—
National Level
A major goal of the national review of the data from the collocation of all the Pb-PEP samplers is
to determine if the repeatability of the samplers varies greatly by region. OAQPS will check for
equal variances across all regions by using standard statistical tests, such as the Bartlett test (an
all-purpose statistical test that can be used for equal and unequal sample sizes), the Hartley test
(a statistical test that requires equal sample sizes but is designed to find differences between the
largest and smallest variances), and Levene's test (an alternative to Bartlett's test for testing for
differences among the dispersions of several groups. Levene's test has greater power than
Bartlett's for non-normal distributions of data)12'13. The conclusions from these tests will allow
OAQPS to determine whether corrective action must be taken to reduce the variability for any of
the Regions or laboratories. Corrective action will include a formal review of the training and
operations to see if the cause for the disparity can be uncovered and corrected. With these data,
OAQPS will also be able to evaluate with what certainty the bias of the routine program can be
estimated.
12 Neter, I, W. Wasserman, and M.H. Kutner. 1985. Applied Linear Statistical Models (2nd edition). Homewood,
IL: Richard D. Irwin, Inc.
13 U.S. EPA (Environmental Protection Agency). 2000. Guidance for Data Quality Assessment: Practical Methods
for Data Analysis; EPA QA/G-9,QAOO UPDATE. United States Environmental Protection Agency, Office of
Environmental Information, Washington, DC, EPA/600/R-96/084. July.
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United States Office of Air Quality Planning and Standards Publication No. EPA-457/B-14-00 la
Environmental Protection Air Quality Assessment Division September 2014
Agency Research Triangle Park, NC
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