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QAPP outline

QAPP outline. 2 Element 1: Title Page with Approval Signatures Title of QAPP Name(s) of organizations implementing project Approval personnel Assistance

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Page 1: QAPP outline. 2 Element 1: Title Page with Approval Signatures Title of QAPP Name(s) of organizations implementing project Approval personnel Assistance

QAPP outline

Page 2: QAPP outline. 2 Element 1: Title Page with Approval Signatures Title of QAPP Name(s) of organizations implementing project Approval personnel Assistance

2

Element 1: Title Page with Approval

SignaturesTitle of QAPPName(s) of organizations

implementing projectApproval personnelAssistance agreement or

contract number(s)

Page 3: QAPP outline. 2 Element 1: Title Page with Approval Signatures Title of QAPP Name(s) of organizations implementing project Approval personnel Assistance

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Element 2: Table of Contents

List of all required elements and their page numbers

AppendicesReferences

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Element 3: Distribution List

Lists people who will get original and revised QAPP•Everyone who does the work•Everyone who manages them•Funding agency

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4-Organization of Project

Governmental Entities, Contractors, and Key Individuals.

Roles and Responsibilities.How often will these be done?How will each person do their

job? To whom will they report?

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Examples of Agencies

Required Agencies•Tribal Environmental Program•USEPA

Other Agencies•TAMS Center•State and Local Partners

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Possible Contractors

SamplingLaboratory Data AnalysisQA/QC Audit

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Examples of Key Individuals

Required Tribal employees•Air Quality Program Manager•Quality Assurance Coordinator

Optional positions (may be contractors)•Environmental Specialist•Environmental Technician

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Program Manager:Roles &

ResponsibilitiesOversees monitoring projectPrepares or reviews quarterly

& annual reports for submittal to EPA

Ensures staff is hired and trained

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Program Manager:Roles & Responsibilities

(cont.)Prepares & maintains project

work plan & budgetCommunicates with

Environmental Director & EPA Project Officer

Responsible for approval & modifications of project QAPP

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QA Coordinator: Roles &

Responsibilities Prepares or coordinates

preparation of QAPPsReviews and approves

corrective actionsConducts system audits

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QA Coordinator:Roles &

Responsibilities (cont.)Oversees or conducts method

performance auditsPrepares QA reportsConducts or oversees data

verification, validation and assessment

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Environmental Specialist:

Roles & Responsibilities

Conducts sample transport, handling & exchange

Delivers samples to laboratory (by mail or actual drop off)

Signs off on chain of custody forms

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Environmental Specialist:

Roles & Responsibilities

(cont.)Conducts quarterly calibrations, quarterly audits

Records sample information on data forms

Reports all aspects of monitoring project to Program Manager

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Project Organizational Chart (Example)

John W. SmithDirector

Navajo Tribe

Alexandria WashingtonAir Quality Program

Manager

Samuel VaughnAir Quality Specialist

EPA as appropriate

Michelle WinstonAir Quality Specialist

Tom LambAir Quality Technician

Laboratory

Sue JonesQA Officer

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5-Project Background

HistoryContextAssume an

“ignorant” reader (e.g., member of public)

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Why is this work important?

Are there health effects in your community that may result from this problem (asthma, bronchitis)?

Reduced visibility?

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More reasons why this work is important:

Concern about possible regional transport of pollutant (ozone precursors)?

Increased development, more roads, businesses, residents?

Concern about children’s exposure?

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Summarize Existing Information

Previous results from earlier studies?

Results from nearby areas? (if you did not gather the data, you may not be able to use it with your data but it can be useful to you in planning)

Results from emissions inventory?Results from compliance

monitoring of nearby facilities?

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Who are the Decision-makers?

Tribal CouncilTribal

Environmental Office director

EPA Region

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Element 6: Project Description

Ondrea BarberSalt River Pima-Maricopa

Indian Community

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Summarize Purpose of Project

Why are we making these measurements?

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Standards

What standard will the measurement

results be compared against (if

applicable)?

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Field Work-Summary

What kinds of measurements are being made?

What kind of samplers are being used?

How many measurements over what time period?

Site locations

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Field Activities-Summary

Routine field samplingSample collectionMonthly calibrations/auditsInstrument maintenance

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Laboratory Work

How are the samples being analyzed?• state the method• can refer to a standard method)

Who is doing the analysis?

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Schedule

1. Hiring deadlines

2. Training• Dry runs with

equipment

3. Field measurements

4. Analysis5. Reporting

Activity Frequency

Test sampler

October 1, 2005

First sampling

December 1, 2005

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Assessments

How will you check on yours and the lab’s work to ensure data is good (summarize)?

Who is involved and what are their roles (summarize)?

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Records of Assessment

Internal assessments (readiness review)

External assessmentsa. PEP audits for PM2.5, NPAP for othersb. Technical Systems Audits

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YOUR Assessments of the Analysis Lab

Initial review of their QAPP and calibration certificates when you agree to the contract

Onsite visit during the contract

Ongoing review of their QC results

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Records

BRIEF description of project’s records, • Information on where they are

stored•Ensure that detailed

information is in Section 19 What reports are required?

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Element 7: Project Quality Objectives

Mathew Plate US EPA Region 9

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Project Objectives

Why are we making these measurements?•Conformance with NAAQS•Obtain baseline data•To determine need for additional

monitoring•Health risk evaluation

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Project Objectives

What will we do with the results?• Compare with

NAAQS• Report to

community, EPA, health officials

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Systematic Planning

Required by grant regs: 48 CFR 46

Performance criteriaQAPP or equivalentData assessmentCorrective actionQA training for management

and staff

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Why Systematic Planning

Quality is the extent to which our data is sufficient for purposes it is being used

We need a process that defines objectives for our monitoring data and ensures that we know when these objectives are met

Program objectives should be developed in consultation with decision makers

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Decision Maker(s)

Those who use data for decisions or conclusions, such as• Is a standard violated?•Should we take action to improve

the air quality?•What is the air quality now, so

that we will know if it gets worse or better?

•Should we be taking more measurements?

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Who are the Decision Makers for Air

Monitoring Data?

Required Decision Makers for EPA grants•EPA•The Tribe’s Environmental

ProgramOther Decision Makers the

Tribe may consider in quality planning•State and local organizations•Researchers

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Types of Objectives

Project and Program ObjectivesData Quality Objectives (DQOs)

• Based on Program Objectives• Qualitative and quantitative

Measurement Quality Objectives (MQOs)• Specific criteria which when met should

produce data of acceptable quality• Quantitative

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Information in DQOs

How data will be used Type of data neededHow data should be collected

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DQOs Work Backwards...

Degree of uncertainty you can tolerate

Acceptable degree of uncertainty in

each measurement & number of

measurements to take

From

To

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DQO Functions

DQOs •Link answers to actual

measurements•Set limits on uncertainty so

that data produce required uncertainty in the answer

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Example

"We know that we meet the standard with 80%

confidence—this means there is a 20% chance that we

could be wrong and we are higher than that standard."

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Balancing Cost vs. Degree of

Uncertainty Balances costs of taking many

samples with desired uncertainty in Taking many samples with expensive devices yields low decision errors

Taking few samples at low cost yields high decision errors

Result—may have to change objectives, e.g. minivols to see if you need to monitor and ask for more $

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Accuracy

DQOs are concerned with determining the accuracy of measurements

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Accuracy

Accuracy = Total error• Includes both bias and precision•Measured by true audit and/or by

evaluating method quality objectives

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Translating DQOs into Useable Criteria

DQOs should be defined in terms of data quality indicators

Criteria set for the data quality indicators are method quality objectives

MQOs are set by using empirical data, conservative assumptions, statistical assumptions, and/or common sense.

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Data Quality Indicators

These are sometimes Called the PARCCS

Precision (P)Bias (A) (bias is sometimes called

accuracy)Representativeness (R)Completeness (C)Comparability (C)Detectability (S) (also called

sensitivity)

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Precision

...how well different measurements of the same thing under prescribed similar conditions agree with each other

“Random” component of error—sometimes high, sometimes low

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Precision

Precision =“wiggle” (variability within many measurements of the same thing)

You are trying to estimate the variability within the population of “all” your measurements of the same thing (concentration)

Two ways to estimate precision for a single instrument• If you have enough equipment, side-by-side,

can be two or more devices measuring the same concentration

• If you have only one continuous instrument, you must estimate precision by how much the measurement fluctuates over time when it is measuring the same concentration?

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Precision for Manual Methods

Relative percent difference (RPD)

RPD =*difference between two monitors*

their average

Example: RPD= * -0.05 *=0.05, or 5%

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Precision Exercise for Manual Methods #1

SiteB

Splr#1

Splr #2 Avg Diff RPD Correc.Action?

Jan 15µ/m3

16µ/m3

15.5 1 -6.5%

Feb 22 20

Mar

24 27

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Precision Exercise for Manual Methods #2

SiteB

Splr #1 Splr #2 Avg Diff RPD Correc.Action?

Jan 10 µ/m3 9 µ/m3

Feb 6 5

Mar 19 15

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Bias

A systematic distortion of a measurement process, which

causes errors in one direction (i.e., generally

positive or generally negative)

-15.0

-10.0

-5.0

0.0

5.0

10.0

15.0

Apr-02

May-02

J un-02

Jul-02

Aug-02

Sep-02

Oct-02

Nov-02

Dec-02

J an-03

Feb-03

Mar-03

month

% di

ffere

nce

%differencelower limitupper limit

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Bias

Bias = how far from “truth” you are, in terms of percentage

Bias = audit result – your result

audit result

Expressed as a percentage, so multiply by 100.

0.03 would be 3%0.11 would be 11%

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Bias Exercise #1

SiteA

Auditresult

Yourresult

Bias Correctiveaction?

Jan 42ppm

44ppm

Feb 39 42

Mar 32 36

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Bias Exercise #2

SiteB

Auditresult

Yourresult

Bias Correctiveaction?

Jan 12ppm

11ppm

Feb 19 18

Mar 22 19

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Bias Exercise #3

SiteC

Auditresult

Yourresult

Bias Correctiveaction?

Jan 55ppm

60ppm

Feb 50 16

Mar 48 47

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Representativeness

...a measure of how well your measurements represent the entire population of what you

are trying to measure

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Detectability

…how low can this be reliably measured with this equipment? Is this low enough to measure trends

and evaluate regulatory compliance?

this value is in instrumentation manuals or laboratory QA plan

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Completeness

... the amount of valid data obtained from a measurement system compared to amount

expected to be obtained under correct, normal conditions

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Completeness (cont.)

Completeness = # results that are usable (valid)

# measurements necessary

80% completeness 8 valid results

for Quarter 1 10 necessary

Also can do make-up runs to make up missed days

=

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Comparability

...measure of confidence with which one data set can be compared to another

Beware of apples and oranges in disguise

EPA tries to control this by the method designation process

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Manual Methods

Our precision measured by side-by-side monitors is 10% or less for all checks

Our bias measured by independent audits (PEP for PM2.5, NPEP for other criteria pollutants and PM10 flow) is 10% or less for all checks

NPEP is mail-in or van program required for all SLAMS and PSD monitors

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Automatic (Continuous) Methods

Our precision measured by bi-weekly one-point precision checks (flow rate for PM, span gas for other

criteria pollutants) is 15% or less for all checks

Our accuracy, measured by independent audits, is 15% or less for all audits

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Measurement Quality

Objectives (MQOs)

PM2.5 example considering:•Bias error•Precision error•Completeness

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EPA’s DQO Standards

for the PM2.5 NAAQS

The question: Does this air meet the annual standard of 15

mg/m3 ?

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Decision Error Limits

EPA decision: acceptable to make correct decision on attainment 95% of time

5% of time, decision may be wrong

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EPA Measurement Assumptions

EPA based their calculations on 137 samples in a 3-year period, which is 75% completeness with

a 1 in 6 day schedule

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MQO Calculations

Using acceptable uncertainty and the other assumptions, EPA calculated that each measurement must have a bias and a precision error (MQOs) of 10% or less

(See element 7 in the EPA PM2.5 Model QAPP)

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MQOs

If these MQOs are met, then the conclusion about attainment

will be correct 95% of the time

(Maybe - - This assumption needs to be verified when the data is assessed and the DQOs

are reviewed)

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Element 8: Special Training

Requirements

Melinda Ronca-BattistaITEP/TAMS

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Specialized Training

Identify & describe for each person all specialized training/certifications needed

How will training be provided?How will training be

documented (memos to the file of on-the-job training, personnel files with certificates of training, annual appraisals)?

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What Training Is Necessary?

Technical (equipment, QA/QC, etc.)• From instrument manufacturer• From TAMS

Allot TIME allowed/expected for reading manuals, doing on-line courses—40 hrs?

Document that you have spent 16 (or more) hours reading the QAPP and understand its requirements, using a sign-off sheet, and this will count as necessary training for anyone working on the project

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What Training Is Necessary? (cont.)

Computer use:• Word processing• Excel (see excellent on-line

courses)• Access

GIS/GPS?On-the-job training/staff

orientationSafety courses? (24-hour field

safety, first aid/CPR etc.) TAMS AQS training

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Examples of Training Options:

EPA (regional, headquarters, OAQPS [[email protected]], etc.)

ITEP: AIAQTP and TAMS CenterCalifornia Air Resources Board

(CARB)Local or state agencies with whom

you have a good relationship• borrow their manuals• accompany them in the field• document this in your personal logbook

(# hrs spent, activity, instruments, your initials and date; make photocopy for personnel file)

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Examples of Training

Options (cont.)US EPA’s Air Pollution Training

Institute (APTI); can view tapesTribal/state/local agenciesUniversity/college courses

(college credit, CEUs, etc.)Air & Waste Management

Association (www.awma.org)

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Element 9: Documentation

and Records

Melinda Ronca-BattistaITEP/TAMS

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This section needed to:

Protect legal and financial rights of the agency and persons affected by agency’s activities

Ensure that data are legally defensible (e.g., all changes are documented [who/when/why WRITTEN DOWN] )

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This section:

Is short—complete data management is described in element 19

Think of data management as:• What (requirements)• Why• Who• How• Where• When

Goes in element 19

Element 9

(can be very brief if you reference SOPs!)

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“What”

This element lists the requirements for the records—what do you require of these records?•Records of planning•Records of operation•Records of data management

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Records created during project

planning:Hiring and training recordsInitial contracts with instrument

vendors, contractorsBudget recordsPlans for instrument specs,

network, site locations, site visitsLIST THESE RECORDS, WHO WILL

WRITE/REVISE/APPROVE THEM, HOW OFTEN, WHERE YOU WILL STORE THEM

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Records created during project

operations:Site visitsData transferAudits and assessmentsQC checks (internal and external)CalibrationsLIST THESE RECORDS, WHO WILL

WRITE/REVISE/APPROVE THEM, HOW OFTEN, WHERE YOU WILL STORE THEM

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Records created during data

management:Download and transferFile naming, moving, pw-protecting,

archivingReview, range checks, flagging,

calculationsReporting to tribe, EPALIST THESE RECORDS, WHO WILL

WRITE/REVISE/APPROVE THEM, HOW OFTEN, WHERE YOU WILL STORE THEM

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A little detail please…

In the text or table, list for each item :• Any rules—must be written in pen,

dated and initialed• Changes must be made so that original

data is kept legible• Computer files are password-protected

for making changes• Duplicate copies made and stored

where?• How long are they kept and who

decides to throw them away?• File naming conventions?

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Requirements for data transfer:

Specify rules for:•never over-writing files• frequency of downloading files

from instrument, backing up files•Keeping files on paper (may be

summary if very long) and on disk and in PC (designate PC)

•File structure (see example)

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File naming convention example:

All your files follow the same format (example): pppp_ssss_dddddd_nnn_rev# • Post this on a wall and changes to it to add

fields • Where pppp=pollutant• Ssss=site name or number• Dddddd=date when measurements made• Nnn=initials of person saving the file• Rev # is the revision number

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List all documents:

SOPs, QAPP (this one and that of any lab analyzing your samples)

Site logbooks, personal logbooksRepair and maintenance recordsReports drafted, final, sent out to

tribal authorities, EPAPhotos of sitesLetters from community, EPA, etc.

are kept and filed

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Data handling procedures:

Example: state that this project will use an Access database for all transcribed or input records and data

State that the requirements for data handling are in element 19; this element only lists the records and the requirements for the records

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List your plans for reports received and

sent out:

Quarterly & Annual Reports submitted to tribe, EPA

Quarterly Laboratory Data Report

Audit reports Quarterly AIRS-AQS Data

submittal to EPAList these in a table

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References

QA documentsSOPsOther documents

Have all references available in your office

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Element 10: Network Design

Ondrea BarberSalt River Pima-Maricopa

Indian Community

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Rationale for Measurement Location

and FrequencyRefer to the data quality objectives

(Element 7)Use the objectives when you decide

where/how often to monitor• Near where people live? • Overall community background? • Near sources?

Discuss purpose of primary & collocated samplers

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Design Assumptions

Document what you are assuming: •That a source will impact air

quality in the monitored area? •Weather patterns, road use,

community development in the future, whatever

Are your locations reasonable in terms of CFRs and other guidance documents (see ITEP CD)

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Data Generation/Collection Design

What type of equipment will be used to generate/collect data?

How many will be used? Primary and collocated, meteorological eqmnt

Frequency of data collection (24 hours)? Saturdays & Sundays? How many calendar years?

Is the monitoring equipment FRM or FEM? If so, what is designation number?

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Sampling Network Design

Do you have special purpose samplers (SPMS) measuring for baseline conditions?

Do you have a SLAMS-designated site that will provide EPA with national data?

Discuss siting requirements • (40 CFR Part 58 App. D & E; although

these may be impossible to meet so do your best, and confer with your EPA regional office)

Monitor location: Roof? Platform? Other?

Spatial scale of representativeness • (40 CFR Part 58 App. D)

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Monitoring Objectives could

include:1. To determine highest

concentrations expected to occur in area covered by network

2. To determine representative concentrations in areas of high population density

3. To determine impact on ambient pollution levels of significant sources or source categories

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More possible monitoring objectives

4. To determine general background concentration levels

5. To determine extent of regional pollutant transport among populated areas, and in support of secondary standards

6. To determine culture [EPA calls welfare]-related impacts in more rural & remote areas (i.e., visibility impairment, effects on vegetation)

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TABLE 1.—RELATIONSHIP AMONG MONITORING

OBJECTIVES AND SCALE OF REPRESENTATIVENESS

Monitoring Objective Appropriate Siting Scales

Population…………..

Source impact……….

General background…

Regional transport…..

Welfare-related impacts...

Micro, Middle, neighborhood

(sometimes urban1)

Neighborhood, urban

Neighborhood, urban, regional

Urban/Regional

Urban/Regional

1 Urban denotes a geographic scale applicable to both cities and rural areas

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Critical / Non-critical

MeasurementsCritical measurements are required

to achieve project objectives or limits on decision errors• Field measurement requirements (i.e.

ambient temperature, barometric pressure, etc.)

• -What you would include when submitting data to AQS

Non critical measurements are those that are “nice to know” but not make-or-break

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“Standard” Measurements

Federal Reference Methods (FRMs) and Federal Equivalent Methods (FEMs) provide standard measurements as required by EPA for comparison to the NAAQS

Use of any non-standard measurement method can provide useful information

Also pertains to filter-weighing laboratories – EPA requirements must be met

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Element 11: Sampling Methods

Requirements

Melinda Ronca-BattistaITEP/TAMS

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Sampling Method Requirements

Requirements, not procedures go in the QAPP

Attach your SOPs!

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Sampling Equipment, Preservation,

& Holding Time Requirements

Requirements for getting samples (data) to lab without losing what you are measuring or making it stink…

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Requirements for the Sample

Volume of air or whatever medium you are collecting

Object with which you are collecting the medium

Data for automatic methods (complete, copied onto floppy, file named correctly, never overwritten)

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Requirements for PM2.5 Samplers

Installed & operated with adherence to requirements in •40 CFR Parts 50, 53 and 58;•Section 2:12 of EPA QA

Handbook;• the sampler manufacturer’s

operation manual, •SOPs, • and this QAPP

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Sample (Data) Collection Overview

Schedule of receiving filters (data)

Schedule of samplingSample routeDescribe procedures (may be

in SOP) for when retrieving samples (data) do not go as planned

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Prevention of Contamination

Requirements for•Temperature•Humidity•Time• Integrity•Custody•Data handling

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Sample Preservation Requirements for

PM2.5Filter cassettes stored in filter

cassette storage containersStored with the particulate side up.Temperature (40 CFR Part 50,

Appendix L)• No direct sunlight or closed-up

car during summerTime before sample recovery and

time before weighing

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Set-Up Requirements

WhenWhere How (ref. SOPs)Who Documentation

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Sample (or data) Recovery

RequirementsWhen

•PM2.5 must occur within 96 hours of end of sample period for that filter

Where (sites)How (order)WhoDocumentation

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Support Facilities for

Sampling MethodsOffice, trailer, truck, & cooler must be consistent with requirements for•Temperature•Humidity• Integrity•Custody•Storage capacity

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Field Safety:

State that safety comes before getting the sample (data)

Reference health and safety plan

Provide training if appropriate

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Field Corrective Action

Who is responsible for fixing it? Verifying that it is fixed? Reporting the fix to?

Where do they write how they fixed it?

When do they have to fix it by?How do you make sure it does

not happen again?Where is the documentation

stored?

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Corrective Action Responsibilities

(cont.)Who makes sure problem was

solvedWho makes sure it doesn’t

happen againwho approves changes to

sampling locations, personnel, SOPs, QAPP

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Element 12: Sample & Data

Custody

Ondrea BarberSalt River Pima-Maricopa

Indian Community

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Sample (Data) Integrity

Packing List Shipping Receipt Annual Shipping Schedule Log BookOther

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External Sample Custody Procedure

Formal Chain of Custody Form/Record

Dates/Times SignaturePre-samplingPost-sampling

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Internal Sample Custody Procedure

Sampling media (filter) receipt

Tracked in Logbooks and/or Computers

StorageAccessArchiveDisposal

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Data Custody Procedure

Data storageData transferData securityData backup (logger/strip

chart)

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Element 13: Analytical Methods

Requirements

Melinda Ronca-BattistaITEP/TAMS

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This element is important for comparability:

Requirements of all FRM monitors are the same, so that data from different sites can be compared

Performance of all labs meeting these requirements is the same, so that data from different labs can be compared

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Summarize method:

In one paragraph summarize how the lab or instrument conducts the measurement

If FRM or FEM cite the method number

List special components, modifications, inlets

List requirements for equipment you are using (scales, thermometers)

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List in this element:

Requirements for how well the lab or instrument performs

List analytical methods and equipment

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Instrument or lab environment:

Limits for temperature, humidity

If the instrument requires a shelter, describe the requirements here

If lab or instrument changes their procedures or performance, who approves it? What are the requirements they/it must meet?

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Element 14: Quality Control

Melinda Ronca-Battista

ITEP/TAMS

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QC: An Ongoing System

MeasuringComparing with

MQOGraphing itFixing it when

needed

Everything must be documented and, when significant, reported

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Evaluate Where Things Can Go Wrong—and How

To Check

Preparing for the fieldSampling in the fieldAnalyzing the samplesEntering the dataReporting the data

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Error

…the difference between your answer

and the “truth”

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Bias Error

Minimized by calibrating your equipment against a standard•Make sure the standard has

TRACEABILITY to a NIST standard

•Compare standard to field and/or lab equipment

Measures any bias in your

equipment

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Verifying the Accuracy of Your

Transfer StandardIf necessary, send your standard to the

manufacturer, who has NIST-traceable equipment, and they send you back your standard with a certificate of traceability

If appropriate, use natural standards, such as freezing ice water for temperature, and carefully document your calibration according to a standard method

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Single (One) Point Verifications

Single-point verification is when you conduct a check using one flow rate or concentration or value

Span is an example of a one-point check

Verifications DO NOT involve any changes to your equipment or settings

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Multi-Point Verifications

Check of the response of the instrument to more than one flow rate, concentration, or value

Usually zero, a low level, and at the upper end of the range expected to be measured

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Example of Verification

Perform a check of your equipment:• flow rate for PM• concentration for gas• internal mass for TEOM

This may be single-point or multi-point

If this is within specifications, record this and continue

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Calibrations

If results are NOT within specs, then the instrument must be adjusted

This adjustment means that the response of the instrument is changed, which is defined as a CALIBRATION

Must be multi-pointAfter calibrating, check again

at a single point

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Example for PM2.5

Corrective Action if the flow rate difference between the transfer standard and the sampler is > 4%

Check sampler for internal and external leaks

Ensure that temp. and pressure are within normal ranges

Run check a 2nd time If still > 4%, perform a multipoint

calibration followed by a single-point verification

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Who can conduct verifications?

Routine checks of instrument stability can be conducted by the site operator

Periodic assessments (may be every six months, may be every year, should be quarterly check of flow rate for PM2.5) should be conducted by someone OTHER than the site operator

QAPP specifies how often these checks are conducted, by whom, what to do if results are off

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Calculations for Results of

VerificationsConsider the standard to be the

“ideal truth” for your equipment Difference between the “ideal

truth” and your equipment is the instrument error (this may include bias [error either usually high or usually low], and imprecision [wiggle sometimes high and sometimes low])

How is instrument error quantified?

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Quantifying instrument error:

Truth = the standard’s result

Y = your equipment’s resultYour equipment’s error Truth – Y

Truth

=

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Remember...

0.02 = 2 %0.10 = 10 %

Bias calculations exercise

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Precision Error

Some imprecision is unavoidable

Sometimes up, sometimes down–“random”

Estimated by measuring the same thing several times

Minimized by carefully following procedures

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Two Sources of Precision Error

Field

Lab

Cows can be problems….

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Estimating Precision

in the FieldEstimate the random “wiggle” errorIf you have more than one of the

same type of instrument, place side-by-side (measuring the same sample of air within a room or small area)

If you only have one instrument make repeated measurements (same sample of air, quickly in time so the air does not “change”)

Verify that results are within limits

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Estimating Precision

in the LabRepeated filter weighings OF THE

SAME FILTER or standard weightVerify that results are within limits

—if results are very different then there is a lot of imprecision and there may be an intermittent power draw, a breeze blowing onto the scale, changes in humidity….

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Next steps of QC

If you are outside the limits:Review procedures & logs to

identify problemGo back and review data—may

have to throw out data to the last good check

Fix, document and report (when significant)

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Calculating Precision Error

Because we don’t know which device is better, there is no “truth,” so use the average as “truth” X = one sampler Y = the other sampler then precision error is

( )x y

x y

2(multiplied by 100 to yield a value in percent)

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Coefficient of Variation (COV)

COV = coefficient of variation

Where “s” is the sample standard deviation

COV = s/(average)

See the Tribal Data Analysis spreadsheets for example calculations that you can use

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Remember...

0.05 = 5%0.10 = 10%

Precision calculations exercises

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Accuracy = Total Error

“Accuracy” for EPA means “total error”

Comparison conducted with completely different system can be used to estimate total error

For PM2.5, this is a performance evaluation conducted with a side-by-side FRM device, with the filter weighed by a different lab

Total error includes both precision and bias errors

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Blanks

Measure anything that affects the result outside of what you are measuring

May make the result greater (contamination)

Or decrease the result

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Types of Blanks

For real-time measurements zero checks display the value with no air

Manual methods using filters must use field blanks—accompany “real” samples

Labs must measure their own blanks to assess whether there is any contamination in the lab

If it is possible that samples get damaged or contaminated during shipping use shipping blanks (trip blanks)

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Field Blanks

Handled exactly as field samples

Some field blanks go everywhere field samples go

With each operator, site, procedure

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Control Charts

• Try to keep something steady, but it naturally varies

• 95% of time within 2 s of average • 99.8% of time within 3 s of average

red lines within 2 s of average

S = sample standard deviation

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Element 15: Equipment Testing, Inspection, and

Maintenance Requirements (General Principles)

Ondrea BarberSalt River Pima-Maricopa

Indian Community

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Purpose of T.I.&M.

Increase system reliabilityData completenessMinimize down timeDocument credibility of data

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Types of instrumentsEmphasize those instruments

that impact data quality Acceptance testing of

equipmentOutside person to review final

testsProvide a table – referencing

SOPs is okay!

Ensuring your data meets its quality

objectives:

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Checks

Check equipment before you go into field

Check in field before you make measurements

Check after you make measurements

Ongoing checks and maintenance

Checklists! (include in QAPP, even if you know it will be revised)

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Personnel

Delineate responsibilities•Person(s) to do T.I.&M.•Person(s) to order equipment and

supplies•Person report to for replacement

parts or potential problems•Person(s) to report problems to

and to contact for corrective actions

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Procedures

Describe how T.I.&M. will be done • Schedule of T.I.&M.• Documentation in QAPP appendices

(maintenance checklists kept in sampler case and logbook, standard forms with boxes to list values for parameters or check that tubing and wiring is in satisfactory condition)

• Location/storage of completed checklists

• Maintenance history – inventory of replacement parts, suppliers, spare parts, other consumables

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Visual Inspections

Inspect forDamage to monitorCondition of filter and surroundings

(i.e., cleanliness)Consistent power supply so that

start/stop times are reliableO-rings in place and not tornWires and tubes all attached

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Inspections

Specify what is done in the field or in the office

Be practicalAllow for adequate time to do

inspections and document their results

Take spare parts such as o-rings with you—add this to the checklist

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Inspection Considerations

FrequencyInspection parameter – what do you

look for?Action if item fails inspection – how

do you fix it?Documentation (logbooks for each

piece of equipment & inventory of spare parts, oil, etc., instrument or site visit checklists—include in QAPP or reference owner’s manual)

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Site-Specific Factors

TemperaturePrecipitationWindCurious peopleBirds, bugs,

leaves

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Toolbox

Screwdrivers (Phillips, flat head, tiny)

WrenchesGlovesDigital multimeter – trouble shoot

electrical componentsExtra batteries – to charge

computer board, etc.Duct tapeState this in the

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Maintenance

Spare partsLocation of partsInventory of partsWhere parts or equipment are

purchased

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Schedule of Maintenance

Field or transfer standard traceability to NIST or certificate

of calibration referenced

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Cleaning Supplies

Ammonia-based general purpose cleaner – clean hub unit

Cotton swabs – clean vent tubes

Soft bristle brushes – air screen, bug screen, etc.

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Cleaning Supplies (cont.)

KimWipes – lint-freeSilicone-based lubricant –

ensure leak-free fit of rain jar, O-rings, other connections

Powder-free rubber gloves – sample handling, transport

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Be sure to include:

How you conduct T.I.&M. (reference SOPs, pages from owner’s manuals) or briefly summarize

ScheduleSpare partsCorrective actionChecklists, documentation

sheets

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Element 16: Instrument Calibration

Ondrea BarberSalt River Pima-Maricopa

Indian Community

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Calibration

Calibration is defined as•Comparison of instrument

response to a standard and•Adjusting response to fall within

planned limits (remember that if you just check the response and it is okay then that is a verification)

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List Equipment that Requires Calibration

Identify all tools, gauges, instruments, and anything that produces values

Make a table that lists the frequency of calibration and how it is to be conducted and who is responsible for ensuring that it gets done

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List Equipment that Requires Calibration

(cont.)

Limit to equipment you will be responsible for

If you use transfer standards (temperature, flow rate, BGI delta-cal) then these must be periodically recalibrated, so that you know they is producing valid results and this is documented

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Reference Attached SOPs and...

Describe briefly or reference SOP:•How calibration is done•When to calibrate

Summarize calculationsSummarize calibration

records (logbooks, forms, reports)

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Calibration Standards

Primary standards—keep as the “gold standard”

Field, transfer, or working standards are used in the field

These apply to flow rate, temp., pressure, etc.

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Types of Calibration

Multiple pointZero-levelRepetitions at each

concentrationAlways verify stable operation

after a calibration by checking at least one point again

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Changes to Calibration Schedule

You may have to recalibrate if you:

Move, repair, or reassemble equipment

If QC checks show degradationIf QC checks show great

stability, then may not have to recalibrate so soon

Change in weatherChange in pollutant

concentration

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Justification for Changes

Documentation—write a memo to the files (see example on CD)

External reviewer—get a reality check from another person

Periodic verifications of your calibration schedule and procedures

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Do Calibrations Yourself?

Requires careful documentation

Use standards calibrated by vendor or another certified lab•Use these standards to

calibrate your instruments

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If you need a Laboratory

Get copy of laboratory’s QAPP, include as appendix to your QAPP

Conduct tour of facility if possible

Communicate regularly with facility personnel

Make sure lab documents everything, provides reports

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Documents to you from analysis lab:

Copy of their QAPPCopies of their internal

performance evaluations within the last year, and throughout the project

Agreement that they provide you data on paper and electronically (via email) in excel or whatever format you agree to

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Documents to you from the lab that certifies your

calibration standards:

Copy of calibration certificate showing what standard they use to calibrate your equipment

Traceability of this standard to the National Institute of Standard and Technology (NIST)

Agreement that they provide you a calibration certificate and detailed report on paper and electronically (via email) in excel or whatever format you agree to

Outline of calibration procedure

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Element 17: Inspection and Acceptance for

Supplies

Ondrea BarberSalt River Pima-Maricopa

Indian Community

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Requirements

What are the requirements for the equipment / supplies

you will use during the project?

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Provide a Table Listing

DescriptionVendorSpecifications Model numberCall the sales rep. and ask

them to fax you a list of what parts will be needed

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Two tables may be needed:

(1) listing of critical supplies, parts (hoses, filters, disks, etc.)

(2) list of their acceptance criteria (diameter/type of hose, type of filter, disks preformatted, whatever is appropriate)

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(1) List of Critical Supplies:

Example First Table for PM2.5: Critical Supplies and Consumables (excerpt)

Area Item Description Vendor Model Number

Sampler Impactor Oil Tetramethyltetraphenyl-trisiloxane (30ml)

Dow Corning@ 704 Oil

Sampler 37 mm GlassFiber Filter

For use in impactor well XYZ Company xxxx

Sampler Rain Collector Glass XYZ Company xxxx

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(2) Acceptance Criteria

List criteria for each itemShould be consistent with

project’s overall technical and quality criteria

Should reflect common sense, but need to document the basic requirements, even if they seem obvious to you

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(2) Acceptance-Criteria Table

Second Table: Example Acceptance Criteria for Supplies and Consumables

Equipment Acceptance Criteria Action if requirements not met

Impactor Oil Is the oil identified asTetramethyltetraphenyl-trisiloxane

Return

37 mm Glass Fiber Filter Filters of the correct size andquality

Return

Rain Collector Not broken Call Vendor, will likely notreturn

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Element 18: Data Acquisition Requirements

for Non-Direct Measurements

Melinda Ronca-BattistaITEP/TAMS

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What is non-direct data?

Any data that you do not gather, such as•Weather information•Housing information•Physical constants• Instrument parameters

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Examples

Chemical and physical properties data

Operations manualsGeographic data – site, boundary

conditions, met sitesData from previous studiesMeteorological information – U.S.

Weather Service Data, wind rose information

Census data, housing office data

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Be sure to include:

Any non-direct data you plan to use

How you plan to use itIf you are using historical

monitoring data, how you will keep track of which data you gather and which data you have gotten from another source

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Why is the QA Significant?

If you plan to use the data with yours, data that you do not gather should:•Have undergone QA review•Meet quality objectives

established for your programThis means that you need to get

a copy of their QAPP or QA report and compare with this QAPP

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Step 1 – Describe your Requirements:

How you are going to use this data

Whether this could change conclusions

What are your quality objectives for this data

If the data is critical describe some or all QC parameters

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Step 2 – Describe the Data Sources:

Nationally recognized source (USGS, NWS, & NIST)

Peer Reviewed Source (published in a peer reviewed journal)

Monitoring data from another study

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Step 3 – Determine if Data Validation will be

Performed:If the data is from a nationally

recognized source and is being used for a similar purpose validation is probably not needed

If the data has not undergone external review and/or the data will be used to meet a different purpose than intended (when collected) some level of validation is required

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Step 4 – Describe Data Validation for data you plan to use but did not

gatherReview QC checksReview QA evaluationsCompare to other data setsPerform QC measurementsDon’t be afraid to discard data

that you don’t trustReference validation in elem.

24

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Element 19: Data Management

Melinda Ronca-BattistaITEP/TAMS

Ondrea BarberSalt River Pima-Maricopa

Indian Community

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Six Elements of Data Management

(1) Data processing and transmission (WHAT)

(2) Data end use and integrity protection (WHY)

(3) Data access (WHO)

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Six Elements of Data Management (cont.)

(4) Data dissemination (WHERE)

(5) Data storage and retrieval (HOW)

(6) Data disposal (WHEN)

Document everything!

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Describe in the QAPP:

Brief description of•Data management objectives (all

data is retrievable)•How you will meet these objectives

(no data erased, no files overwritten, use sharpies, date and initial)

•Describe (briefly) your paper filing system

•Describe logbooks: personal, instrument

•Electronic filing system, file naming system

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Data Flow

Step by step data trackingWho has access to readWho has access to change dataVersion tracking of filesHow changes are approvedHow file integrity is checked

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Files for each instrument and any

extra sensors:Request as much information

as possible electronically and on paper from vendors to allow you to make extra copies

Maintain file for each instrument with contact information, calibration records, manuals

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Material Receipt and Storage

Use logs for everything (see examples in template QAPPs)

Use indelible markers Use tagsUse designated shelves with

labelsUse SOP that is POSTED

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Types of Field Data Sheets

Site Data Sheets • document the site information• in site files and in database

Sampler run data sheets• go into field• input info into database

Verification data sheets• every 4 weeks (1-point flow rate, temp,

pressure, time) Internal audit data sheets

• for the sampler and extra sensors (your own audits)

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Before leaving office for the field:

Review the number of each item you will need, and bring backups (use a checklist)

Check field data sheet from previous visit to site

PM2.5: Ensure that there are filter cassettes for routine, field blanks, and collocated samples

PM2.5: Ensure there are enough field transport containers, ice substitutes, max/min thermometers, preprinted mailing labels, if mailing immediately

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Write in pen and update the documents:

Continuously update the checklist in pen• make photocopy• put in “to-do” pile to

– add the information to the database– change the form in the computer if

appropriate

At the site draw a map on the field data sheet

Take photos if possible

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Sampler Placement Records

Unobstructed air flow for a minimum of 1 m in all directions

Inlet at a height of 2 to 15 m above ground level

If collocated with any other PM sampler, the spacing between sampler inlets must be > 1 m for other PM2.5 samplers and > 2 m for PM10

All samplers that are called collocated must be within 4 m

Sampler inlet must be level Vertical distance between two inlets < 1

m

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Sampler Maintenance and Cleaning Records

Plan all required maintenance 12 months ahead—post 3 months on a calendar

Use a checklist that includes items to bring with you and what to do for:• Every visit (filter change data sheet)• Every month (1/3 day schedule) or

quarter (1/6 day) (verification data sheet)

• Every quarter (flow rate audit data sheet)

• See examples

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Computer Backups

Every two weeks or as data are gathered—add “back up today” to calendar

Alternate between two sets of backup ZIP or JAZ disks

Store backup disks in a relatively fireproof location (another building, garage)

Plan for the time and money it takes to save copies of files

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Supplementary records must be kept for only 3

years

Chain of custody formsNotebooksField data sheetsField data sheets

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Keep records organized in

readiness for an audit

Paper copies must be available to auditor to attach to their reports in the categories of:• Management and organization• Site information• Field operations• Raw data• Data reporting• QA

THE BEST WAY TO GET RID OF AN AUDITOR QUICKLY IS TO GIVE HER PAPER COPIES OF EVERYTHING SHE WANTS

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Site information files to include:

Site Data SheetsSite mapsSite photosSummary of instruments at

each site and shelter, trailer information

Addresses, names, phone numbers

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Field Operations files to include:

Instrument manuals, warranties, calibration certificates in a file for each instrument

Standard operating procedures (SOPs)

Field notebooks and communications

Copies of most recent field sheetsInspection/maintenance records

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Raw Data files to include:

Any original data (routine and QC data on disk and paper)

Reports from laboratory or external audits

Strip chartsDisksSupporting data, such as NWS

data

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Data Reporting files to include:

Internal reports Weekly/monthly summariesCorrective action reportsReports to EPACopies of presentations to

community

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QA files to include:

For each instrument, copies of instrument check reports (verifications)

Calibration reports (multipoint using some standard)

Archived control chartsQA reportsAudit reports and reports on how

problems were solved (corrective action reports)

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Measurement results should be kept

indefinitely

Data must be accessible for 5 years

All official reports kept for 5 years

Paper copies can be discarded after 5 years and electronic copies archived on disk/CD

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Data Transformation & Analysis

Data analysis requirements contained in 40 CFR Part 58, Appendix A

Show equations you will use (usually simple relative percent difference)

Show examples of charts (use example control chart in the template QAPP)

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QAPP outlines plans for data transmittal:

How data gets from equipment into your computer

How (who, how often) data is input

How (who, how often, how much) someone double checks data entry

How data is sent electronically How you will transfer data into

AQS

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Describe plans for data flagging

Criteria for flagging dataFlags may be generated by the

instrumentFlags may be noted by you on

the site data sheet (e.g., high winds) and entered into the database later

Flags may be automatically written into a column in excel if values are outside a specified range (see example on CD)

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Describe plans for data storage &

retrieval

Data archival policies: where, how long, on paper and disk

Security of data; locked cabinet; password-protected

Database management

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Element 20: Assessments &

Response

Mathew PlateUS EPA Region 9

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Corrective Action

Designed to identify and correct flaws in your system

Anyone can start and document corrective action

Documented by a formal process (a review by a supervisor and a memo to the file; see example)

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Internal Assessments

May be qualitative, such as a review of whether documentation is in order, or technical, checking procedures, and

May be conducted by your tribal air organization•Someone who has common sense

and is technically competent •Someone from another program,

such as water, solid waste

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Internal Assessments, cont.

May be informal and consist of a review between you and your supervisor on progress

IF this is to be considered an assessment it must be DOCUMENTED; use a checklist or memo

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External Assessments

Performed by outsiders such as another tribe, EPA region, or consultant who is technically qualified

andUnderstands project’s QA

requirementsA real auditor

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Types of Assessments

Surveillance• “Over-the-shoulder” monitoring of

project & records; this can be internal or external

Technical Systems Audit (TSA)• On-site examination of facilities,

equipment, personnel, training, procedures, and record keeping, usually conducted by EPA

Performance Evaluation (PE)• involves numeric comparison of

results between auditor’s equipment and yours

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Performance Evaluations:

Internal• that you conduct as a “test” with a

borrowed standard, during an inter-comparison with other agencies—VERY useful, esp. before an external audit

External• side-by-side on-site with another

device independently calibrated Comparison of your results with

equipment mailed to you or in an EPA van (NPEP)

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Definitions of Assessments

Audits of data quality – qualitative • are you working toward your

objectives? Do your measurements make sense?

Data Quality Assessments – quantitative • comparison of results with someone

else’sManagement Systems Reviews

• review of QA system; usually conducted by EPA

Network Reviews • are your locations/instruments

appropriate?

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All Assessments:

Basically compare•What is actually being done in the

field and the office•Against what is stated in the

QAPP and SOPs

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Readiness Review—one type of Internal

AuditConducted before starting routine

measurements to assess: “are we ready?”

Technical components – equipmentTrainingThe report should be approved by

an uninvolved personReadiness review can be counted as

an internal assessment, IF it is documented and any problems are resolved and documented as well

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Technical Systems Audits

Every three yearsLook at reports, computer

files, logbooks, control chartsFollow people around Compare what is happening

with QAPP and SOPs

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Technical Systems Audit (cont.)

Field operations: sampling, shipping

QA – corrective actionQC – field checks, data

flagging, record keepingData management: securityReporting – accuracy

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Audit of Data Quality

Evaluating your data before you report it•How data are handled•What judgments were made•Do your conclusions make sense?

Annually and as part of a technical systems audit

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Network Review

40 CFR Part 58 Appendices D and E

How well is your network meeting its objectives?

How should it be modified?Conducted formally annually,

but you should be continually assessing your results

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Describe in your QAPP

Number, frequency, and types of assessments

People or organizations doing the assessments

ScheduleCriteria for assessmentsReporting and responsibility for

follow-up

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Element 20 includes a table listing assessments:

Assessment Activity

Frequency Personnel Responsible

Schedule Report Completion

Reporting/Resolution

Network Reviews App E

Ongoing informally and annually

Describe the first schedule and how often after that

30 days after formal review

Who is responsible for doing the assessment, who makes sure the problems get corrected?

Technical Systems Audits

1/3 years 30 days after activity

Performance Evaluation--Internal

Quarterly?

Performance Evaluation--External

Annual?

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Responsibility for Follow-Up and Verification of Corrective Action

CLOSE THE LOOP (fix problems and take action to

make sure they do not happen again)

And make sure it is documented

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Element 21: Reports to Management

Ondrea BarberSalt River Pima-Maricopa

Indian Community

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Purposes of Reports

CommunicateDocument TrackCYA

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PM2.5 Reporting

Pictures are worth a thousand words— CHART YOUR DATA—by site, by date

Flow Rate Audits conducted quarterly by someone other than the routine site operator

Results of collocated FRM samplersResults in ranges of concentrations

(see tribal data analysis spreadsheet)

40 CFR 58 Appendix A (Section 3.5)

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Corrective Action Reports

OngoingWhat, where, when, who, how,

whyVerification of permanent

solution

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Report Tracking

ListThose responsible for

generating and reviewing reports

What is in each report (brief)How often each type of report

is issuedWho receives each type of

report

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Element 23:Data Review Methods

Melinda Ronca-Battista

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Data Validation

Can the data be used for the purpose it is intended?

Is the data invalid or can it be used with qualifications?

Is the data generation process likely to produce invalid data in the future?

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Data Validation Templates

Developed by OAQPS, EPA Regions and monitoring organizations

Three tables generated

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Data Validation Tables

•Critical – In CFR with acceptance requirements

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Data Validation Tables

•Operational – In CFR without acceptance criteria or identified in guidance

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Data Validation Tables

•Systematic – important for correct interpretation of data but do not usually impact validity of sample or group of samples

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Template for PM2.5

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Template for Ozone