Environmental Technology Verification Source Water Protection Pilot

Mercury Amalgam Removal Technologies

PROTOCOL FOR THE VERIFICATION OF MERCURY AMALGAM

REMOVAL TECHNOLOGIES

Prepared by:

NSF International
P. O. Box 130140
Ann Arbor, MI 48113-0140
734-769-8010
800-673-6275

with support from the
U.S. Environmental Protection Agency

Copyright 2001 NSF International 40CFR35.6450.

Permission is hereby granted to reproduce all or part of this work, subject to the limitation that
users may not sell all or any part of the work and may not create any derivative work therefrom.
Contact the ETV Source Water Protection Pilot Manager at (800) NSF-MARK with any
questions regarding authorized or unauthorized uses of this work.

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FOREWORD

In 1995, the U.S. Environmental Protection Agency (EPA) instituted a program, the
Environmental Technology Verification Program (ETV), to verify the performance
characteristics of commercial-ready environmental technologies through the evaluation of
objective and quality-assured data. Managed by EPA's Office of Research and Development,
ETV was created to substantially accelerate the entrance of innovative environmental
technologies into the domestic and international marketplaces. ETV provides purchasers and
permitters of technologies with an independent and credible assessment of the technology they
are purchasing or permitting.

During its pilot phase, EPA has cooperatively managed twelve ETV pilots in conjunction with
partner organizations, including states, federal laboratories, associations, and private sector
testing and standards organizations. The pilots have focused on each of the major environmental
media and various categories of environmental technologies and have been guided by the
expertise of a Stakeholder Group. Stakeholder Groups consist of representatives of all
verification customer groups for the particular technology sector, including buyers and users of
technology, developers and vendors, state and federal regulatory personnel, and consulting
engineers. All technology verification activities are based on testing and quality assurance
protocols that have been developed with input from the major stakeholder/customer groups.

NSF International is an independent, not-for-profit organization, dedicated to public health,
safety, and protection of the environment. NSF develops standards, provides educational
services, and offers superior third-party conformity assessment services, while representing the
interests of all stakeholders. In addition to well-established standards-development and
certification programs, NSF specifically responds to and manages research projects, one-time
evaluations and special studies.

NSF is the verification partner organization for three pilots under EPA's ETV Program: Drinking
Water Systems, which has completed the pilot stage and is now a center, Wet Weather Flow
Technologies, and Source Water Protection Technologies. This Protocol for the Verification of
Mercury Amalgam Removal Technologies was developed under the Source Water Protection
Pilot, whose goal is to verify the performance of commercial-ready technologies used to protect
ground and surface waters from contamination. Testing conducted under the ETV program
using this protocol does not constitute an NSF or EPA certification of the product tested. Rather,
it recognizes that the performance of the equipment has been determined and verified by these
organizations.

Verification differs from certification in that it employs a broad, public distribution of test
reports and does not use pass/fail criteria. In addition, there are differences in policy issues
relative to certification versus verification. Certification, unlike verification, requires auditing of
manufacturing facilities, periodic retesting, mandatory review of product changes and use of the
NSF Mark. Both processes are similar, however, in regard to having standardized test methods

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and independent performance evaluations and test result preparation. This protocol is subject to
revision; please contact NSF to confirm this revision is current.

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ACKNOWLEDGEMENTS

EPA and NSF acknowledge and thank those persons who participated in the preparation and
review of this Protocol for the Verification of Mercury Amalgam Removal Technologies.
Without their hard work and dedication to the project, this document would not have been
approved through the process that has been set forth for this ETV project.

Protocol Writers

Lynne Maclennan	XCG Consultants Ltd.

NSF Staff

Thomas Stevens
Maren Roush
Bruce DeMaine

Project Manager, ETV Source Water Protection Pilot
Project Coordinator, ETV Source Water Protection Pilot
Manager, QA & Safety

EPA Staff

Raymond Frederick
Carolyn Esposito
Sam Hayes

EPA ETV Source Water Protection Pilot Manager
NRMRL-Ci QA Reviewer
NRMRL-Ci QA Reviewer

ETV Source Water Protection Pilot — Technolosv Panel Participants

Peter Berglund
Charles Bering

Metropolitan Council St. Paul, Minnesota
Massachusetts Water Resources Authority
University of Illinois - Chicago

Industrial Waste Division - Metropolitan Sewer District of

Greater Cincinnati

USEPA

James Drummond
Beverly Head

James Kreissl
Conrad Naleway
Tim Reber
Mark Stone

Argonne National Laboratory
Rebec LLC

Naval Dental Research Institute, Great Lakes

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GLOSSARY OF TERMS

Accuracy - a measure of the closeness of an individual measurement or the average of a number
of measurements to the true value and includes random error and systematic error.

Bias - the systematic or persistent distortion of a measurement process that causes errors in one
direction.

Commissioning - the installation of the mercury amalgam removal technology (free of mercury
residuals) and start-up of the technology using test site wastewater.

Comparability - a qualitative term that expresses confidence that two data sets can contribute to
a common analysis and interpolation.

Completeness - a qualitative term that expresses confidence that all necessary data have been
included.

Owner - the owner of a dental office used as a test site for verification testing.

Precision - a measure of the agreement between replicate measurements of the same property
made under similar conditions.

Protocol - a written document that clearly states the objectives, goals, scope and procedures for
the study. A protocol shall be used for reference during Vendor participation in the verification
testing program.

Quality Assurance Project Plan - a written document that describes the implementation of
quality assurance and quality control activities during the life cycle of the project.

Residuals - the waste streams, excluding final effluent, which are retained by or discharged
from the technology.

Representativeness - a measure of the degree to which data accurately and precisely represent a
characteristic of a population parameter at a sampling point or for a process conditions or
environmental condition.

Source Water Protection Stakeholder Advisory Group - a group of individuals consisting of
any or all of the following: buyers and users of mercury amalgam removal and other
technologies, developers and vendors, consulting engineers, the finance and export communities,
and permit writers and regulators.

Standard Operating Procedure - a written document containing specific procedures and
protocols to ensure that quality assurance requirements are maintained.

Technology Panel - a group of individuals with expertise and knowledge in mercury amalgam
removal technologies.

Test Plan - a written document that describes the procedures for conducting a test or study
according to the verification protocol requirements for the application of mercury amalgam
removal equipment at a particular test site. At a minimum, the Test Plan shall include detailed
instructions for sample and data collection, sample handling and preservation, precision,
accuracy, goals, and quality assurance and quality control requirements relevant to the particular
dental office test site.

Testing Organization - an independent organization qualified to conduct studies and testing of
mercury amalgam removal technologies in accordance with protocols and test plans. A list of
qualified Testing Organizations shall be maintained by the Verification Organization.

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Vendor - a business that assembles or sells mercury amalgam removal equipment.

Verification - to establish the evidence on the performance of mercury amalgam removal
technologies under specific conditions, following a predetermined study protocol(s) and test
plan(s).

Verification Organization - an organization qualified by USEPA to verify Test Plans and
Verification Reports, and to issue Verification Statements.

Verification Report - a written document prepared by the Testing Organization containing all
raw and analyzed data, all QA/QC data sheets, descriptions of all collected data, a detailed
description of all procedures and methods used in the verification testing, and all QA/QC results.
The Test Plan(s) shall be included as part of this document.

Verification Statement - a document that summarizes the Verification Report reviewed and
approved by the Verification Organization on behalf of USEPA, or directly by USEPA.

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ABBREVIATIONS AND ACRONYMS

ANSI	American National Standards Institute

ASQC	American Society for Quality Control

DQI	data quality indicators

ETV	Environmental Technologies Verification

MSDS	material safety data sheets

NSF	NSF International

O&M	operational and maintenance

ORD	Office of Research and Development

OSHA	Occupational Safety and Health Administration

QA	quality assurance

QAPP	quality assurance project plan

QC	quality control

QMP	quality management plan

SOP	standard operating procedure

TCLP	toxicity characteristic leaching procedure

USEPA	United States Environmental Protection Agency

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TABLE OF CONTENTS

FOREWORD	II

ACKNOWLEDGEMENTS	IV

GLOSSARY OF TERMS	V

ABBREVIATIONS AM) ACRONYMS	VII

1.0	INTRODUCTION	1

1.1	THE ENVIRONMENTAL TECHNOLOGIES VERIFICATION PROGRAM	1

1.2	OBJECTIVES 01 VERIFICATION TESTING	1

1.3	PURPOSE AM) SCOPE 01 PROTOCOL	2

1.4	VERIFICATION TESTING PROCESS	2

1.4.1	Planning	2

1.4.2	Verification Testing	3

1.4.3	Data Assessment and Reporting	3

1.5	POLICIES AND PROGRAM SPECIFICATIONS AND GUIDELINES	3

2.0	RESPONSIBILITIES OF INVOLVED AGENCIES	5

2.1	RESPONSIBILITIES 01 VENDOR	5

2.2	RESPONSIBILITIES OF TESTING ORGANIZATION	6

2.3	RESPONSIBILITIES 01 OWNER	6

2.4	RESPONSIBILITIES OF VERIFICATION ORGANIZATION	7

2.5	RESPONSIBILITIES 01 USEPA	7

2.6	RESPONSIBILITIES OF TECHNOLOGY PANEL	7

2.7	RESPONSIBILITIES OF STAKEHOLDER ADVISORY GROUP	7

3.0	TECHNOLOGY CAPABILITIES AND DESCRIPTION	8

3.1	TYPES OF EQUIPMENT	8

3.2	PERFORMANCE OBJECTIVES	8

3.3	ACCEPTABILITY I OR TESTING	8

4.0	TEST SITE DESCRIPTION AND ACCEPTANCE	10

4.1	SITE SUITABILITY	10

4.2	SITE ACCEPTANCE	11

5.0	EXPERIMENTAL DESIGN	12

5.1	PURPOSE AND SCOPE OF EXPERIMENTAL DESIGN	12

5.2	TEST PLAN DEVELOPMENT	12

5.3	INFLUENT CHARACTERIZATION	13

5.3.1	Introducti on	13

5.3.2	Objectives	13

5.3.3	Requirements	13

5.4	COMMISSIONING	18

5.4.1	Introducti on	18

5.4.2	Objectives	19

5.4.3	Requirements	19

5.5	VERIFICATION TESTING	19

5.5.1	Introducti on	19

5.5.2	Objectives	19

5.5.3	Requirements	20

6.0 QUALITY ASSURANCE AND QUALITY CONTROL	24

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6.1	VERIFICATION 01 TEST DATA	24

6.2	MANAGEMENT	25

6.3	MEASUREMENT AND DATA ACQUISITION	25

6.4	ASSESSMENT	25

6.5	CORRECTIVE ACTIONS	26

7.0	DATA MANAGEMENT, ANALYSIS AND PRESENTATION	27

7.1	DAT A MANAGEMENT	27

7.1.1	Manual Data Collection	27

7.1.2	Electronic Data Collection	27

7.2	DATA ANALYSIS AM) PRESENTATION	28

7.2.1	Flow Data	29

7.2.2	Treatment Performance Quality Data	29

7.2.3	Operations and Maintenance Parameters	30

7.2.4	Equations	30

7.3	VERIFICATION REPORT	31

8.0 ENVIRONMENTAL, HEALTH AND SAFETY PLAN	32

9.0 REFERENCES	33

APPENDIX A	34

TEST PLAN OUTLINE AND CONTENT REQUIREMENTS	34

1.0 OUTLINE OF THE TEST PLAN	35

2.0 OBJECTIVES AND DESCRIPTION OF VERIFICATION TESTING	35

3.0 VERIFICATION TESTING RESPONSIBILITIES	36

4.0 TECHNOLOGY DESCRIPTION	36

5.0	EXPERIMENTAL DESIGN	37

5.1	WORK PLAN FOR INFLUENT WASTEWATER CHARACTERIZATION	37

5.2	WORK PLAN FOR COMMISSIONING	38

5.3	VERIFICATION TESTING WORK PLAN AND EXPERIMENTAL DESIGN	38

6.0 PROCEDURES	39

7.0 QUALITY ASSURANCE PROJECT PLAN	39

8.0	DATA MANAGEMENT, ANALYSIS AND PRESENTATION	40

8.1	DATA MANAGEMENT	40

8.2	DATA ANALYSIS AM) PRESENTATION	40

9.0 ASSESSMENTS	40

10.0 APPENDICES 	41

LIST OF TABLES

Table 1: Summary of Influent Analytical Requirements	18

Table 2: Summary of Effluent and Residual Analytical Requirements	21

LIST OF FIGURES

Figure 1: Verification Testing Process	4

Figure 2: Dental Clinic Liquid-Ring Vacuum Pump System	15

Figure 3: Dental Clinic Turbine (Dry) Vacuum Pump System	16

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1.0	INTRODUCTION

This document contains the generic protocol to be employed for the verification testing of
mercury amalgam removal technologies used for the removal of mercury from dental wastewater
at individual dental offices. The protocol has been prepared under the United States
Environmental Protection Agency (USEPA) Environmental Technologies Verification (ETV)
program.

1.1	The Environmental Technologies Verification Program

The ETV Program was established by the United States Environmental Protection Agency
(USEPA) and is intended to:

•	evaluate the performance of innovative and commercially available environmental
technologies;

•	provide permit writers, buyers and users, among others, with objective information about
technology performance; and,

•	facilitate "real world" implementation of promising technologies.

The verification testing protocol is intended to serve as a template for conducting verification
tests for various technologies. The goal of the verification testing process is to generate high
quality data for verification of equipment performance.

The ETV Program is subdivided into twelve individual pilot projects, one of which is the Source
Water Protection Pilot. This Pilot includes the verification testing of mercury amalgam removal
technologies appropriate for the removal of amalgam and mercury from wastewater produced by
dental practices.

NSF International is overseeing the verification testing pilot project for mercury amalgam
removal technologies with the participation of vendors, under the sponsorship of the USEPA
Office of Research and Development (ORD). The role of NSF is to provide technical and
administrative leadership in conducting the testing.

It is important to note that verification of the equipment does not mean that the equipment is
"certified" by NSF or USEPA. Instead, the verification testing pilot projects are a formal
mechanism by which the performance of equipment can be determined by these two Agencies,
and which can result in the issuance of a Verification Statement by NSF/USEPA.

1.2	Objectives of Verification Testing

The general and specific objectives of the proposed verification testing should be specific to the
treatment claims made by the Vendor and the desired Verification Statement.

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In general, the objectives of verification testing shall be to determine the following:

•	the performance of a specific mercury amalgam removal technology relative to the
Vendor's stated range of technology capabilities, operating under field conditions;

•	the necessary inputs (power, chemicals, labor, etc.) and the operating costs of the
technology; and,

•	the range of operating conditions and the ease of operation and maintenance of the
equipment.

Verification testing conducted at a single site may not represent the complete range of treatment
capabilities of the technology being tested. However, it will provide quality assurance to enable
potential users of the technology to determine the applicability of the technology for the
treatment of similar dental wastewaters.

1.3	Purpose and Scope of Protocol

This document contains guidance to Testing Organizations, Vendors and test facility Owners for
verification testing of mercury amalgam removal technologies. Instructions are provided for
preparation of Test Plans, execution of testing, data management and analysis, and reporting.

Adherence to the guidelines presented in this document is intended to provide sufficient
information to the Verification Organization to make a determination about the performance of
particular technologies tested at specific sites, and can lead to issuance of a Verification
Statement.

1.4	Verification Testing Process

The verification testing process consists of three phases, as shown in Figure 1. These three
phases are briefly described below.

1.4.1 Planning

Prior to the verification testing of any mercury amalgam removal technology, the testing
program must be properly planned. The planning phase involves a number of characterization
activities culminating in the preparation of a site specific Test Plan.

The main activities involved in the planning stage are as follows:

•	identifying the individuals or organizations that will be involved in the testing, and the
responsibilities of all parties;

•	identifying the general and specific objectives of the testing;

•	identifying a suitable test site;

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•	designing the experimental program for the testing, including sampling, analysis and
scheduling;

•	determining the quality assurance and quality control program;

•	determining how data will be handled and verified; and,

•	preparing a site specific Test Plan.

1.4.2	Verification Testing

This phase includes the actual verification testing activities, using the activities specified in the
Test Plan. The mercury amalgam removal technology will be operated in order to assess its
ability to meet the objectives identified in the planning stage.

1.4.3	Data Assessment and Reporting

This last phase includes all data analysis and data verification steps, as well as Verification
Report preparation.

1.5 Policies and Program Specifications and Guidelines

Figure 1 shows the relationship of the verification testing process to USEPA policies and
consensus standards such as ANSI/ASQC E4(1) and quality management plans (QMPs).

The ETV QMP(2) provides specifications and guidelines on test-specific activities. The Source
Water Protection Technologies Pilot QMP(3) addresses the quality systems for testing activities.

The verification testing process shall be in accordance with USEPA and ETV policies,
specifications and guidelines. Further information on USEPA policies and ETV Program QMPs
is available from NSF/USEPA and on the ETV website (http://www.epa.gov/etv).

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Figure 1: Verification Testing Process

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2.0	RESPONSIBILITIES OF INVOLVED AGENCIES

The testing of mercury amalgam removal technologies will usually involve seven parties, each
with responsibilities during verification testing. Agencies that will be involved include the
following:

•	the vendor of the technology (Vendor);

•	the Testing Organization;

•	the dental office test site owner (Owner);

•	the Verification Organization;

. the USEPA;

•	the Technology Panel; and,

•	the Stakeholder Advisory Group.

The responsibilities of each party are presented in the following sub-sections.

Due to their approval and permitting powers, regulatory agencies can have an important role to
play following verification testing. It is therefore recommended that the appropriate local and
state regulatory agencies be advised of proposed testing, and that they be requested to indicate
their particular requirements or issues. In turn, the Testing Organization, in conjunction with the
Vendor and Owner, should incorporate regulatory agency requirements and issues within the site
specific Test Plan as much as possible. In particular, the removal of other amalgam metals
(copper, zinc and silver) may be of interest to Publicly Owned Treatment Works.

2.1	Responsibilities of Vendor

The Vendor shall have the following responsibilities:

•	initiation of application to ETV for testing;

•	selection of the Testing Organization from the Verification Organization qualified list;

•	provision of verification testing objectives to be incorporated into the Test Plan;

•	selection of the test site;

•	provision of any available site data (e.g., representative historical flow and
characterization data);

•	provision of complete, field-ready equipment and the operations and maintenance
(O&M) manual(s) typically provided with the technology (including instructions on
installation, start-up, operation and maintenance) for verification testing;

•	provision of existing relevant performance data for the technology if it has been
tested/operated at other locations;

•	provision of logistical and technical support as required;

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•	provision of assistance to the Testing Organization on the operation and monitoring of
the technology during the verification testing on an "as needed" basis; and,

•	review and comment on the site-specific Test Plan.

2.2	Responsibilities of Testing Organization

The Testing Organization shall have the following responsibilities:

•	preparation of the site specific Test Plan;

•	conducting Verification Testing, according to the Test Plan;

•	operation and maintenance of the technology in accordance with the Vendor's O&M
manual(s);

•	controlling access to the area where verification testing is being carried out;

•	maintaining safe conditions at the test site for the health and safety of all personnel
involved with verification testing;

•	scheduling and coordinating all the activities of all verification testing participants,
including establishing a communication network and providing logistical and technical
support on an "as needed" basis;

•	resolve any quality concerns that may be encountered and report all findings to the
Verification Organization;

•	managing, evaluating, interpreting and reporting on data generated by verification testing;

•	evaluation and reporting on the performance of the technology; and,

•	if necessary, document changes in plans for testing and analysis, and notify the
Verification Organization of any and all such changes before changes are executed.

2.3	Responsibilities of Owner

The Owner shall have the following responsibilities:

•	provision of logistical and technical support as may be agreed upon by the Testing
Organization, Vendor and Owner;

•	provision of assistance during testing as may be agreed upon by the Testing Organization,
Vendor and Owner;

•	notifying the Testing Organization of any significant changes in dental practices that
could affect the volume and composition of wastewater produced at the site; and,

•	record the tooth number and number of amalgam surfaces placed and removed, the
flushing procedure (chemicals used, volume and frequency) and when chairside traps or
vacuum filters are changed.

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2.4	Responsibilities of Verification Organization

The Verification Organization shall have the following responsibilities:

•	qualification of Testing Organizations;

•	provision of a list of qualified Testing Organizations;

•	provision of a list of approved analytical laboratories;

•	reviewing and commenting on the site specific Test Plan;

•	approving the Test Plan in conjunction with reviewers from the Technology Panel;

•	carrying out an on-site audit of test procedures;

•	reviewing, commenting on and disseminating the Verification Report;

•	approving the Verification Report in conjunction with the Stakeholder Advisory Group;

•	preparation and dissemination of the Verification Statement; and,

•	in some cases act as the testing organization/analytical facility.

2.5	Responsibilities of USEPA

This protocol was developed with financial and quality assurance assistance from the
Environmental Technology Verification (ETV) Program, which is overseen by the USEPA. Any
Verification Report developed under the ETV Program using this protocol will be subject to the
approval of the ORD laboratory director. The USEPA shall have technical and quality assurance
review responsibilities throughout the various phases associated with the verification of mercury
amalgam removal technologies, including:

•	Verification Test Plan development;

•	Verification Report development; and

•	Verification Statement development.

2.6	Responsibilities of Technology Panel

Representatives from the Technology Panel will assist the Verification Organization in
reviewing and commenting on the site specific Test Plan.

2.7	Responsibilities of Stakeholder Advisory Group

The Source Water Protection Stakeholder Advisory Group assists the Verification Organization
in the approval of the Verification Report.

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3.0	TECHNOLOGY CAPABILITIES AND DESCRIPTION

3.1	Types of Equipment

For the purpose of this Verification Testing program, mercury amalgam removal technologies
are defined as pre-engineered, self-contained treatment units that are used for treatment of dental
wastewater at individual dental offices. They will provide for the removal of amalgam and
mercury, rendering the wastewater suitable for disposal to the sanitary sewer system.

3.2	Performance Objectives

The performance objectives of the technology are provided by the Vendor's stated claim of
technology capabilities. In addition to the Vendor's claims, there is a minimum requirement for
performance objectives for acceptability to receive a Verification Statement. These are the core
treatment performance parameters to be measured for all technologies tested.

The performance evaluation of wastewater treatment technologies is based on the assessment
through site specific testing of the following:

•	treatment performance, measured by removal efficiencies for specific wastewater quality
parameters under a normal range of influent conditions; and,

•	O&M performance, measured by a number of quantitative and qualitative O&M
indicators, including the use of consumables (i.e., water, chemicals and power), labor
requirements, residual generation, ease of operation, and any other factors.

The specific wastewater quality parameters used to assess treatment performance include two
categories of parameters.

•	The core parameters are wastewater quality parameters used in testing at all sites. The
core parameter list is the minimum required for testing purposes.

•	Additional parameters may be necessary to verify the Vendor's claims. The Testing
Organization shall select additional parameters in conjunction with the Vendor.

The core and additional parameters required for influent and effluent wastewater streams are
discussed in Sections 5.3 and 5.5, respectively. O&M parameters are discussed in Section 5.5.

3.3	Acceptability for Testing

The Verification Organization and USEPA are committed to fairness for all technology vendors.
However, the Verification Organization and USEPA reserve the right to reject offered mercury

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amalgam removal technologies that do not have a demonstrable application for dental office
wastewater treatment or which, for technical reasons, cannot be accommodated in the evaluation.

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4.0	TEST SITE DESCRIPTION AND ACCEPTANCE

The Vendor may select or work with the Verification Organization to identify the site(s) where
verification testing will be performed. The criteria for site selection shall be consistent with the
Vendor-specified treatment performance, operating levels and known limitations for the
technology.

The wastewater at the test site should challenge the capabilities of the technology with respect to
hydraulic and mass loadings, but shall not be beyond the reasonable range of flow and
wastewater quality parameters suitable for treatment by the technology as identified by the
Vendor.

Configuration of the technology to be tested shall be compatible with the test site with minimal
modifications and disturbance to the operation of the dental office, at the discretion of the
Vendor and with the approval of the site Owner. The technology shall be installed such that the
settlement of suspended solids between operatories (chairs) and the inlet of the of the technology
is minimized. The Vendor shall be responsible for leaving the site in a condition acceptable to
the Owner.

4.1	Site Suitability

The test site shall be a general dentistry office that places and/or removes amalgams. A site shall
be considered suitable by the Verification Organization if it places and/or removes a minimum of
forty amalgam surfaces per week and if the line flushing procedure will not affect influent
characterization or verification testing (due to volume or chemicals used).

As a minimum, line flushing at a test site shall be carried out twice a week and use
approximately one litre of flushing solution (water plus any flushing chemical used) per chair for
each flush. Those sites that use sodium hypochlorite-based or ammonium chloride-based
chemicals for flushing are not suitable for verification testing due to the effect of these chemicals
on mercury solubility. Sites that do not routinely follow these flushing requirements may be
considered acceptable if flushing is carried out as specified for a minimum of five weeks prior to
influent characterization and throughout the influent characterization and verification testing
periods.

Other site suitability factors that should be taken into account when selecting sites are the space
availability for the installation of the technology and the effect of the vacuum system in place on
the installation of the technology.

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4.2 Site Acceptance

The Verification Organization shall be responsible for accepting site locations for Verification
Testing. As a minimum, the Vendor shall provide the Verification Organization with the
following information to facilitate site acceptance:

•	the site location and contact details for the Owner;

•	the number of chairs at the dental office;

•	the average number of amalgams placed and/or removed per week;

•	the line flushing procedure (frequency and volume) and flushing chemical(s) used;

•	a schematic of the site showing the location of any existing mercury amalgam removal
system and the planned location of the mercury amalgam removal technology to be
tested;

•	a description of how the mercury amalgam removal technology will be installed, how the
influent will be diverted to the technology, and how effluent and residues will be
disposed of;

•	a schematic showing the technology and sampling equipment elevations to illustrate any
changes in vertical flow dynamics from the existing plumbing arrangements at the test
site;

•	the proposed influent and verification testing monitoring and sampling locations;

•	representative historical influent wastewater flow and quality data, if available; and,

•	any other relevant or unique features of the test site.

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5.0	EXPERIMENTAL DESIGN

5.1	Purpose and Scope of Experimental Design

The preparation of the experimental design is the initial planning stage of verification testing and
includes the development of the Test Plan. The purpose of the experimental design is to define
the test conditions, performance measures, measurement requirements and data quality indicators
for verification testing. The experimental design, which is developed by the Testing
Organization, shall reflect the general and specific objectives of the proposed verification testing.

5.2	Test Plan Development

Before verification testing can begin, the Testing Organization shall prepare the site specific Test
Plan that presents the specific objectives and tasks for verification testing, the testing
experimental design, and the specific procedures to be followed throughout testing. A Test Plan
shall be developed for each site where testing occurs.

The Test Plan shall be prepared in conjunction with the Vendor and Owner, and shall be
reviewed by representatives from the Technology Panel, by the Verification Organization, and
by USEPA prior to implementation. Any substantive comments from the review of the Test Plan
shall be addressed in a revised Test Plan to the satisfaction of the Verification Organization and
USEPA.

The specific contents of the Test Plan can vary from site to site. As a minimum, the Test Plan
shall contain the following components.

•	Title Page and Table of Contents

•	Test Plan Approval by Project Participants

•	Executive Summary

•	Objectives and Description of Verification Testing

•	Verification Testing Responsibilities

•	Technology Description

•	Experimental Design

•	Field Procedures

•	Sampling Procedures

•	Analytical Procedures

•	Quality Assurance Project Plan

•	Data Management, Analysis and Presentation

•	Assessments

•	References

•	Appendices:

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Historical Influent Flow and Wastewater Quality Records
O&M Manual(s) Supplied by the Vendor

Environmental, Health and Safety Plan and Material Safety Data Sheets
Other Documents and Applicable Data
The content requirements for the Test Plan are discussed in more detail in Appendix A.

5.3 Influent Characterization

5.3.1	Introduction

The purpose of influent characterization is to obtain an understanding of the influent wastewater
flow and quality characteristics before verification testing of the technology is carried out.

Influent characterization shall be carried out for a minimum five-week period before the
technology is installed for testing. Results of this characterization will be used to define system
operating conditions and process monitoring requirements. The influent characterization results
shall be presented in the Test Plan.

5.3.2	Objectives

The objectives of influent characterization are to:

•	determine the daily flow of the wastewater stream to be used for verification testing;

•	evaluate the concentrations and daily mass loading of target constituents;

•	determine specific operational conditions for the technology to be tested;

•	determine process monitoring requirements;

•	record and document all influent characterization conditions and results; and,

•	identify any required modifications to the Test Plan (e.g., sampling method).

5.3.3	Requirements

The Testing Organization shall prepare a work plan to be included as part of the Test Plan that
addresses the following influent characterization requirements:

•	the location of sampling;

•	the sampling method;

•	the frequency of sampling; and,

•	the data to be collected.

Guidance on these requirements is presented in the following sub-sections.

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Sampling Location

Sampling for quality characterization of the influent shall be carried out at a representative
location, at or near the location that the technology will be installed, and should be before the
dental wastewater has mixed with any other building wastewater streams. Sampling for influent
characterization shall be carried out at a similar elevation to the inlet of the technology to be
tested after installation to minimize any difference in solids settlement in the vacuum system
before and after verification testing.

For dental offices using wet ring pumps in the vacuum system, sampling will be upstream of the
vacuum filter. Samples will be taken after the air water separator upstream of the vacuum pump
for dry vacuum pump systems. Any modifications to the sampling location requirements will be
detailed in the Test Plan, together with the rationale as to why the sampling location was
modified. The location of influent sampling shall be identified in the Test Plan.

New chairside traps will be installed just before the start of the influent characterization program.
Sampling Method

All sampling equipment used shall be non-metallic and free of material that may contain metals.
Influent shall be diverted into a container constructed of polypropylene, fluoropolymer,
borosilicate glass or other approved material. The minimum volume of the container shall be
sufficient to hold the estimated maximum influent wastewater flow over 36 hours (including line
flushing). The container shall not interfere with normal operation of the dental office vacuum
wastewater disposal system. The container shall be kept under vacuum during collection for wet
vacuum pump systems, unless sampling is required to be carried out downstream of the vacuum
pump (refer to "Sampling Location" above).

The container shall be used to collect all of the influent over a 24 hour period. In the event that
the liquid volume collected in the container is at or above the outlet elevation for the container,
the sample shall be considered unsuitable for analysis and discarded. The container shall have an
overflow into the existing vacuum system (or floor drain where appropriate) in the event that the
wastewater volume exceeds the container volume between sampling events.

The container contents shall be collected every 24 hours when the dental office is operating. The
total volume collected shall be transferred within four hours to a settling tank capable of
separating the solid fraction from the liquid fraction. The settling tank shall be non-metallic or
coated with a material free of metals. The settling tank shall be constructed in such a way to
allow settled solids to be collected from the bottom of the tank.

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Figure 2: Dental Clinic Liquid-Ring Vacuum Pump System

* separator with air vent may
be required by plumbing code

water supply

0}

chairside trap 0.7 mm

vacuum pump

\W/

vacuum filter

vent

optional

air/water

separator*

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Figure 3: Dental Clinic Turbine (Dry) Vacuum Pump System

vent

vacuum pump

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The sampling container shall be rinsed with distilled or deionized water containing less than 0.2
|_ig/L of mercury and the rinse water also transferred to the settling tank. The volume of water
used for container rinsing shall be recorded and taken into account when analyzing the samples.

The sample and rinse water shall be settled for a minimum of eight hours and maximum of 16
hours. The total solids settled shall be collected for analysis. The supernatant will be decanted
and mixed sufficiently to ensure suspension of any remaining solids before it is sub-sampled for
analysis. Refer to Table 1 for the solid and liquid fraction analysis required.

The method used for total sample collection, sample settlement, sampling of the solid fraction
and subsampling of the liquid fraction shall be described in the Test Plan. The methods
employed for sample collection, preservation and storage shall comply with USEPA Methods(4)
or Standard Methods(5). Any modifications to USEPA or Standard Methods shall be detailed,
together with the rationale as to why the method was modified. Details of sampling methods and
storage and preservation techniques shall be documented in the Test Plan.

Thorough cleaning of the sampling container(s) and any fittings is required at the end of influent
characterization. Cleaning will involve scraping to remove any solids adhered to the surface of
the container or fittings, rinsing with mercury-free water and a final 1% nitric acid rinse using
mercury-free water. Any solids collected during cleaning and all water used during cleaning
shall be settled and sampled as for influent characterization samples for analysis. The method
used to clean the sampling container shall be described in the Test Plan.

Sampling Frequency and Data Collection

A minimum of 25 samples shall be collected over a minimum five-week period. Table 1 presents
the core influent parameters to be measured for the solids collected and liquid sub-sample. The
influent shall be characterized for all core performance parameters. There may be a need to
monitor additional parameters, in line with Vendor's claims (e.g., copper, zinc, silver). These
parameters shall be selected by the Testing Organization in agreement with the Vendor.

Industry standard procedures (USEPA Methods(4) or Standard Methods(5)) shall be employed for
sample analysis. Any modifications to USEPA or Standard Methods will be detailed, together
with the rationale as to why the method was modified. All samples shall be analyzed in triplicate
for mercury. For solid mercury analysis, the method used for digestion should be validated using
a standard sample. The source of the standard sample will be specified by the verification
organization. Details of analytical methods and field and laboratory QA/QC procedures shall be
documented in the Test Plan. The laboratory to be used for analysis shall be approved by the
Verification Organization.

A record of the tooth number and number of amalgam surfaces placed and removed, the flushing
procedure (chemicals used, volume and frequency) and when chairside traps are changed will be

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recorded for the period of influent characterization. The procedure used to record and report this
information shall be provided in the Test Plan.

In some cases, existing data may be available such that the Testing Agency can forego some of
the influent quality characterization as part of verification testing. Such data would include
existing influent characterization data for the test site. In the event that existing data are
employed, the Testing Agency must present details of the data collection procedures, including
monitoring and sampling methods, quality assurance (QA) and quality control (QC), and data
analysis and reporting procedures in the Test Plan for approval by the Verification Organization.
A discussion of QA and QC requirements is provided in Section 6.

Table 1: Summary of Influent Analytical Requirements

Parameter

Solid Fraction1

Liquid Fraction1

Core parameters





Volume (liters)2



V

pH



V

Approximate volume of solids (particle(s)) (mL)3

V



Solid (Particle) mercury (mg)4

V



Total mercury (mg/L)5



V

Soluble mercury (mg/L)5



V

Supplemental parameters6

V

V

Note:





1. Minimum of 25 samples, each a complete sample of all the waste generated over a 24 hour period.

2. Total volume of wastewater and rinse water recorded separately.



3. Volume estimated after as much as possible of the liquid fraction has been removed.

4. Digestion required before analysis.





5. Analysis carried out on a representative sub-sample of the liquid fraction.



6. To be determined by the Testing Organization

in agreement with the Vendor.

5.4 Commissioning

5.4.1 Introduction

The wastewater treatment technology to be tested shall be commissioned in accordance with
Vendor instructions provided in the O&M manual(s), which shall be incorporated into and
attached to the Test Plan. The Vendor shall indicate a length of time required for commissioning.
The Vendor shall specify the factors that may affect commissioning and modifications or
procedures that may be required to achieve operation. This information shall also be
incorporated into the Test Plan. The commissioning conditions and observations shall be
presented in the final Verification Testing report.

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5.4.2	Objectives

The objectives of the commissioning task are to:

•	commission the mercury amalgam removal technology in accordance with the Vendor's
O&M manual(s);

•	make modifications as needed to achieve operation; and,

•	record and document all commissioning conditions and observations.

5.4.3	Requirements

The Testing Organization shall prepare a work plan to be included as a part of the Test Plan that
addresses the following commissioning requirements:

•	The Testing Organization shall commission the mercury amalgam removal technology in
accordance with the Vendor's O&M manuals(s).

•	The mercury amalgam removal technology installed shall be clean and free of any
mercury residuals.

•	The Testing Organization shall conduct commissioning for the period specified by the
Vendor. Any modifications needed to ensure operation of the technology shall be
identified.

•	The Testing Organization shall document conditions and observations made throughout
the commissioning period. These details are to be presented in the Verification Report.

5.5 Verification Testing

5.5.1	Introduction

The treatment performance of the technology under field conditions shall be evaluated and
documented during verification testing. This shall be accomplished by sampling effluent
generated by the technology and sampling residuals retained by the technology. O&M
conditions shall also be monitored and documented. Verification testing conditions,
observations and results shall be presented in the Verification Report.

5.5.2	Objectives

The objectives of verification testing are to:

•	evaluate the treatment performance of the technology, relative to removal of specific
parameters, operating under Vendor-specified conditions;

•	evaluate the technology O&M conditions; and,

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•	record and document test conditions, observations and results.

5.5.3 Requirements

The Testing Organization shall prepare a work plan to be included as part of the Test Plan that
addresses the following verification testing requirements:

•	the location of sampling;

•	the effluent sampling method;

•	the residuals sampling method;

•	the frequency of sampling; and,

•	the data to be collected

Sampling Locations

Sampling for quality characterization of the effluent shall be carried out at a representative
location at or near the outlet of the technology, and before the dental wastewater has mixed with
any other building wastewater streams. Sampling shall be carried out at a similar elevation to
that for influent characterization to minimize any difference in solids settlement in the vacuum
system before and after verification testing. The location of effluent sampling shall be clearly
identified in the Test Plan.

New chairside traps shall be installed just before the start of verification testing.

Effluent Sampling Method

All sampling equipment used shall be non-metallic and free of material that may contain metals.
Effluent shall be diverted into a container constructed of polypropylene, fluoropolymer,
borosilicate glass or other approved material. The minimum volume of the container shall be
sufficient to hold the estimated maximum effluent wastewater flow over 36 hours (including line
flushing). The container shall not interfere with normal operation of the dental office vacuum
wastewater disposal system. The container shall be kept under vacuum during collection for wet
vacuum pump systems, unless sampling is required to be carried out downstream of the vacuum
pump.

The container shall be used to collect all of the effluent over a 24 hour period. In the event that
the liquid volume collected in the container is at or above the outlet elevation for the container,
the sample shall be considered unsuitable for analysis and discarded. The container will have an
overflow into the existing vacuum system (or floor drain where appropriate) in the event that the
wastewater volume exceeds the container volume between sampling events.

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The container contents shall be collected every 24 hours when the dental office is operating. The
total volume collected shall be transferred within four hours to a settling tank capable of
separating the solid fraction from the liquid fraction. The settling tank shall be non-metallic or
coated with a material free of metals. The settling tank will be constructed in such a way to
allow settled solids to be collected from the bottom of the tank.

The sampling container will be rinsed with distilled or deionized water containing less than 0.2
|_ig/L of mercury and the rinse water also transferred to the settling tank. The volume of water
used for container rinsing will be recorded and taken into account when analyzing the samples.

The sample and rinse water shall be settled for a minimum of eight hours and maximum of 16
hours. The total solids settled shall be collected for analysis. The supernatant shall be decanted
and mixed sufficiently to ensure suspension of any remaining solids before it is sub-sampled for
analysis. Refer to Table 2 for the solid and liquid fraction analysis required.

Table 2: Summary of Effluent and Residual Analytical Requirements

Parameter

Effluent1'2

Residuals



Solid
Fraction

Liquid
Fraction

Solid
Fraction

Liquid
Fraction

Core parameters









Volume (litres)3



V



V

pH



V



V

Approximate volume of solids (particle(s)) (mL)4

V



V



Solid (particle) mercury (mg)5

V



V



Total mercury (mg/L)6



V



V

Soluble mercury (mg/L)6



V



V

TCLP7





V



Supplemental parameters8

V

V

V

V

Note:









1. Minimum of 25 samples, except for TCLP analysis.







2. Collect all of the effluent over a 24 hour period.







3. Total volume of wastewater and rinse water recorded separately.





4. Volume estimated after as much as possible of the liquid fraction has been removed.



5. Digestion required before analysis.









6. Analysis carried out on a representative sample of the liquid fraction.





7. Toxicity characteristic leaching potential, as per USEPA method SW 846 1311. Required for minimum of
one sample.

8. To be determined by the Testing Organization

in agreement with the Vendor.





The method used for total sample collection, sample settlement, sampling of the solid fraction
and subsampling of the liquid fraction shall be described in the Test Plan. The methods
employed for sample collection, preservation and storage shall comply with USEPA Methods(4)
or Standard Methods(5). Any modifications to USEPA or Standard Methods shall be detailed,

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together with the rationale as to why the method was modified. Details of sampling methods and
storage and preservation techniques shall be documented in the Test Plan.

Thorough cleaning of the sampling container(s) and any fittings is required at the end of
verification testing. Cleaning shall involve scraping to remove any solids adhered to the surface
of the container or fittings, rinsing with mercury-free water and a final 1% nitric acid rinse using
mercury-free water. Any solids collected during cleaning and all water used during cleaning
shall be settled and sampled for analysis, as for influent characterization samples. The method
used to clean the sampling container shall be described in the Test Plan.

Residuals Sampling Method

All sampling equipment used should be non-metallic and free of material that may contain
metals. Residuals retained by the technology shall be sampled once a week, unless the Vendor
indicates otherwise. For those technologies where it is not feasible to regularly collect residuals
samples for some or all of the equipment, e.g., cartridge filters, the residuals shall be sampled at
the end of verification testing or when the equipment containing the residuals is replaced,
whichever occurs first.

All residual solids shall be collected. If liquids are present with the residual solids, the residuals
will be settled as in Section 5.5.3 above to separate the liquids from the solids. The methods
used for collecting residual samples and processing shall be described in the Test Plan.

USEPA Methods(4) or Standard Methods(5) shall be employed for sample collection, preservation
and storage. Any modifications to USEPA or Standard Methods shall be detailed, together with
the rationale as to why the method was modified. Details of sampling methods and storage and
preservation techniques shall be documented in the Test Plan.

Sampling Frequency and Data Collection

A minimum of 25 effluent samples shall be collected over a minimum five-week period. Table 2
presents the core effluent and residual parameters to be measured. The effluent and residual
samples shall be characterized for all core performance parameters. There may be a need to
monitor additional parameters, in line with Vendor's claims (e.g., copper, zinc, silver). These
parameters shall be selected by the Testing Organization in agreement with the Vendor.

Industry standard procedures (USEPA Methods(4) or Standard Methods(5)) shall be employed for
sample analysis. Any modifications to USEPA or Standard Methods shall be detailed, together
with the rationale as to why the method was modified. All samples shall be analyzed in triplicate
for mercury. For solid mercury analysis, the method used for digestion should be validated using
a standard sample. Details of analytical methods and field and laboratory QA/QC procedures

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shall be documented in the Test Plan. The laboratory to be used for analysis must be approved
by the Verification Organization.

A record of the tooth number and number of amalgam surfaces placed and removed, the flushing
procedure (chemicals used, volume and frequency) and when chairside traps are changed shall be
recorded for the period of verification testing. The procedure used to record and report this
information shall be provided in the Test Plan.

In some cases, existing data may be available such that the Testing Agency can forego some of
the quality characterization as part of verification testing. Such data include test data from
previous studies for the technology. In the event that existing data are to be employed, the
Testing Agency must present details of the data collection procedures, including monitoring and
sampling methods, quality assurance (QA) and quality control (QC), and data analysis and
reporting procedures in the Test Plan for approval by the Verification Organization. A
discussion of QA and QC requirements is provided in Section 6.

Operations and Maintenance Performance

Both quantitative and qualitative performance indicators shall be evaluated to assess test
equipment O&M performance. The Testing Organization shall prepare O&M performance
indicators in conjunction with the Vendor.

Qualitative O&M performance indicators shall include, but are not limited to, the following:

•	observations regarding ease of operation;

•	observations regarding the effect of the technology, if any, on the operation of the
vacuum system;

•	a log of any operating problems recorded during testing;

•	quality of the O&M manual (e.g., actual O&M compared to that indicated in the manual,
clarity of instructions); and,

•	observations regarding labor requirements.

Quantitative O&M performance indicators shall include the following:

•	duration (in hours) of typical clean-out operations (if any);

•	frequency and duration (in hours) of any preventative or breakdown maintenance
activities;

•	electrical consumption (if any) for all unit processes, measured as kilowatt hours
consumed and the number of hours the equipment was operational, where possible;

•	chemical consumption (if any) for all unit processes, measured as kg per day; and,

•	records of any other consumables used by the technology over the test period.

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6.0	QUALITY ASSURANCE AND QUALITY CONTROL

QA activities and procedures for the verification testing shall be provided in a Quality Assurance
Project Plan (QAPP). The QAPP shall provide information on data review, validation, and
verification requirements, including the criteria used to review and validate data, validation and
verification methods, and reconciliation with data quality objectives.

The QAPP shall apply to all organizations involved in verification testing, including analytical
laboratories. The Testing Organization shall have the primary day-to-day responsibility for
ensuring that all individuals involved in verification testing comply with QA/QC procedures.
The Verification Organization Manager of Corporate QA and Safety or a designee shall monitor
and audit subcontracting laboratories in accordance with their corporate Quality Assurance
Manual, and, for Verification Testing activities conducted under the ETV Source Water
Protection Pilot, the Source Water Protection Pilot Quality Management Plan. A copy of the
Test Plan, including the QAPP, shall be forwarded to all parties involved with Verification
Testing, including analytical laboratories.

Reference shall be made to USEPA's Guidance for Quality Assurance Project Plans(6) and
Guidance for the Data Quality Objectives Process(7).

6.1	Verification of Test Data

All performance measurements carried out should be verifiable by a statistical analysis of the
data. As part of the assessment of data quality, six data quality indicators (DQIs) can be used to
interpret the degree of acceptability or utility of the data. The QAPP shall include a protocol for
assessing the following DQIs (refer to Glossary of Terms for definitions), and acceptable limits
and criteria for each of these indicators.

The DQIs include the following:

•	precision;

•	bias;

•	accuracy;

•	representativeness;

•	comparability; and,

•	completeness.

The Testing Organization shall determine acceptable values or qualitative descriptors for all
DQIs in advance of verification testing as part of the experimental design. The assessment of
data quality will require specific field and laboratory procedures to determine the data quality
indicators. All details of DQI selection and values shall be documented in the QAPP.

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6.2	Management

The QAPP shall include documentation on the management of the project, the project history
and objectives, and the responsibilities of each of the participants. The purpose of this element is
to ensure that the project approach and goals are clearly stated and understood by all participants.
This area shall include a list of individuals involved in the project, their roles and
responsibilities, a concise definition of the purpose of the study, a project schedule including a
task chart, documentation of the data quality objectives, special training and certification
requirements, and a complete list of required documentation for the study.

6.3	Measurement and Data Acquisition

The QA discussion shall include specific information on all aspects of the experimental design
including a detailed description of each component. Specific requirements in the area of
measurement and data acquisition are described below.

•	A schedule of project sampling, analysis, and data peer-review activities shall be
provided.

•	Any assumptions made in the design of the experiment and all procedures for locating
and selecting environmental samples shall be documented.

•	Any non-standard sampling or measurement techniques and equipment used to assess the
potential impact on the representativeness of the data generated shall be validated.

•	The requirements for sample handling and custody in the field, laboratory and in
transport shall be described. The description shall include examples of sample labels,
custody forms, and sample custody logs.

•	Analytical methods, equipment and the specific performance for each method shall be
documented. Reference may be made to USEPA Methods(4) or Standard Methods(5).

•	Required measurement quality control checks for both the field and the laboratory shall
be identified. Information presented shall include the frequency of each type of QC
check and references for the procedures used to calculate each of the QC statistics.

•	All equipment calibration requirements including standards for calibration, and
calibration methods, shall be identified.

•	Any types of data needed for project implementation obtained from non-measurement
sources shall be identified, including definition of acceptance criteria and discussion on
the limitations on the use of any such data.

6.4	Assessment

The QAPP shall include a detailed section on the methods to be used to assess the effectiveness
of the implementation of the QA/QC activities. Specifically, this section shall provide
information on the types of assessments to be completed, description of response actions, and
details on the types of reports to management to be completed.

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The number, frequency and type of assessment activities to be used in the project shall be
specified including a definition of the scope of the authority of the Testing Organization
assessors and when they are authorized to act, how responses to non-conforming conditions will
be addressed, and the individuals responsible for implementation of the response action.

6.5 Corrective Actions

Each Test Plan shall include a corrective action plan. This plan shall include the predetermined
acceptance limits, the corrective action to be initiated whenever such acceptance criteria are not
met, and the names of the individuals responsible for implementation. Routine corrective action
may result from common monitoring activities, such as:

•	Performance evaluation audits

•	Technical systems audits

Ultimately, responsibility for project quality assurance/quality control (QA/QC) during
implementation of this protocol rests with the Verification Organization, specifically the
Verification Organization Project Manager, with appropriate input from the Verification
Organization QA/QC Manager. However, immediate QA/QC for individual tasks (e.g. sample
collection, handling, preparation, and analysis) rests with the individuals and organization
performing the task at hand, as described in this chapter and throughout the protocol. The
Verification Organization Project Manager will coordinate oversight and/or audits of these tasks
with the Testing Organization Project Manager to ensure that the Test Plan is being executed as
written, and that nonconformances are appropriately reported and documented.

Corrective action shall be taken whenever a nonconformance with the Test Plan occurs.
Nonconformances can occur within the realm of sampling procedures, sample receipt, sample
storage, sample analysis, data reporting, and computations.

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7.0	DATA MANAGEMENT, ANALYSIS AND PRESENTATION

Data that will be generated by Verification Testing include, but are not limited to, flow data,
influent and effluent wastewater quality data, residuals data, treatment performance of the
technology under specific operating conditions, and O&M parameters. These data will be
managed, analyzed and presented as described in the following sub-sections.

7.1	Data Management

Verification testing will generate a significant amount of data. The Test Plan shall present the
procedures to be followed for data collection, recording, and storage. Data may be collected by
manual and/or electronic means. The Testing Organization shall determine the most appropriate
data collection format as part of the experimental design.

Each sampling event shall be assigned a specific identification number that will be tied to all data
from that sampling event through each step of data entry and analysis. The data from a sampling
event shall include the wastewater flow and quality data as well as operational settings and
conditions, sampling locations, day, time, personnel involved, etc. The identification numbers
shall track samples delivered to analytical laboratories that have been approved by the
Verification Organization, along with the results in the laboratory reports. Laboratory reports
shall be received and reviewed by the Testing Organization. These data will be entered into the
data spreadsheets, cross-checked, and verified in the same manner as previously discussed.

The QA/QC procedures for managing, reviewing and verifying data shall be presented in the
QAPP contained in the Test Plan. The means to obtain, record, verify and store data obtained
manually and electronically (data loggers, computers, etc.) shall be discussed in the QAPP.
Refer to Section 6 for further QA/QC information.

7.1.1 Manual Data Collection

For manual data recording, the Testing Organization shall record all data and calculations by
hand in laboratory notebooks with carbon copies. Daily measurements and other information
shall be recorded on specially prepared data log sheets, as appropriate. The original notebooks
shall be stored at the test site and the carbon copy sheets shall be forwarded to the Testing
Organization project manager at least once per week. Logs shall include a description of the
system, test runs, dates and times, any problems or issues, corrective actions (as required),
experimental calculations, and other pertinent items.

7.1.2 Electronic Data Collection

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Data in electronic format shall be included in commercially available programs for word
processing, spreadsheet or database processing, or commercial software developed especially for
data collection and processing on a specific hardware instrument or piece of equipment. A
database for the project shall be set up in the form of custom-designed spreadsheets. The
spreadsheets shall be capable of storing and manipulating the wastewater quality data from each
sampling event, along with the corresponding operational parameters, sampling location, day and
time, etc.

All manually entered data from laboratory notebooks and data log sheets shall be entered into the
appropriate spreadsheet on a weekly basis as a minimum. All recorded calculations shall be
verified by the Testing Organization during entry into the spreadsheet. Following data entry, the
spreadsheet shall be printed out and the printout shall be verified against the handwritten data
sheet, preferably by Testing Organization personnel not involved with the data entry. Any
corrections shall be noted on the hardcopies of the data sheets and corrected on the electronic
copy, and then a corrected version of the spreadsheet shall be printed out. The printouts shall be
initialled and dated by the Testing Organization personnel performing the data verification.

The printouts shall be stored onsite in chronological order in a project binder. Copies of the
verified and corrected printouts shall be forwarded to the Testing Organization project manager
at least once per week. At least two electronic backups of the data spreadsheets shall be kept
(e.g., one copy on computer hard drive and one copy on disk).

If formulae and functions are written into the spreadsheets for data manipulation and
calculations, then these formulae and functions shall be verified periodically to ensure that they
are being used and entered correctly. The spreadsheets shall undergo a monthly audit, as a
minimum, by the Testing Organization to ensure the formulae and functions are being used and
are entered correctly. Verification may involve reviewing sample formulae and making sure the
correct cells are referenced, the formula is entered correctly (e.g., parenthesis and operations are
correct), as well as performing random hand calculations and comparing the results to those
calculated by the spreadsheet program. The spreadsheet audits shall be recorded in a log with
the date, reviewer initials, name and timeframe of data set inspected for identification, audit
findings, and any modifications made to the spreadsheets.

7.2 Data Analysis and Presentation

All results, including statistical analysis, will be provided in the Verification Report. Any data
not included in statistical analysis will also be reported, together with the rationale as to why it
was not included in the analysis.

The data obtained during influent characterization and verification testing shall be statistically
analyzed, reduced, and presented in tables, graphs and/or charts in a clear and concise manner.
Raw data shall be included as an appendix to the Verification Report. The statistical methods
and any statistical programs used will be described in the Verification Report.

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It must be possible to compare the results as presented to the original raw data and test
conditions that the results were obtained under. The QAPP contained in the Test Plan shall
address this requirement.

A detailed discussion of the results shall accompany the tables, graphs and/or charts and shall be
presented in the Verification Report (see Section 7.3). The Testing Organization shall provide
and discuss conclusions drawn from the test results.

Guidance on analysis and presentation for specific data is presented in the following sub-
sections.

7.2.1	Flow Data

Flow data obtained during the influent characterization and verification testing periods shall be
analyzed and presented as follows:

•	a graph showing daily flows; the date, time, and sample number corresponding to the data
presented shall be shown on the graph, as applicable; and,

•	a table showing average, maximum and minimum daily flow, and 95% confidence
interval.

7.2.2	Treatment Performance Quality Data

Valid wastewater quality data obtained during the influent characterization and verification
testing periods shall be analyzed and presented as follows:

•	graphs showing the daily influent sampling results obtained for all core and additional
parameters;

•	tables showing the average, maximum and minimum influent concentration for the
sampling events and the 95% confidence interval for all core and additional parameters;

•	graphs showing the daily effluent sampling results obtained for all core and additional
parameters;

•	tables showing the average, maximum and minimum effluent concentration for the
sampling events and the 95% confidence interval for all core and additional parameters;

•	table showing the average and the 95% confidence interval for the mass of mercury in the
residual stream (where there is sufficient data);

•	tables showing the average removal efficiency by the technology and the 95% confidence
limit for total mercury, soluble mercury and any additional parameters measured; and,

•	date, time, and sample number corresponding to the data presented shall be shown on the
graphs, as applicable.

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7.2.3	Operations and Maintenance Parameters

Results of monitoring operations and maintenance parameters (see Section 5.5.3) during
verification testing shall be presented in tables or other appropriate format and thoroughly
discussed in the final Verification Report.

All O&M performance data shall be reported in the Verification Report as an average value for
the duration of verification testing.

7.2.4	Equations

Equations to be used in the data analysis are provided below.

Removal Efficiency (as
percent)

Sample Mean (Average)

Example of removal technology installed in a "dry
vacuum" system, or installed in a "wet vacuum"
system.

= (mg Hg captured in removal technology) X 100
(mg Hg capt'ed in rem. tech. + mg Hg in
samples* taken after removal technology)

* Samples are settled prior to analysis, resulting in
a liquid component and a solids component.
Therefore, data for each sample will include a mass
for the liquid component (mg/1 X liters) and a mass
for the solids component.

ybar = YjV / n

Where:



ybar

is

Ev

is

n

is

is the number of samples

Standard Deviation

s = (Y.(y-ybar)2/n)1/2

Where:

s is the sample standard deviation
y is an individual sample value
ybar is the sample mean

95% Confidence Interval

ybar i toJ2 (s / Tl )

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Where



ybar

is the sample mean

S

is the sample standard deviation

n

is the number of samples

to/2

is the Student's t-distribution with n-1



degrees of freedom, with a/2=0.025

and

tot/2 = 2.068 for n=25
Refer to statistical references for other values.

7.3 Verification Report

The Verification Report shall be a comprehensive document containing all raw and analyzed
data, all QA/QC data sheets, a description of all types of data collected, a detailed description of
the testing procedure and methods, results and QA/QC results.

A recommended Table of Contents for the Verification Report is as follows.

•	Preface

•	Glossary

•	Acknowledgements

•	Executive Summary

•	Introduction and Background

•	Procedures and Methods Used In Testing (summarizing essential information from the
Test Plan)

•	Results and Discussion

•	Limitations

•	Conclusions

•	Recommendations

•	References

•	Appendices (including raw data)

The exact details of the Verification report shall be at the discretion of the Testing Organization.

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8.0 ENVIRONMENTAL, HEALTH AND SAFETY PLAN

The Testing Organization shall strictly follow and enforce environmental, health and safety
measures during influent characterization and verification testing. An environmental, health and
safety plan shall be included in the Test Plan. The plan shall identify all environmental concerns
and potential hazards associated with the testing and the test location, and the required measures
to prevent exposure to these hazards. The Testing Organization shall be responsible for
informing all personnel at the test site, including site employees not associated with the testing
program, of the potential hazards at the test site and the safety measures to be employed.

Environmental, health and safety procedures in the plan shall address the following, as
applicable:

•	biological, chemical and electrical hazards;

•	storage, handling and disposal of hazardous chemicals and biological materials (including
wastewater samples);

•	material safety data sheets (MSDS);

•	conformance with applicable electrical and plumbing codes at the test site;

•	ventilation equipment for trailers or housing equipment if gases are present that may pose
a safety hazard;

•	confined space entry hazards;

•	any other specific safety or environmental issues associated with the technology or a
specific piece of equipment;

•	emergency contact details for the nearest hospital (provide directions), local fire
department, the Site Owner, and the Testing Organization project manager; and,

•	any permitting requirements for disposal of residues.

A copy of the Test Plan's environmental, health and safety procedures, including all MSDS,
shall be maintained and readily accessible at the test site. A one-page summary of emergency
contact details shall be placed inside a clear plastic cover and kept in a clearly visible place in the
vicinity of the technology test unit.

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9.0 REFERENCES

(1)	ANSI/ASQC: Specifications and Guidelines for Quality Systems for Environmental Data
Collection and Environmental Technology Programs (E4), 1994.

(2)	United States Environmental Protection Agency: Environmental Technology Verification
Program - Quality and Management Plan for the Pilot Period (1995 - 2000),
USEPA/600/R-98/064, 1998. Office of Research and Development, Cincinnati, Ohio.

(3)	NSF International, Environmental Technology Verification - Source Water Protection
Technologies Pilot Quality Management Plan, 2000. Ann Arbor, Michigan.

(4)	United States Environmental Protection Agency: Methods and Guidance for Analysis of
Water, EPA 821-C-99-008, 1999. Office of Water, Washington, DC.

(5)	APHA, AWWA, and WEF: Standard Methods for the Examination of Water and
Wastewater, 1998. Washington, DC.

(6)	United States Environmental Protection Agency: USEPA Guidance for Quality
Assurance Project Plans, USEPA QA/G-5, USEPA/600/R-98-018, 1998. Office of
Research and Development, Washington, DC.

(7)	United States Environmental Protection Agency, Guidance for the Data Quality
Objectives Process, USEPA QA/G-4, USEPA/600/R-96-055, 1996. Office of Research
and Development, Washington, DC.

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APPENDIX A

TEST PLAN OUTLINE AND CONTENT REQUIREMENTS

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1.0 OUTLINE OF THE TEST PLAN

The Testing Organization shall prepare the site-specific Test Plan. The specific contents of the
Test Plan may vary from site to site. As a minimum, the Test Plan must contain the following
components.

•	Title Page and Table of Contents

•	Test Plan Approval by Project Participants

•	Executive Summary

•	Objectives and Description of Verification Testing

•	Verification Testing Responsibilities

•	Technology Description

•	Experimental Design

•	Field Procedures

•	Sampling Procedures

•	Analytical Procedures

•	Quality Assurance Project Plan

•	Data Management, Analysis and Presentation

•	Assessments

•	References

•	Appendices:

historical influent flow and wastewater quality records (where this data is to be
used with the approval of the Verification Organization)

effluent and residuals data from previous tests (where this data is to be used, with
the approval of the Verification Organization)

O&M manual(s) supplied by the Vendor

Environmental, Health and Safety Plan and Material Safety Data Sheets
other documents and applicable data

A brief description of selected Test Plan requirements is presented in the following sections.

2.0 OBJECTIVES AND DESCRIPTION OF VERIFICATION TESTING

This section of the Test Plan shall include the following:

•	the objectives (including Vendor claims) and an overview of the testing to be performed;

•	a description of the test site, flushing procedure used and the number of amalgams placed
and/or removed per week;

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•	a map showing the location of the test site;

•	the site name and address, including street number/fire number, state, county, and
telephone number;

•	the name and address of the site owner;

•	the number of chairs dedicated to hygiene only and the number of chairs for general
dentistry at the dental office;

•	a description of any current method(s) of wastewater handling/treatment at the test site;

•	a summary of any existing data on the wastewater flowrate and strength;

•	a description of how the mercury amalgam removal technology will be installed, how the
influent will be diverted to the technology, and what will be done with effluent and
residues generated;

•	a site plan/layout showing the configuration of the technology to be tested and the
sampling equipment, including elevations of the technology and sampling equipment;
and

•	approximate timeframes for influent characterization, system installation and
commissioning, and the verification testing period.

3.0 VERIFICATION TESTING RESPONSIBILITIES

Key staff in the Testing Organization and other organizations involved in the verification testing
shall be identified. A description of the responsibilities for all parties shall be provided. Contact
details for key staff within each party shall be provided.

4.0 TECHNOLOGY DESCRIPTION

The Test Plan shall include the following information on the wastewater treatment technology to
be tested:

•	a simple schematic of the technology, showing all major components;

•	a brief introduction and discussion of the engineering and scientific concepts (process
kinetics and hydraulics) on which the mercury amalgam removal technology is based;

•	a description of the mercury amalgam removal technology, including the following:

specifications;

full description of each unit process, along with relevant photographic
perspectives or schematics;

equipment capacity and dimensions;

physical construction/components of the equipment, including materials of
construction;

general environmental requirements and limitations;

required consumables; and,

weight, transportability, and power requirements;

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•	a description of any scaling up or down of the test equipment compared to a typical full-
scale installation, and the impact this may have on treatment performance;

•	a description of the applications of the technology, the flow and load capacity, and the
expected removal capabilities of the technology;

•	an estimate of the O&M requirements, including chemicals and materials requirements
(specifying type and purpose), power requirements and labor requirements;

•	instructions on installation, start-up, operation, routine maintenance, and troubleshooting;

•	a description of the biological, physical and chemical nature of residues generated by the
technology, and rates of waste produced (e.g., concentration and volume of residues,
material replacement frequency);

•	requirements and/or recommendations for residuals handling;

•	identification of any special licensing requirements associated with the operation of the
technology;

•	the level of operator skill required to successfully operate the technology; and,

•	any noise and/or odor control and housing requirements.

Data plates provided by the Vendor shall be permanent and securely attached to each piece of
equipment used for verification testing. The data plate shall be easy to read in English or the
language of the intended user, located where it is readily accessible, and contain at least the
following information:

•	equipment name;

•	model number;

•	serial number;

•	Vendor's name and address;

•	electrical requirements (volts, phase, amps, Hertz);

•	shipping requirements and special handling precautions;

•	warning and caution statements in legible and easily discernible print size; and,

•	capacity or output rate (where applicable).

In addition, the Vendor shall provide the O&M manual(s) and all OSHA-required safety devices
(where applicable) for the equipment. O&M manuals should include information on installation,
start-up, operation, maintenance requirements, component calibration and replacement,
troubleshooting, spare parts, optimum operating/environmental conditions, and tolerance to
changes in conditions.

5.0	EXPERIMENTAL DESIGN

5.1	Work Plan for Influent Wastewater Characterization

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This work plan shall present the plan and procedures for influent characterization. The work plan
shall include, but is not restricted to, the following information:

•	sampling locations;

•	sampling methods;

•	sampling frequency and periods;

•	the type of sampling equipment (including materials of construction);

•	sample preservation and storage methods;

•	the type of analysis;

•	details on the analytical laboratory carrying out the analysis;

•	the method to be used for recording the flushing procedures (frequency, volume and
chemicals used), replacement of chairside traps and vacuum filters and number of
surfaces placed and/or removed during influent characterization that will enter the
influent stream;

•	the methods to be used for documenting the results; and,

•	the methods to be used to obtain statistically valid sampling results.

5.2	Work Plan for Commissioning

This work plan shall provide the procedures for commissioning of the technology to be tested.
The work plan shall include, but is not restricted to, the following information:

•	the estimated length of time required for commissioning of the technology;

•	the operating methods and monitoring required to ensure effective operation has been
achieved, including the limits for each parameter; and,

•	the methods for documenting the commissioning and attainment of effective operating
conditions.

5.3	Verification Testing Work Plan and Experimental Design

The work plan and experimental design for verification testing shall be provided. This section
shall present, but is not limited to, the following details regarding operating the technology:

•	the following sampling and analysis details for effluent and residual streams:

sampling locations
sampling methods
sampling frequency and periods

type of sampling equipment (including materials of construction)
sample preservation and storage
type of analysis

details on the analytical laboratory carrying out the analysis

•	O&M procedures that contain details on the following:

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type(s) of consumables to be monitored (e.g., chemicals, water, etc.), and the
method, frequency and period of monitoring

the method, frequency and period of monitoring of power consumption

the type(s) of O&M parameters to be monitored, and the method(s) to be used for

monitoring O&M labor requirements and other maintenance requirements

the method to be used for recording the flushing procedures (frequency, volume
and chemicals used), replacement of chairside traps and vacuum filters and
number of surfaces placed and/or removed during verification testing

•	procedures for managing and reporting the data collected; and,

•	the methods used to obtain statistically valid sampling results.

6.0 PROCEDURES

The Test Plan shall identify field, sampling, and analytical procedures to be followed throughout
the entire verification testing process. Field procedures may include instructions for sampling,
washing sampling containers, calibration of components, etc.

Sampling procedures shall include instructions regarding sample location, type, frequency,
method of sample collection, container type, sample preservation, QA/QC samples, holding
times, transporting, chain of custody requirements, sample logging, etc. Analytical procedures
shall identify the approved measurement methods (USEPA, Standard Methods) for sample
analyses, system calibration procedures, etc.

7.0 QUALITY ASSURANCE PROJECT PLAN

A Quality Assurance Project Plan (QAPP) shall be included in the Test Plan, which addresses the
following:

•	a description of the methodology for using analytical method blanks, the materials used,
the frequency of use, the criteria for acceptable method blanks, and the actions to be
taken if criteria are not met;

•	a description of the methodology for using spiked samples, the materials used, and the
frequency of use;

•	a description of any specific procedures appropriate to the analysis of performance
evaluation samples;

•	an outline of the procedure for determining samples to be analyzed in duplicate or
triplicate, including the frequency and approximate number;

•	a description of the methodology and/or equations used to measure any necessary data
quality indicators for performance measurements, which includes precision, bias,
accuracy, representativeness, comparability and completeness;

•	an outline of the format, content and frequency of Testing Organization self-assessments
and their technical systems;

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•	an outline of the format, content and frequency of assessment reports to the Verification
Organization;

•	the development of a corrective action plan responding to audit findings;

•	the requirement to provide all QA/QC information such as calibrations, blanks and
reference samples in an appendix to the report; all raw data shall also be reported in an
appendix; and,

•	the provision of all data in hardcopy and electronic form in a common spreadsheet or
database format.

8.0	DATA MANAGEMENT, ANALYSIS AND PRESENTATION

8.1	Data Management

The Test Plan shall present a plan for data management and handling. The Test Plan shall
identify the various types of data that will be generated throughout the verification testing
process (e.g., field notes, maintenance forms, laboratory reports, computer spreadsheets, graphs,
tables, photographs, and videotapes), and the format of data collection for each (i.e., hard copy or
electronic). The Test Plan shall present the methods for verifying the data.

The Testing Organization shall designate a person or group of persons responsible for data
handling in the Test Plan. It is recommended that one person be responsible for data
management to ensure consistency and correctness, and that another person be responsible for
QA/QC for the data set.

8.2	Data Analysis and Presentation

The Test Plan shall detail the methods to be used for analyzing and reducing the data. Details on
statistical references/equations shall be provided. A discussion on statistical analysis of the data
is provided in Section 7.2 of the protocol.

The Test Plan shall identify the data to be presented and the format of presentation (e.g., tables,
graphs).

9.0 ASSESSMENTS

The Test Plan shall identify all internal systems audits and internal performance audits (where
applicable) to be performed, as well as information on the party(ies) responsible for performing
the audits.

The corrective action procedures to be performed in response to audit findings shall be provided,
together with the responsible party(ies) for implementing corrective actions, and the party(ies)

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that will receive the audit reports. The types and frequencies of audits required for verification
testing can be found in the Source Water Protection Pilot Quality Management Plan(3).

10.0 APPENDICES

The following shall be provided as appendices to the Test Plan:

•	historical influent flow and wastewater quality data (where this data is to be used with the
approval of the Verification Organization);

•	effluent and residuals data from previous tests (where this data is to be used, with the
approval of the Verification Organization)

•	O&M manuals supplied by the Vendor;

•	Environmental, Health and Safety Plan, including material safety data sheets; and,

•	other documentation and data as applicable.

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