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National Office of Pollution Prevention
Table of Contents
Abstract
Summary
1. Introduction
2. Monitoring/Direct Measurement of Releases
3. Analytical Methods
4. Quality Assurance/Quality Control
5. Estimation of Releases
6. Reporting
7. Validation / Verification
Glossary of Terms and Acronyms
References
Bibliography
Appendix A: Standardized Release Reporting Template
Appendix B: Error Estimation
Appendix C: US EPA AP-42 Emission Factors
GUIDANCE DOCUMENT FOR REPORTING OF RELEASES FROM THE BASE METALS SMELTING SECTOR

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3. Analytical Methods

This section describes parameters to be analyzed and appropriate analytical methods for analyzing the samples collected. A discussion on the appropriate detection limits and laboratory certification is provided. Applicable Standard Reference Methods are also identified.

3.1 Parameters to be Analyzed

3.1.1 Air

Air samples should be analyzed as required by regulations or permits. Where specific requirements are not specified in regulation or permits, samples from air monitoring should be analyzed for (at a minimum):

  • CEPA-toxics (i.e., inorganic arsenic compounds, inorganic cadmium compounds, lead, mercury and oxidic, sulphidic and soluble inorganic nickel compounds);

  • particulate matter (PM, PM10 and PM2.5); and

  • sulphur dioxide.

It is recommended that a full metals scan should be conducted on air samples.

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3.1.2 Water

Water samples should be analyzed as required by regulations or permits.

Relevant parameters to be measured for the Metal Mining Effluent Regulation are arsenic, copper, lead, nickel, zinc, total suspended solids, radium 226, total cyanide, pH, aluminum, cadmium, iron, manganese, molybdenum, mercury, selenium, uranium, fluoride, total ammonia nitrogen, nitrate+nitrite, total phosphorus, chloride, sulphate, calcium, magnesium, potassium, sodium, conductivity, hardness, alkalinity and acidity.

Where specific requirements are not specified in regulation or permits, wastewater samples should be analyzed for (at a minimum):

  • CEPA-toxics;

  • total suspended solids; and

  • pH.

It is recommended that a full metals scan should be conducted on water samples.

The samples should also be analyzed for other parameters that can be used to characterize the discharge (e.g., fluoride, chloride, magnesium, calcium).

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3.1.3 Parameters Not Present

When it is believed that a particular parameter is not present in the releases based on technical knowledge and experience of the facility, analysis for this parameter should be periodically undertaken, but is not necessary on every sample. Documentation should be maintained to validate that the parameter is not present in the releases including reasons the parameter is unlikely to be released. However, when significant changes to process inputs or processes have occurred, analysis for all parameters should be conducted.

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3.2 Analytical Methods

The selection of analytical methods should be appropriate to meet the data quality objectives. Methods selected should be generally accepted and in common use in laboratories in Canada. A list of reference documents on analytical methods which may be applicable to the BMSS are presented in Section 3.5.

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3.3 Laboratory Certification

In 1994, the Canadian Association for Environmental Analytical Laboratories (CAEAL) and the Standards Council of Canada (SCC) signed a partnership agreement, producing a formal accreditation program for environmental laboratories across Canada. Under the jointly administered program, CAEAL conducts site audits and evaluates each laboratory's performance at regular intervals, and SCC grants accreditation to the laboratory on CAEAL's recommendation. Laboratories are assessed in accordance with ISO standards. To obtain SCC/CAEAL accreditation, each laboratory must comply with Canada's national standard, called the Requirements for the Competence of Environmental Laboratories, which is based on ISO Guide 25 and addresses specific quality and technical aspects related to environmental laboratories. More information on these standards are provided in Section 4.3 on Reference Documents for Quality Assurance/Quality Control.

It is recommended that all environmental samples be analyzed by a SCC/CAEAL accredited laboratory. A list of SCC/CAEAL accredited laboratories can be found on the SCC web-site at www.scc.ca/certific/labs.html.

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3.4 Detection Limit Issues

A detection limit is "the smallest concentration or amount of parameter or analyte that can be measured with a stated level of confidence or quality assurance". A laboratory method detection limit (LMDL) can be defined as the "detection limit calculated and stated by the laboratory performing the analysis". The LMDL is determined through standard methods such as the USEPA Definition and Method for MDL, 40 CFR (7-1-95 Edition) Part 136, Appendix B Definition And Procedure For The Determination Of The Method Detection Limit.

Laboratory method detection limits are specified in Environment Canada's Guidance Document for the Sampling and Analysis of Metal Mining Effluents. Method detection limits may also be specified in other federal or provincial guidelines.

The Mining Association of Canada (Data Integrity Group) in the its Guideline for Reporting ARET Data recommends that the LMDL be 2 to 10 times lower than the government-regulated discharge limits for the facility.

The MAC Guideline explains that this recommendation is based on practices in Ontario where the Ministry of Environment has developed a list of Regulatory Method Detection Limits (RMDL) which specify maximum allowable value for a LMDL. The Ontario Ministry of Environment recommends that the LMDL be about half the RMDL. For example, if the RMDL is 0.50 mg/L, the LMDL should be about 0.25 mg/L. Also, the LMDL should not be less than 1/10th the RMDL. The MAC concluded that a recommendation based on the RMDL was not possible, since RMDL only applies to Ontario operations.

The laboratory method detection limit (LMDL) should be limits specified in Environment Canada's Guidance Document for the Sampling and Analysis of Metal Mining Effluents or 2 to 10 times lower than the government-regulated discharge limits for the facility, where requirements are not specified.

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3.5 Standard Reference Methods

The following methods may be applicable to the analysis of samples from the Base Metals Smelting Sector.

3.5.1 Air

The list of methods presented in the section on sampling air releases (Section 2.3.1) contain guidance on analysis of the samples and may be applicable to the analysis of samples obtained from stack testing of air releases from the Base Metals Smelting Sector.

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3.5.2 Water

The following methods may be applicable to the analysis of water samples from the Base Metals Smelting Sector:

  • Environment Canada's Guidance Document for the Sampling and Analysis of Metal Mining Effluents

    • This document discusses sampling and chemical analysis considerations and procedures for use with metal mining effluents. The document stresses performance- based methods and how such methods should be applied to the mining industry. Data quality measures and objectives and overall quality control procedures are outlined for effluent sampling and analysis. References to suitable analytical methods are also provided.

  • Standard Methods for the Examination of Water and Wastewater31

    • This comprehensive reference covers all aspects of water analysis techniques. It includes more than 400 methods. Published jointly by the American Water Works Association, the American Public Health Association, and the Water Environment Federation.

  • Ontario Ministry of Environment's Protocol for the Sampling and Analysis of Industrial/Municipal Wastewater32

    • This guidance document is described in the previous section on sampling.

  • British Columbia Environmental Lab Manual -For the Analysis of Water, Wastewater, Sediment and Biological Materials.

    • This electronic Manual is produced by the Ministry of Environment Land and Parks, in cooperation with the BC Laboratory Quality Assurance Advisory Committee. The manual is used for the analysis of water, wastewater, sediment and biological materials.

  • Biological Test Method: Acute Lethality Test Using Rainbow Trout33

    • Methods recommended by Environment Canada for performing acute lethality tests with rainbow trout (Oncorhynchus mykiss) are described in this report. Universal conditions and procedures are outlined for undertaking an acute lethality test using a variety of materials. Additional conditions and procedures stipulated are specific for assessing samples of chemicals, effluents, elutriates, leachates, or receiving waters. Included are instructions on care and acclimatization of test organisms, sample handling and storage, test facility requirements, procedures for preparing test solutions and test initiation, specified test conditions, appropriate observations and measurements, endpoints, methods of calculation, and the use of reference toxicants.

  • Biological Test Method: Reference Method for Determining Acute Lethality of Effluents to Rainbow Trout 34

    • This document describes procedures for measuring the acute lethality of effluents to rainbow trout and completes the guidance provided in the generic methodology report "Acute Lethality Test Using Rainbow Trout" (EPS 1/RM/9). Methods are given for a single-concentration test, a multi-concentration test, and a test with a reference toxicant. Instructions are included on care of trout in the laboratory, facilities and water supply, handling and storage of samples, preparation of test solutions, test conditions, observations, endpoints, methods of calculation, and reporting requirements.

  • Biological Test Method: Acute Lethality Test Using Daphnia spp.35

    • This is the method recommended by Environment Canada for performing acute lethality toxicity tests using daphnids (Daphnia magna and/or D. pulex). Procedures and standard test conditions are outlined for undertaking an acute lethality test using various samples of chemicals, effluents, elutriates, leachates, or receiving waters. Included are instructions on culturing conditions and requirements, sample handling and storage, test facility requirements, procedures for preparing test solutions and test initiation, specified test conditions, appropriate observations and measurements, endpoints, methods of calculation, and the use of reference toxicants.

  • Biological Test Method: Reference Method for Determining Acute Lethality of Effluents to Daphnia magna36

    • This report describes procedures for measuring the acute lethality of effluents to Daphnia magna and completes the guidance provided in the generic methodology report "Acute Lethality Test Using Daphnia spp." (EPS 1/RM/11). Methods are given for a single-concentration test, a multi-concentration test, and a test with a reference toxicant. Instructions are included on care and culture of the daphnid crustaceans, facilities and water supply, handling and storage of samples, preparation of solutions, test conditions, observations, endpoints with methods of calculation, and reporting requirements.

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31 AWWA, AHPA,WEF, Standard Methods for the Examination of Water and Wastewaters, 1998, 20th Edition.

32 Ontario Ministry of Environment, Protocol for the Sampling and Analysis of Industrial/Municipal Wastewater, 1994, ISON 0-7778-1880-9.

33 Environment Canada, Biological Test Method: Acute Lethality Test Using Rainbow Trout, EPS 1/RM/9, 1990, Cat. No. EN 49-24/1-9E, ISBN 0-662-18074-7.

34 Environment Canada, Biological Test Method: Reference Method for Determining Acute Lethality of Effluents to Rainbow Trout, EPS 1/RM/13, 1990, Cat. No. EN 49-24/1-13, ISBN 0-662-57746-9.

35 Environment Canada, Biological Test Method: Acute Lethality Test Using Daphnia spp, EPS 1/RM/11 1990, Cat. No. EN 49-24/1-11E, ISBN 0-662-18076-3.

36 Environment Canada, Biological Test Method: Reference Method for Determining Acute Lethality of Effluents to Daphnia magna, EPS 1/RM/14, 1990, Cat. No. EN 49-24/1-14, ISBN 0-662-57747-7.

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