Submission of Lake Ontario Waterkeeper - Relicensing hearing before the Canadian Nuclear Safety Commission (CNSC) for the Cameco Corporation Port Hope Conversion Facility
Cameco Corporation (Cameco) is currently applying to renew its Fuel Facility Operating Licence FFOL-3631.0/2017 (the licence) for its Port Hope Conversion Facility (PHCF). This licence was issued on February 28, 2012, (valid from March 1, 2012) and will expire February 28, 2017.
The requested licence is for a ten-year period and would permit Cameco to continue to produce nuclear fuel for reactors in Canada and abroad. Currently, the facility is permitted to process and produce up to 2,800 tonnes of uranium as UO2 which is used for CANDU reactor fuel and up to 12,500 tonnes of UF6 which is exported for processing into light water reactor fuel. The requested licence would also permit Cameco to make significant changes to its facility, renovating some buildings, decommissioning others, and building entirely new facilities on the
PHCF site. These changes collectively comprise its Vision in Motion (VIM) project. More specifically, Cameco’s proposed VIM project involves:
• Removing up to 150,000 cubic metres (m3) of radioactive contaminated waste. This includes contaminated soil excavation, “legacy” drummed waste generated at the facility before 1988, and rubble from demolished older buildings at the PHCF site and Center Pier). This waste will be taken to Canadian Nuclear Laboratories’ secure long-term waste management facility in Port Hope;
• Removing 11 older or under-utilized buildings from the PHCF site and Center Pier;
• Constructing of 4 new buildings and the refurbishment or modification of 7 other buildings at the site;
• Installing of new pump and treat wells to address the groundwater contamination that will remain under the PHCF site after VIM is completed;
• Improving the facility’s stormwater management infrastructure; and
• Moving the eastern fence-line of the PHCF away from the harbour to help facilitate greater public access to Port Hope’s waterfront.
Waterkeeper has been involved in several other past decision-making processes before the CNSC concerning this facility, including its environmental assessment (EA) under the Canadian Environmental Assessment Act, 1992, as well as its application for a Certificate of Approval from the then Ontario Ministry of Environment for its industrial sewage permit. During these processes, Waterkeeper expressed concerns regarding the facility’s poor stormwater management, the need for better cooling water technology, and the need for better environmental monitoring and public communication.
In the last five years, some progress has been made to ensure the initiative supports a more swimmable, drinkable, and fishable Lake Ontario. But more work is still needed.
Submission of Lake Ontario Waterkeeper - Reviewing Canadian Nuclear Safety Co...LOWaterkeeper
The Port Hope Area Initiative (PHAI) is an internationally significant undertaking. It is the biggest radioactive waste clean-up project in Canadian history, and involves one of the largest nuclear waste holding facilities in North America. The PHAI is comprised of two distinct projects: the Port Hope waste relocation project (“Port Hope Project”), and the Port Granby waste relocation project (“Port Granby Project”). Together, both projects seek to clean up a combined two-million cubic metres (m3) of low-level radioactive waste from various sites across Port Hope and Port Granby.
The Port Hope Project involves excavating 1,223,250 m3 of historic radioactive waste from several sites around the town of Port Hope to a Long-term Waste Management Facility (PH LTWMF) just north of the community. The project was subject to an environmental assessment (EA) under the Canadian Environmental Assessment Act, 1992 (CEAA, 1992) which was conducted from 2001 to 2007. In 2009, the CNSC granted a five-year Nuclear Waste Substance Licence to Atomic Energy Canada Limited (AECL) to implement the project. In 2012, AECL applied to have its licence extended for ten years. This was granted by the Canadian Nuclear Safety Commission (CNSC), making the current licence valid until December 31, 2022.
The Port Granby Project involves the removal of 450,000 m3 of historic radioactive waste from the existing and poorly contained Port Granby waste management facility to a new above ground waste management facility (the PG LTWMF) 700 metres north of the Lake Ontario shoreline. The Port Granby Project was also subject to a federal EA under CEAA, 1992 and the project was approved in 2009. After a public hearing in September 2010, the CNSC granted AECL a ten-year licence to implement this project.
In the last five years, some progress has been made to ensure the initiative supports a more swimmable, drinkable, and fishable Lake Ontario. But more work is still needed.
Waterkeeper's Review of CNSC's Regulatory Oversight Report for Uranium and Nu...LOWaterkeeper
The CNSC asked Swim Drink Fish Canada/Lake Ontario to look into its 2016 Regulatory Oversight Report for
Uranium and Nuclear Substance Processing Facilities in Canada. CNSC provided funding for the review.
The document provides a draft supplemental environmental impact statement/report on a proposed crude oil terminal project in the Port of Los Angeles. The draft report analyzes the project's potential environmental impacts, alternatives, and proposed mitigation measures. Key aspects of the proposed project include constructing a marine terminal, 4 million barrel tank farm, and pipelines to connect to local refineries. The report finds some unavoidable significant air quality and noise impacts even with mitigation measures like using low sulfur fuel and alternative maritime power.
This document provides an independent review of the CNSC's 2016 Regulatory Oversight Report for uranium and nuclear substance processing facilities. The review focuses on the adequacy of describing environmental impacts related to contaminants and the environmental performance of Cameco's Port Hope Conversion Facility.
The review finds inconsistencies in how each facility is described in the report, with some providing detailed data on parameters like groundwater concentrations and others providing little detail. It also finds the facility descriptions are often incomplete, failing to discuss all potential pathways for contamination or providing monitoring data to fully assess performance. Specific issues are identified at several facilities. The review concludes the report could be significantly improved by taking a more systematic approach to facility descriptions and providing references
Lake Ontario Waterkeeper's submissions for Pickering Waste Management Facilit...LOWaterkeeper
Ontario Power Generation (OPG) is currently applying to renew its Waste Facility Operating Licence for its Pickering Waste Management Facility (PWMF). The current licence
will expire March 31, 2018.
OPG is currently requesting a licence term of approximately 11 years that will expire on August 31, 2028.
Waterkeeper's written submissions discuss several identified concerns with the PWMF and provide
recommendations for improving the facility’s planned expansion and routine operations.
New Developments in the Natural Gas Industryenergypipeline
The document discusses pipeline abandonments and conversions. It notes that pipelines are increasingly facing issues like declining revenues and stranded assets. To address this, companies are exploring creative alternatives to traditional abandonment like converting pipelines to transport other commodities. FERC regulates such conversions and considers public interest and environmental impacts. The process involves various permits and agencies.
Eia kpt deep water container port - reportzubeditufail
This document provides an environmental impact assessment report for the proposed Pakistan Deep Water Container Port (PDWCP) project located off the coast of Karachi, Pakistan. Key points:
1) The PDWCP project involves constructing breakwaters, dredging an approach channel and basin, and reclaiming land to develop a new deepwater container terminal that can accommodate larger ships.
2) Three alternatives were considered for the project location, with the preferred option being a new site east of the existing Keamari Groyne that provides the most direct channel access.
3) Potential environmental impacts of the project are assessed, along with mitigation measures. Key impacts include effects of dredging and disposal on water quality
This document provides a preliminary design report for a proposed water system to service the Upper Fintry, Shalal Road, and Valley of the Sun neighbourhoods. It identifies groundwater from wells located on Lot 19 in the Fintry Delta as the preferred water source. The system will have two pressure zones, with the Valley of the Sun area serviced from a 608m reservoir and Upper Fintry serviced from a 555m pressure reducing valve. The design includes a well pump station, 405m booster station, 608m reservoir, and supply and distribution piping. The preliminary cost estimate and potential for expanding the service area are also discussed.
Submission of Lake Ontario Waterkeeper - Reviewing Canadian Nuclear Safety Co...LOWaterkeeper
The Port Hope Area Initiative (PHAI) is an internationally significant undertaking. It is the biggest radioactive waste clean-up project in Canadian history, and involves one of the largest nuclear waste holding facilities in North America. The PHAI is comprised of two distinct projects: the Port Hope waste relocation project (“Port Hope Project”), and the Port Granby waste relocation project (“Port Granby Project”). Together, both projects seek to clean up a combined two-million cubic metres (m3) of low-level radioactive waste from various sites across Port Hope and Port Granby.
The Port Hope Project involves excavating 1,223,250 m3 of historic radioactive waste from several sites around the town of Port Hope to a Long-term Waste Management Facility (PH LTWMF) just north of the community. The project was subject to an environmental assessment (EA) under the Canadian Environmental Assessment Act, 1992 (CEAA, 1992) which was conducted from 2001 to 2007. In 2009, the CNSC granted a five-year Nuclear Waste Substance Licence to Atomic Energy Canada Limited (AECL) to implement the project. In 2012, AECL applied to have its licence extended for ten years. This was granted by the Canadian Nuclear Safety Commission (CNSC), making the current licence valid until December 31, 2022.
The Port Granby Project involves the removal of 450,000 m3 of historic radioactive waste from the existing and poorly contained Port Granby waste management facility to a new above ground waste management facility (the PG LTWMF) 700 metres north of the Lake Ontario shoreline. The Port Granby Project was also subject to a federal EA under CEAA, 1992 and the project was approved in 2009. After a public hearing in September 2010, the CNSC granted AECL a ten-year licence to implement this project.
In the last five years, some progress has been made to ensure the initiative supports a more swimmable, drinkable, and fishable Lake Ontario. But more work is still needed.
Waterkeeper's Review of CNSC's Regulatory Oversight Report for Uranium and Nu...LOWaterkeeper
The CNSC asked Swim Drink Fish Canada/Lake Ontario to look into its 2016 Regulatory Oversight Report for
Uranium and Nuclear Substance Processing Facilities in Canada. CNSC provided funding for the review.
The document provides a draft supplemental environmental impact statement/report on a proposed crude oil terminal project in the Port of Los Angeles. The draft report analyzes the project's potential environmental impacts, alternatives, and proposed mitigation measures. Key aspects of the proposed project include constructing a marine terminal, 4 million barrel tank farm, and pipelines to connect to local refineries. The report finds some unavoidable significant air quality and noise impacts even with mitigation measures like using low sulfur fuel and alternative maritime power.
This document provides an independent review of the CNSC's 2016 Regulatory Oversight Report for uranium and nuclear substance processing facilities. The review focuses on the adequacy of describing environmental impacts related to contaminants and the environmental performance of Cameco's Port Hope Conversion Facility.
The review finds inconsistencies in how each facility is described in the report, with some providing detailed data on parameters like groundwater concentrations and others providing little detail. It also finds the facility descriptions are often incomplete, failing to discuss all potential pathways for contamination or providing monitoring data to fully assess performance. Specific issues are identified at several facilities. The review concludes the report could be significantly improved by taking a more systematic approach to facility descriptions and providing references
Lake Ontario Waterkeeper's submissions for Pickering Waste Management Facilit...LOWaterkeeper
Ontario Power Generation (OPG) is currently applying to renew its Waste Facility Operating Licence for its Pickering Waste Management Facility (PWMF). The current licence
will expire March 31, 2018.
OPG is currently requesting a licence term of approximately 11 years that will expire on August 31, 2028.
Waterkeeper's written submissions discuss several identified concerns with the PWMF and provide
recommendations for improving the facility’s planned expansion and routine operations.
New Developments in the Natural Gas Industryenergypipeline
The document discusses pipeline abandonments and conversions. It notes that pipelines are increasingly facing issues like declining revenues and stranded assets. To address this, companies are exploring creative alternatives to traditional abandonment like converting pipelines to transport other commodities. FERC regulates such conversions and considers public interest and environmental impacts. The process involves various permits and agencies.
Eia kpt deep water container port - reportzubeditufail
This document provides an environmental impact assessment report for the proposed Pakistan Deep Water Container Port (PDWCP) project located off the coast of Karachi, Pakistan. Key points:
1) The PDWCP project involves constructing breakwaters, dredging an approach channel and basin, and reclaiming land to develop a new deepwater container terminal that can accommodate larger ships.
2) Three alternatives were considered for the project location, with the preferred option being a new site east of the existing Keamari Groyne that provides the most direct channel access.
3) Potential environmental impacts of the project are assessed, along with mitigation measures. Key impacts include effects of dredging and disposal on water quality
This document provides a preliminary design report for a proposed water system to service the Upper Fintry, Shalal Road, and Valley of the Sun neighbourhoods. It identifies groundwater from wells located on Lot 19 in the Fintry Delta as the preferred water source. The system will have two pressure zones, with the Valley of the Sun area serviced from a 608m reservoir and Upper Fintry serviced from a 555m pressure reducing valve. The design includes a well pump station, 405m booster station, 608m reservoir, and supply and distribution piping. The preliminary cost estimate and potential for expanding the service area are also discussed.
Delaware Riverkeeper Letter to DRBC Requesting Intervention to Stop PennEast ...Marcellus Drilling News
A letter authored by THE Delaware Riverkeeper herself, Maya van Rossum, petitioning the Delaware River Basin Commission to interject itself into the permitting process of the PennEast Pipeline that is slated to run from Wilkes-Barre, PA all the way to Trenton, NJ, carrying abundant, cheap Marcellus Shale natural gas.
This document is a request for proposals from the Tahoe Keys Property Owners Association for implementation services related to the Tahoe Keys Lagoons Aquatic Weed Control Methods Test Project. It provides background on the aquatic weed issue in Tahoe Keys lagoons and describes the approved multi-year project to test herbicides, UV light, and other control methods. It outlines the scope of work, including herbicide and dye application, monitoring well water, and other tasks. Proposals are due by March 29th, 2022 and should address the services needed to implement the rigorous monitoring program required for the project.
The document is a question and answer addendum from the Tahoe Keys Property Owners Association regarding their Control Methods Test Implementation Services Request for Proposal. It provides responses to 12 questions received from bidders on the RFP, seeking clarification on various aspects of the project scope, requirements, and logistics. Key details addressed include submitting separate bids for each scope of work, having separate contracts for each activity, encouragement for bidders to submit bids on multiple scopes, and clarification on sampling and equipment requirements.
This document discusses several issues related to hydraulic fracturing including water usage, fracking fluid disclosure, infrastructure concerns, wastewater discharge, groundwater protection, and other side effects like earthquakes and air pollution. It outlines recent federal actions by the EPA to regulate air emissions and require reporting. It also discusses a study by the National Academy of Sciences on fracking and earthquakes. Finally, it provides updates on state actions and regulations in places like North Carolina, Vermont, New York, Maryland, and Mississippi regarding hydraulic fracturing and related activities.
MASE Consultants provided Lochmueller Group with a final design report for reducing combined sewer overflows in Peru, Indiana. The design includes a new interceptor and conveyance piping system, a detention basin to hold excess flow from the first flush of a 10-year storm, and a wetland to treat remaining excess flow. A roadway design was also provided for Canal Street, where a new interceptor sewer will be installed. The three-phase construction plan includes building the treatment systems first, followed by the interceptor and force main, with final tie-ins and commissioning. The design aims to meet the city and EPA's standards by treating all overflow from storms up to the 10-year event
The SPE Foundation and member donations primarily fund the SPE Distinguished Lecturer Program. Companies also support the program by allowing employees to serve as lecturers. Additional support comes from AIME. The program provides 30 minute presentations on reservoir topics. Robert Hawkes will present on hydraulic fracture flowback dynamics, discussing load fluid recovery and its implications for long term production. His presentation will cover laboratory observations, field data, and diagnostic tools to understand flowback mechanisms and estimate ultimate load fluid recovery.
This permit authorizes a three-year aquatic weed control test project in the Tahoe Keys lagoons. The project will test various control methods, including herbicides, ultraviolet light, and laminar flow aeration. A total of 21 test sites covering 41.5 acres will be established to test the standalone and combined effects of different control treatments. Monitoring will be conducted to evaluate the effectiveness of reducing target aquatic weeds by 75% within test sites. Three control sites will also be monitored for comparison. The permit details the approved control methods, application procedures, monitoring requirements, and establishes conditions to minimize environmental impacts.
Applying federal environmental laws to co2 enhanced oil recovery pptHolland & Hart LLP
This document provides an overview of federal environmental laws as they apply to CO2 enhanced oil recovery. It discusses how the EPA regulates CO2 injection under the Underground Injection Control program and the Resource Conservation and Recovery Act. Key issues addressed include how the EPA is encouraging CO2 injection for storage through new regulations, concerns about additional regulatory burdens, and legal challenges regarding how the EPA classifies and regulates CO2 streams from industrial facilities.
- The document discusses changes to the National Pollutant Discharge Elimination System General Permit for Stormwater Discharges from construction sites, including: establishing three risk levels; requiring best management practices, effluent monitoring and reporting, and receiving water monitoring; and specifying post-construction stormwater requirements.
- It also summarizes a California Department of Transportation bridge project that received awards for avoiding permitted environmental impacts and protecting water quality during construction.
- The document questions whether substantial evidence supports allegations in an Administrative Civil Liability complaint issued to the construction contractor, arguing some claims are based on ambiguous or unclear evidence.
The new Center for Sustainable Shale Development, a collective of both drilling companies and environmentalist groups, have proposed a new standards certification program. These 15 standards are the initial "first cut" at promoting more environmentally-friendly shale in the Marcellus Shale region. The intent is for drillers and pipeline companies to become certified by the CSSD. Without certification? Persona non grata.
This Memorandum of Understanding (MOU) is between Arapahoe County and an oil and gas operator to establish conditions for developing and operating future oil and gas facilities in unincorporated parts of the county. It aims to foster efficient production while protecting health, safety, environment, and providing a predictable permitting process. Key points include: the operator will use closed-loop systems where possible; water storage pits must meet fresh/brine water standards; additional pit types require county review; berms must be inspected weekly; and the parties will meet quarterly to discuss issues.
Lake Restoration Projects Being Undertaken by BDA_Bangalore Development Autho...Ekonnect
The document discusses lake restoration projects being undertaken by the Bangalore Development Authority (BDA). It provides background on BDA's aims, jurisdiction, and environmental conservation initiatives including lake restoration. It then summarizes the current state of Bangalore's lakes, which are largely encroached, polluted, and in need of restoration. The methodology for BDA's lake restoration projects is described, including removing encroachments, desilting, constructing wetlands and sewage diversion channels. Status updates and challenges to progress are also summarized, such as pending encroachment clearances and need for improved sewage networks and rehabilitation efforts.
Section 7 Determinations – How to complete a Section 7 - Randy Welsh, Steve C...rshimoda2014
This course presents an introduction to and how to complete a Section 7 Determination for the Wild and Scenic Rivers Act (WSRA). The content of this course is derived from Wild and Scenic Rivers Act: Section 7, a technical report of the Interagency Wild and Scenic Rivers Council (Council) (www.rivers.gov/publications.html).
Participation will result in improvements in future applications of Section 7, based on increased knowledge of its intent, content and procedures.
After completing this course, participants will be able to:
• Apply appropriate evaluative standards.
• Develop an integrated approach with appropriate interdisciplinary team members.
• Conduct an analysis adequate to support the determination.
• Provide early consultation/collaboration to federal assisting agency.
• Share information with landowners, local and state governments, and nongovernmental organizations.
Participants will increase their knowledge in:
• What a water resources project is under Section 7 of the WSRA.
• How to apply Section 7 to state-administered, federally designated rivers; congressionally designated rivers; and congressionally authorized study rivers.
• Definitions.
• Roles of the involved agencies.
• Evaluation standards for a designated river.
• Evaluation standards for a congressionally authorized study river.
• Evaluation procedures.
• The timing of a Section 7 analysis and determination, and the responsible official.
• Riverine stewardship.
The webinar covered recent regulatory developments in construction and post-construction stormwater management. It discussed changes to the EPA's Construction General Permit including new buffer requirements and timelines for stabilization. It also summarized EPA's proposed rulemaking to strengthen post-construction stormwater requirements and establish national performance standards for new development. Finally, it reviewed federal requirements for stormwater management on federal facilities.
The document discusses several actions the San Diego County Water Authority Board will need to take to fully implement the Carlsbad Desalination Project, including: approving a design-build agreement for the product water pipeline, adjusting capital improvement project budgets, amending existing contracts, and approving bond financing agreements. It also notes member agencies will need to finalize contracts to purchase water from the desalination plant.
The document provides guidelines for the design of flood protection embankments. Some key points include:
1. The spacing between embankments on both river banks should not be less than 3 times the Lacey wetted perimeter for the design flood discharge.
2. The design high flood level should generally correspond to a 25-year flood for agricultural areas and a 100-year flood to protect towns.
3. A minimum freeboard of 1.5 meters over the design flood level should be provided, or 1.8 meters for higher discharges or aggrading rivers.
4. The top width of embankments should generally be 5 meters wide with 15-30 meter long turning platforms
A critique of New York's draft drilling regulations for hydraulic fracturing submitted by Judith Enck, Region 2 Administrator for the federal Environmental Protection Agency. The critique was submitted on Weds, Jan 11 just hours before the filing deadline closed at the New York State DEC.
Federal Energy Regulatory approval and certificate that allows the Eastern Shore Natural Gas Company to build their White Oak Mainline Expansion Project--with new pipeline and compressor station upgrades in Chester County, PA and New Castle County, DE. It is a short, 7-mile pipeline to help de-bottleneck natural gas flows coming from the PA Marcellus Shale into ESNG's Delmarva Peninsula pipeline network.
The document summarizes several case studies related to shale gas exploration and development applications in the UK:
- Applications were approved, refused, or appealed for reasons including environmental impacts, public interest, highway safety, and compliance with local plans.
- A decision in Fernhurst focused on tests for protected landscapes in the National Planning Policy Framework.
- While public debate around shale gas existed, most decisions cited "traditional" planning factors like noise, traffic, and compliance with local policy.
Submission by Lake Ontario Waterkeeper for the Darlington Nuclear Relicensing...LOWaterkeeper
On September 28, 2015, Lake Ontario Waterkeeper submitted a request to the Canadian Nuclear Safety Committee to intervene during the Day 2 Relicensing Hearing for the Darlington Nuclear Generating Station.
The document summarizes the Cleaner Seas for Sussex Project, which involved constructing a new wastewater treatment works and sludge recycling center serving 300,000 people in Peacehaven, UK. The 12-year, £300 million project included building 11km of new sewer tunnels, three pumping stations, and a treatment facility with preliminary treatment, primary settlement, anaerobic digestion of sludge, and final biological treatment before discharge. After over four years of construction and commissioning in phases, compliance testing was completed successfully in 2013, meeting all regulatory standards for the treated wastewater and sludge products.
Delaware Riverkeeper Letter to DRBC Requesting Intervention to Stop PennEast ...Marcellus Drilling News
A letter authored by THE Delaware Riverkeeper herself, Maya van Rossum, petitioning the Delaware River Basin Commission to interject itself into the permitting process of the PennEast Pipeline that is slated to run from Wilkes-Barre, PA all the way to Trenton, NJ, carrying abundant, cheap Marcellus Shale natural gas.
This document is a request for proposals from the Tahoe Keys Property Owners Association for implementation services related to the Tahoe Keys Lagoons Aquatic Weed Control Methods Test Project. It provides background on the aquatic weed issue in Tahoe Keys lagoons and describes the approved multi-year project to test herbicides, UV light, and other control methods. It outlines the scope of work, including herbicide and dye application, monitoring well water, and other tasks. Proposals are due by March 29th, 2022 and should address the services needed to implement the rigorous monitoring program required for the project.
The document is a question and answer addendum from the Tahoe Keys Property Owners Association regarding their Control Methods Test Implementation Services Request for Proposal. It provides responses to 12 questions received from bidders on the RFP, seeking clarification on various aspects of the project scope, requirements, and logistics. Key details addressed include submitting separate bids for each scope of work, having separate contracts for each activity, encouragement for bidders to submit bids on multiple scopes, and clarification on sampling and equipment requirements.
This document discusses several issues related to hydraulic fracturing including water usage, fracking fluid disclosure, infrastructure concerns, wastewater discharge, groundwater protection, and other side effects like earthquakes and air pollution. It outlines recent federal actions by the EPA to regulate air emissions and require reporting. It also discusses a study by the National Academy of Sciences on fracking and earthquakes. Finally, it provides updates on state actions and regulations in places like North Carolina, Vermont, New York, Maryland, and Mississippi regarding hydraulic fracturing and related activities.
MASE Consultants provided Lochmueller Group with a final design report for reducing combined sewer overflows in Peru, Indiana. The design includes a new interceptor and conveyance piping system, a detention basin to hold excess flow from the first flush of a 10-year storm, and a wetland to treat remaining excess flow. A roadway design was also provided for Canal Street, where a new interceptor sewer will be installed. The three-phase construction plan includes building the treatment systems first, followed by the interceptor and force main, with final tie-ins and commissioning. The design aims to meet the city and EPA's standards by treating all overflow from storms up to the 10-year event
The SPE Foundation and member donations primarily fund the SPE Distinguished Lecturer Program. Companies also support the program by allowing employees to serve as lecturers. Additional support comes from AIME. The program provides 30 minute presentations on reservoir topics. Robert Hawkes will present on hydraulic fracture flowback dynamics, discussing load fluid recovery and its implications for long term production. His presentation will cover laboratory observations, field data, and diagnostic tools to understand flowback mechanisms and estimate ultimate load fluid recovery.
This permit authorizes a three-year aquatic weed control test project in the Tahoe Keys lagoons. The project will test various control methods, including herbicides, ultraviolet light, and laminar flow aeration. A total of 21 test sites covering 41.5 acres will be established to test the standalone and combined effects of different control treatments. Monitoring will be conducted to evaluate the effectiveness of reducing target aquatic weeds by 75% within test sites. Three control sites will also be monitored for comparison. The permit details the approved control methods, application procedures, monitoring requirements, and establishes conditions to minimize environmental impacts.
Applying federal environmental laws to co2 enhanced oil recovery pptHolland & Hart LLP
This document provides an overview of federal environmental laws as they apply to CO2 enhanced oil recovery. It discusses how the EPA regulates CO2 injection under the Underground Injection Control program and the Resource Conservation and Recovery Act. Key issues addressed include how the EPA is encouraging CO2 injection for storage through new regulations, concerns about additional regulatory burdens, and legal challenges regarding how the EPA classifies and regulates CO2 streams from industrial facilities.
- The document discusses changes to the National Pollutant Discharge Elimination System General Permit for Stormwater Discharges from construction sites, including: establishing three risk levels; requiring best management practices, effluent monitoring and reporting, and receiving water monitoring; and specifying post-construction stormwater requirements.
- It also summarizes a California Department of Transportation bridge project that received awards for avoiding permitted environmental impacts and protecting water quality during construction.
- The document questions whether substantial evidence supports allegations in an Administrative Civil Liability complaint issued to the construction contractor, arguing some claims are based on ambiguous or unclear evidence.
The new Center for Sustainable Shale Development, a collective of both drilling companies and environmentalist groups, have proposed a new standards certification program. These 15 standards are the initial "first cut" at promoting more environmentally-friendly shale in the Marcellus Shale region. The intent is for drillers and pipeline companies to become certified by the CSSD. Without certification? Persona non grata.
This Memorandum of Understanding (MOU) is between Arapahoe County and an oil and gas operator to establish conditions for developing and operating future oil and gas facilities in unincorporated parts of the county. It aims to foster efficient production while protecting health, safety, environment, and providing a predictable permitting process. Key points include: the operator will use closed-loop systems where possible; water storage pits must meet fresh/brine water standards; additional pit types require county review; berms must be inspected weekly; and the parties will meet quarterly to discuss issues.
Lake Restoration Projects Being Undertaken by BDA_Bangalore Development Autho...Ekonnect
The document discusses lake restoration projects being undertaken by the Bangalore Development Authority (BDA). It provides background on BDA's aims, jurisdiction, and environmental conservation initiatives including lake restoration. It then summarizes the current state of Bangalore's lakes, which are largely encroached, polluted, and in need of restoration. The methodology for BDA's lake restoration projects is described, including removing encroachments, desilting, constructing wetlands and sewage diversion channels. Status updates and challenges to progress are also summarized, such as pending encroachment clearances and need for improved sewage networks and rehabilitation efforts.
Section 7 Determinations – How to complete a Section 7 - Randy Welsh, Steve C...rshimoda2014
This course presents an introduction to and how to complete a Section 7 Determination for the Wild and Scenic Rivers Act (WSRA). The content of this course is derived from Wild and Scenic Rivers Act: Section 7, a technical report of the Interagency Wild and Scenic Rivers Council (Council) (www.rivers.gov/publications.html).
Participation will result in improvements in future applications of Section 7, based on increased knowledge of its intent, content and procedures.
After completing this course, participants will be able to:
• Apply appropriate evaluative standards.
• Develop an integrated approach with appropriate interdisciplinary team members.
• Conduct an analysis adequate to support the determination.
• Provide early consultation/collaboration to federal assisting agency.
• Share information with landowners, local and state governments, and nongovernmental organizations.
Participants will increase their knowledge in:
• What a water resources project is under Section 7 of the WSRA.
• How to apply Section 7 to state-administered, federally designated rivers; congressionally designated rivers; and congressionally authorized study rivers.
• Definitions.
• Roles of the involved agencies.
• Evaluation standards for a designated river.
• Evaluation standards for a congressionally authorized study river.
• Evaluation procedures.
• The timing of a Section 7 analysis and determination, and the responsible official.
• Riverine stewardship.
The webinar covered recent regulatory developments in construction and post-construction stormwater management. It discussed changes to the EPA's Construction General Permit including new buffer requirements and timelines for stabilization. It also summarized EPA's proposed rulemaking to strengthen post-construction stormwater requirements and establish national performance standards for new development. Finally, it reviewed federal requirements for stormwater management on federal facilities.
The document discusses several actions the San Diego County Water Authority Board will need to take to fully implement the Carlsbad Desalination Project, including: approving a design-build agreement for the product water pipeline, adjusting capital improvement project budgets, amending existing contracts, and approving bond financing agreements. It also notes member agencies will need to finalize contracts to purchase water from the desalination plant.
The document provides guidelines for the design of flood protection embankments. Some key points include:
1. The spacing between embankments on both river banks should not be less than 3 times the Lacey wetted perimeter for the design flood discharge.
2. The design high flood level should generally correspond to a 25-year flood for agricultural areas and a 100-year flood to protect towns.
3. A minimum freeboard of 1.5 meters over the design flood level should be provided, or 1.8 meters for higher discharges or aggrading rivers.
4. The top width of embankments should generally be 5 meters wide with 15-30 meter long turning platforms
A critique of New York's draft drilling regulations for hydraulic fracturing submitted by Judith Enck, Region 2 Administrator for the federal Environmental Protection Agency. The critique was submitted on Weds, Jan 11 just hours before the filing deadline closed at the New York State DEC.
Federal Energy Regulatory approval and certificate that allows the Eastern Shore Natural Gas Company to build their White Oak Mainline Expansion Project--with new pipeline and compressor station upgrades in Chester County, PA and New Castle County, DE. It is a short, 7-mile pipeline to help de-bottleneck natural gas flows coming from the PA Marcellus Shale into ESNG's Delmarva Peninsula pipeline network.
The document summarizes several case studies related to shale gas exploration and development applications in the UK:
- Applications were approved, refused, or appealed for reasons including environmental impacts, public interest, highway safety, and compliance with local plans.
- A decision in Fernhurst focused on tests for protected landscapes in the National Planning Policy Framework.
- While public debate around shale gas existed, most decisions cited "traditional" planning factors like noise, traffic, and compliance with local policy.
Similar to Submission of Lake Ontario Waterkeeper - Relicensing hearing before the Canadian Nuclear Safety Commission (CNSC) for the Cameco Corporation Port Hope Conversion Facility
Submission by Lake Ontario Waterkeeper for the Darlington Nuclear Relicensing...LOWaterkeeper
On September 28, 2015, Lake Ontario Waterkeeper submitted a request to the Canadian Nuclear Safety Committee to intervene during the Day 2 Relicensing Hearing for the Darlington Nuclear Generating Station.
The document summarizes the Cleaner Seas for Sussex Project, which involved constructing a new wastewater treatment works and sludge recycling center serving 300,000 people in Peacehaven, UK. The 12-year, £300 million project included building 11km of new sewer tunnels, three pumping stations, and a treatment facility with preliminary treatment, primary settlement, anaerobic digestion of sludge, and final biological treatment before discharge. After over four years of construction and commissioning in phases, compliance testing was completed successfully in 2013, meeting all regulatory standards for the treated wastewater and sludge products.
Swim Drink Fish's Preliminary Submission on Pickering Nuclear Generating StationLOWaterkeeper
Here is Swim Drink Fish’s preliminary submission to the CNSC Tribunal as it reviews the PNGS licence conditions. OPG withholds vital information about the PNGS’ environmental impacts needed for Swim Drink Fish’s complete submission.
Do not include any personal information as all posted material on this site is considered to be part of a public record as defined by section 27 of the Municipal Freedom of Information and Protection of Privacy Act.
We reserve the right to remove inappropriate comments. Please see Terms of Use for City of Toronto Social Media Sites at http://www.toronto.ca/e-updates/termsofuse.htm.
June 26, 2020 -- PEC seeks to secure contracted professional engineering services to complete (1) a Geotechnical Report and (2) a Final Design for fish-friendly and flood-resilient structures to replace culverts at ONLY the Piney River (VA Rt. 653) pilot project site in Rappahannock County, VA.
A presentation delivered by the Development Bank of Latin America on March 6, 2017 at the Sea Water Air Conditioning in the Caribbean Workshop at the Caribbean Development Bank.
The document provides an environmental impact assessment for the proposed rehabilitation of the Liberia Petroleum Refinery Company. It identifies key issues raised during stakeholder consultations, including concerns about the current site location, waste management, oil spills, air quality, and community benefits. It describes the project, which involves rehabilitating storage tanks and installing new pipelines, tanks, loading racks, and other infrastructure. Specialist studies were conducted on visual impacts, air quality, waste management, water resources, flora and fauna, and socioeconomic impacts. The document recommends applying international standards to storage tanks and piping systems to improve integrity and safety. It also recommends remediation measures, installing sprinklers and firefighting equipment, and re
The document discusses considerations for using water quality offsets to help sewage treatment plants meet effluent discharge requirements for substances like total phosphorus. It outlines two mechanisms Ontario allows for offsets - site-specific arrangements and a potential trading program. Key criteria the Ministry may require are demonstrating offsets are a last resort, having monitoring agreements, contingency plans if offsets underperform, and consultation during project planning. The article provides an overview of evaluation criteria still under development to help practitioners explore offset options.
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This document summarizes updates on Salton Sea restoration programs and projects presented at a USCID conference. It describes the status of legislative actions and state agencies involved in restoration efforts. Near-term habitat and pilot projects being implemented by IID and state agencies are outlined, including Red Hill Bay, Species Conservation Habitat, and a marine habitat pilot project. IID's Salton Sea Backbone Infrastructure Project is introduced, which aims to develop infrastructure to manage drainage water for restoration uses over time. Salinity increases in the shrinking sea pose risks to public health from dust emissions if restoration is not accelerated.
EIA an introduction - Case study wrt Coastal development & AquacultureKANTHARAJAN GANESAN
This document summarizes an environmental impact assessment for the Mumbai Coastal Road Project. It describes the objectives of the EIA study as establishing the baseline environmental conditions, identifying elements that could be affected, predicting impacts, and developing mitigation measures. The report structure includes chapters on project description, alternatives analysis, environmental description, anticipated impacts and mitigation measures, and an environmental management plan. The coastal road project aims to address traffic issues in the dense city of Mumbai by constructing a 29.2 km road along the western coast, and the EIA aims to assess the project's environmental impacts and ensure sustainable development.
The Cameron LNG liquefaction project in Hackberry, Louisiana will develop natural gas liquefaction and export facilities next to its existing LNG terminal. The $10 billion project will include three liquefaction trains each with capacity of 4.5 million tonnes per year. It has received all necessary approvals and will create thousands of construction and permanent jobs. First commercial operation of the three trains is scheduled for 2019.
The document provides information about the Office of River Protection's budget and plans for fiscal year 2013. It discusses treating and disposing of radioactive waste stored in underground tanks at Hanford, continuing construction of the Waste Treatment Plant, and meeting regulatory milestones for emptying waste tanks and processing waste by certain deadlines. The budget request supports ongoing tank farm operations, waste retrieval projects, and construction and commissioning of the Waste Treatment Plant facilities.
PLN 360/560 Environmental Impact Assessment Homework No. 4 1. An applicant has applied
to the U.S. Army Corps of Engineers (USACE) for a Clean Water Act (CWA) Section 404
Permit to construct a marina at the mouth of Chaotic Creek on Bagel Bay on Lake Promise, a
Water of the United States and Class \"B\" surface water in New York State. This site is located
in the upper reach of a large commercial harbor used for deep-draft navigation. The project
entails (1) construction of a breakwall; (2) dredging (and future maintenance dredging) of
navigation entrance and creek channels; (3) installation of 50 docks with boat slips; and (4)
construction of a boat launching ramp. During construction, it is estimated that a total of 60,000
cubic yards of material will be dredged and need to be managed, and about 2,500 cubic yards of
fill will need to be placed in Lake Promise. Management alternatives for the dredged material
include placement at an upland permitted municipal landfill, or discharge at a designated open-
water site in the harbor. The site is an abandoned \"hole\" and since discharge of the dredged
sediment is conceived to have benefits through reducing DDE bioaccumulation through capping
and restoration of shallow water aquatic habitat, it is referred to as a habitat restoration site
(HRS). The applicant had a consultant sample the sediments to be dredged for the marina as well
as a lake reference area and HRS, and had the samples analyzed by a laboratory. The following
is a summary of the test results that are to be submitted with the application: Contaminant
Concentration in sediment sample of Concentration in Concentration in reference bulk HRS bulk
marina sediment to be sediment sample sediment sample dredged Bulk Standard sediment
elutriate (mg/kg)(mg/L) (mg/kg) (mg/kg) 13 0.02 Barium Cyanide Iron Mercury Dieldrin p.p\'-
DDE Chlorobenzene 16 65 0.70 13,000 120 14 53 0.40 12,500 130 0.60 11,000 100 0.02 3x10-7
8x10 1.3x10 0.32 0.008 0.0034 0.12 1.3 38,000 Total organic 21,000 10,300 carbon (TOC) a.
What type of CWA regulatory approvals (i.e., permits, etc.) would be required for this project?
(2 pts.)
Solution
Approvals required for this project -
Storm Water permit - Clean Water Act (CWA) permit coverage for discharge of storm water
runoff from the construction site which are issued throught the US Environmental protection
agency\'s NPDES (national pollutant discharge elimination system) or the state NPDES authority
Permit under section 404 of the CWA issued by US Army Crops for Engineers
Resource Conservation and Recovery Act (RCRA) permit for generators of hazardous wastes
(The RCRA regulations list quantities of hazardous wastes that determine whether a generator is
large or small.), Storage of hazardous wastes (The RCRA regulations specify the time hazardous
wastes can be stored at a site. If the storage time is exceeded, a RCRA permit is required) and
Transport, treatment, and disposal of hazardous wastes (a transporter should be a .
Some 6,500 km of CO2 pipelines has been operating for years, primarily in the United States. More recently, a number of these pipelines have been used for CO2 re-use or carbon capture and storage (CCS) operations in Europe and the Americas. Valuable experience and lessons learnt are available from these projects relevant for all phases of CO2 pipeline projects:, from early identification to execution and operation.
Based on a wide range of interviews and literature, Ecofys and SNC-Lavalin gathered information on 29 CO2 pipeline projects and then made the results accessible in a database. A reference manual was then written based on this information. This comprehensive document offers an overview of results and lessons learnt, serving as a guide to key issues on CO2 pipelines. The document relates to a number of examples in the database.
In this webinar, Frank Wiersma from Ecofys presented an overview of the study, discussing the process, lessons learnt, and findings relevant for the development, realisation and operation of CO2 pipelines.
This study was commissioned by the IEA GHG on behalf of the Global CCS Institute.
MEC401 Directed Studies In Mechanical Engineering.docxstirlingvwriters
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Aim:
A healthy, safe, secure and sustainable solid waste management system fit for a world – class city.
Improve and protect the public health of Nairobi residents and visitors.
Ecological health, diversity and productivity and maximize resource recovery through the participatory approach.
Goals:
Build awareness and capacity for source separation as essential components of sustainable waste management.
Build new environmentally sound infrastructure and systems for safe disposal of residual waste and replacing current dumpsites which should be commissioned.
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The status.
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collection efficiently is at about 50%.
Actors i.e. city authorities, CBO’s , private firms and self-disposal
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Solid waste generation – collection – dumping
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• Nairobi is one of the C40 cities in this respect , various actors in the solid waste management space have adopted a variety of technologies to reduce short lived climate pollutants including source separation , recycling , marketing of the recycled products.
• Through the network, it should expect to benefit from expertise of the different actors in the network in terms of applicable technologies and practices in reducing the short-lived climate pollutants.
Good practices:
Despite the dismal collection of solid waste in Nairobi city, there are practices and activities of informal actors (CBOs, CBO-SACCOs and yard shop operators) and other formal industrial actors on solid waste collection, recycling and waste reduction.
Practices and activities of these actor groups are viewed as innovations with the potential to change the way solid waste is handled.
CHALLENGES:
• Resource Allocation.
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Submission of Lake Ontario Waterkeeper - Relicensing hearing before the Canadian Nuclear Safety Commission (CNSC) for the Cameco Corporation Port Hope Conversion Facility
1. 1
Submissions of Lake Ontario Waterkeeper
Re: Relicensing hearing before the Canadian
Nuclear Safety Commission (CNSC) for the Cameco
Corporation Port Hope Conversion Facility
Notice of Public Hearing, Ref. 2016-H-03
October 3, 2016
Submitted to:
Participant Funding Program Administrators cnsc.pfp.ccsn@canada.ca
and the CNSC Secretariat cnsc.interventions.ccsn@canada.ca
Cc: Julia Szymanski julia.szymanski@canada.ca, and Adam Levine
adam.levine@canada.ca
2. 2
TABLE OF CONTENTS
Executive Summary …………………………………………………………………………………… 3
Background ………………………………………………………………………………………..…… 6
• About Lake Ontario Waterkeeper ……………………………………………………………. 6
• About the PHCF and its VIM project ………………………………………………………… 6
Water quality concerns at the PHCF ……………………………………………………………….. 8
• Current threats to local water quality for PHCF discharges……………………………….. 8
• Impacts of the VIM project on local waterbodies …………………………………………. 10
• Regulatory limits for liquid contaminant discharges from the PHCF ……………………. 10
• Monitoring releases from the PHCF into the Port Hope Harbour ……………………….. 11
Local aquatic ecosystems and the PHCF’s once-through cooling water system ………… 12
Public information sharing and the PHCF ………………………………………………………. 15
• Cameco’s Public Information Program ……………………………………………………. 15
• Release event reporting ……………………………………………………………………… 16
• Public information to assist with reviews of the current licensing application ………… 16
The requested licence period ……………………………………………………………………… 17
Conclusion …………………………………………………………………………………………….. 17
Appendix I: Independent Review of Hydrological Issues Pertaining to a Review of Cameco Vision
in Motion Initiative and Cameco’s Application for 2017 Renewal of Site License, Wilf
Ruland, October 3, 2016
Appendix II: Wilf Ruland, p. Geo CV
Appendix III: Pippa Feinstein, JD CV
Appendix IV: Compiled Questions and Answers between Mr. Ruland, Ms. Feinstein, Cameco staff
and CNSC staff
Appendix V: Meeting notes from Site Visit, September 26, 2016
3. 3
EXECUTIVE SUMMARY
Cameco Corporation (Cameco) is currently applying to renew its Fuel Facility Operating Licence
FFOL-3631.0/2017 (the licence) for its Port Hope Conversion Facility (PHCF). This licence was
issued on February 28, 2012, (valid from March 1, 2012) and will expire February 28, 2017.
The requested licence is for a ten-year period and would permit Cameco to continue to produce
nuclear fuel for reactors in Canada and abroad. Currently, the facility is permitted to process and
produce up to 2,800 tonnes of uranium as UO2 which is used for CANDU reactor fuel and up to
12,500 tonnes of UF6 which is exported for processing into light water reactor fuel.
The requested licence would also permit Cameco to make significant changes to its facility,
renovating some buildings, decommissioning others, and building entirely new facilities on the
PHCF site. These changes collectively comprise its Vision in Motion (VIM) project. More
specifically, Cameco’s proposed VIM project involves:
• Removing up to 150,000 cubic metres (m3
) of radioactive contaminated waste. This
includes contaminated soil excavation, “legacy” drummed waste generated at the facility
before 1988, and rubble from demolished older buildings at the PHCF site and Center
Pier). This waste will be taken to Canadian Nuclear Laboratories’ secure long-term waste
management facility in Port Hope;
• Removing 11 older or under-utilized buildings from the PHCF site and Center Pier;
• Constructing of 4 new buildings and the refurbishment or modification of 7 other buildings
at the site;
• Installing of new pump and treat wells to address the groundwater contamination that
will remain under the PHCF site after VIM is completed;
• Improving the facility’s stormwater management infrastructure; and
• Moving the eastern fence-line of the PHCF away from the harbour to help facilitate greater
public access to Port Hope’s waterfront.
Waterkeeper has been involved in several other past decision-making processes before the
CNSC concerning this facility, including its environmental assessment (EA) under the Canadian
Environmental Assessment Act, 1992, as well as its application for a Certificate of Approval from
the then Ontario Ministry of Environment for its industrial sewage permit. During these processes,
Waterkeeper expressed concerns regarding the facility’s poor stormwater management, the
need for better cooling water technology, and the need for better environmental monitoring and
public communication.
Waterkeeper was provided with participant funding in order to be able to intervene in this matter
before the CNSC and has retained two experts to examine the PHAI and make recommendations
for its improvement:
• Wilf Ruland, P. Geo, an experienced Hydrogeologist who examined the potential
impacts of the PHCF and VIM on local surface water and groundwater quality; and
• Pippa Feinstein, JD, counsel and case manager for Waterkeeper who examined and
made recommendations concerning the PHCF’s Public Information Program (PIP) and
Fisheries Act compliance.
Overall, Waterkeeper has noticed an improvement in Cameco’s operations at the PHCF. More
environmental monitoring is being undertaken, the VIM should address several legacy issues
4. 4
hindering the facility’s environmental performance, and communications and information sharing
between the facility and local residents is becoming more robust. That being said, more work is
needed.
Cameco explains its VIM project “is an opportunity to make [its facility] more visually appealing,
improve environmental performance and operational efficiency, return the Center Pier to the
Municipality and improve public access to the waterfront”.1
These are all very important goals
that Waterkeeper wholeheartedly supports. Such efforts to increase and support the
swimmability, drinkability and fishability of the Port Hope Harbour and lakeshore are long
overdue.
Since the early 1930s, refining activity around the PHCF site has proved detrimental to the
swimmability, drinkability, and fishability of the Port Hope Harbour and surrounding lakeshore,
Alexander Creek, and the Ganaraska River. While much of the initial environmental degradation
was due to a lack of understanding of the harmful substances being refined there, more recently
effluent discharge limits and environmental monitoring requirements have remained lax,
contributing further to historical pollution.
The PHCF’s location in the heart of the community’s harbour, embedded in a densely populated
town, is important to acknowledge. Many homes, business, and important aquatic communities
and habitats lie within its 1km exclusion zone. As a result, Waterkeeper stresses it is especially
important for Cameco’s VIM and its continuing conversion operations to be thoroughly
scrutinized to ensure both are undertaken in a precautionary, responsible, and effective way.
Further, fully transparent, accountable, and ongoing communication with the public about the
progress of its VIM and continuing conversion operations will be crucial. These are the
ingredients necessary for the facility’s social licence to continue operate in the community.
Should the CNSC grant Cameco’s licence renewal request, Waterkeeper recommends that the
following conditions be placed on its approval:
Recommendations concerning the PHCF’s effluent discharges and effluent monitoring
programs:
1) A final VIM-specific wastewater treatment plan should be provided for public review upon
its completion;
2) A final plan for handling contaminated water from Port Hope Harbour during and after the
completion of VIM and PHAI remediation efforts. This plan should also be provided for
public review;
3) The proposed1825 kg/year release limit for Uranium from the sanitary sewer system into
the harbour must be lowered. Reasonable Action Levels for Uranium and all other COPCs
from all three pathways to the environment are required. These limits should be provided
for public review once completed;
4) Future quarterly and annual compliance compliance monitoring reports should provide
the full list of COPCs which are being monitored for in the sanitary sewer discharges.
Additionally, the combined annual mass loading of Uranium from the sanitary sewer
discharges should also be reported;
5) In the post-VIM period, uncontrolled contaminated stormwater discharges via the storm
sewer system should be monitored at least quarterly;
1
Cameco’s relicensing application, CMD 16-H8.1 at p6.
5. 5
o This should be done at all active storm sewer lines,
o Monitoring should be conducted for all identified COPCs,
o Monitoring results should be included in all quarterly and annual compliance
reports,
o A calculation of the combined annual mass loading of Uranium to the harbour
from all active sewers should be reported in annual compliance reports;
6) Monitoring of the Pump and Treat system should continue as planned;
o Groundwater monitoring results showing the areas of contaminated groundwater
discharges not being contained by the system should also be reported in quarterly
and annual compliance reports,
o Future quarterly and annual compliance reports should contain the full list of
COPCs, those that are being monitored, and any reasons for the exclusion of
others from being monitored,
o A calculation of the combined annual mass loading of Uranium to the harbour
from all areas of uncontained contaminated groundwater should be reported in
annual compliance reports.
Recommendations concerning the PHCF’s Fisheries Act compliance:
7) Cameco’s Fisheries Act self-assessment report should be made publicly accessible as
well as CNSC staff’s review of it once it has been completed.
Recommendations concerning the PHCF’s Public information and disclosure programs:
8) The webpage reporting incidents should be included as a shortcut tab to the homepage
for the facility, as its current location is difficult to find;
9) The incident reports should include actual data of measured releases;
10) Appropriate Effluent Release Limits and Action Limits should be included in these reports
to provide the public with a better understanding of the severity of the incident;
11) The date on the first line of each report should be specified as its posting date.
Recommendation concerning the requested licence period’s length:
1) Based on the lack of information currently available to the Commission, Cameco's
relicensing application should be denied until all relevant information is available for the
Commission to make a more informed decision. In the alternative, a three to five-year
licence should be granted rather than a ten-year licence.
6. 6
Background
About Lake Ontario Waterkeeper
Waterkeeper is a grassroots environmental organization that uses research, education, and legal
tools to protect and restore the public’s right to swim, drink, and fish in Lake Ontario. Founded
in 2001, Waterkeeper is a non- political registered charity focusing on research and justice issues
in the public interest. It is dedicated to protecting and celebrating the Lake Ontario watershed,
including the wetlands, streams, rivers, and creeks that flow into the lake.
Waterkeeper also works with communities to facilitate the use of environmental laws to protect
their rights to swim, drink, and fish. The organization participates in legal processes to help
ensure that environmental decisions are made on the basis of sound and tested scientific
evidence by independent decision-makers and in the public interest. Waterkeeper is
participating in the current PHCF relicensing process to ensure the Commission considers the
public’s need for a swimmable, drinkable, fishable Lake Ontario when considering whether to
renew the PHCF licence and/or add any new licence terms.
About the PHCF and the VIM Project
Cameco first applied to make certain improvements to its Port Hope facility in 2008 – a project
that was called Vision 2010. Waterkeeper participated in the CNSC’s public hearing for this
application and raised the following:
• That Cameco’s project could be an important opportunity to remediate contaminated
lands and restore Port Hope’s waterfront from industrial to public use; and
• That Cameco’s project would be difficult for an EA to assess because it involved
simultaneously decommissioning, remediating, and refurbishing different parts of its
facility, as well as constructing completely new buildings.
Waterkeeper also requested that the EA, once undertaken, be based on real data rather than risk
assessment.
In 2009, Cameco requested a Certificate of Approval (CoA) for sewage works which would permit
it to release cooling water effluent into Lake Ontario.2
Waterkeeper prepared submissions to the
CNSC, Environmental Commissioner of Ontario, and the then Ontario Minister of Environment
(MOE) raising the following:
• That the MOE was obligated to consider the CoA application in light of the extensive
historic contamination in Port Hope;
• That cooling water can degrade the environment (due to both chemical and thermal
pollution) and that Cameco must mitigate this impact by implementing ‘gold-standard’
cooling water technology; and
• That the terms of both federal and provincial permits related to Cameco’s facility should
be better coordinated.
In 2011, the Environmental Impact Statement (EIS) for Cameco’s refurbishing and
decommissioning project was released. Waterkeeper was an intervener in the CNSC’s public
2
Although, it appears it had been releasing effluent into the lake for decades prior to this point, without
any permit to do so.
7. 7
hearing to consider the EIS and determine whether to grant Cameco a licence that would cover
its planned renovations. For its intervention, Waterkeeper retained the services of David
Dillenbeck and Wilf Ruland who provided expert reports concerning stormwater and wastewater
issues at the site. The following is a brief summary of Waterkeeper’s submissions concerning
the EIS:
• That the Cameco site is contaminated with a variety of pollutants (including over 87,500
cubic metres of contaminated soil) that fall under both federal and provincial jurisdiction
(containing Uranium, Petroleum Hydrocarbons, Vinyl Chloride, Trichloroethylene,
Ammonia, Radium-226, and Arsenic);
• That the site is located in a designated Area of Concern (A of C) and that there are many
pathways for the contaminated site to pollute surrounding surface and groundwater;
• That there was no stormwater quantity or quality management system at the facility and
that stormwater from the facility ran directly into Port Hope’s harbour via outfalls and
terrestrial runoff;
• That the EIS lacked sufficient information (especially with regards to baseline
characterization) and that it lacked a commitment to conduct surface water monitoring
during the project’s operations;
• That the project provided an opportunity to institute a stormwater management system.
Here, Waterkeeper made several recommendations concerning preferable options for
such a system;
• That a better plan to address flooding and spills was required;
• That wastewater estimates according to Cameco (48,000 m3
) may be low and that there
was contradictory information about these estimates in Cameco’s application.
Clarification of its plans, and the data used to inform them, were requested;
• That a plan be instituted for the contaminated water produced from the dewatering
process for contaminated soil, as no such plan was specified;
• That the harbour wall be made impermeable to prevent further groundwater movement
from the site, as no such plan was specified; and
• That the methods for sampling, processing, and disposal of contaminated soil be further
clarified. Waterkeeper recommended that Cameco use best industry practices when
addressing these issues at their facility.
The EA for the project proceeded as a comprehensive report which was released in May 2012.
It concluded that Cameco’s proposed changes to its facility would not cause significant
environmental effects, taking specific mitigation measures into account.
Since these past processes, some of Waterkeeper’s past concerns have been addressed by
Cameco and the plans for its VIM project: new impenetrable harbour walls will be installed along
the west wall of the harbour, plans to address flooding and spilling are being developed with
adequate ‘severe storm’ scenarios being taken into account, monitoring and sampling plans for
the site have been improved, stormwater infrastructure will be upgraded, and public information-
sharing with the public has increased.
At the same time, many concerns persist: additional environmental monitoring is still required to
better understand the PHCF’s effects on the local environment, more comprehensive and
demanding effluent release limits must be developed and made legally enforceable, information-
sharing with the public must be more robust and include better data sharing.
8. 8
The Commission can only renew Cameco’s a licence if it finds the legal test in section 24(4) of
the Nuclear Safety and Control Act (NSCA) is met. This section specifies:
No licence shall be issued, renewed, amended or replaced — and no authorization to
transfer one given — unless, in the opinion of the Commission, the applicant or, in the case
of an application for an authorization to transfer the licence, the transferee
(a) is qualified to carry on the activity that the licence will authorize the licensee to carry
on; and
(b) will, in carrying on that activity, make adequate provision for the protection of the
environment, the health and safety of persons and the maintenance of national security
and measures required to implement international obligations to which Canada has
agreed.
Waterkeeper submits that this test will only be met if the Commission adopts the
recommendations included in these submissions.
Water quality concerns and the PHCF
Mr. Ruland has been retained by Waterkeeper to review Cameco’s plans for its VIM project as
well as its continuing conversion operations. He had previously reviewed the VIM and Cameco’s
operations for Waterkeeper in 2011, and was thus familiar with the facility, its operations, and
areas in which its impact on local water quality could be improved.
In his review for this current relicensing process, Mr. Ruland noted that Cameco’s operations
and plans have generally improved over the last five years. At the same time, he has still identified
several areas that require more work. Waterkeeper accepts all of Mr. Ruland’s recommendations
and submits them for the Commission’s consideration. There are four categories of findings and
recommendations below:
• An overview of current threats to local water quality posed by the PHCF’s effluent
discharges;
• The adverse impacts the VIM project will have on local waterbodies and
recommendations for how they should be addressed;
• The current effluent release limits for the facility and recommendations for how they
should be strengthened; and
• The current water quality monitoring plans and how they should be improved.
Current threats to local water quality from PHCF discharges
Due to decades of refining operations around the Port Hope Harbour, and due to the lack of
knowledge in the early days of this activity about the adverse impacts of these substances could
have on the health of locals and the environment, refining operations were not adequately
contained and local water quality was severely degraded. Mr. Ruland explains that local
groundwater and soils on the PHCF site and its surroundings have long been contaminated with
the following Contaminants of Primary Concern (COPC): Uranium, Arsenic, Ammonia, Nitrate,
Flouride, Radium-226, Trecholoroethylene, Dichloroethylene, and Vinyl Chloride.
9. 9
Contaminated soils and groundwater are present across the main PHCF site, as well as the
Center Pier, and Port Hope Harbour. Mr. Ruland has found that Uranium levels below certain
portions of the PHCF measure in the 1000s of ug/L, with peak levels of over 20,000 ug/L; this is
between 50 and 1000 times higher than the Ontario Drinking Water Quality Standard for Uranium
(which is 20 ug/L), and between 200 and 4000 times higher than the Ontario Provincial Water
Quality Objectives for Uranium (5 ug/L).3
While the Center Pier, harbour, and a few meters into the harbour’s west wall will be excavated
down to bedrock by the Port Hope Area Initiative (PHAI), much of the contaminated soils and
water below the PHCF will remain.
Cameco is trying to remediate this contamination below its facility. Approximately 60% of
contaminated groundwater is currently contained by the facility’s pump and treat system,
reducing the previous release of 25-30 kg/yr of Uranium into the harbour down to 5 kg/yr.
Cameco expects that these emissions will be further reduced after the VIM project is completed
and the new impermeable harbour walls are installed. Cameco is expecting the pump and treat
system to capture 95% percent of groundwater flow to the harbour once the VIM is completed.4
Other contaminated water is also discharged into the harbour via the stormwater system for the
facility. Mr. Ruland believes that there are leaks and breaks in the PHCF’s aging stormwater
network, and that some amount of contaminated groundwater enters the pipes and is released
directly into the harbour. While Mr. Ruland stresses this issue is not as serious as it was when
he first identified it back in 2011, it is still a significant cause for concern. In particular, he found
that the PHCF lacked any Effluent Release Limits or Action Levels for these stormwater
discharges, meaning that these pollution pathways were essentially not being regulated at all.
There is a significant lack of transparency with regards to current monitoring plans to track
stormwater discharges into the harbour. While Cameco has asserted it monitors stormwater
discharge points semi-annually, there is no additional publicly available information concerning
this monitoring plan. This ultimately prevents public scrutiny of the plan (for instance, Mr. Ruland
has been unable to determine whether it adequately protects local water quality, or whether it
could be improved in certain ways). It also raises questions with regards to the extent to which
the CNSC is aware of this situation.
Mr. Ruland found that the majority of water contamination in the harbour was a result of the
PHCF’s contaminated stormwater discharges and that average Uranium concentrations in the
storm sewer discharges to the harbour were 218 ug/L.5
Uranium is a “key indicator” of low-level
radioactive waste and a surrogate for the presence of many other potentially harmful
contaminants, thus these findings for Uranium would likely be similar for other COPCs being
released into the harbour via PHCF’s stormwater system.
The PHCF also releases wastewater into the municipal sewer system where it is fed into the Port
Hope’s municipal Water Treatment Plant and treated (to an unknown extent) before being
3
Independent Review of Hydrological Issues Pertaining to a Review of Cameco Vision in Motion Initiative
and Cameco’s Application for 2017 Renewal of Site License, Wilf Ruland, October 3, 2016 at p 7, (the
“Ruland Report”).
4
Appendix V to this submission, Meeting notes from September 26 Site Visit.
5
Ruland Report at p 7.
10. 10
released into Lake Ontario. Mr. Ruland found that the PHCF’s discharges of Uranium into the
municipal sewer systems averaged at 19 ug/L, almost four times the PWQO for this
contaminant.6
Impacts of the VIM Project on local waterbodies
During the implementation phase of the VIM project, the PHCF will generate considerably more
contaminated waste water in need of treatment. Cameco does not yet have a plan for addressing
this issue, instead assuring that it will either be treated at the municipal treatment plant, or else
its own water treatment system (which evaporates wastewater). However, it is unclear whether
either of these facilities will have the capacity to treat this additional PHCF wastewater. This plan
also raises questions concerning the ability of the municipal treatment plant to adequately treat
the contaminants present in PHCF wastewater. Most municipal treatment plants in Ontario do
not have the capacity to treat for radioactive contaminants.7
The additional wastewater present in the harbour during excavation activities is also cause for
concern. As the dredging and excavation work in and around the harbour progresses, the
contaminant concentrations in the harbour water will become increasingly elevated. While the
harbour will be sealed off to prevent the entry of fish during this work, Mr. Ruland highlighted
questions about what will happen once the harbour is opened up to the lake again. It will be
important, and difficult, to ensure contaminants in the harbour water are not freely discharged
into the lake once the harbour mouth is reopened.
To address this, Mr. Ruland recommends that regular monitoring of both the harbour and beyond
the harbour’s mouth be undertaken (at least monthly, and after any rain events) to determine
how contaminants in the water are behaving. He also believes the results of these samples
should be made publicly available.8
Waterkeeper strongly supports both recommendations.
Regulatory limits for liquid contaminant discharges from the PHCF
Mr. Ruland explains in his expert report that he has “grave concerns” about the licencing
oversight by the CNSC of the PHCF’s operations. These concerns extend to the regulation of
contaminated liquid effluents from the site, effluent monitoring, and lack of publicly available
information concerning this monitoring.
The PHCF discharges contaminated water into the Port Hope Harbour and Lake Ontario via three
pathways: 1) contaminated stormwater discharges to the municipal sewer system (which are
ultimately released into the Lake after an unknown level of treatment); 2) releases of
contaminated stormwater (via PHCF’s storm sewer network) into the harbour; and 3)
groundwater from contaminated areas of the PHCF site discharging to the harbour. However,
6
Ruland Report at p 8.
7
Review of the State of Knowledge of Municipal Effluent Science and Research Report, Prepared for:
The Development Committee for the MWWE Canada-Wide Strategy Canadian Council of Ministers of
the Environment, Hydromantis Inc., University of Waterloo, Dept. of Civil Engineering, January 2006, at p
30.
8
Ruland Report at pp 10-11.
11. 11
none of these discharges are being addressed in the current CNSC licence which constitutes a
“significant failure in oversight”.9
According to CNSC staff’s draft Licence Conditions Handbook, it appears as though only the
sanitary sewer system (the least contaminated of the three pathways) will be subject to a release
limit. Further, this release limit is only for Uranium and is astronomically high: 1825 kg/yr or 1.8
tonnes per year. Cameco has explained this is a theoretical limit which was arrived at by
calculating the maximum amount that could be discharged to the water until the regulatory limit
of a 1mSv public dose would be reached for Port Hope inhabitants. Mr. Ruland notes that this
limit fails to take into consideration the fact that Uranium contamination adversely impacts
humans and aquatic biota not only due of its radioactivity, but also its toxic chemical properties.
Furthermore, as already explained in this submission above, Uranium as an indicator substance
and surrogate for other contaminants, As such, permitting exceptionally large discharges of
Uranium will by extension also likely permit similarly high levels of other COPCs.
This proposed release limit for Uranium is over 90 times higher than the ODWQs for Uranium
and 365 times higher than the PWQO for Uranium. Mr. Ruland warns that,
The CNSC’s proposed release limit of 1825 kg/year in sanitary sewer discharges is so
absurdly high that there would be appalling exceedances of the ODWQs and PWQOs in
whatever surface water body was receiving these discharges, with dire consequences
for aquatic life. If discharged to the Port Hope Harbour, 1825 kg/year of Uranium would
turn the Harbour into a killing zone for aquatic life.10
If released to the lake, elevated contaminant levels would cause this killing zone extend into the
lake itself.
To address this concern, Mr. Ruland recommends that Cameco and CNSC staff immediately
develop more appropriate Action Levels for Uranium for all three pathways through which
contaminated water reaches the harbour and lake. He also recommends that similarly
appropriate Action Levels, and more responsible Effluent Release Limits for all COPCs being
released into the environment via these pathways. All these limits should be included as
conditions for Cameco’s new licence. Waterkeeper strongly supports these recommendations.
Monitoring of releases from the PHCF into the Port Hope Harbour
There is a lack of publicly available information concerning the specifics of much of the
wastewater monitoring at the PHCF. It appears as though wastewater discharges from the
sanitary sewers are monitored weekly for Uranium, Flouride, Ammonia and Nitrates, although
there is no available information as to whether any other COPCs are tested for.
Mr. Ruland recommends that monitoring should include all COPCs for the site, if it doesn’t
already and that these monitoring results be included with other monitoring results currently
reported in Cameco’s quarterly compliance reports. Mr. Ruland also recommends a calculation
of the combined annual mass loading of Uranium to the harbour from all sanitary sewer
discharges be done every year and reported in the annual compliance monitoring reports for the
facility. Waterkeeper strongly supports these recommendations
9
Ruland Report at p 11.
10
Ruland Report at p12.
12. 12
Monitoring results from the uncontrolled stormwater releases (via the storm sewer system) are
also not publicly available. Current monitoring plans are also inadequate with monitoring only
being conducted at seven of ten active outfalls, and only semi annually. It is also unclear which
contaminants are being tested for.
Mr. Ruland recommends that monitoring should be conducted at least quarterly and that all
discharge points be monitored for all COPCs. The results of this monitoring should be included
in quarterly and annual compliance reports, and a calculation of the combined annual mass
loading of Uranium to the harbour from all active storm sewers should be done every year and
reported in annual compliance monitoring reports for the facility. Waterkeeper strongly supports
these recommendations
The results of Cameco’s Pump and Treat monitoring system are not publicly reported. However,
Mr. Ruland was able to obtain a report from Cameco staff after his site visit that contains
monitoring results from 2015. The report he obtained shows that pumping wells are monitored
monthly for a short list of COPCs (Uranium, Radium-226, Arsenic, Nitrate, Flouride, and
Ammonia) and annual monitoring occurs at these wells for a longer list of general chemistry
parameters, VOCs and metals. Much of the contaminated water is extracted and evaporated at
the facility’s treatment system, while the remainder leaks into the harbour.
Mr. Ruland recommends that the combined annual mass loading of Uranium to the harbour from
all areas of uncontained contaminated groundwater be assessed and reported in the facility’s
annual compliance reports. Waterkeeper strongly supports these recommendations and
would also recommend that the results of this pump and treat monitoring be publicly released in
quarterly and annual compliance reports.
Local aquatic ecosystem and the PHCF’s once-through cooling water
system
Port Hope supports significant fish populations. The Environmental Risk Assessment (ERA) for
the facility includes a description of the local aquatic environment. It explains that alewife,
rainbow smelt, threespine stickleback, and lake whitefish spawn along the shoreline of Lake
Ontario in Port Hope. It notes the Ganaraska River has resident populations of brown trout, brook
trout, rainbow trout, and walleye. Northern pike and lake whitefish also spawn in the river which
provides nursery habitat for these species. The ERA explains that the Ganaraska River is a (“key
producer”) spawning site for wild chinook salmon and coho salmon. It also explains the harbour
provides sheltered warmer water for a modest aquatic community including smallmouth bass,
yellow perch, and spottail shiner.11
The PHCF relies on a once-through cooling system for its conversion operations. The system
draws in water from an intake pipe in the harbour, close the open lake. The water then gets
passed through pipes around the UO2 and UF6 facilities’ machinery, absorbing the heat
generated in processing the substances, and thus cooling them down. Once the water passes
11
Appendix E, the Environmental Assessment Report for Cameco’s Port Hope Conversion Facility
Relicensing Application, CNSC Staff CMD 16-H8 at p21 (the “PHCF Environmental Assessment
Report”).
13. 13
through the facilities, it is discharged back into the harbour at a higher temperature, and with
some degree of contamination picked up while passing through the pipes. The system is subject
to conditions in an Environmental Compliance Approval (ECA) as well as a permit to take water
(PTW), both issued by the Ontario Ministry of Environment and Climate Change (MOECC).
Over its past licence term, Cameco initiated a self-assessment to determine whether it would
require a permit from the Department of Fisheries and Oceans Canada (DFO) to operate its once-
through cooling system.
Baseline impingement12
sampling was conducted from October to December 2012, and then
again from April to July 2013. Apparently only round goby, alewife and crayfish were found to
have been impinged and not in significant numbers. Baseline entrainment13
sampling occurred
from June to July 13 and March to July 2014. During 2013 testing, rainbow trout, brown trout,
blue gill, smallmouth bass, and crayfish juveniles were identified as well as round goby eggs,
and white sucker eggs and larva. The ERA for Cameco’s application confirms no species at risk
were identified during these studies except for an incident between April and May 2014 when
the north side of the intake structure breached and allowed fish to pass through the cooling
system, bypassing the intake screen. During that incident, round goby, rainbow trout, brook
sickleback, white sucker, yellow perch and a juvenile snapping turtle were sucked into the
system. The snapping turtle is a federal and provincial species of concern, subject to a federal
management plan. The intake structure was subsequently repaired and no more snapping turtles
have been found to be impacted by the cooling water system.14
No action is mentioned with regards to preventing similar incidents from happening again. Nor
does it appear as though there is regular monitoring of the cooling water system’s intake outside
of these self-assessment periods.
The ERA also discusses three thermal studies which were conducted on behalf of the PHCF
between 2011 and 2014. In assessing thermal discharges from the cooling system, CNSC staff
observed thermal exceedances in the summer months of 2011 but noted they were probably
due to natural processes in the harbour. Staff also noticed that exceedances were observed or
predicted between September and December (of an unspecified year). They were associated
with one of the two cooling water outfalls, and risks to different species were identified on the
assumption that fish spent the entire period in the turning basin during the exceedances.
However, further study indicated that fish did not necessarily spend a significant amount of time
in the turning basin during October and November. No tagging study was done to determine fish
movement during December, which was the month that exhibited the highest number of thermal
exceedances.
It does not appear as though any further efforts were undertaken to verify the cause of thermal
exceedances, better map how fish populations may be have been affected, determine whether
12
The term impingement refers to a process whereby larger aquatic species are killed by being drawn up
and crushed against the intake grate of the cooling water system.
13
The term entrainment refers to a process whereby juvenile fish, eggs, and larvae are drawn through
the intake grates and into the cooling water system, often resulting in death or serious injury.
14
PHCF Environmental Assessment Report at p31.
14. 14
these exceedances have continued since 2014, or determine the adequacy of thermal discharge
limits for the facility.15
If any impingement, entrainment, thermal pollution, or other monitoring is conducted to asses
the PHCF’s cooling water system system, Waterkeeper recommends that their findings be
included in quarterly or annual compliance reports.
In its current relicensing application, Cameco explains, “[t]he self-assessment determined that
much less that one kilogram of fish was lost to the ecosystem with the existing cooling water
operation and mitigation in place. At this low potential impact, an authorization is not required”.16
Cameco fails to mention over what period this one kilogram of fish is killed. And despite asserting
a permit would not be needed, Cameco also concedes that CNSC staff were still reviewing its
study to determine whether this is in fact the case.
In CNSC staff’s CMD for this hearing, they confirm that they are still in the process of reviewing
this document, although they provide no estimated completion date for their review.17
When Ms.
Feinstein requested a copy of this report, or more information about its findings, Cameco refused
to provide further information. When Ms. Feinstein inquired with the Commission about when
CNSC staff would complete their review of this assessment, staff explained their review would
not be completed by the hearing in November. Staff also asserted that “[w]hile Cameco has
submitted the self-assessment and it is discussed in the CMD, it is not linked to Cameco’s
licence application for the renewal of the PHCF and therefore, does not impact or impede the
decision for Cameco’s licence application”.18
However, a Memorandum of Understanding (MOU) between the CNSC and DFO requires that
when rendering a licence decision, Commission Members must consider “the intent and
requirements of the Fishers Act, [Species at Risk Act], and their associated regulatory and policy
frameworks”.19
Licence hearings determine the conditions to be applied to facilities’ operations.
Cameco’s self-assessment should have been made available to help inform any need for CNSC
licence conditions to be drafted concerning the cooling water system.
Waterkeeper submits that CNSC staff should have completed their assessment for the licence
hearing so that the results of Cameco’s assessment and staff’s recommendations concerning
the need for a DFO permit could be subject to public review, and if needed incorporated into the
facility’s licence conditions. However, Waterkeeper does not necessarily accept that such a
licence, if needed, should be granted to the facility without a full public review of the facts.
Waterkeeper recommends that this report be made publicly accessible, in addition to the
findings of CNSC staff’s review of it, as soon as the review is completed.
15
PHCF Environmental Assessment Report at p32.
16
Cameco’s relicensing application, CMD 16-H8.1 at p61.
17
CNSC Staff CMD 16-H8 at p76.
18
Appendix IV to these submissions, Ms. Feinstein’s personal communication with CNSC staff,
September 23.
19
Canadian Nuclear Safety Commission and Fisheries and Oceans Canada, “Memorandum of
Understanding Between Fisheries and Oceans Canada and the Canadian Nuclear Safety Commission
for Cooperation and Administration of the Fisheries Act and Species at Risk Act Related to Regulating
Nuclear Materials and Energy Development”, December 16, 2013, at sections 3 and 4.
15. 15
Public information sharing at the PHCF
Cameco’s Public Information Program
According to the proposed Licence Conditions Handbook for the PHCF, “The primary goal of a
public information and disclosure program is to ensure that information related to the health,
safety and security of persons and the environment, and other issues associated with the
lifecycle of the nuclear facilities are effectively communicated to the public”.20
A robust and
transparent PIP also lies at the heart of any facility’s social licence to operate within a community.
Section 2.6 of the PHCF’s current licence requires a Public Information Program (PIP).21
Public
Disclosure protocols are usually developed as part of the PIP.
Ms. Feinstein requested a copy of the facility’s PIP for review, however, Cameco only provided
its Public Disclosure Protocol (PDP), which is already publicly available via an embedded link on
the PHCF’s website. When asked about why the full PIP couldn’t be released, Cameco explained
that it never discloses program documents to the public, and that its PIP is considered a program
document.
From what Ms. Feinstein has been able to gather, the PIP involves public presentations and
“community forums” about the facility and provides tours of its facility to interested members of
the public. At the same time, it appears the company relies on its website as its main public
interface and forum for public information disclosure.
CNSC staff’s CMD noted that CNSC staff had made recommended improvements to the PHCF’s
PIP.22
When Ms. Feinstein asked about the improvements CNSC staff had recommended, staff
replied that there were two separate discussions between Cameco and CNSC staff concerning
their program. One concerned some “administrative changes” to its program that Cameco made
in September 2015. The other concerned a generic request by CNSC staff in 2016 that required
all Class 1A and 1B facilities to review how events are reported to the CNSC and the public.23
This seems inconsistent with Cameco’s explanation of the improvements they were asked to
make to their PIP. At the September 26 site visit, Cameco staff explained that CNSC staff’s
recommendations for the company’s PIP were in response to an incident earlier that year which
involved a transport accident in which transported yellow cake was released from a vehicle after
it was involved in an accident on Highway 4 near Swift Current, SK.24
Cameco has since refused
to disclose any further information about what their current PIP improvements concern.
20
Draft licence condition 1.4, in CNSC Staff CMD 16-H8.
21
Current Nuclear Fuel Facility Operating Licence, Cameco Corporation Port Hope Conversion Facility,
FFOL-3631.00/2017, section 2.6.
22
CNSC Staff CMD 16-H8 at p75.
23
Regulatory action – Issued to multiple licensees: Class 1 nuclear facilities and uranium mines and
mills, 2016, “Request pursuant to subsection 12(2) of the General Nuclear Safety and Control
Regulations – reporting processes”, February 25, 2016, online: http://nuclearsafety.gc.ca.
24
See: “Nuclear-related event reports”, 2016 Transport/In Transit events, online:
http://nuclearsafety.gc.ca.
16. 16
With such limited information, it is difficult to provide general comments about Cameco’s PIP.
Furthermore, the opacity with regards to Cameco’s PIP is concerning as one would expect the
public communications strategy to be especially open to the public and available for broad
inquiry and input.
Release event reporting
Over this past licence period, there have been 15 “minor spills” from the PHCF. Each was
reported to the CNSC and MOECC. These release events involved discharges of potable water,
steam condensate, contaminated groundwater, and hydraulic fluid to the harbour.25
Cameco has
assured the Commission in its application that all these events were disclosed to the public by
being posted to their website. Cameco’s Public Disclosure Protocol for the PHCF confirms that
the company undertakes to provide “timely information postings” on its website about “unusual
operational events” that may have off-site consequences. The Protocol also confirms that
environmental incidents reported to the CNSC under section 29 of the General Nuclear Safety
and Control Regulations and non-routine environmental incidents reported to the MOECC
Ontario Spills Action Center are also posted online.
Cameco’s webpage for the Port Hope Conversion facility contains a lot of important information
about the PHCF, presented in very accessible ways. This homepage26
contains simplified
explanations of its current licence renewal application, notes from recent community forum
events, a 2016 survey of public attitudes to the facility, and the most recent quarterly compliance
report for the PHCF. This homepage for the facility also contains links to a simplified version of
its Vision in Motion project description, a description of its UF6 conversion process and a
frequently asked questions (FAQ) page. Entering “Cameco Port Hope” into a Google search
engine, this is the first page that appears.
The homepage also contains three tabs to the right of the webpage each containing more
information about “Environment and Safety”, “Community”, and “Economy”. The bottom of the
main “Environment and Safety” webpage is an embedded link that when clicked on opens a new
webpage with incident reports. Incidents are listed and briefly described, in some instances with
follow-up comments or updated notes added to them.
While Waterkeeper commends Cameco for posting these events, postings should be more
prominent on the facility’s website, as their current location is easily missed. These alerts are
presumably intended as public warnings, and thus should be easily and quickly accessible.
Waterkeeper recommends that a link to this webpage with reported incidents be included as a
shortcut tab to the homepage for the PHCF. Waterkeeper also recommends that each incident
report include actual data of measurable releases. If the data is not available at the time of
posting, it should be added as an update to the report once quantities have been assessed.
Applicable Effluent Release Limits or Action Limits should also be included in each report so that
the public the public can gauge the severity of the incident. Finally, Waterkeeper recommends
that the date on the first line of each report be specified as its posting date so that members of
the public can more easily compare posting dates with event dates.
25
Cameco’s relicensing application, CMD 16-H8.1 at p 40.
26
This webpage is found online at: https://www.cameco.com/fuel_services/port_hope_conversion/.
17. 17
Public information to assist with reviews of the current relicensing application
There have been several points over the course of preparing for these hearings that Mr. Ruland
and Ms. Feinstein have not had access to sufficient information. These public information
shortages concerned water treatment issues during VIM construction and implementation,
Cameco’s Fisheries Act self-assessment, Cameco’s full PIP, and the PHCF’s stormwater
management plan.
At the site visit between Cameco staff, Mr. Ruland and Ms. Feinstein, Cameco’s hesitancy to
release raw data and large reports was discussed. Apparently, Cameco’s past disclosures had
at some point been taken and used out of context by members of the public, causing difficulties
for the company. Waterkeeper is sensitive to this issue, and at the same time believes that this
past experience should not permit the company’s operations to remain opaque or exempt from
public scrutiny. Cameco may still provide the context it deems appropriate to accompany any
release of raw monitoring data or plans, helping to ensure that it is properly understood by the
public.
The requested licence period
The next ten years will see significant changes to the PHCF, not to mention significant changes
to the ecosystems in which it is situated (especially Port Hope Harbour). Ten years is simply too
long a period to go without proposer public review of the facility and its operations.
Based on the lack of information available to the Commission to fully assess the PHCF’s impact
on the local environment, or its mitigation plans, Cameco's relicensing application should be
denied until all relevant information is available.
Should the CNSC decide to renew the PHCF’s licence, Waterkeeper submits this should only be
done for a three to five-year term rather than ten years. This will provide Cameco with enough
time to gather additional information the Commission will require to make a more informed
licensing decision. Given the changes to its facility in the last five years since Waterkeeper’s
involvement in Cameco’s last relicensing application, this seems like a more reasonable licence
term that ensures accountability and proper public review of its operations. Certain documents,
including the PHCF’s Environmental Risk Assessment (ERA), already have to be updated every
five years.27
Conclusion
Since Waterkeeper’s last review of the PHCF and VIM project, several improvements to
Cameco’s environmental footprint have occurred or been planned: new impenetrable harbour
walls will be installed along the west wall of the harbour, plans to address flooding and spilling
are being developed with adequate ‘severe storm’ characteristics being taken into account,
27
Cameco’s relicensing application, CMD 16-H8.1 at p18.
18. 18
monitoring and sampling plans for the site have been improved, stormwater infrastructure will
be upgraded, and public information-sharing with the public has increased.
At the same time, many concerns persist: additional environmental monitoring is still required to
better understand the PHCF’s effects on the local environment, more comprehensive and
demanding effluent release limits must be developed for the PHCF and made legally enforceable
as licence terms, information-sharing with the public must be more robust and include increased
disclosure of monitoring plans and sampling data.
If the Commission chooses to approve Cameco’s relicensing application, Waterkeeper submits
the following recommendations should be adopted by the Commission and added as conditions
on Cameco’s new licence.
Recommendations concerning the PHCF’s effluent discharges and effluent monitoring
programs:
2) A final VIM-specific wastewater treatment plan should be provided for public review upon
its completion;
3) A final plan for handling contaminated water from Port Hope Harbour during and after the
completion of VIM and PHAI remediation efforts. This plan should also be provided for
public review;
4) The proposed1825 kg/year release limit for Uranium from the sanitary sewer system into
the harbour must be lowered. Reasonable Action Levels for Uranium and all other COPCs
from all three pathways to the environment are required. These limits should be provided
for public review once completed;
5) Future quarterly and annual compliance compliance monitoring reports should provide
the full list of COPCs which are being monitored for in the sanitary sewer discharges.
Additionally, the combined annual mass loading of Uranium from the sanitary sewer
discharges should also be reported;
6) In the post-VIM period, uncontrolled contaminated stormwater discharges via the storm
sewer system should be monitored at least quarterly;
o This should be done at all active storm sewer lines,
o Monitoring should be conducted for all identified COPCs,
o Monitoring results should be included in all quarterly and annual compliance
reports,
o A calculation of the combined annual mass loading of Uranium to the harbour
from all active sewers should be reported in annual compliance reports;
7) Monitoring of the Pump and Treat system should continue as planned;
o Groundwater monitoring results showing the areas of contaminated groundwater
discharges not being contained by the system should also be reported in quarterly
and annual compliance reports,
o Future quarterly and annual compliance reports should contain the full list of
COPCs, those that are being monitored, and any reasons for the exclusion of
others from being monitored,
o A calculation of the combined annual mass loading of Uranium to the harbour
from all areas of uncontained contaminated groundwater should be reported in
annual compliance reports.
Recommendations concerning the PHCF’s Fisheries Act compliance:
19. 19
8) Cameco’s Fisheries Act self-assessment report should be made publicly accessible as
well as CNSC staff’s review of it once it has been completed.
Recommendations concerning the PHCF’s Public information and disclosure programs:
9) The webpage reporting incidents should be included as a shortcut tab to the homepage
for the facility, as its current location is difficult to find;
10) The incident reports should include actual data of measured releases;
11) Appropriate Effluent Release Limits and Action Limits should be included in these reports
to provide the public with a better understanding of the severity of the incident;
12) The date on the first line of each report should be specified as its posting date.
Recommendation concerning the requested licence period’s length:
13) Based on the lack of information currently available to the Commission, Cameco's
relicensing application should be denied until all relevant information is available for the
Commission to make a more informed decision. In the alternative, a three to five-year
licence should be granted rather than a ten-year licence.
20. Independent Review of Hydrogeological Issues
Pertaining to a Review of the Cameco Vision in Motion Initiative
and Cameco’s Application for 2017 Renewal of Site License
Prepared for:
Lake Ontario Waterkeeper
c/o Mr. Mark Mattson, President
Prepared by Wilf Ruland (P. Geo.)
766 Sulphur Springs Road
Dundas, Ontario
L9H 5E3
(905) 648-1296
deerspring1@gmail.com
October 3rd, 2016
page 1
21. Table of Contents
1) Introduction.............................................................................................................................! 3
2) Background and Overview of the PHCF................................................................................! 4
3) Brief Overview of the PHAI...................................................................................................! 5
4) Description of the Contamination at the PHCF ....................................................................! 5
.................................................................................................................a) Introduction ! 5
................................................................................b) Contaminated Soils at the PHCF ! 6
........................................................c) Contaminated Sediments in Port Hope Harbour ! 6
d) ....................................................................Contaminated Groundwater at the PHCF! 7
..................................e) PHCF-Contaminated Storm Sewer Discharges to the Harbour! 7
......................................f) Discharges from the PHCF to the Municipal Sanitary Sewer! 8
5) Vision in Motion Project - Opportunities and Concerns .......................................................! 8
.................................................................................................................a) Introduction ! 8
..............................................................................................b) VIM Project Description! 9
.................................................................c) Potential for Flooding of VIM Excavations! 9
........................................d) Treatment of Contaminated Wastewater from VIM Project! 10
...............e) Management of Water in Port Hope Harbour During PHAI/VIM Projects! 10
.........................................................................f) Incomplete Remediation of the PHCF! 11
6) 2017 Site License Renewal and Concerns about Effluent Releases and Monitoring ........! 11
...............................................................................................................a) Introduction ! 11
.............b) Inadequate Regulation of Contaminated Liquid Emissions from the PHCF! 11
........c) Improvements Needed for Monitoring/Reporting of Contaminated Discharges! 13
7) Discussion ..............................................................................................................................! 14
8) Conclusions............................................................................................................................! 15
9) Recommendations..................................................................................................................! 16
Appendix 1) List of Documentation Reviewed or Referenced.................................................! 18
page 2
22. 1) Introduction
I am a hydrogeologist, and I have worked as a professional for 30 years (2 years in Germany and
28 years in Canada). I am a specialist in groundwater and surface water contamination issues,
and have investigated many such issues over the course of my consulting career. I have given
testimony as an expert witness on hydrogeological issues before various boards, including the
Environmental Review Tribunal, the Environmental Assessment Board, the Joint Board, the
Ontario Municipal Board, the Niagara Escarpment Commission, and the Canadian Nuclear
Safety Commission (CNSC). A copy of my Curriculum Vitae is available upon request.
I have been retained as an expert by Lake Ontario Waterkeeper (LOW) to provide an
independent review of the Cameco Vision in Motion (VIM) initiative and the associated 2017
Site License Renewal Application for the Cameco Port Hope Conversion Facility (PHCF). I
should note that LOW received CNSC funding to support my review.
Vision in Motion is Cameco’s name for a process by which the company will be permitted
(through legal agreement with the Canadian government and local municipalities) to bring up to
150,000 m3 of Low Level Radioactive Wastes (LLRWs) including contaminated soils and
building demolition debris into the soon to be opened Port Hope Long Term Waste Management
Facility (LTWMF) for long-term storage/disposal.
The 2017 License Renewal Application (if approved) will provide a 10-year extension to
Cameco’s operating license for the PHCF including explicit approval to carry out the activities
associated with VIM.
The focus of my review are the potential groundwater and surface water quality impacts related
to inorganic, organic, and radiological contaminants which may be associated with any aspect of
VIM and/or the PHCF’s current and proposed future operations under the proposed new site
license. Such impacts can affect water quality and aquatic life in Port Hope Harbour and/or Lake
Ontario.
The adequacy of VIM and the proposed 2017 site license renewal (from a water quality
protection perspective) can be measured at this time by the degree to which Cameco’s associated
documentation provides:
- an accurate understanding of existing soil, groundwater and surface water conditions on
the Cameco PHCF property and its surroundings;
- a well thought-out and comprehensive plan to remove the LLRW from the PHCF
property;
- plans for operating the PHCF through the 10-year license period such that there will be
progressive improvement to the facility’s current impacts on groundwater and surface
water quality;
- appropriate water quality monitoring plans and follow-up monitoring plans;
- realistic contingency plans;
- adequate oversight and regulation by the CNSC for the VIM project and the PHCF over
the 2017 to 2027 license period.
In order to carry out my work, I have reviewed numerous documents and the most important of
these are listed as references in Appendix 1 of this review.
page 3
23. I toured the PHCF and surrounding area (on September 26th, 2016), and asked questions about
various aspects of the VIM proposal of the Cameco representatives with whom I was touring the
PHCF. I had submitted (through LOW) an information request and a series of questions - most
of which were discussed during or immediately following the site tour. I also attended a Sept.
26th public meeting hosted by Cameco and the Port Hope Area Initiative (or PHAI) on the
remediation of the Port Hope waterfront including the PHCF clean-up under the VIM process.
This review outlines my findings, conclusions and recommendations following my review of the
documentation prepared by Cameco in support of the 2017 license renewal application and the
associated VIM project. This documentation as well as other related information can be found
here:
https://www.cameco.com/fuel_services/port_hope_conversion/
In the course of my review I have also carefully considered other background documents which
are available regarding the PHCF, and regarding the PHAI which is the larger process under
which the Port Hope LTWMF is being developed and under which up to 150,000 m3 of
Cameco’s LLRW will be allowed to be brought to the LTWMF.
In my comments which follow below I will be highlighting some key aspects of the information
which has been provided in the documentation which I have reviewed, and I will be outlining
some areas where I believe that environmental protections in VIM process and the 2017-2027
PHCF operations should be strengthened going forward.
2) Background and Overview of the PHCF
The Port Hope Conversion Facility (PHCF) is an active Uranium processing facility which has
been the site of operations for the processing of nuclear materials since 1932. Initially the site
was used by a private corporation to extract Radium from ore, and subsequently the PHCF was
used to process Uranium. Uranium processing was carried out by a federal Crown Corporation
at the site from 1942 through 1988), after which the crown corporation was privatized.
Up to 150,000 m3 of the wastes generated by the Crown Corporation prior to its privatization in
1988 are now being allowed to be deposited in the Port Hope LTWMF, as per the Federal
Agreement which established the Port Hope Area Initiative (PHAI) which governs the operations
of the LTWMF. The PHAI is briefly described in the next section of this review.
Because of its long history, the site of the PHCF has experienced significant environmental
contamination including contamination of on-site soils and groundwater - and there are currently
emissions of liquids from the PHCF property which are contaminated with Uranium and other
parameters. Contaminated materials are also found in sediments in the adjacent Port Hope
Harbour, which is one of 43 designated Great Lakes Areas of Concern under the Canada - United
States Great Lakes Water Quality Agreement.
The Vision in Motion (VIM) project provides Cameco with a unique, one-time opportunity to
carry out significant remediation of PHCF and to unburden itself of up to 150,000 m3 of LLRW
which it has been storing since it became a corporation in 1988.
page 4
24. 3) Brief Overview of the PHAI
The PHAI is a process under which the federal government will be accepting historic low-level
radioactive waste (LLRW) from across Port Hope and environs, and securing these LLRWs in
two dedicated long-term waste management facilities (LTWMFs) - one in Port Hope and one
near Port Granby. The details of this program are spelled out in a Federal Agreement with local
governments.
There are several major LLRW sources in Port Hope, and a multitude of smaller ones. Most of
the wastes from these sources will be going to the Port Hope LTWMF (including the 150,000 m3
coming from Cameco), and a smaller amount will be going to the Port Granby LTWMF.
Both LTWMFs are very well-designed facilities which will provide secure and long-term storage/
disposal of the LLRW. The LTWMFs will hydraulically isolate the wastes (through a very low-
permeability base liner and a similarly low-permeability cover), and each LTWMF has a highly
sophisticated waste water treatment plant (WWTP) which will treat all contaminated liquids
being generated by the LTWMFs.
The legal agreement with the Federal Government allows for up to 150,000 m3 of Cameco-
owned legacy wastes (generated by its Crown Corporation predecessor prior to 1988) as well as
additional contaminated soils and wastes from building demolition associated with the Cameco
Vision in Motion (VIM) project.
Following completion of the PHAI most of Port Hope’s LLRW sources will be remediated - with
the exception of the Cameco Port Hope Conversion Facility, at which even after completion of
the PHAI there will be some contaminated soil and contaminated groundwater under various
parts of the site.
4) Description of the Contamination at the PHCF
a) Introduction
As described previously, there has been processing of nuclear materials ongoing at the PHCF site
since 1932. In the early decades of operations, little was known about the harmful nature of the
materials being handled at the site. More recent investigations have shown that water and soils
on the site and its surroundings have been contaminated by substances from the PHCF including
the following contaminants of primary concern (COPCs):
- Uranium,
- Arsenic,
- Ammonia,
- Nitrate,
- Fluoride,
- Radium-226,
- Trichloroethylene,
- Dichlorethylene, and
- Vinyl Chloride.
page 5
25. Types of water/soil contamination which are of concern include the following:
- there are contaminated soils across significant areas on the PHCF site, including the main plant
site and the Centre Pier;
- there are contaminated sediments (several meters thick) in the Port Hope Harbour;
- there is contaminated groundwater which is present in two main plumes on the PHCF site, and
although most is contained and treated some of this contaminated groundwater is discharging to
the Port Hope Harbour;
- the discharges from the PHCF storm sewer system are carrying contaminants into the Port Hope
Harbour;
- the discharges from the PHCF to the municipal sanitary sewer system are carrying contaminants
into the Port Hope Sewage Treatment Plant (STP).
I will be discussing each of these types of contamination in the next subsections of this review.
b) Contaminated Soils at the PHCF
Contaminated soils are present in various locations across the PHCF, including the main plant
site (with hot spots at the uranium hexafluoride (UF6) plant, and in areas closest to the Harbour)
and the Center Pier. The contaminants include Low Level Radioactive Wastes (LLRWs) such as
Uranium as well as various conventional industrial contaminants.
Much of the PHCF property is paved and almost all unpaved areas are relatively flat, so in most
cases the contaminated soils are locked in place and not subject to erosion. However if water
passes through the contaminated soils, then there is a potential for contaminants to be leached
from the soils and transported to the Harbour via the groundwater flow system. Significant
amounts of contaminated soils (especially those situated in areas closest to the Port Hope
Harbour) are planned to be removed as part of the VIM project.
c) Contaminated Sediments in Port Hope Harbour
Contaminated materials are found in sediments in the Port Hope Harbour, which is adjacent to
and has been contaminated by the PHCF. The Port Hope Harbour is one of 43 designated Great
Lakes Areas of Concern under the Canada - United States Great Lakes Water Quality Agreement.
The International Joint Commission website provides a description of the contaminated harbour
sediments (which it indicates are contaminated with uranium- and thorium-series radionuclides,
heavy metals, and PCBs) here:
http://ijc.org/files/publications/
PortHopeHarbourAreaOfConcernStatusOfBeneficialUseImpairments.pdf
The Canadian Government’s description of the Port Hope Harbour contamination can be found
here:
http://www.ec.gc.ca/raps-pas/default.asp?lang=En&n=8BB3DAED-1
Under the Port Hope Area Initiative, the contaminated sediments in the Port Hope Harbour are to
be excavated and deposited in the Port Hope LTWMF. Close coordination with the PHCF will be
required for this work to be carried out successfully.
page 6
26. d) Contaminated Groundwater at the PHCF
There is extensive and significant groundwater contamination on the PHCF property. The
indicator parameter which in most cases can be used to track this contamination is Uranium,
which is also one of the COPCs.
The Ontario Drinking Water Quality Standard (ODWQS) for Uranium is 20 micrograms per
Liter (ug/L) and the Ontario Provincial Water Quality Objective (PWQO) for Uranium is 5 ug/L.
Uranium levels in the groundwater beneath the Cameco property are often in the 1000s of ug/L,
with peak levels of over 20,000 ug/L.
This contaminated groundwater is mostly being contained and collected through a Pump and
Treat (P+T) system. It is estimated that currently on the order of 60% of the groundwater flow to
the Harbour is contained by the P+T System, and that the original approximately 25-30 kg/year
mass loading of Uranium to the Harbour has been reduced to about 5 kg/year by the P+T system.
Further expansion of the system (with 5 new wells) is planned as part of VIM, which will help to
further reduce the mass loading to the Harbour.
e) PHCF-Contaminated Storm Sewer Discharges to the Harbour
When I first conducted a review of the PHCF under a prior contract for LOW in 2011, I found
evidence of a storm sewer system which had not been well maintained and monitored - and
which was leaking significant amounts of contaminated water into the Port Hope Harbour. It was
(and still is) my interpretation that the majority of the contamination in the storm sewer
discharges to the Harbour is caused by discharge of contaminated groundwater into the system
via leaks and breaks in the aging storm sewer network.
At the time of my review in 2011 the available information indicated that average Uranium
concentrations in the storm sewer discharges to the Harbour were 218 ug/L, compared to the
PWQO for Uranium of 5 ug/L. I was quite concerned about what I found in my 2011 review, and
I provided a number of recommendations for Cameco to address the problem.
I am pleased to report that significant progress has been made by Cameco in the 5 years since I
issued my original report:
- a major study of the storm sewer system was conducted in 2011;
- the volume of water being captured by the P+T System was increased significantly, reducing the
amount of groundwater available to leak into the storm sewer system;
- a number of the storm sewer lines and outfalls have been decommissioned, reducing the
number of active storm sewer outlets to the Harbour to 10;
- regular semi-annual water quality monitoring is now being conducted on 6 of the 10 active
outlets, with more frequent monitoring of a 7th outlet.
This having been said, there are still significant problems associated with Cameco’s storm sewer
discharges to the Port Hope Harbour:
1) There are no specific Effluent Release Limits for the storm sewer discharges, nor are
there specific Action Levels for the storm sewer discharges - in effect, these
discharges are currently unregulated.
page 7
27. 2) Although there is a semi-annual storm sewer discharge monitoring program, there is
no information from that monitoring program presented in either the current
(2015/2016) Quarterly Compliance Monitoring and Operational Performance Reports
or the 2015 Annual Compliance Monitoring and Operational Performance Report.
The information is also not presented in the 2015 Annual Groundwater and Surface
Water Review Report. It is effectively hidden from public scrutiny. Perhaps it is also
effectively hidden from scrutiny by Cameco’s regulator - the CNSC.
3) My expectation is that the majority of the water contamination in the Harbour is
currently coming from the contaminated storm sewer discharges, which in 2009 had
average Uranium concentrations of 218 ug/L. I have no information available to me
that would allow me to in any way quantify the more recent releases of Uranium and
other harmful contaminants to the Port Hope Harbour from the Cameco PHCF’s
storm sewer discharges. Average 2015 levels of Uranium in Port Hope Harbour were
2.9 ug/L, so there is clearly considerable mixing and dilution occurring in the
Harbour. By comparison, the PWQO for Uranium is 5 ug/L.
4) Please note that I have only been discussing Uranium as it is the site indicator
parameter and one of the site COPCs - but there are also many other contaminants
which will be present in the unregulated and undisclosed storm sewer discharges to
the Harbour from the PHCF.
f) Discharges from the PHCF to the Municipal Sanitary Sewer
There are also discharges of wastewater from the PHCF to the municipal sanitary sewer.
Contained in these discharges are inputs from washrooms, showers, site laundry facilities, and
Powerhouse boiler blowdown.
Average Uranium levels in the sanitary sewer discharges were 19 ug/L in 2015, vs. the PWQO
for Uranium of 5 ug/L. Following treatment at the Port Hope STP, the treated PHCF wastewater
is discharged to Lake Ontario. I have not found water quality monitoring information for Lake
Ontario in the reports I’ve seen, however such information is available in the annual monitoring
reports for the PHAI - average Uranium levels in Lake Ontario in 2015 were 0.4 ug/L.
It is not clear whether the Port Hope STP is able to remove the low levels of Uranium and other
contaminants in the wastewater from the PHCF - but it will certainly provide significant dilution,
as will the lake.
5) Vision in Motion Project - Opportunities and Concerns
a) Introduction
The significance and beneficial aspects of the Vision in Motion (VIM) project for Cameco’s
PHCF are tremendous. The Vision in Motion (VIM) project provides Cameco with a unique,
one-time opportunity to carry out significant remediation of PHCF and to unburden itself of up to
150,000 m3 of LLRW which it has been storing since it became a corporation in 1988.
page 8
28. There is no cost to Cameco for the storage/disposal of the LLRW at the Port Hope LTWMF, but
Cameco is responsible for the costs of removing the materials from its property. Although these
costs will be significant, there are nonetheless very considerable benefits to Cameco in making
the best use of the 150,000 m3 waste allotment which it has under the Federal Agreement.
I strongly urge Cameco to make the greatest possible use of the opportunities for site
improvements and historic waste removal that the VIM project presents.
b) VIM Project Description
The VIM project is described in various documents, including the “2017 License Renewal
Application for the Port Hope Conversion Facility - Supplemental VIM Submission” which is
hereafter referred to as the VIM Submission.
The VIM project (which at the time was named Vision 2010) went through an Environmental
Assessment process, which culminated in the release of an Environmental Impact Statement
(EIS) and Comprehensive Study Report (CSR) which ultimately were accepted by the CNSC and
the Canadian government. Since then, the VIM project has been refined such that there will be
less building removals and somewhat less excavation of contaminated soils on the PHCF
property than originally envisioned.
An overview list of VIM project activities which will result in environmental improvements is
provided on page 12 of the VIM Submission and includes the following:
- removal of drummed legacy wastes (from Cameco’s Crown Corporation predecessor) from
three Cameco storage locations in Port Hope;
- demolition of 6 buildings and partial demolition of another on the PHCF property;
- demolition of 3 buildings on the Centre Pier;
- removal of contaminated soils from the Centre Pier (in cooperation with the PHAI) and the
PHCF property;
- removal of redundant equipment from various buildings;
- construction of berms/barriers which will provide flood protection, visual, noise and gamma
radiation shielding along the east property fenceline;
- installation of 5 new wells for the groundwater pump and treat system;
- improvements to the storm sewer infrastructure including installation of oil/grit separators,
backflow prevention valves to prevent incursions of Harbour water during periods of wind-
driven higher lake levels, and new piping in areas of soil excavation.
c) Potential for Flooding of VIM Excavations
In my previous review of the Vision 2010 project I had expressed significant concerns about the
potential for flooding of excavation sites during major storm events, resulting in major
contamination of Port Hope Harbour.
I no longer have this concern, in part because the extent of the VIM excavations has been scaled
back significantly, in part because the VIM documentation now tries to address this issue, and in
part because I have learned that for the harbour dredging period (which will cover much of the
VIM duration) the entire Port Hope Harbour will be sealed off from access by fish - which will
have been removed from the Harbour beforehand.
page 9
29. d) Treatment of Contaminated Wastewater from VIM Project
During the period when building removal and soil excavations are occurring as part of the VIM
project, these areas will be generating contaminated wastewater additional to what is currently
generated by the PHCF.
Cameco has not yet decided how to ensure treatment of this contaminated wastewater - the
options being considered are either upgrading the capacity of the existing on-site waste water
treatment system (done through evaporation of waste liquids) or releasing the waste water to the
Port Hope STP (assuming acceptable conditions can be negotiated). If additional contaminated
waste water is being sent to the Port Hope STP then it will be important to make sure that the
STP can handle the increased volumes and contaminant load.
It would have been good for this issue to have been clarified in time for the public review of the
VIM proposal and 2017 license application - the fact that it has not been clarified means that
there will likely not be any opportunity for public review and comment prior to the site license
being issued. It is also not clear what process for CNSC review will be followed regarding this
issue. I recommend that the final proposal for the VIM project’s wastewater treatment be
provided for public review once it has been completed.
e) Management of Water in Port Hope Harbour During PHAI/VIM Projects
As indicated previously, PHAI/VIM plans include a provision for fish to be removed from the
Port Hope Harbour beforehand - with the Harbour then being sealed off for the duration of the
project during which Harbour impacts are anticipated. While this provides assurance that efforts
are being made to prevent harm to fish, there is a broader question regarding how the
contaminated water in the Harbour is gojng to be handled.
The various VIM and PHAI operations taking place in and around the harbour will be causing the
harbour water to be contaminated during a years-long period. This would not be a problem,
except that there are ongoing inflows to the harbour (of rainfall, groundwater and storm water)
and the Harbour mouth is to be sealed off so there will be no place for the surplus (contaminated)
water to go.
I have not been able to find any information in the VIM or PHAI documentation on how the
surplus contaminated water from the Port Hope Harbour is going to be handled during the VIM/
PHAI project period. This is clearly an issue which needs to addressed, as otherwise there will
be an ongoing poorly controlled and untreated flow of contaminated Harbour water into Lake
Ontario.
Monitoring will be critical to ensure that impacted Harbour water is not causing unacceptable
contamination of Lake Ontario. The VIM monitoring proposal is provided on page 24 of the
VIM submission. I have not been able to find any reference to plans to monitor water quality in
Lake Ontario (just beyond the Harbour mouth), but I strongly recommend that such monitoring
should be carried out.
Lake Ontario water quality monitoring should be done frequently (at minimum on a monthly
basis, plus after any rain events exceeding 50 mm), and should include the full list of COPCs
identified for the PHCF. The results of this monitoring should be made publicly available.
page 10
30. It could be argued that the Lake Ontario monitoring should be done either partly or entirely
through the PHAI project (rather than through the VIM project), but the question of who does the
monitoring is immaterial from my perspective - what is important is that the monitoring be done,
that it be reviewed by competent technical people who will ensure that any developing issues are
dealt with quickly and thoroughly, and that the results will be made publicly available.
f) Incomplete Remediation of the PHCF
The PHCF site will not be completely remediated following this work, but given that this is a
working industrial site this is not required.
What is important however is that the 2017-2027 CNSC site license (which will include
authorization to proceed with the VIM project) should include regulatory levels for contaminated
water discharges which will be protective of the aquatic environment and water quality in Port
Hope Harbour and Lake Ontario during and after the VIM project. As will be discussed in more
detail in following sections of this review, the proposed regulatory levels in the new site license
do not meet this test.
6) 2017 Site License Renewal and Concerns about Effluent Releases and Monitoring
a) Introduction
The CNSC Hearing for which this review has been prepared and at which it will be presented is
being held in regard to the 2017 License Renewal Application (which includes authorization for
the VIM project). My concerns regarding the VIM project were provided in the previous section
of this review.
I also have grave concerns about the licensing and oversight by CNSC of the Cameco PHCF with
respect to the regulation of contaminated liquid emissions from the PHCF, about the monitoring
of such emissions, and about the disclosure of information regarding such monitoring.
b) Inadequate Regulation of Contaminated Liquid Emissions from the Cameco PHCF
There are 3 streams of liquid emissions from the PHCF, all of which are carrying contaminants
from the site into the Port Hope Harbour or Lake Ontario:
- mildly contaminated waste water is being discharged to the sanitary sewer system, and from
there to the Port Hope STP and ultimately into Lake Ontario;
- contaminated stormwater is discharging to the Harbour via the storm sewer network;
- contaminated groundwater from the site is discharging into the Harbour.
The existing CNSC Site License does not include any mention of any regulatory levels regarding
these contaminated liquid emissions from the PHCF - they are currently not being regulated in
any way that I can find by the CNSC.
I consider this to be a significant failure in oversight of the PHCF by the CNSC. It needs to be
corrected in the proposed 2017 Site License Renewal which is being applied for by Cameco.
page 11
31. However review of the CNSC’s draft License Conditions Handbook reveals that under the
Environmental Protection section of the Handbook only 1 of the 3 streams of liquid discharges
from the site is proposed to be addressed, namely the sanitary sewer discharges (which are the
least contaminated of the 3 streams). Moreover, the only regulatory level which is mentioned for
the sanitary sewer stream is a release limit of 1825 kg/year of Uranium.
I understand from conversations with PHCF staff and from a report which they have prepared
entitled “Calculating Doses to the Public - Derived Release Limits and Operating Release
Levels” hereafter referred to as the “DRL/ORL Report” that this release limit of 1825 kg/year of
Uranium is a theoretical upper limit on Uranium releases which has been derived by calculating
how much Uranium would have to be released from the PHCF in order to cause a radioactivity
dose to a person exceeding the regulatory limit of 1 mSv/year.
What this sole release limit for the contaminated liquid discharges from the PHCF fails to do is to
address the fact that Uranium aside from its radioactive properties is also a toxic chemical
contaminant if ingested (it damages the kidneys), that Uranium is also harmful to aquatic life,
and that at this site Uranium is a surrogate for many other COPCs which are all present in
varying quantities in the contaminated liquid streams discharging from the PHCF into the
Harbour and Lake Ontario. The draft CNSC Site License and draft License Conditions
Handbook utterly fail to address these concerns.
The PHCF is a federal facility, and thus its liquid discharges are not being meaningfully regulated
by Ontario’s Ministry of the Environment and Climate Change (MOECC). In the absence of
MOECC regulation, the CNSC is the sole regulator of this facility when it comes to discharges of
contaminated liquids to the environment. The CNSC is failing in this regard.
The Ontario Drinking Water Quality Standard (ODWQS) for Uranium is 20 ug/L and the
Provincial Water Quality Objective (PWQO) in surface waters is 5 ug/L. The CNSC’s proposed
release limit of 1825 kg/year in sanitary sewer discharges is so absurdly high that there would be
appalling exceedences of the PWQO and the ODWQS in whatever surface water body was
receiving these discharges, with dire consequences for aquatic life.
If discharged to the Port Hope Harbour, 1825 kg/year of Uranium would turn the Harbour into a
killing zone for aquatic life. A rough estimate suggests that the Harbour holds about 50,000,000
Liters of water. 1825 kg/year equals 5 kg/day or 5,000,000,000 ug/day. Thus 1825 kg/year
translates into a Harbour’s worth of water contaminated to 100 ug/L (20 times the PWQO for
Uranium) every day, throughout the 10-year license period. If discharged into Lake Ontario,
1825 kg/year of Uranium would cause the formation of a killing zone for aquatic life in the area
where the discharge was mixing with the lake water.
These extreme numbers arise from calculations using the only regulatory level which Cameco’s
and the CNSCs documents are currently indicating would be applied to contaminated water
discharges from the PHCF - namely the 1825 kg/year release limit for Uranium.
I strongly recommend that Action Levels or some other form of effluent quality limits are needed
for all of the water-related COPCs at the Cameco PHCF (they are listed on page 5 of this review)
and for each of the 3 streams of contaminated water discharges from the PHCF. I strongly
recommend that Cameco and CNSC staff get to work on developing them.
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32. c) Improvements Needed for Monitoring and Reporting of Contaminated Discharges from PHCF
To recap, there are 3 streams of liquid emissions from the PHCF, all of which are carrying
contaminants from the site into the Port Hope Harbour or Lake Ontario:
- mildly contaminated waste water is being discharged to the sanitary sewer system, and from
there to the Port Hope STP and ultimately into Lake Ontario;
- contaminated stormwater is discharging to the Harbour via the storm sewer network;
- contaminated groundwater from the site is discharging into the Harbour.
Monitoring of Sanitary Sewer Discharges
The monitoring of wastewater discharges to the sanitary sewer system is reported in the
quarterly and annual Compliance Monitoring Reports. Wastewater monitoring is
occurring at a frequency of weekly, which is appropriate. The list of COPCs which are
reported on for the sanitary sewer monitoring is limited to Uranium, Fluoride, Ammonia
and Nitrates in these reports. It is not clear if there is monitoring for the other PHCF
COPCs - I recommend that future quarterly and annual Compliance Monitoring Reports
should provide the full list of COPCs which are being monitored, and if results are not
being reported for some COPCs then this should be explained.
Otherwise I find the reporting of the results of monitoring of sanitary sewer discharges
from the site to be satisfactory. I should note that I recommend that the calculation of
the combined annual mass loading of Uranium in the sanitary sewer discharges be
continued and reported in the Annual Compliance Monitoring Reports.
Monitoring of Contaminated Storm Sewer Discharges
The monitoring results for the uncontrolled discharges to the Harbour via the storm
sewer system are not reported in the quarterly or annual Compliance Monitoring
Reports, or in any other report which I could find or obtain from Cameco. Wastewater
monitoring is occurring at a frequency of semi-annually, which is not frequent enough - I
recommend quarterly monitoring.
Storm sewer monitoring is currently done at only 7 of 10 active storm sewer lines with
outlets to the Harbour - I recommend that all active storm sewer lines should be
monitored.
I do not know which parameters from the list of COPCs for the site are included in the
storm sewer monitoring - the only results available to me are the Uranium results for
2015. It is not clear if there is monitoring for the other PHCF COPCs. I recommend
that monitoring should be for the full list of PHCF COPCs (which are provided on
page 5 of this review for easy reference)
I recommend that storm sewer monitoring results should be reported in future quarterly
and Annual Compliance Monitoring Reports, that these reports should provide a list or
table showing the full list of COPCs which are being monitored, and if results are not
being reported for some COPCs then this should be explained.
I also recommend that a calculation of the combined annual mass loading of Uranium to
the Harbour from all active storm sewers be done every year and reported in the Annual
Compliance Monitoring Reports.
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33. Monitoring of Pump and Treat System Water Quality
The monitoring of Pump and Treat (P+T) system water quality is reported in the 2015
Annual Groundwater and Surface Water Quality Monitoring Report. Pumping well
water quality monitoring is occurring at a frequency of monthly for a short list of
COPCs (Uranium, Radium-226, Arsenic, Nitrate, Fluoride, and Ammonia), which is
appropriate. Water quality in observation wells is generally monitored quarterly for the
same short list, which is likewise appropriate. There is also annual water quality
monitoring for a considerably longer list of general chemistry parameters, VOCs and
metals which provides helpful information.
The contaminated water pumped from the P+T System wells is treated through on-site
evaporation by Cameco - there are no liquid discharges from this treatment system.
However a small portion of the contaminated groundwater beneath the site escapes the
P+T system and discharges to the Harbour.
I recommend that a calculation of the combined annual mass loading of Uranium to the
Harbour from all areas of uncontained contaminated groundwater be done every year
and reported in the Annual Compliance Monitoring Reports.
In summary, I believe that all 3 streams of contaminated liquids which are being discharged from
the site should be properly monitored for water quality, and that the monitoring information on
these discharges should be presented in the Annual Compliance Monitoring Reports for the
PHCF. This would mark a significant change from current practice, in which the results of the
monitoring of contaminated storm sewer discharges to the Port Hope Harbour are not disclosed
in the publicly available monitoring reports.
7) Discussion
The Cameco website indicates that the PHCF is one of only 4 uranium conversion facilities in the
western world. At a world class facility, I think it is reasonable for the public to expect world
class oversight by the regulator of the facility (the CNSC) and world class monitoring of the
facility’s impacts. My review of the CNSC oversight and the PHCF’s water quality monitoring
programs suggest that improvements to both are needed.
The VIM project and the associated 2017 PHCF License Renewal Application provide a unique
and major opportunity for Cameco to improve the PHCF site and its operations, and to reduce its
impacts on soil, groundwater and surface water. The 2017 License Application which is intended
to authorize the VIM project and extend the license of the facility also provides an opportunity to
strengthen CFSC oversight of the facility and its operations, and to make improvements to site
water quality monitoring and Cameco’s reporting on that aspect of the monitoring program.
Overall, I find the Cameco PHCF to be a reasonably well run industrial facility from a water
quality perspective. There are no discharges of liquid effluent from plant processes.
Historic soil and groundwater contamination at such sites is not uncommon, and what
differentiates good from bad facilities is how they go about dealing with them. Cameco is doing
a better job than many, although there is need for further improvement as set out in this review.
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34. 8) Conclusions
1) The Cameco Port Hope Conversion Facility (PHCF) is an active Uranium processing facility
which has been the site of operations for the processing of nuclear materials since 1932.
2) Because of its long history, the site of the PHCF has experienced significant environmental
contamination including contamination of on-site soils and groundwater - and there are
currently emissions of liquids from the PHCF property which are contaminated with Uranium
and other parameters. Contaminated materials are also found in sediments in the adjacent Port
Hope Harbour, which is one of 43 designated Great Lakes Areas of Concern.
3) The Port Hope Area Initiative (PHAI) is a unique and major Low Level Radioactive Waste
(LLRW) remediation project, which is aimed at providing secure long-term management of
the LLRWs from around Port Hope. The legal agreement which established the PHAI
provides for 150,000 m3 of legacy LLRWs from Cameco’s PHCF to be brought to the
LTWMF.
4) The Vision in Motion (VIM) project is Cameco’s name for this unique, one-time opportunity
to carry out significant remediation of PHCF and to unburden itself of up to 150,000 m3 of
LLRW which it has been storing since it became a private corporation in 1988.
5) A description of the soil and water contamination at the PHCF is provided in Section 4 of this
review. The list of contaminants of primary concern (COPCs) in soil and water includes both
radioactive parameters such as Uranium as well as conventional industrial contaminants such
as ammonia, TCE and vinyl chloride.
6) The impacted liquid stream which is least-well monitored and which is poorly disclosed by
Cameco is the flow of contaminated water going into Port Hope Harbour from the PCHF’s
aging storm sewer system. While it appears that there has likely been significant progress
made in reducing the site’s contaminated storm water discharges, the lack of disclosure makes
it impossible to determine just how much progress has been made.
7) Opportunities and concerns associated with the VIM project are discussed in Section 5 of this
review. My most significant concern is the dearth of information on how surplus
contaminated water from the sealed off Port Hope Harbour is going to be handled during the
VIM/PHAI project period. This is an issue which needs to addressed by Cameco or the PHAI
process, as otherwise there will be an ongoing poorly controlled and untreated flow of
contaminated Harbour water into Lake Ontario. Monitoring of the lake’s water quality just
beyond the Harbour will be required, but does not seem to be planned at present.
8) In my professional opinion there has been a significant failure in oversight of the PHCF by the
CNSC with regard to the issue of contaminated liquid emissions from the facility, and the
monitoring and reporting of these emissions. The 2017 License Renewal application provides
an opportunity to address this concern - which is discussed in detail in Section 6 of this review.
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35. 9) Recommendations
1) The significance and beneficial aspects of the Vision in Motion (VIM) project for Cameco’s
PHCF are tremendous. I strongly urge Cameco to make the greatest possible use of the
opportunities for site improvements and historic waste removal that the VIM project presents.
2) I recommend that the final plan for the VIM project’s wastewater treatment be provided for
public/stakeholder review once it has been completed.
3) The final plan for handling contaminated water from the Port Hope Harbour during the VIM/
PHAI project should be provided for public/stakeholder review once it has been completed. It
is not clear from the documentation who is responsible for this issue, but it needs to be
addressed by either Cameco or the PHAI.
4) The plan for monitoring Lake Ontario outside the Harbour mouth during the VIM/PHAI
project period should also be provided for public/stakeholder review at that time. Lake Ontario
water quality monitoring is required and should be done frequently (at minimum on a monthly
basis, plus after any rain events exceeding 50 mm), and should include the full list of COPCs
identified for the PHCF. The results of this monitoring should be made publicly available.
Cameco and the PHAI will need to determine who is responsible for the monitoring.
5) The 1825 kg/year release limit for Uranium for the PHCF in the 2017 License Application
documents is not acceptable as the sole regulatory level for COPCs in liquid emissions from
the facility. There are 3 contaminated liquid streams coming from the facility, and Action
Levels or some other form of effluent quality limits are needed for the water-related COPCs
for each of the 3 stream of contaminated water discharges from the PHCF. Once they have
been developed they should be circulated for public/stakeholder review.
6) The monitoring of wastewater discharges to the sanitary sewer system should continue to be
reported in the quarterly and annual Compliance Monitoring Reports. Wastewater monitoring
is occurring at a frequency of weekly, which is appropriate. I recommend that future quarterly
and annual Compliance Monitoring Reports should provide the full list of COPCs which are
being monitored, and if results are not being reported for some COPCs then this should be
explained. The calculation of the combined annual mass loading of Uranium in the sanitary
sewer discharges should be continued and reported in the Annual Compliance Monitoring
Reports.
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