Guideline for the Management of Sites Contaminated with Light Non-Aqueous Phase Liquids

Light Non-Aqueous Phase Liquid (LNAPL) Management is the process of LNAPL site assessment, monitoring, LNAPL Conceptual Site Model development, identification and validation of relevant LNAPL concerns, and the possible application of remediation technologies. The presence of LNAPL can create challenges at any site.  Examples of LNAPLs include gasoline, diesel fuel, and petroleum oil.

In 2009, the United States Interstate Technology and Regulatory Council (ITRC) published LNAPL-1: Evaluating Natural Source Zone Depletion at Sites with LNAPL (ITRC 2009b) and LNAPL-2: Evaluating LNAPL Remedial Technologies for Achieving Project Goals (ITRC 2009a) to aid in the understanding, cleanup, and management of LNAPL at thousands of sites with varied uses and complexities. These documents have been effective in assisting implementing agencies, responsible parties, and other practitioners to identify concerns, discriminate between LNAPL composition and saturation-based goals, to screen remedial technologies efficiently, to better define metrics and endpoints for removal of LNAPL to the “maximum extent practicable,” and to move sites toward an acceptable resolution and eventual case closure.

This guidance, LNAPL-3: LNAPL Site Management: LCSM Evolution, Decision Process, and Remedial Technologies, builds upon and supersedes both previous ITRC LNAPL guidance documents in an updated, web-based format. LNAPL-1 and LNAPL-2 are still available for review; however, LNAPL-3 is inclusive of those materials with new topics presented and previous topics elaborated upon and further clarified.

This guidance can be used for any LNAPL site regardless of size and site use and provides a systematic framework to:

  • develop a comprehensive LNAPL Conceptual Site Model (LCSM) for the purpose of identifying specific LNAPL concerns;
  • establish appropriate LNAPL remedial goals and specific, measurable, attainable, relevant, and timely (SMART) objectives for identified LNAPL concerns that may warrant remedial consideration;
  • inform stakeholders of the applicability and capability of various LNAPL remedial technologies
  • select remedial technologies that will best achieve the LNAPL remedial goals for a site, in the context of the identified LNAPL concerns and conditions;
  • describe the process for transitioning between LNAPL strategies or technologies as the site moves through investigation, cleanup, and beyond; and
  • evaluate the implemented remedial technologies to measure progress toward an identified technology specific endpoint.

Initial development and continued refinement of the LCSM is important to the identification and ultimate abatement of site-specific LNAPL concerns. Figure 1-1 identifies the stepwise evolution of the LCSM, the specific purpose of each LCSM phase, and the tools presented within this guidance to aid in the development of the LCSM. As depicted, the LCSM is the driving force for identifying actions to bring an LNAPL site to regulatory closure.

LNAPL remediation process and evolution of the LNAPL conceptual site model (LCSM).

This guidance document is organized into sections that lead you through the LNAPL site management process:

  • Section 2 – LNAPL Regulatory Context, Challenges, and Outreach
    Section 2 identifies some of the challenges implementing agencies face when investigating, evaluating, or remediating LNAPL sites. These challenges include regulatory or guidance constraints, a lack of familiarity or understanding of LNAPL issues, and poorly or undefined objectives and strategies. This section also stresses the importance of identifying and communicating with stakeholders early in the process in order to address issues or concerns that can lead to delays or changes in strategy. Understanding and recognizing these challenges and concerns during development of a comprehensive LCSM can help reduce costs and lead to a more effective and efficient resolution at an LNAPL site.
  • Section 3 – Key LNAPL Concepts
    Section 3 provides an overview of key LNAPL terminology and concepts including LNAPL behavior following a release to the subsurface (i.e., how LNAPL spreads away from the primary release point, its behavior above and below the water table, and how its migration eventually stops and naturally depletes). An understanding of these basic terms and concepts is crucial for developing a comprehensive LCSM and an effective LNAPL management plan.
  • Section 4 – LNAPL Conceptual Site Model (LCSM)
    The LCSM is a component of the overall conceptual site model (CSM), and emphasizes the concern source (i.e., the LNAPL) of the CSM. The presence of LNAPL necessitates an additional level of site understanding. The unique elements of the LCSM are presented as a series of questions for the user to answer to help build their site-specific LCSM. Ultimately, a thoroughly-developed, initial LCSM provides the basis for identifying the LNAPL concerns associated with an LNAPL release.
  • Section 5 – LNAPL Concerns, Remedial Goals, Remediation Objectives, and Remedial Technology Groups
    Section 5 describes the decision process for identifying LNAPL concerns, verifying concerns through the application of threshold metrics, establishing LNAPL remedial goals, and determining LNAPL remediation objectives. This section also introduces remedial technology groups, the concept of a treatment train approach, and how to transition between technologies to address the identified LNAPL concern(s) systematically and effectively. It is important to understand the content of this section prior to selecting and implementing an LNAPL remedial strategy.
  • Section 6 – LNAPL Remedial Technology Selection
    Section 6 describes the remedial technology screening, selection, and performance monitoring process. This section begins by identifying technologies recognized as effective for mitigating specific LNAPL concerns and achieving site-specific LNAPL remediation objectives based on the collective experience of the LNAPL Update Team. The LNAPL Technologies Appendix summarizes each of the technologies in detail and presents a systematic framework to aid the user in screening out technologies that are unlikely to be effective, ultimately leading to selection of the most appropriate technology(ies) to address the specific LNAPL concerns.

This guidance also includes relevant, state-of-the-science appendices for more detailed information on LNAPL specific topics:

  • LNAPL Technologies Appendix 
    This appendix describes in more detail each of the 21 LNAPL technologies introduced in the main document. The A-series tables describe information to evaluate the potential effectiveness of each technology for achieving LNAPL goals under site-specific conditions. Information includes the basic remediation process of each technology, the applicability of each technology to specific remedial goals, and technology-specific geologic screening factors. The B-series tables describe information to evaluate the potential implementability of each technology considering the most common site-specific factors. The C-series tables describe the minimum data requirements to make a final technology selection through bench-scale, pilot, and/or full-scale testing; they also describe metrics for tracking remedial technology performance and progress.
  • Natural Source Zone Depletion (NSZD) Appendix
    This appendix provides a technical overview of NSZD for LNAPL and the methods by which rates can be estimated and measured. It also provides a discussion of long-term LNAPL site management and how NSZD can be applied as a remedy including decision charts to support integration of NSZD and case studies demonstrating its use. For this document, the original ITRC NSZD document (ITRC LNAPL-1) was updated and incorporated into the main body and appendix.
  • Transmissivity (Tn) Appendix
    LNAPL transmissivity has application throughout the life cycle of a LNAPL project. This appendix provides an understanding of how transmissivity connects to the broader framework for LNAPL management including LNAPL recovery and mobility, and the potential for NSZD to decrease LNAPL transmissivity and mobility over time.
  • Fractured Rock Appendix
    This appendix describes the behavior and differences of how LNAPL behaves in fractured bedrock formations. While some of the same physical principles apply for multiphase flow in fractured aquifers as in porous aquifers, unique characteristics of finite and restricted fluid flow paths can lead to unexpected results in fractured settings.
  • LNAPL Sheens Appendix
    This appendix details how LNAPL sheens form, the concerns and challenges of sheens, and potential sheen mitigation technologies.

LNAPL Contamination of the Subsurface

IATA rolls out DG AutoCheck to enhance safety in dangerous goods transport

The International Air Transport Association (IATA) recently launched Dangerous Goods AutoCheck (DG AutoCheck), a new innovative solution for the air cargo industry, which will enhance safety and improve efficiency in the transport of dangerous goods by air, and support the industry’s goal of a fully digitised supply chain.

“The air transport industry handles over 1.25 million dangerous goods shipments transported every year. With the air cargo growth forecasted at 4.9 percent every year over the next five years, the number is expected to rise significantly. To ensure that the air cargo industry is ready to benefit from this growth, it needs to adopt modern and harmonised standards that will facilitate safe, secure and efficient operations, particularly in relations to carriage of dangerous goods. DG AutoCheck is a significant step towards achieving this goal,” said Nick Careen, senior vice president, airport, passenger, cargo and security, IATA.

FACILITATING ACCEPTANCE CHECKS

DG AutoCheck is a digital solution that allows the air cargo supply chain to check the compliance of the Shipper’s Declaration for Dangerous Goods (DGD) against all relevant rules and regulations contained in the IATA Dangerous Goods Regulations.

The tool enables electronic consignment data to be received directly, which supports the digitisation of the cargo supply chain. Optical Character Recognition (OCR) technology also transforms a paper DGD into electronic data. This data is then processed and verified automatically using the XML data version of the DGR.

DG AutoCheck also facilitates a ground handlers or airline’s decision to accept or reject a shipment during the physical inspection stage, by providing a pictorial representation of the package, with the marking and labelling required for air transport.

“The DGR lists over 3,000 entries for dangerous goods. Each one must comply with the DGR when shipped. The paper DGR consists of 1,100 pages. Manually checking each shipper’s declaration is a complex and time consuming task. Automation with DG AutoCheck offers us a giant step forward. The cargo supply chain will benefit from greater efficiency, streamlined processes and enhanced safety,” said David Brennan, assistant director, cargo safety and standards, IATA.

INDUSTRY COLLABORATION

Collaboration is critical in driving industry transformation, especially for a business with such a complex supply chain. DG AutoCheck is a good example of effective industry partnerships.

An industry working group made up of more than twenty global organisations supported the development of DG AutoCheck. The group comprises airlines, freight forwarders, ground handlers and express integrators, including Air France-KLM CargoSwissportPanalpina and DHL Express.

“The air cargo supply chain is currently undergoing a major digital evolution. Collaboration across the industry is essential if the goal of a digitised electronic end-to-end messaging platform is to be realised. There is no time to lose as there is a growing demand from our customers for efficiency of electronic documentation throughout the supply chain,” said Nick Careen, senior vice president, airport, passenger, cargo and security, IATA.

 

Microbial Biotechnology in Environmental Monitoring and Cleanup

A new book on the advances in microbial biotechnology in environmental monitoring and clean-up has just be published by IGI Global.  The book is part of the Advances in Environmental Engineering and Green Technologies Book Series.

In the book, the authors state that pollutants are increasing day by day in the environment due to human interference. Thus, it has become necessary to find solutions to clean up these hazardous pollutants to improve human, animal, and plant health.

Microbial Biotechnology in Environmental Monitoring and Cleanup is a critical scholarly resource that examines the toxic hazardous substances and their impact on the environment. Featuring coverage on a broad range of topics such as pollution of microorganisms, phytoremediation, and bioremediation, this book is geared towards academics, professionals, graduate students, and practitioners interested in emerging techniques for environmental decontamination.

This book is a collection of various eco-friendly technologies which are proposed to under take environmental pollution in a sustainable manner. the role of microbial systems has been taken as a tool for rapid degradation of xenobiotic compounds. Application of microbes as bio-inoculants for quality crop production has been emphasized by some authors. Conventional method of bioremediation using
hyper-accumulator tree species has been given proper weightage. The emerging role of nanotechnology in different fields has been discussed. The contents of book are organized in various sections which deal about microbial biodegradation, phytoremediation and emerging technology of nanocompounds in agriculture sector.

Chapter 18, which covers phytoremedation, acknowledges that environmental pollution with xenobiotics is a global problem and development of inventive remediationtechnologies for the decontamination of impacted sites are therefore of paramount importance.
Phytoremediation capitalizes on plant systems for removal of pollutants from the environment.  Phytoremediation is a low maintenance remediation strategy and less destructive than physical or chemical remediation.  Phytoremediation may occur directly through uptake,translocation into plant shoots and metabolism (phytodegradation) or volatilization (phytovolatilization) or indirectly through plant microbe-contaminant interactions within plant root zones(rhizospheres).  In recent years, researchers have engineered plants with genes that can bestow superior degradation abilities. Thus, phytoremediation can be more explored, demonstrated, and/or implemented for the cleanup of metal contaminants, inorganic pollutants, and organic contaminants.

Topics Covered

The 400-page, 20 chapter book covers many academic areas covered including, but are not limited to:

  • Bio-Fertilizers
  • Bioremediation
  • Microbial Degradation
  • Microorganisms
  • Organic Farming
  • Pesticide Biodegradation
  • Phytoremediation

 

 

U.S. DOD Rapid Innovation Fund for Innovative Technology in Emergency Response Tools

The United States Department of Defence (U.S. DoD) Rapid Innovation Fund facilitates the rapid insertion of innovative technologies into military systems or programs that meet critical national security needs. DoD seeks mature prototypes for final development, testing, evaluation, and integration. These opportunities are advertised under NAICS codes 541714 and 541715. Awardees may receive up to $3 million in funding and will have up to two years to perform the work. The two phases of source selection are (1) white paper submission and (2) invited proposal submission. The window of opportunity for submitting white papers expires on April 12, 2018 (due by 3:00 PM ET).
Among the numerous R&D opportunities described in the BAA are topics relevant to the development of environmental monitoring and emergency response tools:

  • Handheld automated post-blast explosive analysis device (USDR&E-18-BAA-RIF-RRTO-0001). Handheld automated detection and characterization of explosive residue collected on-scene after an explosion.
  • Handheld networked radiation detection, indication and computation (RADIAC) (DTRA-17-BAA-RIF-0004). A lighter, more compact system for integration into CBBNE situational awareness software architecture of Mobile Field Kit and Tactical Assault Kit.
  • 3-D scene data fusion for rapid radiation mapping/characterization (DTRA-17-BAA-RIF-0005).
  • Immediate decontamination (CBD-18-BAA-RIF-0001). A spray-on decontaminant that can be applied in a single step in ~15 minutes on hardened military equipment.
  • Hyperspectral aerial cueing for chemical, biological, radiological, nuclear and explosive (CBRNE) mobile operations (PACOM-18-BAA-RIF-0001). Real-time detection via drone.
  • Mobile automated object identification and text translation for lab equipment (DTRA-17-BAA-RIF-0003). A tool to help users recognize equipment, chemicals, and potentially hazardous material in real time.

https://www.fbo.gov/spg/ODA/WHS/REF/HQ0034-18-BAA-RIF-0001A/listing.html
[NOTE: This BAA was also issued as HQ0034-18-BAA-RIF-0001B.]

BC Ministry of the Environment: Staffing Announcement

The British Columbia Environment Ministry recently announced that Danielle Grbavac has been named as as Director, Land Remediation within the Environmental Emergencies and Land Remediation Branch, Environmental Protection Division, Ministry of Environment and Climate Change Strategy.

 

Danielle has 15 years of experience working in environmental science, including marine geoscience, coastal geomorphology, climate change and most recently contaminated sites, both for the provincial and federal governments. She holds a Bachelor of Science in Geography (hons) from the University of Victoria and a Master of Science in Environmental Geomorphology from the University of Oxford. She has also completed graduate level studies in public administration from the University of Victoria.

Before joining the BC public service, Danielle worked as a marine geoscientist for the Geological Survey of Canada. Since joining the ministry she has worked on regulatory development in the Climate Action Secretariat and issues management for BC Parks and the Conservation Officer Service. She joined the Land Remediation Section in 2015, as Operations Manager, leading a diverse team of professionals responsible for oversight of high risk site classification and site identification, as well as the development of policy for legislative and regulatory change and related guidance for BC’s site remediation program. Additionally, Danielle has held an associate faculty position at Royal Roads University for nearly a decade teaching in the School of Environment and Sustainability and the International Study Centre.

Danielle brings a wealth of knowledge and background, and great interpersonal skills to her new role. She is looking forward to identifying priorities for contaminated sites work after the recent standards updates in the Stage 10 & 11 Contaminated Sites Regulation amendments in November 2017. She intends to maintain and strengthen the ministry’s relationships with its partners and stakeholders within the contaminated sites community.

Canada: $150K fine for improper storage of petroleum products

It could be a sign of a toughening of enforcement in Canada.  A company in Saskatchewan was recently fined $150,000 for improper storage of petroleum hydrocarbons under the Storage Tank Systems for Petroleum Products and Allied Petroleum Products Regulations, made pursuant to the Canadian Environmental Protection Act, 1999.  The company, Crop Production Services (Canada) Inc., recently plead guilty to transferring petroleum products into unidentified storage-tank systems.  Storage of petroleum products in unmarked containers is a violation of the federal regulations.

In 2016, enforcement officers from Environment Canada and Climate Change conducted an investigation of Crop Production Services (Canada) Inc.  During the course of the inspection, they discovered the petroleum product in an unmarked container.  No spillage of petroleum product had occurred.

The Court ordered the company to pay a total penalty of $150,000 to be directed to the federal Environmental Damages Fund.  As a result of this conviction, the company’s name will be added to the Environmental Offenders Registry.

Crop Production Services (Canada) Inc. (CPS) is a leading provider of agricultural products and services for western Canadian growers. A subsidiary of Nutrien Ltd., CPS provides a wide range of services to the agricultural industry including agronomy Services; crop protection;  plant nutrition; precision agriculture; fuel, oil and lubricants; and storage and handling. CPS has over 220 retail locations in communities across Western Canada.

CPS offers Esso bulk fuels to the farm and commercial market across the Prairies through an agreement with Imperial Oil

The Storage Tank Systems for Petroleum Products and Allied Petroleum Products Regulations aim to reduce the risk of contaminating soil and groundwater due to spills and leaks of petroleum products from storage-tank systems.  The regulations require owners and operators to identify their storage-tank systems with an identification number from Environment and Climate Change Canada. This requirement allows an inventory of storage-tank systems to be maintained in a registry that captures the type of tank, the type of piping, and the year of installation of the storage-tank system. Suppliers that deliver petroleum products and allied petroleum products (e.g., thinner for vinyl coatings) are prohibited from transferring petroleum products into any storage tank, unless the storage-tank system identification number is visible.

Using GPS trackers to fight toxic soil dumping

As reported by the CBC News and the Montreal Gazette, the Province of Quebec and the City of Montreal are joining forces to try to crack down on a possible link between organized crime and the dumping of contaminated soil on agricultural land.

The solution? A GPS system that can track where toxic soil is — and isn’t — being dumped.

According to the province, there are about two million metric tonnes of contaminated soil to be disposed of every year.

Toxic soil is supposed to be dumped on designated sites at treatment centres. But the Sûreté du Québec has confirmed it believes members of organized crime have been dumping soil from contaminated excavation sites onto farmland.

Quebec Provincial police confirm they are investigating a possible link between organized crime and the dumping of contaminated soil.

“It’s a constant battle. The city and all municipalities have to be very vigilant about any types of possible corruption,” said Montreal Mayor Valérie Plante.

“What we are talking about today supports a solution, but again, we always have to be proactive.”

The new pilot project, called Traces Québec, is set to launch in May. Companies would have to register for the web platform, which can track in real time where soil is being transported — from the time it leaves a contaminated site to the time it’s disposed of.

Some environmentalists say they’re concerned about the impact the toxic soil has had on agricultural land where it’s been dumped. They’re also uncertain about how a computerized tracking system will put an end to corruption and collusion.

“Right now, there’s no environmental police force in Quebec so there have been investigations into these toxic soils being dumped but unfortunately nobody’s been held accountable yet,” said Alex Tyrrell, leader of the Quebec Green Party.

“There’s really a lack of a coherent strategy for how Quebec is going to decontaminate all of these different toxic sites all over the province. There’s no announcement of any new money.”

The city and the province say this is a first step at addressing the issue and more announcements will be on the way in the coming months.

The pilot project — a joint effort with the city of Montreal — will test a system, known as Traces Québec, that uses GPS and other technologies to track contaminated soil. The first test case will involve a city plan to turn a former municipal yard in Outremont into a 1.7-hectare park. Work is to start in the fall.  All bidders on the project will have to agree to use the Traces Québec system.

Using the system, an official cargo document is created that includes the soil’s origin and destination and its level of contamination. Trucks are equipped with GPS chips that allow officials to trace the route from pickup to drop-off.

Mayor Valérie Plante said the pilot project is “a concrete response to a concrete problem.”

She said she wants to protect construction workers and residents by ensuring contaminated soil is disposed of properly. The city also wants to make sure the money it spends on decontamination is going to companies that disposed of soil safely and legally.

“Municipalities have to be very vigilant about any types of possible corruption,” she said. “We know there are cracks in the system and some people have decided to use them and it’s not acceptable.”

Plante said Montreal will study the results of the pilot project before deciding whether to make the system mandatory on all city projects.

The Traces Québec system was developed by Réseau Environnement, a non-profit group that represents 2,700 environmental experts.

Pierre Lacroix, president of the group, said today some scofflaws dispose of contaminated soil illegally at a very low cost by producing false documents and colluding with other companies to circumvent laws.

He said the Traces Québec system was tested on a few construction sites to ensure it is robust and can’t be circumvented. “We will have the truck’s licence plate number, there will be GPS tracking, trucks will be weighed,” Lacroix said.

“If the truck, for example, doesn’t take the agreed-upon route, the software will send an alert and we’ll be able to say, ‘Why did you drive that extra kilometre and why did it take you an extra 15 minutes to reach your destination?’”

Organized crime can be creative in finding new ways to avoid detection and Lacroix admitted “no system is perfect.”

But he noted that “at the moment, it’s anything goes, there are no controls. Technology today can help take big, big, big steps” toward thwarting criminals.

With files from CBC reporter Sudha Krishnan

How the GPS tracking system will work

Contaminated sites could pose issue for Saskatoon’s transit plan

As reported in the Phil Tank in the Saskatoon Star Phoenix, the city of Saskatoon has tested the soil at several locations where transit stations are planned for the bus rapid transit (BRT) system. The results of the tests will not be known until later this month, but Mayor Charlie Clark says contaminated sites, like former gas stations, pose a big issue for Canadian cities.

The testing took place along the proposed BRT red line, which is expected to run on 22nd Street on the west side of the river and on Eighth Street on the east side.

“Brownfields (contaminated sites) along some of these major streets are a real problem,” Clark told reporters Tuesday at city hall. “We have a lot of gas stations that have been abandoned, left there and the owners are just sitting on them and not allowing them to be sold and redeveloped.”

The CP railway crossing on 22nd Street, one of the main routes of the BRT system. (Google Maps)

Clark, who was promoting an event to gather residents’ input on the city’s various growth plans, said he would like to see clearer rules from the province and the federal government on contaminated sites.

The City of Saskatoon has limited tools to force sites to be sold or redeveloped or to compel owners to clean up contamination, he said.

“We frankly don’t think the taxpayers of Saskatoon should have to pay to clean up contaminated sites where somebody was operating a gas station or a fuel distribution site for many years, generating a profit off of it, and then leaving it as a barren and wasted piece of land,” Clark said.

The city’s brownfield renewal strategy is among a number of different planks in its overall growth strategy, which was featured at a community open house in early March.

Brownfield Renewal Strategy

Saskatoon’s Brownfield Renewal Srategy (“BRS”) states that abandoned, vacant, derelict, underutilized properties shouldn’t stop revitalization.  The strategy supports redevelopment of brownfield sites to maximize their potential and revitalize the main transportation corridors within the City.  The goal of the BRS is to create environmental guidance manuals, provide advisory services, and implement incentive programs to encourage brownfield redevelopment.

The City of Saskatoon sees the BRS as requirement for achieving the City’s target of achieving 50% growth through infill.

The BRS will create a suite of tools and programs designed to assist prospective developers and property owners with the environmental requirements associated with impacted and potentially impacted brownfields.

Mayor Clark noted Saskatoon and its surrounding region has been identified as the fastest growing metropolitan area in Canada, with 250,000 additional residents anticipated in the next few decades.

Lesley Anderson, the director of planning and development with the City of Saskatoon, talks renewal strategy

Ontario Announces Cleantech Strategy & Support for Cleantech Companies

Article by Richard CorleySophie Langlois and Catherine Lyons

Goodmans LLP

Recently, the Ontario Minister of Research, Innovation and Science, Reza Moridi, launched Ontario’s Cleantech Strategy (the “Cleantech Strategy“) which aims to catalyze the growth of Ontario’s clean technology sector to support sales into a global market which is expected to grow to $2.5 trillion by 2022. The Cleantech Strategy is aligned with Ontario’s five-year Climate Change Action Plan (CCAP) to fight climate change, reduce greenhouse gas (GHG) pollution, and drive the transition to a low-carbon economy.  It is also aligned with Ontario’s Business Growth Initiative (BGI), which is, among other things, assisting innovative companies to scale up.

Purpose of the Cleantech Strategy

The Cleantech Strategy bolsters Ontario’s commitment to support the development of new, globally competitive low-carbon technologies that will contribute to fighting climate change and to meeting Ontario’s GHG pollution reduction targets of 15% below 1990 levels by 2020, 37% by 2030 and 80% by 2050. As Minister Moridi explained:

By helping our cleantech companies get ready to scale – and helping them to connect to early customers here in Ontario – Ontario is supporting innovation and reducing emissions and environmental impact across industries. Over the longer term, we expect to see more scaled-up Ontario cleantech companies recognized as North American leaders.

Ontario has the largest share of cleantech companies in Canada and the Cleantech Strategy further supports the province’s leadership in GHG pollution reduction through the development and scaling of cleantech solutions.

Principal Elements of the Cleantech Strategy

Based on Ontario’s strengths in cleantech and global demand, the Cleantech Strategy prioritizes the following four cleantech sub-sectors: energy generation and storage, energy infrastructure, bio-products and bio-chemicals, and water and wastewater.

The Cleantech Strategy has four interrelated pillars through which the province intends to meet its objective of helping cleantech companies scale up and meet global demand:

  1. Venture and scale readiness – strengthening opportunities for in-house research and development, strengthening entrepreneur knowledge of key global markets, reducing regulatory uncertainty to facilitate access to capital, and attracting and developing a strong pool of sales, marketing and management talent
  2. Access to capital – increasing access to scaling capital, providing guidance on available provincial and federal cleantech funding, and simplifying access to such capital
  3. Regulatory modernization – streamlining the regulatory environment where possible to reduce barriers for cleantech market entry, supporting performance-based standards and approvals processes, and supporting the development of harmonized industry standards
  4. Adoption and procurement – increasing demonstration and pilot opportunities to de-risk and validate new technologies, and addressing prescriptive and risk-averse procurement practices

Initiatives funded through Ontario’s carbon market as part of the Cleantech Strategy include the Global Market Acceleration Fund (GMAF) and the Green Focus on Innovation and Technology (GreenFIT).

The Global Market Acceleration Fund

The GMAF will help companies lower the risk associated with expanding production of a proven clean technology.  The fund will also assist companies with the cost of scaling up inventory, distribution and sales to domestic and global markets.  The GMAF can provide between $2 million and$5 million of funding to Ontario-based companies with promising GHG reduction technologies and scale-up and export potential.  To receive funding, these companies must be able to demonstrate funding commitments for at least 50% of the eligible project costs. A total of $27 million has been allotted to the GMAF.

Green Focus on Innovation and Technology

Through the GreenFIT program, Ontario will commit $10 million towards demonstration projects of new technologies and services. Early adoption of these new technologies and services will benefit both the adopting public sector institutions with support for their emissions reductions and participating companies with opportunities for validation and credibility for their products.

The content of this article does not constitute legal advice and should not be relied on in that way. Specific advice should be sought about your specific circumstances.

_________________

About the Authors

Richard Corley is a partner at Goodmans LLP and leads the firm’s Cleantech Practice Group.

Sophie Langlois is an associate at Goodmans LLP.  She practices in the area of corporate and securities law and mergers and acquisitions.

Catherine Lyons is a partner at Goodmans LLP.  She dedicates her practice to representing both private and public sector clients at the intersection of municipal and environmental law.

 

This article was first published on the Goodmans LLP website.

Recycling end-of-life materials may be perpetuating toxic chemicals in new products

A researcher from the Canadian Environmental Law Association and paralegal, Fe de Leon, recently co-published a paper with HEJSupport International Co-Director Olga Speranskaya to bring public attention to toxic chemicals that appear in new products made out of recycled materials.  The authors of the paper argue that many countries have made investments into achieving progress towards a circular economy, but little or no attention is paid on toxic chemicals that appear in new products made out of recycled materials. The paper cites a growing body of evidence of how a circular economy fails to address concerns regarding toxic chemicals in products.

Fe de Leon, Researcher and Paralegal, CELA

In the paper, the authors cite a 2017 study prepared by IPEN, an environmental activist organization that focuses on synthetic chemicals, which revealed elevated concentrations of globally targeted toxic flame retardants in plastic toys.  The IPEN study claimed to have found elevated concentrations of toxic persistent organic pollutants (POPs) in samples of plastic toys purchased in different stores in Canada and other 25 countries globally.  The study further stated that the levels of some chemicals were more than five times higher than recommended international limits.  These chemicals include PBDEs (polybrominated diphenyl ethers) such as octabromodiphenyl ether (OctaBDE), decabromodiphenyl ether (DecaBDE); and SCCPs (short chain chlorinated paraffins).  They are listed under the Stockholm Convention on Persistent Organic Pollutants and are internationally banned or restricted due to their hazardous characteristics.  They all are persistent, highly toxic, travel long distances and build up in the food chain.  However, their presence in new products, although they are banned or restricted, opens up the discussion of a problem regarding recycling as a key component of a circular economy.

The paper concludes that product recycling and a focus on a circular economy should be encouraged.  However, material flows should be free from hazardous chemicals, at the minimum those chemicals which have already been regulated under the international treaties.

Olga Speranskaya, HEJSupport International Co-Director, IPEN CoChair