Jump to main content.


GLBTS Links

______________________

Back to Index
exit EPA (About PDF)

Great Lakes Binational Toxics Strategy

Polychlorinated Biphenyls (PCB) Workgroup

Toronto Meeting Minutes 
May 17, 2001

Below are minutes of the PCB Workgroup meeting of May 17, 2001. Follow-up action items identified during the meeting are summarized under the Path Forward heading.

Progress since November 16, 2000 Workgroup Meeting
Progress since the PCB Workgroup meeting of November 16, 2000 was reviewed. A summary report of the workgroup’s progress was distributed to attendees and will be posted on the PCB workgroup’s web-site: www.epa.gov/glnpo/bns/pcb/.

PCB Reduction Commitments
An update on the voluntary commitment letters was provided. In addition to the information in the progress report, it was noted that GM in Canada notified Environment Canada that 1000 tones of high level PCB had been recently destroyed and approximately 3800 tones of low level contaminated soil had been treated and that Ford and Daimler-Chrysler have sent similar responses.

The workgroup discussed that companies sometimes are not able to commit immediately to PCB reduction because, 1) reduction/replacement is dependent on companies’ internal planning and budgeting cycle, and 2) reduction/replacement is tied to market conditions. EPA and Environment Canada will continue mailing out the voluntary reduction and commitment letters to the priority sectors and associations seeking additional commitments to reduce PCBs.

Presentation on PCB Destruction in Canada
Gordon Godin and Al Wakelin of Sensor Environmental gave a presentation on Swan Hills waste management facility in Alberta and touched on PCB destruction in Canada. The Swan Hills facility is under new management who’s mandate includes a review of options for its future. One of the issues is the continuing high cost to operate the facility. Sensor Environmental is currently under contract to Alberta government to run Swan Hills until the end of the year 2001. The facility has enough capacity to handle additional waste from both U.S. and Canada.

Fugitive Emissions and Other PCB Air Data
Dr. William J. Mills from the University of Illinois at Chicago presented his findings on additional work he conducted on emissions from the Smithville CWML site in Ontario. The site is an inactive PCB equipment, transfer, and storage site. Remediation activities at the site took place over several years and included excavation, on-site containment, and treatment by incineration. During this period, extensive monitoring was conducted which included measurements of PCBs in ambient air (daily), water effluent and incinerated materials. The presentation included a review of information on the site provided by Dr. Mills at the May 16, 2000, PCB workgroup meeting.

The main conclusions of the additional analysis and presentation were:

  • PCB destruction is required to reduce PCB concentrations in the environment, not storage or landfilling, or continued use,
  • fugitive emissions are more important than process emissions for technologies with 99.9999% destruction removal efficiency, and
  • estimates of annual emissions from the site (fugitive and process) demonstrated a potential for estimating emissions from other sites.
  • An analysis of the ambient air concentrations relation to temperature and wind effects showed that there was a definite correlation between the ambient PCB concentration and ambient temperature and wind speed and that the Smithville site was the source of PCBs detected in off-site monitors.

    Results of air dispersion modeling showed that calculated ambient air PCB concentrations from the incinerator stack emissions were one to four orders of magnitude (10 to 10,000 times) less than those observed. This led to the conclusion that observed PCB concentrations from the site were probably not from the incinerator stack and instead from other on-site sources. Five sources were identified from receptor modeling: 1) the incinerator stack, 2) ground water treatment areas, 3) the containment building, 4) shredder operations, and 5) contaminated soil at the southeast corner of the site. The receptor modeling also identified the water treatment area and shredder operations as the main sources. Additional analysis of ambient PCB concentrations on the dates over which PCB liquids were destroyed showed that stored PCB liquids were also a main source of the ambient PCB concentrations.

    Other incinerator emission parameters were examined and it was observed that:

  • ambient temperature had no effect on the concentration or rate of emissions of PCBs from the incinerator or the incinerator’s destruction removal efficiency,
  • the feed rate to the incinerator had no effect on the incinerator’s PCB emission concentration or destruction removal efficiency, and
  • ambient air PCB concentrations were not effected by the daily feed amount and were not significantly effected by automatic waste feed shut-off events or thermal release vent openings.
  • Some of Dr. Mills conclusions of the analysis of the data were:

  • the incinerator was not the principal source of PCBs from the site since incinerator emissions were not related to ambient temperature and there were elevated air PCB concentrations before incineration began,
  • the destruction of high concentration PCB liquids resulted in a reduction of observed ambient air PCB concentrations,
  • the destruction of all PCBs resulted in a reduction to "background" air concentrations,
  • wind sector scoring worked reasonably well,
  • air dispersion modeling generally corresponded to observed concentration trend,
  • receptor modeling works reasonably well for PCBs by homolog group, and may work even better for congeners, and
  • fugitive site emissions were the main source of PCBs, not the destruction technology.
  • Some of Dr. Mills recommendations for future activities include:

    A question was raised on if there is a correlation between site emissions and PCBs in sediment and would quicker reductions of PCBs come from cleaning sites or cleaning sediments. Opinions differed. More investigation would be needed. One source of PCBs in the lakes is volatilization from contaminated sediment. The data presented by Dr. Mills shows that PCBs in the lakes can also be due to air deposition from contaminated sites.

    As a consideration for addressing releases during handling operations, one workgroup member raised the possibility of using mobile technology for the destruction of PCBs to reduce handling.

    Outreach and Communication
    A workgroup member mentioned that they get inquiries regarding PCBs, that there are no incentives for them or other companies to help their customers, and that there is some concern about possible liabilities for providing information. It was suggested that it would be beneficial to develop and provide stakeholders with an educational package on PCBs that they could distribute to their customers. One potential incentive for assisting or providing information to customers could be positive public recognition.

    The workgroup also discussed the following outreach and communication activities.

  • Submersible well pump fact sheet: Copies of a draft fact sheet on PCBs in submersible well pumps, prepared by a subgroup, was distributed for comment.
  • Standard presentation: Copies of a draft standard presentation was distributed for comment. The standard presentation was prepared for use by stakeholders to educate others on the Strategy and PCB challenges.
  • U.S. Executive Order on Greening of the Government: Copies of the U.S. Federal Register on the Executive Order 13101 on Greening of the Government was distributed.
  • Incentives
    Several comments were made that there are few, if any, incentives for facilities to remove their PCBs or to help their customers do so. Without incentives, some companies will continue to hold on to their PCB equipment. Some incentives suggested include:

  • provide public recognition, including for assisting customers
  • minimizing regulations on disposal facilities could reduce costs for disposal
  • reduce disposal costs (for example, with government subsidies)
  • develop a program where the earlier companies get rid of PCBs, the less expensive it will be
  • reduce costs of replacement equipment
  • consolidating waste may reduce disposal costs
  • Stelco is an example of one company that got rid of the majority of their PCBs early. A workgroup member commented that if incentives were to be provided now, it would be unfair to those that disposed of their PCBs early. A comment was also made that there should be minimum regulatory barriers at the border so there are no hold ups in movements across the border.

    Work group members stressed that economically viable disposal options are needed and it may be useful to work together with stakeholders involved in disposal (e.g., government, equipment owners, and disposal companies) to identify such options. It was also suggested that if disposal companies could work with stakeholders to get consistent quantities of waste, they could operate at a consistent feed and may be able to lower costs.

    PCB Waste Collection Events
    It was stated that many sites, although they say they are PCB free, have ballasts which contain PCBs. It was suggested that collecting ballasts at municipal household hazardous waste depots in partnership with the different levels of governments would encourage spent ballasts to be deposited and recycled according to the regulations. In addition, it was suggested to try and develop incentives for PCB disposal, i.e. "the earlier you get rid of PCBs, the cheaper it will be."

    City of Windsor collection event: Peter Bziuk, City of Windsor, discussed the city’s PCB initiatives and success stories in consolidating small quantities of PCB contaminated material with other local governments in Essex County. Through consolidating the PCB wastes, they amassed enough to make disposal economical.

    Disposal of PCBs in Canada
    Steve Radcliffe of Ontario MOE, Policy Branch, gave an update of the expansion proposal and application of Trans Cycle Industries (TCI) Canada and Benett Environmental. For further details on an environmental assessment for thermal destruction facilities he suggested checking MOE’s web site: and searching the link to the Environmental Bill of Rights for proposal notices on or after April 20th.

    Al Wakelin of Sensor Environmental pointed out that many PCB owners have indicated it is too expensive to dispose of PCBs, and that it is also very expensive to run the Swan Hills Alberta facility. He indicated that Governments and the people should continue to work together to encourage PCB destruction. He suggested developing an accelerated program of legislative requirements for PCB destruction in Canada. These changes would better utilize their facility. He added that many PCB owners will wait until they approach the deadline before destroying their PCBs.

    Gordin Godin of Sensor Environmental noted that they may only be able to operate their facility until December 31 of this year. Since the cost of running their facility is supplemented by Alberta taxpayers, he suggested stakeholders and Environment Canada work together to ensure they aren’t operating at a loss.

    On workgroup member commented on the need for all stakeholders to develop an overall plan to deal with the disposal capacity issue in Canada, including how to manage residuals of disposal, major spills, and replacement equipment.

    Sediment Workshop
    The highlights from the sediment workshop were provided. The sediment workshop was arranged by Binational Strategy stakeholders and was held on April 24 and 25, 2001. Over 100 representatives of governments, environmental organizations, and remediation consultants attended. During the workshop, presentations were made on several treatment technologies and discussions were held on options for and obstacles to remediation. Options for remediation discussed included: natural recovery, capping, in-situ treatment, ex-situ treatment, removal, and disposal. It was discussed that there is no easy solution. Dredging and land disposal seems to be the least costly. Obstacles of remediation discussed included regulatory, resources, social (communication and support), institutional (goals, politics) and stakeholder involvement.

    The messages from the workshop included:

  • technologies to remediate contaminated sediment exist,
  • clear goals need to be set to strategically use the technologies,
  • partnerships are necessary and there is a need to build support and engage communities,
  • there is a need to look at marketable uses for treated end products, and
  • barriers need to be broken down.
  • EPA National Action Plan for PCBs
    EPA is still working on the National Action Plan for PCBs under the agency’s Persistent Bioaccumulative and Toxics (PBT) initiative. One of the actions in the draft plan to reduce PCBs is to seek PCB reduction commitments through efforts like those being implemented by the PCB workgroup. The PCB workgroup activities will be looked at closely as an example.

    Path Forward and List of Action Items
    Below is a summary of the follow-up actions that were identified during the meeting:

    PCB Waste Collection Events

  • EC/EPA/Industrial Stakeholders (OPG/Utilities/municipalities) should consider coordinating efforts to use municipal household hazardous waste collection depot for the collection of PCB ballasts

  • Incentives and Barriers for accelerated PCB destruction

  • Lowering disposal cost: Environment Canada and the Provincial government should support continued operations of Swan Hills.
  • Environment Canada should develop overall strategy and logistics
  • Environment Canada should finalize regulations
  • Emphasize less storage and immediate destruction of high level PCB (due to ever increasing cost and fugitive emissions during storage/handling)
  • Workgroup leaders should summarize incentives and send to workgroup for comment
  • Outreach and Education

  • Environment Canada should continue PCB Outreach Education and Awareness, particularly for Small Quantity generators
  • Workgroup leaders should seek comments on draft Submersible Well Pump Fact Sheet and Standard Presentation
  • Consider development of outreach and education package on PCBs for companies to send to their customers
  • PCB Reduction Commitments

  • Continue mailing out the voluntary reduction and commitment letters to the priority sectors and associations
  • Environment Canada should mail out commitment letters to Great Lakes Basin (e.g. Lake Superior and Erie drainage basins) during July-August, 2001
  • Case Study Report

  • Continue development of PCB reduction case studies which identify reasons companies remove PCBs

  • PCB Releases

  • Circulate data on releases from contaminated sites and seek comments

  • Attendees

    Name Agency/E-mail Phone
    Ken De Environment
    CanadaKen.de@ec.gc.ca
    416/739-5870
    Tony Martig USEPA Region 5
    martig.anton@epa.gov
    312/353-2291
    Rebecca Bowman Environment Canada
    rebecca.bowman@ec.gc.ca
    416/739-5915
    Peter Bziuk City of Windsor
    pbzuik@city.windsor.on.ca
    519/253-7111 x229
    Alice Dove Environment Canada (EHD)
    Alice.Dove@cciw.ca
    905/336-4964
    Gordon Godin Sensor Env. Services
    gord.godin@sesl.ca
    780/437-7272
    John Hall Ontario Power Generation
    j.a.hall@opg.com
    416/592-6999
    Timothy Huxley Stelco Inc. thuxley@attglobal.net 905/528-2511 x4070
    George Kuper CGLI
    ghk@cgli.com 
    734/663-1944
    Lorinda Lamb ComEd
    lorinda.lamb@exeloncorp.com
    630/576-6731
    Jack Lewis SUNPRO
    jlewis@sunproservices.com
    330/966-0910
    William Mills University of Illinois
    wmills1@mediaone.net
    708/524-2166
    Steven Radcliffe Ontario Ministry of the Environment steve.radcliffe@ene.gov.on.ca 416/314-4170
    Evelyn Strader CGLI
    straderco@aol.com
    248/340-7062
    Larry Talbot Talbot and Associates
    talbotla@pathcom.com
    416/694-7211
    Al Wakelin Sensor
    al_wakelin@sesl.ca
    780/333-4197
    Margaret Wooster GLU
    wooter@glu.org
    716/886-0142
    Noel Wylie Hydro One Networks, Inc.
    noel.wylie@HydroOne.com
    416/345-5147

    Local Navigation

     

    Jump to main content.