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TBBPA

Sediment

TBBPA (µg/kg dry weight)

Mussels

TBBPA (µg/kg wet weight)
North
Not detected
Metlakatla
Not detected
Not detected
Prince Rupert
Not detected
Not detected
Wiah Point
Not detected
Not detected
Armentieres Channel
Not detected
Not detected
Bischof Islands
Not detected
Not detected
Haswell Bay
Not detected
Not detected
Louscoone Inlet
Not detected
Not detected
Bella Bella
Not detected
Not detected
Port Neville
Not detected
Not analyzed
Sechelt
Not sampled
Not analyzed
Strait of Georgia 1
Not sampled
Not analyzed
Strait of Georgia 2
Not sampled
Not analyzed
Howe Sound 1
Not sampled
Not detected
Howe Sound 2
Not sampled
Not detected
Howe Sound 3
Not detected
Not detected
Indian Arm 1
Not detected
Not detected
Indian Arm 2
Not detected
Not detected
Burrard Inlet 1
Not detected
Not analyzed
Burrard Inlet 2
Not sampled
Not detected
Burrard Inlet 3
Not sampled
Not analyzed
Burrard Inlet 4
Not sampled
Not analyzed
Burrard Inlet 5
Not sampled
Not detected
Burrard Inlet 6
Not detected
Not analyzed
Burrard Inlet 7
Not sampled
Not detected
Burrard Inlet 8
Not detected
Not sampled
Burrard Inlet 9
Not detected
Not detected
Burrard Inlet 10
Not detected
Not detected
Burrard Inlet 11
Not sampled
Not detected
Burrard Inlet 12
Not sampled
Not detected
Burrard Inlet 13
Not sampled
Not detected
Burrard Inlet 14
Not sampled
Not sampled
Burrard Inlet 15
Not detected
Not detected
Fraser River 1
Not sampled
Not detected
Fraser River 2
Not sampled
Not detected
Fraser River 3
Not sampled
Not detected
Fraser River 4
Not sampled
Not detected
Fraser River 5
Not sampled
Not sampled
Fraser River 6
Not detected
Not sampled
Fraser River 7
Not detected
Not detected
Tsawwassen
Not sampled
Not detected
Lemmens inlet
Not sampled
Not detected
Grice Bay
Not sampled
Not detected
Dixon Island
Not detected
Not detected
Saturna Island
Not detected
Not analyzed
Fulford Harbour 1
Not sampled
Not analyzed
Fulford Harbour 2
Not sampled
Not analyzed
Patricia Bay
Not detected
Not analyzed
Finnerty Cove 1
Not detected
Not analyzed
Finnerty Cove 2
Not sampled
1.99 µg/kg
1.99 µg/kg
Victoria Harbour 1
Not sampled
Not detected
Victoria Harbour 2
Not sampled
Not detected
Victoria Harbour 3
Not sampled
Not analyzed
Victoria Harbour 4
Not sampled
Not detected
Albert Head 1
Not sampled
Not detected
Albert Head 2
Not sampled
South

What is it?

Tetrabromobisphenol A (TBBPA) is a brominated flame retardant used in flame-retarded epoxy and polycarbonate resins and is currently the highest selling brominated flame retardant globally. Resins containing TBBPA have wide-ranging applications, including communications and electronics equipment, automotive parts, and appliances.1 TBBPA is not known to have been manufactured in Canada.

How does it get into the ocean?

The major pathways by which brominated flame retardants enter the marine environment are likely via leaching from finished products into wastewater systems and via landfill runoff.1,2

TBBPA has relatively low solubility in water, and therefore, is likely to bind to organic matter in sediments. TBBPA may also accumulate in the lipids of marine organisms.1

Is it a problem?

Like other brominated flame retardants, TBBPA is persistent in the environment and can accumulate in organisms (bioaccumulative). It has even been detected in the remote Arctic in sediments, plants, fish, and birds.3

FACT: Bisphenol A, a hormone mimic that has received much public attention due to its presence in plastic water bottles, is a breakdown product of TBBPA.

As a group, brominated flame retardants are known to have toxic effects in terrestrial and aquatic organisms, with TBBPA known to have adverse effects on survival, reproduction, and development.1 In bluegill sunfish and rainbow trout, exposure to TBBPA resulted in irritation, twitching, and erratic swimming, while in fathead minnow, exposure resulted in reduced growth.4  Zebrafish embryos exposed to TBBPA experienced swelling, hemorrhage, decreased heart rate, tail malformations, and death.5

One of the degradation products of TBBPA in the environment is bisphenol A. Like TBBPA, bisphenol A is persistent and bioaccumulative, and is toxic to both aquatic and terrestrial organisms.1 It can disrupt hormones, which means that it impacts systems that regulate everything from embryonic development and the formation of reproductive glands to growth and digestion.6,7

What is being done?

TBBPA is still used to manufacture products in Canada, and its use is not yet regulated.

Canadian federal environmental quality guidelines (FEQGs) have been developed for TBBPA for water and sediment.8 In 2017, the federal government also issued water and sediment quality guidelines for bisphenol A.9

What can you do?

As individuals and organizations, we can:

  • Learn more about TBBPA and other brominated flame retardants using the resource links below.
  • Recycle and dispose of waste responsibly and according to local guidelines.
  • Avoid using products that contain TBBPA and other contaminants of concern. The US EPA’s Safer Choice program identifies products that are safer for humans and the environment and can be used as a reference to check product ingredients.10,11 The Green Science Policy Institute also provides information regarding consumer choices.12

More information?

Environment Canada. 2013. Screening Assessment Report. Environment Canada and Health Canada. Available at: http://www.ec.gc.ca/ese-ees/default.asp?lang=En&n=BEE093E4-1\

Morris S, Allchin CR, Zegers, BM, Haftka JJH, Boon JP, Belpaire C, Leonards PEG, van Leeuwen SPJ, de Boer J. 2004. Distribution and fate of HBCD and TBBPA brominated flame retardants in North Sea estuaries and aquatic food webs. Environmental Science and Technology 38: 5497-5504.

de Wit CA, Herzke D, Vorkamp K. 2010. Brominated flame retardants in the Arctic environment—trends and new candidates. Science of the Total Environment. 408(15): 2885-2918.

4 Darnerud PO. 2003. Toxic effects of brominated flame retardants in man and in wildlife. Environment International 29: 841-853.

McCormick JM, Paiva MS, Häggblom MM, Cooper KR, White LA. 2010. Embryonic exposure to tetrabromobisphenol A and its metabolites, bisphenol A and tetrabromobisphenol A dimethyl ether disrupts normal zebrafish (Danio rerio) development and matrix metalloproteinase expression. Aquatic Toxicology 100: 255-262.

Flint S, Markle T, Thompson S, Wallace E. 2012. Bisphenol A exposure, effects, and policy: A wildlife perspective. Journal of Environmental Management 104: 19-34.

Kang JH, Aasi D, Katayama Y. 2007. Bisphenol A in the aquatic environment and its endocrine-disruptive effects on aquatic organisms. Critical Reviews in Toxicology 37: 607-625.

ECCC 2016. Canadian Environmental Protection Act, 1999 Federal Environmental Quality Guidelines: Tetrabromobisphenol A (TBBPA). Environment and Climate Change Canada, May 2016.

ECCC 2017. Canadian Environmental Protection Act, 1999 Federal Environmental Quality Guidelines: Bisphenol A. Environment and Climate Change Canada, February 2017.

10 US EPA. 2018. Safer Choice. Available at: https://www.epa.gov/saferchoice

11 US EPA. 2014. Flame Retardant Alternatives for Hexabromocyclododecane (HBCD). Available at: https://www.epa.gov/sites/production/files/2014-06/documents/hbcd_report.pdf

12 Green Science Policy Institute. 2017. Flame Retardants. Available at: http://www.sixclasses.org/videos/flame-retardants

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