Class: Brominated Flame Retardants
Chemical Name: | Molecular Makeup:[2] | |
PBDE, Polybrominated Diphenyl Ether |
C12H10−xBrxO |
Sources: The PBDE family of chemicals consists of 209 variations, or “cogeners,” with differing numbers of attached bromine ions. These chemicals are used as flame retardants in a variety of consumer products ranging from plastic television cases to textile fibers. In countries where only one type of PBDE is banned, others are generally used in its place until PBDEs are banned entirely. [2] The annual market demand for BFRs is 203,790 metric tons. [2]
Transport Vectors: 49 million pounds of DecaPBDE was added to consumer products in North America in 2001. Products containing PBDEs slowly release them into the air where they are often converted to more toxic forms by sunlight. Due to their prevalence in consumer products, they are ubiquitous throughout America in quantities 10 to 40 times those found in Europe or Japan.[1] PBDEs have a low water solubility and high lipid solubility.[2] BDE-17, a cogener not found at source points, was detected in the air on a Baltic Sea island, indicating that PBDEs are transformed as they move through the environment. Studies have found food responsible for up to 93% of human exposure to PBDEs. [3]
Sample Concentration Levels
Abiotic Media[2]:
House Dust (min/max) |
Soil (min/max, dry weight) |
Air (min/max) |
Sediment (min/max, dry) |
USA: |
China: |
Canadian Arctic: 0.4-47 pg/m3 [7] |
China: |
Biotic Media[3]:
Fish/Sea Life (min-max) ng/g in fat |
Birds |
Mussels |
Food |
Fish: |
China |
Qingdao, China: |
(US Levels) |
Human:
Blood Serum (US), pg/g: |
Blood Serum (World), ng/g: | FatTissue,ng/g: | Breastmilk, ng/g: |
BDE-47 min-max Sweden: .27 - 8.1 UK: .30 – 180 Mexico: 3.0-14.5 Spain: .3-9.0 China: .5-3.6 Korea: 2.2-12.12 New Zealand: .76-12.7 Belgium: 0.2-3.07 [3] |
Note the wide range of concentration in human subjects from region to region. A positive correlation has been shown between working with electronics disassembly and PDBE levels. Sweden’s PDBE levels rose exponentially from 1972 to 1996 then began a gradual decline, possibly due to a voluntary ban in the early 1990’s. [3] Note that none of these studies include every PDBE cogener and generally focus on the most common ten or fifteen; as such, actual total amounts of PDBEs present in every sample are higher than reported.
Health effects:
Citations: