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Regulations on furniture flammability
1977 - Woolworths Manchester Burned down → introduced flame retardants
polyurethane foam in stuffing was highly flammable
Reduced fire related deaths
UK (and a few other EU countries) have regulations covering furniture flammability
GPSD → General Product Safety Directive
EN Standards → especially EN 1021 and EN 597
Flame retardants
example
mechanism
issues
Bromodiphenyl ether (BDE-47)
Halogenated compound which thermally decomposes to release bromine free radicals
halogen free radicals can then quench radicals which sustain combustion (H, OH and O free radicals)
This stops the fire
Poor biodegradability → bromine not found in environment so not used naturally or digested by enzymes
Lipophilic → not water soluble
can cross BBB and accumulate in body fat
LogP ~ 6
Forever chemicals
Persistent organic pollutants (POP)
Bioaccumulates → persist in the environment for long periods of time
Half-life of days/years in humans
Often contain halogens (Br and Cl)
Present from poles to equator
In natural environments (especially water)
in organisms (mammals, fish, birds) → gets into food chain
in people → found in 100% of 298 human milk samples (Canada. 2008-11)
in buildings and vehicles
Includes flame retardants
Half-life of brominated compounds
Half-life of BDE-47 is around 664 days (1.8 years)
time for concentration to half
This is the time for elimination in the absence of further uptake
follows exponential decay
time for elimination varies with diet and metabolism
decay from systemic circulation results in continuous exposure to the nervous system
Can be much longer in other compounds
BDE-47 systematic reviews and meta-analysis
how
findings
collation of data from several studies, with adjustment for major confounders (maternal education, income, smoking, alcohol, home environment, breast feeding)
BDE-47 in maternal blood, child blood and breast milk measured
Blood BDE-47 up to 1470ng/g of lipid
Breast milk BDE-47 up to 200mg/g lipid
BDE-47 in infants is associated with decrements in motor development, cognitive development and attention-related behaviours
IQ decreased by 3.7
Prenatal exposure is the strongest predictor
limited association with ADHD
Exposure begins in-utero by breast feeding
Mechanisms of BDE-47 in neurobiology
studied by in-vitro and in-vivo studies
looked at Cerebellar granule neurones involved in motor learning, coordination and sensory processing
effects on mouse neurones:
alters signal transduction
oxidative stress
apoptosis
Increases reactive oxygen species (ROS) and reactive carbonyls
decrease cell viability
increase apoptotic markers (Caspase-3)
Limitations of using animal studies in BDE-47 studies
In-vivo duration and dosage
micromolar over days
doesn’t represent human exposure
In-vivo tissue concentration
hard to compare to humans as they are an order larger
studies are post-natal not in-utero
No behavioural follow up → learning, memory, motor function
ROS production is a causal factor in the neuronal dysfunction caused by BDE-47
International legislation and mitigation for flame retardands
mitigation and legislation consensus published in Environmental International in 2023
UK has highest use
unsure of whether and to what extent flame retardants contribute to fire safety
flawed tests for fire safety (eg. ignition test)
recommendations:
minimise use
use less combustible materials
evaluate fire risks and therefore need for flame retardants
promote culture which considers environmental impact
implications of global health
prognosis for future generations
UK legislation (2025)
PBDE regulations (poly-BDE)
tetra-, penta-, hexa-, hepta- and deca-BDEs
manufacture and sales banned
Waste containing PBDEs
destroy or irreversibly transform
Electronics
Max 0.1% PBDE content
Water/envrionment
classified as priority hazzardous pollutants
ongoing surevilance
Waste mannagement
no recycling avove POP limits
mandatory destruction by incineration for water exceeding threshold
strict control of old electronics, foams, textiles and plastics