Short-course radiotherapy followed by chemotherapy before total mesorectal excision (TME) versus preoperative chemoradiotherapy, TME, and optional adjuvant chemotherapy in locally advanced rectal cancer (RAPIDO) RAPIDO collaborative investigators; Bahadoer
Hexabromocyclododecanes (HBCDs) are brominated
aliphatic cyclic hydrocarbons used as flame retardants in
thermal insulation building materials, upholstery textiles,
and electronics. As a result of their widespread use and
their physical and chemical properties, HBCDs are
now ubiquitous contaminants in the environment and
humans. This review summarizes HBCD concentrations in
several environmental compartments and analyzes
these data in terms of point sources versus diffuse sources,
biomagnification potential, stereoisomer profiles, time
trends, and global distribution. Generally, higher concentra
tions were measured in samples (air, sediment, and fish)
collected near point sources (plants producing or processing
HBCDs), while lower concentrations were recorded in
samples from locations with no obvious sources of HBCDs.
High concentrations were measured in top predators,
such as marine mammals and birds of prey (up to 9600
and 19 200 ng/g lipid weight, respectively), suggesting a
biomagnification potential for HBCDs. Relatively low HBCD
concentrations were reported in the few human studies
conducted to date (median values varied between 0.35 and
1.1 ng/g lipid weight). HBCD levels in biota are increasing
slowly and seem to reflect the local market demand.
One important observation is the shift from the high percentage
of the γ-HBCD stereoisomer in the technical products to
a dominance of the α-HBCD stereoisomer in biological
samples. A combination of factors such as variations in
solubility, partitioning behavior, uptake, and, possibly, selective
metabolism of individual isomers may explain the observed
changes in stereoisomer patterns. Recommendations
for further work include research on how HBCDs are
transferred from products into the environment upon
production, use, and disposal. Time trends need to be
analyzed more in detail, including HBCD stereoisomers,
and more data on terrestrial organisms are needed, especially
for humans. Whenever possible, HBCDs should be
analyzed as individual stereoisomers in order to address
their fate and effects.
In this paper, we review those data which have recently become available for brominated flame retardants (particularly the brominated diphenyl ethers (BDEs) and hexabromocyclododecane (HBCD)) in samples from the European environment. Environmental compartments studied comprise the atmosphere, sediments and soils, sewage sludges, and a variety of biological samples and food chains. This is currently a very active research area, and we cite over 70 studies reported in the literature during 2003-04. Findings include that the input of BDEs (especially BDE209) to the Baltic Sea by atmospheric deposition now exceeds that of PCBs by a factor of almost 40 times. Sewage sludge samples from both industrial and background locations show concentrations of BDEs, HBCD and tetrabromobisphenol-A (TBBP-A) that are of a similar order, indicating that the major source is from diffuse leaching from products into wastewater streams from users, households and industries generally. Point-sources from industries using BFRs (e.g. the textile industry) also generate local hot-spots. Sediment core studies identified the presence of two of the three PBDE formulations. The penta-mix formulation was clearly present from the beginning of the 1970s, but the deca-mix only appeared in the late 1970s. BDE183, BDE209 and HBCD were detected in peregrine falcons from Sweden and other birds feeding on terrestrial food chains. BDEs are found widely distributed in fish, including those from high mountain lakes in Europe, as a consequence of long-range atmospheric transport and deposition. A temporal trend study in archived freeze-dried mussels from the Seine estuary, France, indicated an exponential increase in BDE concentrations during the period 1982-1993, which levelled off in 1999 and 2001 and then began to decline after 2002. HBCD was detected in liver and blubber samples from harbour seals and harbour porpoises from the Wadden and North Seas, though very few animals yielded positive values for TBBP-A. There are difficulties in comparing data on summation operatorBDE from studies in which different suites of BDE congeners have been determined, and we suggest a common suite which will allow the study of all three commercial PBDE formulations.
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