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It is clear that
many factors can affect an individual's exposure to RFR associated with
cellular telephone use. This makes exposure assessment in a risk study
very difficult to interpret. Ideally the exact exposure dose should
be measured, but no specific measure is available. In experimental situations
the Specific Absorption Rate (SAR) is used. This is the amount of energy
that is deposited in tissue, and is measured in W/kg. SAR has been developed
for quantification of thermal effects of RFR. It is assumed that it
may serve as an adequate measure of other effects, although no biological
mechanism has been established by which possible health effects could
be induced (Auvinen et al., 2006). In epidemiological studies, similar
SAR levels have been assumed for all telephone models, although results
are occasionally presented separately for users of analogue and digital
phones. Since SAR measures are not available, the validity of a proxy
exposure measure is critical. Cumulative exposure is usually used as
a measure of exposure dose, but this does not take into account variations
in the signal for the reasons discussed above. In long-term studies,
estimation of a dose-response relationship is important for assessment
of causality. Exposure assessment in studies of cellular telephones is most often done by self-report. Parslow (2003) reported that users of mobile phones tended to under-report their use. Unfortunately, there was a very low participation rate in this study, which casts doubt on the validity of the findings. Studies by Cooper (2004) and by Ardoino (2004) described the development of specially adapted cell phones that were able to measure various aspects of long-term use. Technology such as this may help to overcome the difficulties of determining RF exposure from cell phones. Morrisey (2006) used software-modified phones (SMPs) that record talk time and dynamically changing transmit power levels. He enlisted the help of Motorola employees in different sites around the world. These volunteers used the SMPs for 2 weeks, and the data was later analyzed. Each volunteer was sent a questionnaire within 2 weeks that included questions on their phone use. He found considerable variability in transmit power within a single call, in separate calls, between individuals in the same study region, and between averaged values from different study groups. Morrisey also found that there was significant inaccuracy (45-60%) in recalling "time of use". Erdreich (2007) also used SMPs to study factors affecting the energy output of GSM phones during operation, and found that the largest factor was study area, followed by user movement and location (inside or outside), use of a hands-free device, and urbanicity. Blas (2007) showed that personal exposure meters are subject to errors associated with perturbations of the electric fields by the presence of the human body. Mild (2005) proposed
a method that would enable combining the use of different mobile (e.g.
analogue and digital) and cordless phones by weighting factors. This
would take account of the fact that analogue phones operate with a maximum
power greater than digital phones, which in turn operate at a greater
power than cordless ones. Auvinen et al. (2006) suggest that an appropriate
measure of exposure would be a weighted average of the cumulative time
of cellular telephone use with weighting by power, stratified by side
and excluding hands-free use. They further suggest that power can be
estimated from the hours of use by adjusting for characteristics of
the telephone and network.SC Kim (2006) proposed a new method to estimate
quantitative and relative RF exposure levels using a neural network
model. The parameters that were used to develop this model were average
usage time per day, total period of usage in years, SAR of the specific
phone, hands-free usage, antenna extraction, and the type of phone (flip
or folder). Bürgi and colleagues (2007), recognizing that personal
measurements to assess long-term exposure are expensive, developed a
geospatial model that allowed the estimation of ambient HF-EMF strengths
with spatial resolution. They included cell phone base stations and
broadcast transmitters in their model, which considers the location
and transmission patterns of the transmitters, the three-dimensional
topography, and shielding effects of buildings. In an evaluation of
their method in the region of Basel in Switzerland, they found good
correlation between modeling and measurements. The Interphone study group carried out a validation study of short-term recall of phone use (Vrijheid 2006). There were moderate to high correlations between recalled and actual use, as measured by operators or through the use of software modified phones. The authors found that there was moderate systematic error and substantial random error. The latter error would tend to reduce the power of the Interphone study to detect an increase in brain tumour risk, if one exists. Auvinen and colleagues
reviewed the factors that can affect the validity of epidemiological
studies on health effects of cell phones. They emphasize the imprecision
of exposure assessment in the studies. They also point out that this
is particularly likely to occur in case-control studies, and that prospective
studies afford the best opportunity to improve the quality of evidence.
A group of German researchers published two papers (Samkange-Zeeb et
al; Berg et al.), in which they assessed the validity of self-reported
use, from a questionnaire used in the Interphone study. They found good
correlation between self-reported use and information provided by network
providers in terms of the number of calls per day. The correlation was
moderate with regard to cumulative use. Schuz (who is an author in the
Berg paper)and Johansen (2007) also compared self-reported cell phone
use with subscriber data. This information had been obtained in separate
studies. They found "fair" agreement between the two sources
of exposure assessment. They contend that both measures have limitations
and may lead to a potential underestimation of an association. Like
Auvinen et al., they are of the opinion that these limitations can be
minimized in prospective follow-up studies, where exposure estimation
would be based on records of subscriber use. SC Kim (2006) proposed
a new method to estimate quantitative and relative RF exposure levels
using a neural network model. The parameters that were used to develop
this model were average usage time per day, total period of usage in
years, SAR of the specific phone, hands-free usage, antenna extraction,
and the type of phone (flip or folder). The above is concerned mainly with cell phone studies. In other radiofrequency radiation studies exposure is usually based either on geographic location (in the case of studies of radio and TV transmitters), or on job title (in occupational studies). Clearly, these methods of exposure assessment are imprecise. Some use death certificates as the source of information on occupation, something that has been shown to be quite inaccurate (Andrews KA, et al., Bioelectromagnetics 1999;20:512-518). References: Ahlbom A, Green A, Kheifets L, Savitz D, Swerdlow A (2004): Epidemiology of health effects of radiofrequency exposure. Environ Health Perspect 112:1741-1754. Alanko T, Hietanen M. A practical method to evaluate radiofrequency exposure of mast workers. Radiat Prot Dosimetry Dec 2 2008 Ahead of print. Alanko T, Hietanen M. A practical method to evaluate radiofrequency exposure of mast workers. Radiat Prot Dosimetry Dec 2 2008 Ahead of print. Andrews KA, Savitz DA (1999): Accuracy of industry and occupation on death certificates of electric utility workers: Implications for epidemiologic studies of magnetic fields and cancer. Bioelectromagnetics 20:512-518. Ardoino L, Barbieri E, Vecchia P (2004): Determinants of exposure to electromagnetic fields from mobile phones. Radiat Prot Dosim 111:403-406. Auvinen A, Toivo T, Tokola K (2006): Epidemiological risk assessment of mobile phones and cancer: where can we improve? European Journal of Cancer Prevention 15:516-523. Bahillo A, Blas J, Fernandez P, Mazuelas S, Vinuela A, Lorenzo RM, Abril EJ. (2008). E-field errors associated with RF dosimeters for RF human exposure assessment in urban environments. Conf Proc IEEE Eng Med Biol Soc. 2821-2824. Bahillo A, Blas J, Fernandez P, Mazuelas S, Vinuela A, Lorenzo RM, Abril EJ. (2008). E-field errors associated with RF dosimeters for RF human exposure assessment in urban environments. Conf Proc IEEE Eng Med Biol Soc. 2821-2824. Belyaev IY, Grigoriev YG. (2007): Problems in assessment of risks from exposures to microwaves of mobile communication. Radiats Biol Radioecol 47(6):727-32. Berg G, Schuz J, Samkange-Zeeb F, Blettner M (2005): Assessment of radiofrequency exposure from cellular telephone daily use in an epidemiological study: German validation study of the international case-control study of cancers of the brain-INTERPHONE-Study. J Expo Anal Environ Epidemiol 15:217-224. Blas J, Lago FA, Fernandez P, Lorenzo RM, et al. (2007): Potential
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