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Epidemiological principles for EMF and EMR studies - Lincoln ...

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50<br />

Conclusions <strong>and</strong> Recommendations:<br />

The fundamental <strong>and</strong> classical epidemiological approach recommended by Sir<br />

Austin Brad<strong>for</strong>d Hill, along with appropriate consideration of a more accurate<br />

exposure assessment approach would result in very different decision outcomes.<br />

Appropriate integration of all of the laboratory evidence that electromagnetic fields<br />

<strong>and</strong> radiation are genotoxic would make scientific sense of a very large body of<br />

epidemiological <strong>studies</strong> showing elevated cancer rates, not only in occupational<br />

exposures but also in residential exposure situations. This strongly challenges <strong>and</strong><br />

rejects the modern interpretation that the only effects are shocks <strong>and</strong> tissue<br />

heating. Accepting that epidemiological evidence is the strongest evidence of<br />

human health effects, points to the same conclusions. The failure to recognize<br />

ubiquitous exposure effect has grossly underestimated <strong>and</strong> masked the true<br />

epidemiological results. An underst<strong>and</strong>ing of the radial radio-frequency <strong>and</strong><br />

microwave exposures around radio/TV towers <strong>and</strong> cell site’s allows dose-response<br />

relationships to be found, <strong>and</strong> all point to a no safe threshold level, consistent with<br />

the genotoxic nature of the <strong>EMF</strong>/<strong>EMR</strong> signals. Underst<strong>and</strong>ing <strong>and</strong> appreciating that<br />

extremely low residential exposure levels to a genotoxic substance causes<br />

elevated cancer rates, along with many other health effects caused by mutations<br />

<strong>and</strong> enhanced cell death rates that has the effect of accelerated aging.<br />

When setting public health st<strong>and</strong>ards <strong>for</strong> air pollution health effects, <strong>for</strong> example,<br />

very fine particles which are recognized by the WHO to have dose-responses with<br />

a safe level of zero exposure, then a st<strong>and</strong>ard authority can choose to set a<br />

st<strong>and</strong>ard such as 50µg/m 3 as a mean daily concentration of PM10, Figure 38.<br />

Figure 38: Increase in daily mortality as a function of PM concentration. WHO<br />

(1999).<br />

The environmental per<strong>for</strong>mance indications of the desired levels can be decided by<br />

national or regional st<strong>and</strong>ards authorities. The New Zeal<strong>and</strong> Ministry <strong>for</strong> the<br />

Environment promotes an approach set out in Table 10. Where exposure levels are<br />

regularly above a practically achievable guideline or st<strong>and</strong>ard, <strong>for</strong> the agents whose<br />

safe level is actually zero, then a management plan should be developed to reduce

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