effect of man-made structures on ambient radiation fields,

indoors.

existed between indoor and outdoor radiation-levels.

Several rooms in each dwelling were surveyed, including
the living-room and at least one bedroom. Again, a strong
uniformity exhibited itself in that the mean indoorlevels
were close to 70 per cent of the corresponding outdoor
levels in each area‘. This may be related to the fact that
the vast majority of the dwellings were of wood-frame
construction, with the building materials appearing to act
generally as y-ray shields with relatively little activity of
their own.
With such data at hand, an estimate of mean population
exposure to environmental radiation can be obtained by
calculating a suitably weighted average of the indoor and
outdoor readings of the survey instruments. Taking into
consideration the greater occupancy time indoors of the
average individual, the mean exposure levels have been
estimated to be 80 per cent of the mean outdoorterrestrial
y-dose rates given in Table 1, plus the contribution from
the ionizing components of the cosmic radiation at the
ground altitudes of the various areas. No correction of
the cosmic-ray figures for typical structural shielding has
been made, since this would be a reduction of the order

Natural

1962+
Cosmic

Outdoor
Total y*

Dunham Dolomite
Beldens Formation
Glacial Drift
Monkton Formation
Fitchburg Granite
Littleton Formation
Binary Granite
Conway Granite

* Includesfall-out, averaged over all locations within an area,
+ Obtained as indicated in the text; in units of air doserate,

Outdoor
Natural y

of 10 per cent or less, which is comparable to the present

6U (p.p.m.)

Geological category

MEAN WEEKLY DOSES IN ME./WEEK
Table 2.

Portabie scintillation detector readings were

made in 160 private homes and apartments in the main
towns to ascertain whether any consistent relationship

|

Mean population exposure

Dosimeters

since most individuals spend a large fraction of their time

uncertainty in the absolute cosmic-ray ionization intensity.
Table 2 shows the population exposure data arranged
by geological region. The mean weekly outdoor doses in
air are given for both natural and total (natural plus fallout) y-radiation and for cosmic rays, and the Health and
Safety Laboratory population exposure estimates for the
time of the survey (August 1962, including fall-out) and
for the natural emitters only (that is, the mean:life-time
levels neglecting fall-out) are also given. The importance
of the spectrometric technique is emphasized by the fact
that estimates of the integrated natural y-dose were obtainable even under conditions of near-maximum fall-out
contamination. In many population investigations, it is
just this quantity that is desired.
The Harvard investigation involved the use of a set of
200 Victoreen model 362 condenser ionization-chamber
pencils, along with a stable pulse height readout system!51?
which is designed to allow readings of 1-0 + 0:2 mr. at
the 95 per cent confidence level with a single pencil.
Mechanical and thermal stability was tested, and correc-

tions made for average leakage rates observed in the
laboratory.

These dosimeters were distributed in pairs to five

individuals in standard occupational categories in each of
16 areal units, half urban and half rural. The dosimeters
5

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