Radiation Doses To The Male Gonadal Area In Dental
Radiography
Tarnjit Saini, BDS, MS, Dip ABOMR,* V. Manoharan, BE,** I.A.N. Al-Agil***
*Creighton University, 2500 California Plaza, Omaha, Nebraska 68178, USA
**King Khalid University Hospital, P.O.Box 7805, Riyadh 11472, Saudi Arabia
***College of Science, KingSaud University, P.O.Box 2455, Riyadh 11451, Saudi Arabia
The radiation
dose to the male gonadal area was measured during routine intra-oral and
panoramic radiography. It was found to
be 0.8 millirad and 0.3 millirad, respectively.
The estimated dose can be compared to one to three days of gonadal dose
a person would receive from the background radiation. It entails a theoretical
risk of very low magnitude.
Ionizing radiation may interact with essential molecules
such as the deoxyribonucleic acid (DNA) to produce changes in the sequence of
the nucleotide bases. The X-ray photons do not have an affinity for the DNA
molecule. It is a matter of chance that the radiation may directly or
indirectly alter the molecular configuration through the medium of free
radicals. This may manifest as a sequential change in the bases of DNA
resulting in mutation. The net result on the affected cell may vary from cell
death to uncontrolled proliferation.1 If the cell happens to be a sperm or ovum, the
altered DNA or chromosome
might lead to a genetic disorder in the offspring. Radiation induced
genetic mutations are thought to be recessive in nature.2 A diploid pair of altered chromosomes is
essential for the manifestation of the disease.
The role of radiation as a mutagen in humans is not
established. Observations of Japanese atomic bomb survivors have shown no
radiation induced genetic effects in the ensuing three generations. It has been
thought that the observation time was not long enough for the recessive
mutations to manifest. Future observations of successive generations of bomb
survivors might establish a cause and effect relationship of radiation as a
mutagenic agent in humans.3
However, the data derived from animal experiments, such as
fruit flies and mice4 indicates a linear
relationship between the radiation exposure and the induced genetic disorders.
It is postulated that the effect is of a non-threshold type. In other words,
any amount of radiation can produce mutational changes in the germ cells. It
was assumed from the data that the magnitude of the induced genetic mutations
would be of the order of 10-7 mutation/rad/gene.5
The animal experiments further proved that radiation
induced genetic mutations were similarto the naturally occuring spontaneous
mutations. With the present scientific tools available, radiation-induced
mutations cannot be distinguished from spontaneous genetic mutations. It was
estimated by extrapolating the animal data to humans that a gonadal exposure of
50 to 250 rads to a population would double the incidence of spontaneous
genetic mutation in that population.6 It is assumed that the radiation exposure of any
magnitude to the gene pool of a human population poses a risk. Even though the
assumed risk is extrapolated from the animal experiments and has not been
proved in humans, prudence demands that in the absence of definite proof, the
assumed risk to a population should be kept to a minimum by judicious use of
ionizing radiation for diagnostic purposes. Indiscriminate exposure to X-rays
will likely result in the appearance of a higher proportion of mutation-related
recessive genes in a given populations.
During intra-oral or panoramic radiography, the gonads are
not in the line of exposure. The dose to the genetic cells results from
scattered radiation in dental radiography. Radiation doses to the gonadal
areas, as estimated by various investigators,7-16 may vary as shown in Table 1. The
variations in the results were due to the utilization of different beam
characteristics such as image geometry. The gonadal exposure from dental
radiography is about 1/10,000th of the total beam exposure (3-6R).17
The present study was conducted to estimate the dose
delivered to the male gonadal areas during intra oral and panoramic radiography
performed in King Saud University's
College of Dentistry
in Riyadh. The
estimated doses are compared to the values previously reported in the
literature and its implications are discussed. The radiation effects on the
growing fetus would be reviewed and recommendation for female patients and
operators would be outlined.
In this study, intra-oral
radiographic examination was conducted using Siemens Heliodent* seventy (70)
dental X-ray units. The X-ray beam characteristics utilized for exposure were
70 kV and 7 mA. The X-ray units had total filtration of 2 mm. thick aluminum
equivalent. The distance between the focal spot and the face of the positioning
cone was 8 inches. The examination included twenty (20) exposures which were
taken with the paralleling technique using Kodak ultraspeed ‘D' films.
The radiation dose to the male gonadal area was measured
by Harshaw 2271 L** Automated Personnel monitoring TLD system [Fig. 1). It has
the capability of evaluating TLD cards containing four dosimeters [Fig. 2]. The
thermo iuminiscent dosimeters (TLD) are Li F crystals (1/8 X 1/8" x
0.035") which are used to measure radiation exposures ranging from 1 mR to
3 x 10R.5
The following set-up was used for exposing the TLD's
during normal diagnostic intra-oral radiography. The patient was asked to place
the card carrying four (4) TLD's in the groin area. It was secured with a
masking tape. A lead apron was used to cover the patient abdominal and thoracic
areas. The second card carrying the four TLD's was placed on top of the lead
apron in the groin area.7
Each reading involved eight TLD's which were consecutively
exposed on ten different adult male patients. The repeated exposures of the
TLD's (ten times) were done to enhance the detection of accumulated dose. The
average dose from the ten exposures to the four TLD's in each card was taken to
estimate the male gonadal dose. This set-up was repeated four times using in
total 32 TLD's or 8 cards. The experimental exposures were made on 40 male
patients who reported to the Radiology Clinic for complete mouth examination
(20 films). The radiation dose to the TLD's was measured by Harshaw TLD counter
and reported in Table 2.
The panoramic exposures were made by Siemens OP 10 unit.
The examination was conducted in the standing position without utilizing a lead
apron. The card carrying the TLD's were placed in the male groin area by the
patient. The second card was placed on the back of the patient at the level of
the groins. Both cards were exposed ten (10) times by placing on ten (10)
different patients. This set up was repeated three (3) times involving six (6)
cards carrying 24 TLD's exposed in 30 panoramic examinations.
The study was conducted over a period of three weeks. Four
dosimeters were kept as controls in a non-radiological area. The accumulated
dose on the control dosimeters was designated as background radiation. The
reported gonadal doses were corrected for the background radiation exposure.
In this study, a radiation dose of 0.88 mrad was measured
in the male gonadal area during 20 films intra-oral radiography in clinical
situations, Table 2. The dose to the gonads would be 1.55 mrad in the absence
of lead apron for shielding the gonadal area during the examination. The study
demonstrates a 50% reduction in dose to the gonads by the use of a lead apron.
The radiation dose to the gonads from panoramic
radiography was measured as 0.35 mrad, Table 2. The dose at the back of the
patient at the level of gonads was o.51 mrad. The higher value is due to the
direction of the X ray beam which revolves around the back of the patient's
head during the exposure. The radiation will be attenuated by the soft and hard
tissues intervening between the gonads and back of the patient.
The study demonstrated that the radiation dose to the
gonads is approximately one-third during panoramic radiography, as compared ot
that from intra oral radiography. The measured doses depend upon the type of
the X-ray unit utilized, beam characteristics, image receptors, and the
acceptability of the quality of image by the clinician.
The radiation dose to the gonadal area during dental
radiography is negligible. The doses were estimated at the skin level in this
study. The actual dose to the female genetic organs is estimated to be 50% less
than the dose to the male gonadal area because of the different anatomical
location.18
The registered dose of 0.8 mrad for 20 films intra oral
radiography (under the lead apron) and .51 mrad (back of the patient) during
panoramic radiography respectively, can be better comprehended in terms of
background radiation equivalency. The earth is bathed in ionizing radiation
originating from solar, cosmic and terrestrial sources. This type of radiation
follows a heterogenous distribution in different areas of the earth. The levels
are usually low at the equator as compared to the polar areas.19 In a prelimianry study, the authors estimated
the annual background radiation level to be 82 mrad in Riyadh, which is about 0.2 mrad per day. A
gonadal dose of 0.8 mrad during intra oral radiography is equivalent to four
days of background radiation exposure. A gonadal dose of 0.4 mrad during
panoramic radiography is equal to two days of background radiation exposure in Saudi Arabia.
The assumed genetic risk from dental radiography is
negligible and theoretical. It is masked by the overall perceptible deleterious
effects of the background radiation. The studies conducted in areas where the
background radiation levels often reached 1000 mrad per annum, had not shown
any increase in genetic disorders.19 The use
of gonadal shields such as lead apron reduces the dose to the gonads by 50
percent.20
In this study, a gonadal dose of 0.8 mrad was measured
during intra oral radiography. It is approximately four times the doses listed
in Table 1 for the same procedure. The discrepancy can be explained on the
basis of the use of short cone and utilization of higher energetic beam in this
tudy. The fluoroscopic survey of lead aprons did not disclose any leakage
areas. In panoramic radiography, the shield has to be put on the back of the
patient owing to the direction of the central ray. The routine use of gonadal
shield during dental radiography alleviates the patient's fear about the
possible radiation damage. Its compulsory use is of dubious value because of
almost negligible scatter to the gonadal area. Secondly, it does not prevent
the exposure to the gonads from internal scatter in the patient's body which is
also very negligible.
Scatter radiation during dental radiography may result in
exposure of the dental personnel in the area. A dentist or dental auxiliary may
accumulate perceptible amounts of radiation doses from his repeated exposure to
scatter radiation. In a study, the authors estimated the occupational radiation
exposure in the radiological facilities in this institution to be about 30 mrad
per annum, equivalent to fifteen days of background radiation.21 The international agencies recommend that a
radiation worker who cumulates a gonadal dose of 0.5 rad of ionizing radiation
in one year may not suffer from any demonstrable somatic or genetic effect
according to the present day knowledge.1 Because of a very limited number of radiation
workers in a given population, the gonadal exposure 0.5 rad to the few
individual workers will not affect the gene pool in that population. In
reality, in any radiological facility where there is emphasis on radiation
hygiene, the dental workers do not get any detectable exposure.
The exposure of pregnant patients to high dose levels may
result in spontaneous abortion, congenital abnormalities, microcephaly and
decreased mental efficiency. Controversies exist about the radiation
sensitivity of a growing fetus to leukemia induction.1 The dose to the fetus during dental
radiography ranges from 0.2 to 0.4 mrad {half of gonad dose), which is
equivalent to one or two days of background radiation. Therefore, pregnancy is
not a contraindication for dental radiography. However, radiographic
examination should be reduced greatly because the patient may
also have non-dental exposures. The radiographic examination should not be a
routine procedure in clinical practice. The examination should be based on
sound clinical judgement. The diagnostic yield from the resultant exposure
should outweigh possible risks. Over exposure of the population has the
potential danger of affecting the gene pool in a deleterious manner. The risks
of genetic mutation or fetal irradiation from dental radiography seems to be
generally exaggerated.
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