ILLINOIS POLLUTION CONTROL BOARD
August 8,
1991
VILLAGE OF BENSENVILLE,
)
)
Petitioner,
PCB 91—66
v.
)
(Variance)
)
ILLINOIS ENVIRONMENTAL
)
PROTECTION AGENCY,
)
)
Respondent.
CONCURRING OPINION
(by J.D. Dumelle):
The Bensenville petition in Paragraph 33 speaks of the need
to do water main looping to eliminate dead ends and to
install
large diameter mains
to obtain increased flows.
(~
Attachment
2).
All of these improvements to a water system can be done now
without a variance from restricted status.
Thus
the
only
hardship
might
be
that
new
development
is
pending.
But that is alleged only in general terms
in Paragraph
32.
No specific developments are mentioned at all.
Benesenville’s radium levels are given as 18.2 pCi/i according
to the IEPA Recommendation (p.4).
The cancer risk at the
5 pCi/i
standard
is l-in—14,300 over a lifetime.
The cancer risk at 18.2
pCi/i
is about 1—in—3,950.
That is an extremely high risk and
about 250 times higher than the usual l—in—1,000,000 risk used to
set limits for chemical exposure.
In late 1991 Benesenville will probably begin to receive Lake
Michigan water.
Full service may occur during 1992.
Thus any new
development
(and
none has been
alleged)
would probably not
be
constructed and inhabited until the low—radium water is
in use.
The Illinois Department of Nuclear safety in its “Background
Document on Radium in Drinking Water” of August 25,
1986 filed in
R85-14 stated on
p.
5,
...Radium
uptake,
i.e.,
fraction
of
radium
absorbed and
transferred to the
bone,
also
appears to vary with age and calcium intake.
Muth
and Globe1
found
an
age dependence
of
radiuin—226 concentration
in human bone that
coincided
with
periods
of
rapid
skeletal
growth.
They
believed
that
during
these
periods of rapid growth
(0-1 yr and 10-16 yr)
it
was
probable
that
radiuiu-226
was
incorporated
into
the
hydroxylapatite
crystals, a component of the bone matrix, with
minimal
discrimination
against
calcium,
125—27
resulting in a higher concentration of radium-
226.
They concluded that the lower intake of
calcium per person per day in Germany explains
their
finding
of higher
transfer
of
radium
from the diet to the skeleton
(“Age Dependent
Concentration of Radium—226 in Human Bone and
Some
Transfer
Factors
from
Diet
to
Human
Tissues”;
Health
Phys.
44,
Suppl.
1,
113—
121).
Parks
and
Keane
suggest
that
younger
people have an increased risk per unit intake
of
radium because of greater bone formation
rates and a higher initial retention of radium
(“Consideration
of
Age-Dependent
Radium
Retention in People on the Basis of the Beagle
Model,”
Health Phys.
44,
Supp.
1,
103—112).
In
addition,
the very
young
have
a
longer
potential
latent
period
(Advisory Report
on
the
Health
Effects
of
Ra-226
in
Drinkinc~
Water,
1978).
Calabrese points out that the
gastrointestinal absorption
of pollutants by
young children
is
significantly higher than
absorption by adults.
A marked sensitivity of
children
to
the
toxic
effects
of
ionizing
radiation has been reported
(Pollutants
and
High—Risk
Groups:
The Biological
Basis
of
Increased
Human
Susceptibility
to
Environmental
and
Occupational
Pollutants,
1978).
It thus appears that children up through age
16 are most at
risk from radium in drinking water.
A
~ewoi~
be to
have them use low-radium wal
J cob D. Dumelle,
P.E.
oard Member
I, Dorothy N.
Gunn,
Cl rk of the Illinois Pollution Control
Board,
hereby
certify jhat
the abov~~
Concurring
Opinion
was
submitted on the
/(~‘
‘-
day of
~6”~-
~‘
c
/
,
1991.
Ddrothy M.
Gu1)z~~’Clerk
Illinois Pol1~ftionControl Board
125—28