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6
Environmental Ejects on Age-Associated
Diseases and Changes in Organ Function
Biologic changes associated with aging can reasonably be ex-
pected to be associated with parallel changes in susceptibility to
disease. For some diseases, such as those for which early anti-
genic stimulation produces lifelong immunity, resistance usually
increases and incidence falls with age. For other diseases, such
as those reflecting cumulative, chronic exposures, rates might in-
crease with age.
Susceptibility to disease changes throughout the human life
cycle and is believed to be a function of many factors, including
changes in the immune system and in the rate of cellular divi-
sion. Thus, exposures to carcinogens or neurotoxins in infancy
and childhood (or in old age) might produce stronger responses
than those occurring in the middle stages of life. Although there
are reasonable theoretical grounds for expecting some disease pat-
terns to be normal functions of age, additional research needs to
be done to clarify possible mechanisms. Controlled studies of an-
imal populations are also needed to determine both the natural
occurrence of diseases with aging and changes in immune response
and in metabolic and kinetic responses to xenobiotics throughout
the life cycle.
This chapter reviews some of the animal and human stud-
ies on the relationships of the environment with age-associated
109
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110
AGING IN TODAY'S ENVIRONMENT
TABLE 6-1 Examples of Age-Associated Changes in Organ Structure and
Function and Possible Related Agents, Medical Conditions, or Life-style$
Organ or System
Agent, Medical Condition, or
Changes in Organ Structure
and Function Often Associated
with Old Age
Skin
Eye
Ear
Nervous system
Coarseness, wrinkling,
malignant neoplasms,
immune suppression
Cataracts
Cataracts,
retinopathy
High-frequency
hearing loss
Dementia, confusion
Peripheral neuropathy
Parkinsonism
Amyotrophic lateral
sclerosis, parkinsonism,
senile dementia of
Alzheimer's type
Renal Increased nephropathy
Immune Reduced decline in immune
Lung
Cardiovascular
Life-style Possibly
Related to Changes in
Organ Structure or
Function
Sunlight
Sunlight
Diabetes
Noise
Anticholinergics,
barbiturates, bromide
Acrylamide, vincristine,
. · · .
~son~az~a
MPTP
Chamorro life-style
(cycad exposure?)
competence
Exacerbation of autoimmune
reactions
Emphysema, cancer
Atherosclerotic
heart disease
Reduced dietary protein
Reduced caloric intake
Procainamide, estrogen
Cotton dust,
tobacco smoking
Dietary lipids
diseases in specific organ systems. It also discusses evidence of
age-associated changes in normal functions, such as vision, bone
metabolism, and the immune system. Table ~1 presents some
examples.
DEMOGRAPHICS OF AGE-ASSOCIATED DISEASES
Age seems to be the most important determinant of incidence
of most human diseases. Characteristic age patterns of risk have
been described for all diseases, and many of the patterns have
provided the basis for important etiologic theories. For example,
the peak in incidence of one type of Hodgkin's disease in the third
decade of life suggested an infectious origin (MacMahon, 1971),
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ENVIRONMENTAL EFFECTS ON DISEASES AND ORGAN FUNCTION 111
350
z
o
F
A 300
o
CL 250
a:
~ 200
LL
o
o
O 150
-
`~ 1 00
LU
of
cat
A
/'
~ /
l
/ /V
.
·
10 20 30 40 50 60 70
AGE GROUP (Years)
1
/
San Francisco
Bay Area
White
(t 969-1 973)
San Francisco
Bay Area
Black
(1 969-1 973)
Yugoslavla
~e°O.O slovenly
(1968-1972)
Japan
Osaka
(t 970-1 971)
FIGURE 6-1 Age-specific incidence rates for female breast cancer in four
population groups. Source: Petrakis et al. (1982~.
and the plateau in incidence of breast cancer around the ages
of 45-55 suggested an effect of the cessation of ovarian function
on the development of the disease (Petrakis et al., 1982~. The
premenopausa] and postmenopausal incidence curves for breast
cancer in different countries suggest that environmental factors
play more important roles in the etiology of postmenopausal breast
cancer, whereas genetic, endocrinologic, and other endogenous
factors strongly influence premenopausal disease (Figure 6-1~.
The role of age as a factor associated with increasing incidence
appears to be direct (or independent) in some diseases. In others,
time and age-associated exposure characteristics, such as obesity
and duration of exposure, are the direct factors, and not age
itself. The association of disease susceptibility with age—which
might be related to intrinsic factors, extrinsic factors, or some
combination needs to be assessed for each disease. For example,
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112
AGING IN TODAY'S ENVIRONMENT
the role of specific intrinsic and extrinsic factors in adult-onset
diabetes meDitus has been extensively investigated, but further
studies are needed for an adequate understanding of the relative
importance and interaction of endogenous and exogenous factors
in the disease.
Both morbidity and mortality data can be used to evaluate
the association of disease with age in the elderly population (65
and over). Morbidity data reflect either the incidence (new cases)
of a disease over a fixed period or its prevalence (total cases) at
a given time, depending on the study design or the method of
data collection. These two measures of disease frequency (inci-
dence and prevalence) provide different information, and both are
important—one for an understanding of the population risk (in-
cidence) and one for an understanding of the burden (prevalence)
of a particular disease. Mortality data, which are more readily
available than morbidity data for the total population, parallel
incidence data for conditions that are life-threatening and of short
duration, such as some forms of cancer and cardiovascular dis-
ease, but are not as useful for other diseases, such as diabetes and
chronic obstructive pulmonary disease.
Two-thirds of all deaths in the United States occur in people
over age 65, and 30~o occur in persons over 80. Three causes of
death heart disease, cancer, and stroke accounted for 75% of
these deaths in the elderly population in 1979 and in 1950 (NCHS,
1981b). Turo features of the recent cause-specific mortality pat-
terns in the elderly are of interest here the decline in mortality
rates for cardiovascular and cerebrovascular diseases among the
elderly and the maintenance of those rates for cancer (Figure ~2~.
From 1950 to 1979, the overall mortality rate for the population 65
and over decreased by Who. When rates are age-adjusted (to allow
for the rapic! increase in the population 85 and over), mortality
declined more than 27% and the decline for females was twice that
for mates (Figure ~3~.
Mortality from heart disease accounted for approximately half
the overall decline during the period, and that from cerebrovas-
cular disease accounted for another 25% of the overall decline.
Heart and cerebrovascular diseases account for the largest and
third largest mortality rates, respectively, in this age group. Can-
cer mortality, the second largest element and the only major one
to show an increase, increased by Who. More than half the deaths
from cancer among the elderly are due to cancers of the lung,
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ENVIRONMENTAL EFFECTS ON DISEASES AND ORGAN FUNCTION 113
3,000
2,000
at
o
-
J
~ 1,000
o
CL
lo
o
o 500
o
Or
`r 300
co
200
LU
100
- Heart Disease
—— Cancer
Stroke
Influenza and pneumonia
Diabetes mellltus
_~
-
_.
195;0 1955 1960 1965
YEAR
-
1970 1975 1980
FIGURE 6-2 Age-adjusted death rates for persons 65 years of age and over,
according to leading causes of death: United States, 1950-1979. Source:
National Center for Health Statistics (1982~.
colon, genital organs, and breast (females). Cancer mortality
trends among males indicate a slight deceleration in the large an-
nual increases in lung cancer mortality and slowly increasing rates
for cancers of the colon and prostate. In contrast with the increase
in overall cancer mortality in males, the overall cancer mortality
rate in women 65 and over decreased slightly from 1950 to 1978
(Figures ~4 and ~5~. The most obvious changes for females are
the large increase in Jung cancer mortality and the decreases in
mortality from cancers of the stomach and uterine cervix.
An exponential increase in mortality with age is evident for
cardiovascular disease (Figure ~6), but absent for all cancers com-
bined (Figure 6-7~. In fact, cancer mortality rates (all sites com-
bined) increase rapidly in middle age and then more slowly with
age to 65. Between ages 65 and 69, cancer accounts for approxi-
mately 30~o of all deaths; by age 80, it accounts for only Who. In
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114
BOOM
90.0
he
o
g 70.0
o
cat
lo
to
to
0 50.0
80.0
60.0
cr:
cat
I 40-D
LL
C]
AGING IN TODAY'S ENVIRONMENT
\/\
_
30.0 1 1 1 1 1 ! I I
1 940
in.
_`
Dyne
~ Female
-
1945 1950 1955 1960
YEAR
1965 1970 1975 1980
FIGURE 6-3 Age-adjusted death rates for persons 65 years of age and over,
according to sex: United States, 1940-1978. Source: National Center for
Health Statistics (1981b).
contrast, the proportion of deaths caused by cardiovascular disease
increases from 50% at ages 65-69 to 65~o by age 80. Brody (1983,
1987) has suggested that the modest increase in age-specific mor-
tality rates for cancer after age 65 might constitute evidence that
cancer pathogenesis is not closely related to the aging processes
and host susceptibility, and that by the year 2000 cancer will ac-
count for fewer than 10% of the deaths in those 85 and over the
age group that will experience half of all deaths.
Before epidemiologic observations associating cancer mortal-
ity with aging processes can be fully evaluated, several considera-
tions are essential. Smoking is the most likely cause of the increase
in respiratory cancer mortality, and cancer mortality in general,
among elderly men and women. Although a higher proportion of
elderly men than women smoke, the sex gap in smoking behavior
has narrowed considerably in recent years. The proportion of men
65 and over reported as current smokers dropped from 28.5~o in
1965 to 17.9~o in 1980; the proportion of women increased from
9.6~o to 16.8~o. The sex differences for former smokers, which
could be more important for respiratory cancer, are even greater:
OCR for page 115
ENVIRONMENTAL EFFECTS ON DISEASES AND ORGAN FUNCTION 115
80
70
60
At
o
-
g 50
o
~ 40
lo
lo
o
lo
o
try 30
LL
LL
a:
CI:
20
10
~ _
l
.
~ . `. ~
O -- 1 1 1 1
1930
Esophagus
Bladder
Pancreas
Leukemia
Liver
Prostate
Lung
Stomach
Colon & Rectum
· .
.
/
i/
!
/
/
.
· .
.
· -A
~ 1~.
.,, -. ~ 4_.
.,
/
.
.
1940 1950 1960 1970 1980
YEAR
FIGURE 6-4 Age-adjusted cancer death rates for selected sites, males:
United States, 1930-1978. Source: U.S. OTA (1985~.
the proportion of men 65 and over reported as former smokers in-
creased from 28.1% in 1965 to 47.4% in 1980, and the proportion
of women increased from 4.5% to 14.2~o.
Differences in smoking among and between elderly men and
women no doubt account for some of the observed differences
OCR for page 116
6
80
70
60
50
40
CC 30
LL
llJ
20
10
AGING IN TODAY'S ENVIRONMENT
.
-
uterus
Breast
Pancreas
Leukemia
Liver
Ovary
Lung
Stomach
Colon & Rectum
~ . _ . ~ __ ~~ ~ ~ -~ ' - at · ~ ~ - e ~ - - - -
O—
1930 1940 1950
1960 1970 1980
YEAR
FIGURE 6-5 Age-adjusted cancer death rates for selected sites, females:
United States, 1930-1978. Source: U.S. OTA (1985~.
in cancer mortality, especially respiratory cancer mortality. It is
estimated that cigarette smoking alone accounts for 8~85~o of
lung cancer mortality and 30~o of all cancer mortality (Doll and
Peto, 1981~.
OCR for page 117
ENVIRONMENTAL EFFECTS ON DISEASES AND ORGAN FUNCTION 117
1 6,000
1 4,000
At
o
1 2,000
Cal
o
to
to
to
to
-
a:
LO
Lo
At:
TV:
1 0,000
8,000
6,000
4,000
2,000
o
Cardlovascular Dlseases
- All Cause Mortality
,' ,
///~
~ /
i' /
20- 25- 30- 35- 40- 45- 50- 55- 60- 65- 70- 75- 80- 85+
24 29 34 39 44 49 54 59 64 69 74 79 84
AGE GROUP
FIGURE 6-6 Major cardiovascular diseases: age-specific mortality rates
versus all causes of mortality. Source: National Center for Health Statistics
(1985a).
It has been suggested that the reason for the rising incidence
of cancer with increasing age might be aging of the immune system
itself, but the available epidemiologic evidence does not support
this view except for some tumors. Because increasing age is "so-
ciated with many time-related factors, including longer exposure
to carcinogens, it ~ difficult to separate the effects of increasing
age from the effects of increased exposure to carcinogens.
Two lines of evidence, however, can address the effect of age
itself on cancer incidence. Peto et al. (1975) conducted a large,
controlled study in mice at various ages whose skin was exposed
to benzota~pyrene. The incidence of epithelial cancers was inde-
pendent of age at the start of exposure and was related directly to
duration of exposure. A recent review of the available experimen-
tal evidence from animate (Hornig, in press) found little support
for the notion of a general increase in susceptibility to the effects
of all carcinogens with increasing age. In addition, the presence
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Representative terms from entire chapter:
cancer mortality
118
1 6,000
~ z 14,000
a: °
~ g 12,000
-
ENVIRONMENTAL EFFECTS ON DISEASES AND ORGAN FUNCTION 119
TABLE 6-2 Death Rates for the 10 Leading Causes of Death for Ages 65 and Over,
by Age, 1976
Deaths per 100,000
65 Years 65-74 75-84 85 Years
Cause of Death and Over Years Years and Over
All causes 5,428.9 3,127.6 7,333.6 15,486.9
Heart diseases 2,393.5 1,286.9 3,263.7 7,384.3
Malignant neoplasms 979.0 786.3 1,248.6 1,441.5
Cerebrovascular diseases 694.6 280.1 1,014.0 2,586.8
Influenza and pneumonia 211.1 70.1 289.3 959.2
Arteriosclerosis 122.2 25.8 152.5 714.3
Diabetes mellitus 108.1 70.0 155.8 219.2
Accidents 104.5 62.2 134.5 306.7
Motor vehicle 25.2 21.7 32.3 26.0
All other 79.3 40.4 102.2 280.7
Bronchitis, emphysema,
and asthma 76.8 60.7 101.4 108.5
Cirrhosis of liver 36.5 42.6 29.3 18.0
Nephritis and nephrosis 25.0 15.2 34.1 64.6
All other causes 677.5 427.8 908.6 1,638.8
SOURCE: National Center for Health Statistics (1978a).
very prompt rise in the incidence of Tymphomas in transplant
recipients after treatment with immunosuppressive agents is in
marked contrast with the long induction times observed for
epithelial tumors resulting from exposure to chern~cal carcinogens
(Hoover and Fraumeni, 1973~. Those observations suggest a differ-
ent, possibly viral, etiologic process for the mesenchymal tumors
that are associated with immune factors. The increased incidence
of squamous carcinoma of the skin in patients receiving immuno-
suppressive agents suggests that this epithelial tumor is also under
immunologic control (Kripke, 1974~.
Mortality rates by age group for diseases of the heart, in-
fluenza and pneumonia, cerebrovascular disease, arteriosclerosis,
and accidents show a marked increase in risk with increasing age,
whereas rates for other causes such as cancer, diabetes mellitus,
bronchitis, emphysema and asthma, and nephritis and nephrosis-
indicate a more modest increase (Table 6-2~. Mortality due to cir-
rhosis of the liver does not appear to be associated with increasing
age in the elderly population.
134
AGING IN TODAY'S ENVIRONMENT
and Raskind, 1980~. Levodopa, arnantidine, corticosteroids, and
many drugs with anticholinergic properties are often responsible.
Barbiturates and other sedative hypnotic agents can also cause
paradoxic agitates] delirium in susceptible patients.
Depression can be a complication of drug therapy. Antihyper-
tensive agents such as reserpine, methyldopa, and clonidine-
have been reported to cause depressive symptoms, but a greater
incidence seems to be associated with beta-blockers than with
those centrally acting agents. There is ample anecdotal evidence
of patients with no prior psychiatric illness who experience malaise,
dysphoria, or outright clinical depression when starting treatment
with beta-adrenergic antagonists, and central nervous system side
effects from propranolol range in frequency from loo to over 70~o
(Paykel et al., 1982~. Reported symptoms include depression,
drowsiness, sleep disorders, and hallucinations.
Furthermore, the use of tricyclic antidepressants has been
found to be significantly higher in patients taking beta-blockers
(23~o over 2 years) than in patients taking hydralazine or hy-
poglycemics (both 15~o) or methyldopa or reserpine (both 10%~.
However, the magnitude of this association between bet~blockers
and treatment for depression was found to decline with advanc-
ing age (Avorn, 1986~. Proposed explanations were d~rninution in
receptor sensitivity with age and failure of physicians to apprise
ciate the dysphoria or other central nervous system side ejects
as abnormal in an older patient. The mechanism of the central
effect of beta-blockers could be interference with nonadrenergic
neurotransmitter function in the brain, a pathway that is thought
to play a causal role in some cases of depression.
In general, the signs and symptoms of drug-induced neuro-
logic disorders are practically indistinguishable from those seen
in nondrug-induced disorders, but are usually reversible if diag-
nosed early enough (Lane and Routledge, 1983~. Neurotoxicity
commonly accompanies prolonged therapeutic treatment with an-
ticonvulsants, anticholinergics, neuroleptics, antineopla~tics, and
antiparkinsonism drugs. In addition, a recently recognized iatro-
genic neurotoxicity is the sensory neuropathy syndrome associated
with pyridoxine megavitarnin therapy (Schaumburg et al., 1983),
which has been prescribed for the treatment of premenstrual ten-
sion.
The incidence of subclinical neurologic and behavioral dis-
orders associated with chemical substances is unknown, but is
ENVIRONMENTAL EFFECTS ON DISEASES AND ORGAN FUNCTION 135
believed by some to be large. Examples include the unresolved
controversies about childhood cognitive impairment from envi-
ronmental lead contamination and the neurobehavioral effects at-
tributed to prolonged occupational exposure to a variety of indus-
trial solvents.
RESPIRATORY SYSTEM
Lung growth and development continue into the second decade
of life, and then pulmonary function begins to decline. The de-
cline is most easily measured with tests of forced expiration. Many
prospective epidern~ologic studies indicate that the forced expira-
tory volume in 1 second (FEW ~ decreases continuously with age,
even in healthy nonsmokers. The rate of loss is greater in older
than in younger people (Beaty et al., 1984; Burrows et al., 1986;
Fletcher, 1976; Higgins et al., 1982~. Smokers lose pulmonary
function much faster than nonsmokers, but if they stop smoking,
their rate of decline reverts to the rate observed in nonsmokers
(FIetcher, 1976~.
Although an understanding of the association between aging
and environmental insults to the lungs is lirn~ted, two features
are noteworthy because of pathophysiologic correlations. First,
when the structure and function of small airways are measured,
age and smoking are found to have important ejects. Even in
young, presumably healthy smokers, evidence of inflammatory re-
sponses in peripheral airways is striking (Niewoehner et al., 1974~.
Small-airway dysfunction increases with age and can be observed
in smokers of all ages (Enjeti et al., 1978~. Those observations
have led to the recognition of the importance of peripheral lung
structure and function in the evolution of lung aging or disease
and to the focus for the last 15 years on studies of peripheral lung
function in the evaluation of environmental exposures (Macklem
1972~.
The second important feature of lung function is airway re-
activity. Acute reactions of the airways are typically increased in
asthmatic subjects, but might be increased in normal subjects who
smoke (Gerrard et al., 1980; Mullen et al., 1986), after viral infec-
tions, and after exposure to oxidants, such as ozone (Boushey et al.,
1980~. Airway reactivity can be measured in the laboratory with
controlled administration of bronchoconstricting agents. A num-
ber of studies now point to the potential importance of increased
136
AGING IN TODAY'S ENVIRONMENT
airway reactivity as a risk factor for accelerated loss of function
with age (Barter and Campbell, 1976; Orie, 1960; Volimer, 1985~.
The evidence implicating ambient concentrations of air pollutants
in the decline of lung function with age is controversial (U.S. EPA,
1986~. However, the potential impact of environmental exposures,
either outdoor or indoor, on susceptible people is real.
Not only Is there clear epidemiologic evidence that age and
environmental factors, such as smoking, are associated with lo"
of lung function, equally clear ~ an important correlation between
Jung dysfunction and mortality from all causes (puhnonary and
nonpulmonary). From epidemiologic studies in Tecurnseh (Hig-
gins and Keller, 1970), Eramingham (Ashley et al., 1975), and
Baltimore (Beaty et al., 1982; Menkes et al., 1985), a consistent,
strong relationship between lung function and mortality has been
reported. It cannot be accounted for by smoking habits and re-
flects (to a small extent) deaths from chronic lung disease or lung
cancer (Skilirud, 1986~.
Although the basis of the intriguing association is not known,
two explanations are attractive. First, because the lung is normally
an interface between the body and the environment, increased ex-
posure to environmental toxins or increased susceptibility of the
host leads to disturbances of the lungs, as well as of other systems
of the body. Second, disturbances of function in organ systems
other than the lungs might leac! to abnormalities in otherwise nor-
mal lungs. Both explanations are suggest the importance of lung
function in estimating environmental exposure and in assessing
individual susceptibility to nonpulmonary, as well as pulmonary,
aging and disease.
CARDIOVASCULAR SYSTEM
Some characteristic aggregated changes in the cardiovascular
system are stenotic coronary vascular disease due to atheroscle-
rosis, stiffening of the large arteries, an increase in systolic blood
pressure, and mild cardiac hypertrophy and concomitant reduced
cardiac filling rate with unchanged cardiac filling volume and rest-
ing cardiac output (Lakatta, 1985a,b, 1986).
More subtle manifestations of aging can be detected with the
imposition of a stress, such as exercise. Age-related changes in the
hemodynam~c response to vigorous exercise include a diminution
in the increment in heart rate, increase in heart size (which is
ENVIRONMENTAL EFFECTS ON DISEASES AND ORGAN FUNCTION 137
.
normal at rest) both at the end of the filling period and at the
end of the contraction period, and reduction in the increment in
ejection fraction (the proportion of the filling volume pumped with
each contraction of the heart) (Rodeheffer et al., 1984~.
These changes can be explained by an age-related diminution
in the response of the cardiovascular system to catecholamines
produced by the activation of the sympathetic nervous system
(which occurs during exercise). Considerable evidence from both
experimental animate and humans indicated that the sensitivity
of cardiac and vascular tissue to ,9-adrenergic agonists' autonomic
modulation declines with age (Bertel et al., 1980; Conway et al.,
1971; FIeisch, 1981; Kuramoto et al., 1978; Vestal et al., 1979; Yin
et al., 1979, 1981~.
Despite a substantial body of information on the effects of
aging on cardiovascular physiology, the extent to which the aged
might be particularly vulnerable to the toxic effects of drugs,
chemicals, and other environmental agents has received scant at-
tention. The possibility of a difference in the response of the aged
myocardium to cardiac glycosides, such as ouabain and digoxin,
has been investigated in animals and humans (AIgeo et al., 1983~.
Developed tension and maximal rate of tension development in
isometric trabeculae carneae were approximately 4 times greater
in young than in aged Wistar rat myocardium (Gerstenblith et al.,
1979~. There was no age-dependent difference in ouabain-induced
Na+-K+-ATPase inhibition, which is a postulated mechanism of
action for ouabain and other digitalis preparations. In contrast,
activity of the Na+-K+ ATPase was 50~o less in aged Fischer 344
rats than in younger rats, and the toxicity of ouabain was inversely
related to enzyme activity (Baskin et al., 1977~.
Ouabain also inhibited enzyme activity more in older than in
younger rats. In guinea pigs, however, the median lethal dose of
ouabain infused into adult and aged (up to about 5-6.5 years old)
guinea pigs did not differ (Wollenberger et al., 1953~.
In elderly humans, an age difference in the Monotropic response
to digitalis was not demonstrated (Cokkinos et al., 1980~. The in-
otropic response, as measured by systolic intervals, to desTanoside
(1.2 mg intravenously) was similar in a group of 20 healthy males
and females (mean age 34.3 years) and a group of 20 healthy older
subjects (mean age 65.3 years). The clinical effects of acetyIdigoxin
in congestive heart failure and digoxin in atrial fibrillation do not
differ with age (Aravanis, 1969; CharnberIain et al., 1970~. Thus,
138
AGING IN TODAY'S ENVIRONMENT
apart from the increase in plasma digoxin due to diminished re-
nal excretion in the elderly, there is little evidence to support the
widely held notion that intrinsic myocardia] sensitivity to digitalis
is increased in old age.
Age-related data on antiarrhythmic agents are even less ex-
tensive than those available on cardiac glycosides; they generally
indicate no significant increase in sensitivity or toxicity in the
absence of abnormal conduction. A recent clinical study demon-
strated altered sensitivity to verapamiT, a calc~um-channe} antago-
nist. Age differences in pharmacokinetics resulted in higher plasma
concentrations in elderly than in young patients (Abernathy et al.,
1986~.
Doxorubicin (adriamycin), an anthracycline cancer chemo-
therapeutic agent, appears to have important age-related cardiac
toxicity. A major problem with administration of doxorubicin for
therapeutic purposes is the development of often irreversible and
often fatal congestive heart failure. The effect seeders to be dose-
related, and cumulative doses greater than 550 mg/m2 result in
a marked increase in the incidence of heart failure (Lefrak et al.,
1973~. If more sensitive measures of cardiac function are used
such as systolic intervals, cardiac impairment after doxorubicin
therapy (greater than 400 mg/m2) is detectable in approximately
15~o of patients (Dresdale et al., 1983~. Degenerative changes in
cardiac histology occur almost universally at doses greater than
240 mg/m2 (Bristow et al., 1978~. Apart from cumulative dose,
old age was the major risk factor observed in a retrospective survey
of 4,000 patients (don Hoff et al., 1979~.
Others have also noted that aging is a risk factor for devel-
opment of cardiotoxicity (Bristow et al., 1978; Dresdale et al.,
IUb3), but not because of a higher incidence of coronary heart
disease in older patients (don Hod et al., 1979~. The mechanism
of cardiotoxicity of doxorubicin is not known, but could be the
production of free radicals (Olson et al., 1981; Unverferth et al.,
1982~. Pathways of free-radical detoxification are depressed in
some tissues of senescent laboratory animals (Stohs et al., 1982),
so myocardial free-radical scavenging might be impaired in elderly
patients.
The clinical observations related to doxorubicin suggest that
other chemicals and environmental agents that produce free rad-
icals might be associated with myocardial damage and that the
effects might increase with age. Surprisingly, data on that point
"d I ~ . . ~ ~ ~ · ~
ENVIRONMENTAL EFFECTS ON DISEASES AND ORGAN FUNCTION 139
are not available; indeed, it appears that the impact of age on
cardiovascular toxicity has been virtually ignored by toxicologists
and epidemiologists.
RENAL SYSTEM
Chronic nephropathy involving glomerular sclerosis, mesan-
gial cell injury, and mesangial matrix overproduction is commonly
found in rats at advanced ages (Coleman et al., 1977; Durand
et al., 1964~. Similar progressive lesions are observed in young
rats after surgical reduction of kidney mass (Chanutin and Ferris,
1932; Purkerson et al., 1976; Shimamura and Morrison, 1975) and
in humans, usually at advanced ages, after disease-induced kidney
damage when the initial disease process is no longer active (Bren-
ner et al., 1982~. Decreasing the protein content of the diet of rats
has been found to retard the development of the nephropathy that
occurs during normal aging (Maeda et al., 1985) and that follows
surgical reduction of kidney mass (Hostetter et al., 1981; Laouari
et al., 1983; Moise and Smith, 1927~.
Moreover, there is evidence that reducing the protein intake
of humans slows the progression of chronic renal failure to end-
stage disease (Mitch, 1984~. Brenner et al. (1982) suggested that
a decrease in dietary protein acts by preventing giomerular hy-
perperfusion and hyperfiltration, which they thought responsible
for the progression of the lesions and for the eventual loss of renal
function.
Iwasaki et al. (1986) recently reported that the development
of kidney lesions in male Fischer 344 rats during normal aging can
be retarded by using soy protein as the source of dietary protein
without reducing protein intake. That finding is important in two
respects: for animal models for the study of aging and in treatment
of chronic renal failure in humans.
The male Fischer 344 rat has been a major animal mode}
(National Research Council, 1981b) for the study of aging, because
it is genetically homogeneous and because it does not develop
the obesity that occurs with advancing age in many rat strains.
However, a major problem with the strain, as with most other rat
strains, has been renal failure with advancing age, which precludes
the study of normal aging processes in some of the rats by the age
of 18 months and in many after the age of 24 months. Diets with
soy protein as the sole protein source might, to a great extent,
140
AGING IN TODAY'S ENVIRONMENT
circumvent the problem and thus facilitate fuR life-span studies
with the Fischer 344 rat.
Although available data indicate that restricting dietary pros
tein in patients with chronic renal failure delays the further loss of
renal function and lengthens the tone before they need dialysis or
transplantation, such treatment has the risk of protein mainutri-
tion, as well as mineral and vitamin depletion (Mitch, 1984~. The
proper selection of the dietary protein source might yield a treat-
ment for chronic renal failure as effective as protein restriction but
without its risks.
IMMUN1: SYSTEM
One of the most important body defenses is the immune gym
tem. Environmental influences on the immune system include the
effects of psycholog~c stress (including bereavement), nutrition,
environmental temperature, housing, light, noise, and chemicals.
Some environmental influences on immune function affect life span
and therefore presumably affect susceptibility to disease or the ag-
ing processes themselves.
Of the environmental factors, nutrition has a most dramatic
effect on both immunity and life span in rodents. Reducing caloric
intake of mice and rats by approximately 50%0 of their ad libitum
intake inhibits the age-associated decline in immune competence,
reduces the incidence of many diseases (including cancer), and
extends life span. Undernutrition has been shown to increase the
life span of a number of short-lived strains of mice (reviewed in
Good et al., 1980~. Whether a similar nutritional regimen would
influence the life span of higher organisms, including humans, }s
unknown.
Clear evidence exists that the barrier between an organism
and its environment ~ altered with age (for a review see Weksier,
1986~. The immune function of the skm and the mucosal lining
of the respiratory and gastrointestinal tracts change with age,
although such change does not always parallel the changes in
systemic immunity.
Far more is known about the changes in systemic immunity
that accompany aging in rodents and humans. The most striking
anatorn~c change Is the involution of the thymus gland that begins
at sexual maturity and is complete by midlife (45-50 years in
humans), and that results in the loss of two thymic functions. The
ENVIRONMENTAL EFFECTS ON DISEASES AND ORGAN FUNCTION 141
first thyme function that declines with age is the capacity to effect
the maturation of T-cell precursors that migrate to the gland from
the bone marrow. The second Is the activity of thymic hormone
in the serum, which begins to decline soon after sexual maturity.
Thymic hormone activity in serum is undetectable in humans after
midlife.
The thymus, the source of mature T lymphocytes, plays a cen-
tral role in cell-mediated immune responses and the regulation of
the immune response. Not surprisingly, therefore, immune Seneca
cence ~ characterized by a loss of thymu~dependent functions
required for both cellular immunity and the regulation of hu-
moral immunity. Inasmuch as the response to many pathogens—
including viruses and fungi, as well as neoplastic cells and some
environmental agents depends on cell-mediated immunity, the
susceptibility of the aged to diseases induced by these agents Is
increased. The striking increase in the morbidity and mortality
associated with influenza in elderly people is a common clinical
consequence of immune senescence.
In addition to the 108s of cell-mediated immunity with age,
the loss of thymic function leads to the dy~regulation of immune
reactions. The striking increases in the frequency of autoantibod-
ies and in the production of monoclonal ~rnmunoglobulins with
age reflect this fact. Impaired suppressor-cell activity in old age is
thought to contribute to the increases in autoantibodies and mon-
oclonal proteins with age. Those autoimmune reactions might be
exacerbated when elderly people take such drugs as procainarn~de,
a-methyIdopa, or estrogens, which themselves stimulate the pros
auction of autoantiboclies. When autoantibodies react with au-
toantigens, they form immune complexes. Circulating immune
complexes can contribute to vascular injury and thereby to the
increasing severity of atherosclerosis in the elderly.
Progress has been made in understanding the cellular basis of
lymphocyte function that Is attributable to a loss of the capacity of
T lymphocytes to divide. The evidence suggests that the cellular
basis of immune senescence Is similar to what Hayflick suggested
20 years ago (Hayflick, 1965) in cultured fibroblasts- the loss of
replicative capacity. Any environmental agent that compromised
the capacity of celb to divide would thus be likely to depress
immune competence and accelerate immune senescence.
142
AGING IN TODAY'S ENVIRONMENT
SEXUALITY
The fear of losing sexual ability or physical attractiveness can
be a source of great anxiety for many people as they grow older.
Men typically are afraid of sexual impotence; women fear the loss
of physical attractiveness and desirability. A number of gradual
and fairly predictable physiologic changes do occur with aging,
but these changes do not preclude active and satisfying sexual
functioning into old age.
Most of the sexual changes in older women result from the
menopausal decline of female hormones, especially estrogen. Envi-
ronmental agents, such as ionizing racliation, pharmaceuticals, and
cigarette smoking, have been shown to alter the age of menopause
(i.e., ovarian failures (Chapman, 1983; Mattison, 1985; Mattison
and Ross, 1983~. However, 60~o of all women do not experi-
ence remarkable physical or emotional symptoms associated with
menopause, and of those who do, most have only minimal to mod-
erate physical problems, including headaches and neckaches, hot
flashes, fatigue, and feelings of emotional instability.
Physically healthy men do not lose their capacity to have
erections and ejaculations as they age, although changes do occur.
With age, men ordinarily begin to take longer to obtain an erection
and to reach orgasm than when they were younger.
Drugs, taken by prescription or otherwise, can aggravate these
effects and cause other sexual problems. Some interfere with the
autonomic nervous system, which is involved in normal sexual re-
sponse. Others affect mood and alertness or change the production
or action of sex hormones. In a study reported in 1983, 25~o of
sexual problems in men were either caused or complicatecl by med-
ications (ButIer and Lewis, 19863. Although less ~ known about
drugs and female sexuality, drugs affecting men can be assumed
to affect women as well (Butler and Lewis, 1986~.
Tranquilizers, antidepressants, and some antihypertensive
agents have all been unplicated in erectile impairment in men.
The effects of these drugs on women is less well understood. The
corticosteroids taken for arthritis can produce temporary impm
fence. Analgesics can reduce sensitivity and therefore affect male
sexual capacity. Aspirin taken over long periods reduces fertility.
Cimetidine (for treatment of ulcers), one of the most widely sold
medicines in the United States, can cause impotence. Alcohol in
more than small amounts reduces potency in mates and orgasmic
ENVIRONMENTAL EFFECTS ON DISEASES AND ORGAN FUNCTION 143
ability in females. Even nicotine can be a factor in impotence.
Although a number of gradual and fairly predictable changes in
sexual function occur with aging, they are often confounded by
the effects of environmental agents.
ROLE OF E:NVI:RONMENT IN BONE M1:TABOLISM
AND VITAMIN D NUTRITION
One of the major problems associated with aging is the loss of
bone mass. It is estimated that upwards of 10 million elderly Amer-
icans suffer from marked reduction In bone ma" that compromises
the architectural integrity of the skeleton and puts them at sum
stantial risk of breaking bones. The magnitude of this public-
health problem is evident in the estimated 200,000 hip fractures
that occur each year. It has been estimated that $6 billion is spent
each year for the acute care of people with age-related fractures
(Cummings et al., 1985~.
Bone loss in the elderly has many causes; among them are
inadequate vitamin D and calcium absorption (influenced by es-
trogen concentration). Although it is well documented in Great
Britain (a country that does not routinely fortify foods with vi-
tamin D) that over 40% of males and 30~o of females with hip
fractures are deficient in vitamin D (Aaron et al., 1974; Chalmers
et al., 1967), it has been assumed that vitamin D deficiency is
not an important health problem in the United States because
foods are fortified with vitamin D. An epidemiologic survey in the
Southwest has revealed that over 60% of the free-living elderly
subjects were obtaining less than 25~o of the RDA of vitamin D
from their diets (Omdah] et al., 1982~. In two other studies, about
30~o of elderly patients with hip fractures had evidence of vitamin
D deficiency (Doppelt et al., 1983; Sokoloff, 1978~.
One of the prunary causes of poor vitarn~n D nutrition in the
elderly in the United States is a decrease in or complete absti-
nence Tom consumption of milk and milk products. The decrease
is related to the common misconception among the elderly that
they no longer need to drink milk because milk is important only
for maintaining a healthy skeleton in growing children, and to
gastrointestinal discomfort caused by lack of lactase, which is re-
sponsible for hydrolyzing the lactose in milk. Very few foods nat-
urally contain vitamin D (these include fish-liver oil, eggs, liver,
and milk) or are fortified with vitamin D (milk, some cereals, and
144
AGING IN TODAY'S ~VIRO~NT
in some countries, margarine). One quart of milk contains 400
international units (10 g) of vitamin D, which ~ the RDA (Holick,
1986~.
If an elclerly person does not consume milk or other foods that
contain vitamin D or take a vitamin D supplement, it is essential
for that person to sunbathe to generate enough vitamin D3 to
maintain a healthy skeleton. However, because of the increased
awareness that exposure to sunlight can cause skin cancer and
dry and wrinkled skin, the elderly are often advised to corer their
skin with clothing or a sunscreen before going outdoors. Those
measures prevent not only the damaging effect of solar irradiation,
but also the beneficial effect the production of vitamin D3 in the
skin (MacLaughlin and Holick, 1985~.