DEVELOPMENT, GLOBAL CHANGE, AND
THE EPIDEMIOLOGICAL ENVIRONMENT
By Gretchen C. Daily & Paul R. Ehrlich
Paper number 0062 -- Revised 1995
G.C.D.: Energy and Resources Group Building T-4, Room 100
University of California Berkeley, California 94720
P.R.E.: Center for Conservation Biology Stanford University
Stanford, California 94305
ABSTRACT
Although improvements in human health represent
a crucial aspect of development worldwide, many trends associated
with development and global change appear to be reducing health
security. In this article, we define the human epidemiological
environment and describe key biophysical, economic,
sociocultural, and political factors that shape it. The potential
impact upon the epidemiological environment of aspects of both
development and global change are then examined: the influences
of human population size, mobility, geographic distribution, and
nutritional status; modernization; loss of indigenous medicinal
knowledge; microbial evolution of antibiotic resistance; land
conversion and biodiversity loss; agricultural intensification;
stratospheric ozone depletion; and climate change. Human
vulnerability to infectious disease is often strongly and
deleteriously influenced by ongoing, intensifying changes in
these factors. An unprecedented level of communication and
cooperation between experts, institutions, and nations is
required to respond to the increasing threat of epidemic disease,
which points to a promising area for enhanced interdisciplinary
collaboration.
When one comes into a city to which he is a
stranger, he ought to consider its situation, how it lies as to
the winds and the rising of the sun; for its influence is not the
same whether it lies to the north or to the south, to the rising
or to the setting sun. These things one ought to consider most
attentively, and concerning the waters which the inhabitants use,
whether they be marshy and soft, or hard and running from
elevated and rocky situations, and then if saltish and unfit for
cooking; and the ground, whether it be naked and deficient in
water, or wooded and well-watered, and whether it lies in a
hollow, confined situation or is elevated and cold...
From these things he must proceed to
investigate everything else. For if one knows all these things
well, ... he cannot miss knowing, when he comes into a strange
city, either the diseases peculiar to the place or the particular
nature of the common diseases, or commit mistakes, as is likely
to be the case provided one had not previously considered these
matters. And in particular, as the season and year advances, he
can tell what epidemic disease will attack the city, ... and what
each individual will be in danger of experiencing from the change
of regimen. -- Hippocrates, On Airs, Waters, and Places, cat 400
B.C. (quoted in Garrett 1994, p. 234).
INTRODUCTION
Good health is such an integral part of human
well-being that, in many languages, everyday greetings and
meal-time toasts are synonymous with best wishes for it. In
English, the very word "salutation" is derived from the
Latin salutare or salus, which refer to health and safety. People
have always been wary of being unexpectedly stricken by disease.
Although the loss of good health is inherently
unpredictable, human behavior at the individual and societal
levels profoundly influences the incidence of disease. This has
been understood since ancient times and, indeed, the same
fundamental factors that determined human vulnerability to
disease early on remain paramount today. The rates and scales
over which these factors now operate are unprecedented, however,
greatly disrupting the epidemiological environment and opening
new opportunities for disease agents.
The epidemiological environment consists of the
conditions and processes, both biophysical and social, that
influence the interaction between human beings and disease
agents. It encompasses a complex of interrelated factors,
including:
* the parasites that are actually or
potentially pathogenic to Homo sapiens, defined broadly to
include subcellular, unicellular, and multicellular organisms
such as prions , viruses, bacteria, fungi, protozoa, helminths,
and arthropods; ( Whether these proteins could be considered
organisms and, indeed, whether they exist at all is a matter of
debate that extends beyond the bounds of this article (see
Prusiner 1995).)
* biophysical determinants of the reproductive
success of such parasites, including conditions such as
temperature and moisture, availability of and transmittancy to
vectors and hosts, the evolution of virulence, and coevolution of
human immunity and parasites' resistance to the immune system and
other human defensive measures;
* social determinants of the reproductive
success of such parasites, including the frequency and nature of
interpersonal contact, travel and migration patterns, access to
health care and information, pharmaceutical markets,
urbanization, poverty, public health policy, medical training,
funding of medical research, and political leadership.
These factors span virtually the entire human
environment. Nonetheless, their nexus is little appreciated
because the pathogenic actors in it are largely invisible -- out
of sight, out of mind (Ornstein and Ehrlich, 1989). Few people
are aware that each human being encloses billions of
microorganisms and is surrounded by trillions more. Some of these
organisms play key roles in keeping people alive; others
represent lethal threats. The two kinds do not have to be very
different. Some strains of Escherichia coli, common bacteria that
live in the human large intestine, are helpful in synthesizing
vitamins that are essential to people. Other strains may cause
lethal disease.
Recent and projected future changes in the
epidemiological environment pose a major threat to health
security, which is presently manifesting itself in a variety of
ways (Ehrlich and Ehrlich, 1970, pp. 148-151; 1972, pp. 181-184;
Ehrlich et al., 1977, pp. 606-609; Leaf, 1989). Old diseases such
as malaria (e.g., Pearce, 1995), tuberculosis (Bloom and Murray,
1992; Brown, 1992), bubonic plague (Altman, 1994; Burns, 1994),
and cholera (Glass et al., 1992) are resurgent; the new epidemic
of AIDS is creating formidable public health problems; some
strains of old bacterial enemies may be becoming more deadly
(Nowak, 1994); "miracle" drugs are losing their
potency; and a variety of nasty viruses such as Ebola appear to
be lurking in the wings (e.g., MacKenzie, 1995; Morell, 1995;
Altmann, 1995). Malaria was once thought to be on the way toward
eradication (Garrett, 1994, p. 31), yet now there are between 300
and 500 million cases annually, resulting in as many as 2.7
million deaths (Nussenzweig and Long, 1994).
These problems mark the second major round in a
coevolutionary (Ehrlich and Raven, 1965) battle between Homo
sapiens and its parasitic enemies. The first began with the
agricultural revolution, some 10,000 years ago. This led to the
development of towns and cities where human populations grew to a
size and density at which they could sustain epidemics of
diseases such as measles, smallpox, flu, cholera, and polio
(Black, 1966, 1975). It also led to concentrations of human and
animal wastes ideal for the propagation of protozoan and helminth
parasites (Inhorn and Brown, 1990).
After World War II, many believed that the
first round was ending in victory for humanity with the defeat of
microbial pathogens through the use of sanitation, water
purification, vaccination, antibiotics, and pesticides. Indeed,
in 1969 U.S. Surgeon General William H. Stewart testified before
Congress that it was time to "close the book on infectious
disease" (Fisher, 1994); like most physicians of his day, he
was deeply ignorant of the nature of the epidemiological
environment.
As the human population has increased to
unprecedented size, it has dramatically changed this vast,
tumultuous, little understood world. Some of these alterations
have been to our benefit; many are already clearly deleterious
and promise to become more so in the future. Alterations in the
epidemiological environment have been little examined, and do not
fit into the heuristic framework by which other aspects of human
activity and the environment have been explored (Ehrlich and
Holdren, 1971; Holdren and Ehrlich, 1974; Ehrlich and Ehrlich,
1990).
In our view, in no aspect of the human
environment are the economic costs of environmental deterioration
clearer, of greater importance to those concerned with
development, or more threatening to the human future. Consider
the warning of the late Howard Temin, who received the Nobel
Prize for his discovery of retroviruses (which include HIV):
"...it is not surprising that a major new epidemic has
accompanied the dramatic post-World War II social changes -- the
greater urbanization and enormous population increases in Africa,
the rise of freer lifestyles in North America and Europe, and the
growth of jet travel everywhere. If anything, the surprise might
be that there has been only one major new epidemic" (Temin,
1989, p. 1).
In this paper, we examine the impact on this
hidden environment of both development and global change. These
two aspects of the increase in scale of the human enterprise are
so tightly interrelated as to make any classification of their
elements quite arbitrary. We have structured our inquiry around
three categories of changes: (i) those in biophysical and social
characteristics of the human population; (ii) those in human
tactics and strategies for controlling disease; and (iii)
dramatic alterations of the biophysical environment, collectively
referred to as "global change" (Lovejoy, 1993), that
for the most part represent unintended consequences of the first
category.
CHANGES IN CHARACTERISTICS OF THE HUMAN POPULATION
Population Size
For successful establishment in a host
population, a parasite must achieve a basic reproductive rate of
greater than one (Macdonald 1952, May and Anderson, 1979). In
general, this means that each infected individual, on average,
infects more than one other individual. This, in turn, means that
a threshold or critical community size is necessary for the
perpetuation of most epidemic diseases. The precise threshold for
disease establishment is determined by complex characteristics of
both the parasite and the host, such as whether transmission is
direct or mediated through a vector and/or animal reservoirs;
seasonality in transmission; incubation, latent, and infectious
periods of the host; the existence and duration of acquired host
immunity; reproductive requirements of the parasite; and so on
(Anderson and May 1991).
The bottom line is that human population size
and density are key variables in epidemiology, influencing the
rate of introduction of new parasites into the population, their
chances of becoming established, the rate of their spread, the
evolution of their virulence, and the capacity of human cultural
evolution to defend against them. Paleolithic groups were
probably relatively free of virulent epidemic disease (Cohen,
1989; Inhorn and Brown, 1990). It was not until a critical
community size was reached in early agricultural societies that
parasites previously confined to nonhuman animals were able to
exploit Homo sapiens. Examples of such diseases include smallpox,
influenza, and measles, which are thought to have evolved from
monkey pox, avian flu, and rinderpest or canine distemper,
respectively (Fenner et al., 1974). Measles apparently could not
get a foothold in human populations until there were aggregations
of about 200,000 to 500,000 people (Bartlett, 1957; Black, 1966).
Today's 5.7 billion people represent a brand
new environment for pathogens and potential pathogens (Mitchison,
1993). It is the densest population the world has ever seen, and
it contains large numbers of immune-compromised people due
primarily to malnourishment, the presence of immunosuppressive
pollutants in the environment (Ross et al., 1992; Repetto, 1992;
Colborn et al., 1996) and, increasingly, to AIDS. That vulnerable
portion of the population makes an especially favorable
environment for the evolution of virulence in viruses, bacteria,
and fungi that in the past were viewed as benign (e.g.,
Sternberg, 1994; Georgopapadakou and Walsh, 1994). For a
parasite, evolving host specificity to humans would amount to
winning the biggest jackpot in history.
It is not clear, at present, how HIV-1 (the
virus that causes the most serious form of AIDS) first entered
the human population, but one possibility is that it was the
result of a transfer by a vector (e.g., a mosquito or tick) from
another primate. Such events are thought to occur very rarely
(Humphery-Smith et al., 1993), but increased human numbers make
more probable such "jumps" from other species.
Moreover, population growth is accompanied by
large families, which increase the vulnerability of populations
by presenting arrays of immune-similar individuals. As viruses
colonize individuals in such families sequentially, they may
evolve greater virulence, as was the case in rural Senegal where
the case fatality rate was higher in children who caught the
measles from relatives than among those that contracted the
disease from nonrelatives (Garenne and Aaby, 1990).
Immune-similarity of individuals may also have contributed to the
near extinction over recent centuries of native Americans and
their cultures (Roberts, 1989). Black (1992, 1994) has argued
that the decimation of these populations by disease was due not
just to a lack of immunological experience that made them highly
susceptible, but also to a relative lack of genetic variability
tracing to their rapid expansion after the genetic
"bottleneck" of the trans-Bering invasion. Sadly, the
genetic mixing through immigration that might protect isolated
cultures would probably simultaneously destroy them (Black,
1994).
Population Mobility: Rapid Transportation
The movement of people has always been an
important mode of spread of disease. The legacy of merchants,
explorers, and conquistadores extends far beyond that assessed by
most historians (McNeill, 1976). European sailors brought
smallpox, measles, and swine flu to the New World; the first
epidemics of leprosy in Europe followed the expansion of the
Roman Empire; the black death of fourteenth-century Europe made
its way from central Asia via the Silk Road; and cholera was
carried unwittingly by traders and armies into Europe from India
in the early 1800s. As we write, world health authorities are
declaring states of emergency in Central America, and port cities
throughout Latin America are on alert, due to the rapid spread of
dengue fever (New York Times, 1995; UPI, 1995).
The spread of epidemics is clearly greatly
facilitated by the development of high-speed modern transport
systems. In recent years, indices of the amount of international
travel were highly associated with the spread of AIDS (Darrow et
al., 1986). Steamships alone made it possible to transport
bubonic plague to all major ports in the world at the end of the
last century, something that could not have occurred earlier
because all of the susceptible passengers on plague-infested,
slow-moving sailing ships would generally have died before the
ships reached ports (McNeill, 1976). People carrying dengue fever
on airplanes have represented an important mode of its recent
spread (Monath, 1993). Rapid transportation helps the spread of
antibiotic-resistant strains of bacterial pathogens (Tauxe et
al., 1990).
Modern high-speed transport also plays a role
in the distribution of recreational drugs; large supplies
produced in the "golden triangle" of southeast Asia or
the mountains of South a flow easily into rich and poor nations
around the world. Almost everywhere, sharing of needles by
addicts contributes to the propagation of infectious diseases.
The problem is especially serious because narcotic addicts are
often immune-compromised, making their bodies ideal environments
for the multiplication of numerous pathogens (e.g., Cherubin,
1971; Levine and Sobel, 1991).
Modern transport also helps to move animals
that are potential vectors or disease reservoirs around the
world, which combined with projected climate change could further
degrade the epidemiological environment (Soule, 1995; Dobson and
Carper, 1992). In Uganda a century ago an agricultural officer
introduced the shrub Lantana camera for use as an ornamental
hedge. The Lantana provided excellent moist habitat for tsetse
flies, and an increase in sleeping sickness followed. Perhaps the
most spectacular recent case of the transfer of a dangerous
vector was the moving from Asia to the United States of a
mosquito (Anopheles albopictus; the Asian tiger mosquito) capable
of transmitting dengue. The mosquito larvae apparently survived a
ship journey in water collected in old tires (Craven et al.,
1988; Monath, 1993). Soon after its introduction, A. albopictus
was found to be carrying another potentially dangerous virus,
that of La Crosse encephalitis (Francy et al., 1990; Henig,
1995). The usual vector of this disease is a woodland mosquito
that relatively rarely bites human beings. George Craig of Notre
Dame, perhaps America's greatest authority on mosquitoes,
considers the combination of that virus and the aggressive tiger
mosquito especially worrying (Henig, 1995). Dengue has returned
to Mexico just south of the border of the United States (Rohter,
1995), from where the tiger mosquito could move it north into
areas in which its normal vector cannot survive the cold winters.
Modern transportation systems certainly improve
the epidemiological environment by making it relatively easy to
move food to the hungry and medical personnel, drugs, and
vaccines to the ill. But even here they are a two-edged sword,
because they are susceptible to disruption during epidemics by
fear and by the disease itself (Ehrlich and Ehrlich, 1970; p.
150). Truck drivers and pilots are generally loath to enter
plague areas.
Population Distribution: Urbanization and Suburbanization
As nations develop, they are characterized by
relatively larger urban populations (Gizewski and Homer-Dixon,
1995). This can improve access to health care, food, and clean
water. For example, in urban areas of poor nations, a minimum of
170 million people do not have access to clean drinking water,
but an estimated 855 million lack that access in rural areas
(World Bank, 1992). About 35 percent of the population of
developing nations (1.5 billion people) now live in cities, so
this suggests that the water-supply element in the
epidemiological environment has been somewhat improved by
urbanization, even among the poor. Only some 15 percent of
urbanites in poor countries may suffer bad drinking water, while
over a quarter of the 3 billion who live in the countryside do.
(These data may overstate the quality of drinking water in many
cities in developing countries, however; much depends on such
things as what is meant by "a minimum of 170 million
people" and interpretation of the statement that "many
of those who officially have access still drink polluted
water"; World Bank, 1992, p. 47).
Urbanization does not have only positive
effects on the epidemiological environment, however (e.g., Morse,
1991). Cities above all bring large numbers of people into
intimate contact. In 1950 only New York, London, and Shanghai had
populations of over 10 million. By the start of the 21st century,
23 cities will have surpassed that number, and more than half of
all human beings are projected to be city dwellers by 2010
(United Nations, 1987). This sudden concentration of humanity
would greatly facilitate disease transmission even if all
urbanites were well fed and supplied with clean water, adequate
shelter, and access to health care. But that is hardly the case,
and it will be difficult to achieve given the tremendous rate of
growth in demand for such resources and services.
In poor countries, urban inhabitants very often
lack clean water and adequate sanitation. In Uganda, unskilled
urban workers often spend 10 percent of their income on small
quantities of poor-quality water (Bradley, 1993b). Yet even poor
quality water can be important for use in washing to restrict the
direct fecal oral transmission of diseases (Bradley, 1993b).
A problem afflicting cities in rich and poor
nations alike is the lack of control of disease reservoirs (e.g.,
rodents) and vectors (e.g., mosquitoes). Rats, for example, are
all too common in New York and other cities in the United States.
Urbanization has contributed to the great spread of dengue fever
(Anonymous, 1995c) by bringing large numbers of people into close
association with the household mosquito Aedes aegypti, the vector
of the causative virus (Monath, 1993). A. aegypti breeds in water
standing in containers, and everything from coke bottles to old
tires that can hold small pools help support it in third-world
slums.
The anonymity associated with large-scale
movement and urbanization is associated with behavior that tends
to be suppressed in small communities. In both rich and poor
nations, urban conditions may promote drug use, prostitution, and
greater sexual promiscuity in general, especially among
homosexual men (Symons, 1978, although time-series data on this
point are lacking). Interestingly, for diseases transmitted
sexually or through the sharing of needles, lack of acquired
immunity in recovered hosts permits persistence in low-density
populations. In such cases, a principal criterion for persistence
is a threshold average number of partners, rather than a general
threshold host density (Anderson and May 1991; Thrall et al.,
1993).
The increase in density that inevitably
accompanies population growth is now thought by some (Ewald,
1994) to increase the virulence of certain parasites, such as
those that cause dysenteries and influenza, which do not depend
on vectors for transmission (and thus whose spread is slowed if
hosts are immobilized by illness). Important evidence for this
comes from the record of the increased virulence of such diseases
during crowding of troops in wartime -- indeed it has been
suggested that the mysterious increase in virulence that made the
1918-19 flu epidemic the worst ever was due to the evolution of
higher virulence in the hideous trench conditions on the western
front (Ewald, 1994).
Finally, another feature of urban (and
suburban) areas that causes deterioration in the epidemiological
environment is the increased "air tightness" of
buildings (in the name of energy efficiency) and air conditioning
(and, incidentally, the reduced rate of airflow in the cabins of
modern jet airliners, also in the name of energy efficiency). All
three factors tend to keep people breathing the same recirculated
air, making the transmission of airborne pathogens all the easier
(Tolchin, 1993), especially if the systems are not operating
optimally (Moser, et al., 1979). In addition, at least one
emerging bacterium has adapted itself beautifully to
air-conditioning systems: Legionella pneumophila, the causative
agent of often-fatal Legionnaire's disease (Hudson, 1979;
Lederberg et al., 1992).
Overpopulation and concomitant urban crowding
also appear to exacerbate the conditions for crime, war, and
other forms of social disruption that degrade the epidemiological
environment, although the connections are complex and disputed
(see, e.g., Percival and Homer-Dixon, 1995). For instance, the
economic and social deterioration in the former Soviet Union has
led to a decline in nutrition, a shattering of the public health
system, higher mortality (especially in males), and, among other
things, epidemics of diptheria (Stone, 1993; Maurice, 1995).
Globally, it appears that the development of urban
infrastructure, including public heath facilities, is retarded by
violence (Gizewski and Homer-Dixon, 1995).
In short, urban centers may be considered
"ecosystem[s] that can amplify infectious diseases" (De
Cock and McCormick, 1988) or, more bluntly, "graveyards of
mankind" (J. Cairns, unpublished, quoted in Garrett 1994).
Suburbanization has also greatly altered the
epidemiological environment, especially in the United States. It
clearly helped improve the epidemiological environment of those
who could flee the cities, while perhaps worsening it for those,
mostly people of color and the elderly, forced to stay behind
with a diminishing tax base and decaying health-care delivery
system.
But other problems have overtaken some
suburbanites as a result of large-scale ecosystem alteration. The
first stage was the massive clearing of eastern forests, with the
removal of both large trees and top predators such as wolves and
mountain lions. Many of farms for which the clearing was done
were then reclaimed by second growth, and this in turn was
fragmented by suburbs. The result is a habitat matrix that is
ideal for deer, which often are also protected from hunting, and
some small rodents, especially the white-footed mouse (Peromyscus
leucopus). Deer and small mammals in turn support the tick,
Ixodes scapularis (=dammini, Oliver et al., 1993) which transmits
the spirochaete (Borrelia burgdorferi) that causes Lyme disease
from its natural reservoir in the mouse to human beings
(Lastavica et al., 1989; Barbour and Fish, 1993). Large
concentrations of deer support dense adult tick populations (the
deer do not serve as important reservoirs of the spirochaete) and
young ticks acquire the spirochaetes from smaller animals. In the
past 15 years Lyme disease has become the most common
arthropod-borne infection in the United States (Lederberg et al.,
1992). Babesiosis, a sometimes-fatal disease similar to malaria,
can be transmitted in the same manner as Lyme, and sometimes
people are infected with both. So can an emerging, sometimes
deadly tick-borne disease, ehrlichiosis, caused by the rickettsia
Ehrlichia chafeensis (Adler, 1994).
Nutritional Status
Although undernutrition is declining globally,
in both relative and absolute terms, roughly 1 billion people
still do not have diets sufficient to support normal daily
activity, and nearly 500 million are essentially slowly starving
to death (summary of data in Uvin, 1994). Hunger, however, is
rarely the proximate cause of mortality; rather, the Grim Reaper
usually makes his appearance in the guise of disease.
Approximately 10 million people die of "hunger-related
disease" annually (Dumont and Rosier, 1969, pp. 34-35; WHO,
1987; WRI, 1987, pp. 18-19; UNICEF, 1992).
A synergistic interaction between
undernutrition and infection is well established (e.g., Smythe et
al., 1971; Beisel, 1984; Harrison and Waterlow, 1990; Ellner and
Neu, 1992). Infections enhance the need for nutrients (by
increasing a person's metabolic rate through fever), while
simultaneously diminishing their supply (through reduced
appetite, lower absorption by the gastrointestinal tract, loss
through faeces, and direct loss in the gut; Beisel, 1984; see
also the excellent summary in Dasgupta, 1993, on. 405-408). This
synergism is especially apparent in young children: both
mortality and morbidity are critically determined by a child's
nutritional status, as measured by a weight-for-height ratio
(Chandra 1983). Interestingly, the synergism is not universal; in
fact, undernourishment may actually confer a survival advantage
in some cases, although this remains speculative (see Dasgupta,
1993, p. 407). Overnutrition, epidemic in some developed
countries, may impair immune function as well (e.g., Chandra,
1981).
MODERNIZATION AND HEALTH CARE
Sanitation and Water Quality
Death rates from many diseases were lowered
dramatically in today's developed nations long before antibiotics
or other effective medical interventions were available (McKeown,
1979). This was accomplished largely with improved nutrition,
housing less vulnerable to vermin, cleaner drinking water,
improved isolation from human fecal contamination, and soap
(e.g., McKeown, 1979; McKeown et al., 1972; 1974). Improvement of
water supplies traces back to Dr. John Snow's work on cholera
(1855). A rough estimate of the positive health impacts of
providing those who now lack it with access to safe drinking
water and adequate sanitation would be the annual prevention of 2
million deaths from diarrhea in children under five, and having
200 million fewer cases of diarrheal illness, 300 million fewer
people infected with roundworms, 150 million fewer infected with
schistosomes, and 2 million fewer infected with guinea worm
(World Bank, 1992).
Interestingly, however, the general improvement
of sanitation carries a risk. By causing the prevalence of
relatively benign diseases to decline, such improvements might
enhance the chances of more virulent parasites to invade. This
appears to have been the case of herpes simplex virus 1 (HSV-1),
the cause of "cold sores" or "fever
blisters," which declined in developed countries due to
improved personal hygiene. Unfortunately, however, the relatively
benign HSV-1 may provide some protection against the development
of genital herpes (caused by HSV-2), which is now an epidemic
sexually transmitted disease (STD). Improved public health
conditions call for careful surveillance of populations that
become increasingly immunologically naive.
Improvements in Medical Care
The level of health care generally rises with
modernization and development. This is apparent in several
indicators, such as the proportion of physicians in a population
(World Bank, 1993). In sub-Saharan Africa, for example, there are
about .12 doctors for every 1000 people; in India, .41; in China,
1.37; in the United States, 2.38, and in Switzerland, 1.59. In
the same areas, hospital beds per 1000 population were 1.1, 0.7,
2.6, 5.3, and 11.0, respectively. Another index of overall health
care is the percentage of children immunized against measles --
52, 77, 96, 80, and 90 in those areas, respectively. Infant
mortality rates (per thousand live births) and life expectancies
(in years) are perhaps the best indices of health, and the
quality and availability of health care are factors in those
statistics (adequacy of food supplies and quality of water supply
are others). Infant mortality and life expectancy respectively in
sub-Saharan Africa are 95/52; India, 74/60; China, 44/69; U.S.,
8/76; and Switzerland, 5.6/78 (Population Reference Bureau,
1995).
Since roughly 1930, the medical system has made
a positive contribution to public health. While there clearly is
no perfect correlation between standard economic measures of
development and the quality of health care, it seems fair to say
that modernization of the health-care system mostly improves the
epidemiological environment. Development, by bringing medical
care to billions of people, has saved innumerable lives through
immunization, use of antibiotics, surgery, and so on.
Nonetheless, physicians and hospitals can also
have negative effects on the epidemiological environment by
helping to spread pathogens. This problem can be particularly
acute in developing nations; at the extreme, it can be
devastating, as when a poorly prepared mission hospital in Zaire
served as a focus for the spread of Ebola virus in a situation
where simple sterilization would have greatly limited the
propagation of the disease (Garrett, 1994). In rich nations as
well, the rate of nosocomial infections (those acquired in
hospitals) remains about 5 or 6 percent. That amounts to 2
million infections per year in the United States, 6 million
excess days of hospital stay, some 20,000 direct deaths, as well
as contributions to perhaps 40-60,000 additional deaths (Last,
1987). Many of these deaths can now be traced to drug-resistant
bacteria.
A classic example of iatrogenic disease
(induced by medical treatment) is blackwater fever, whose victims
were overcome with fever, urinated dark fluid, and often died. It
took decades to discover the cause: in the vast majority of cases
it was overuse of quinine to treat malaria (Manson-Bahr and
Apted, 1982).
Even medical "miracles" can have
negative impacts on the epidemiological environment.
Transfusions, transplants, and deliberate immune-suppression in
connection with transplants provides new ways for pathogens to
move from person to person or (in the rare cases of transplant
from other animals) species to species, while adding to the
immune-compromised population. Hepatitis B and HIV have been
widely spread through blood transfusions. Today HIV is being
spread extensively that way in India, where a quarter of all
HIV-positive individuals in West Bengal are blood donors, and
where up to half of all blood in banks is infected with hepatitis
B (Anonymous, 1995a). The rare prion of Creutzfeldt-Jakob disease
has occasionally been transmitted by corneal transplants (Miller,
1989).
Loss of Indigenous Medicinal Knowledge
Urbanization, modernization, and other forces
have led to the supplanting of indigenous medical systems by
western medicine, in the process leaving a great unmet need for
health care. Ratios of physicians to population as high as one to
more than 10,000 or 15,000 in the world's poorest countries leave
no doubt that most people do not get medical treatment from
trained professionals (Fischer 1994). According to the World
Health Organization, over 80 percent of people rely for their
primary health care on tradition plant medicines (Dobson, 1985).
Meanwhile, traditional medicinal knowledge is
rapidly disappearing with cultural change and declining access,
in both urban and rural areas, to sources of natural medicinal
products. It is estimated that, in the Amazon Basin alone, one
indigenous culture goes extinct annually (Dobson, 1985). The
principal natural sources, upon whose extracts many modern
pharmaceuticals are based, are plants (Farnsworth, 1988; Eisner
and Meinwald, 1995). Most villages in the world are no longer
surrounded by the natural habitat that formerly served as a
medicine cupboard, supporting a diversity of medicinal plants,
animals, and microorganisms. In many regions of the world, bodies
of folk knowledge that have been honed for thousands of years are
disappearing at an alarming rate.
In the absence of traditional medicine, the
role of doctor in most developing nations is played either by the
local pharmacist or by the sick individual and his or her
relatives themselves. Antibiotics and other powerful drugs are
readily available without proper diagnosis and prescription,
through pharmacies and black markets (Levy, 1992). This tragic
situation is made worse by its sinister consequences, microbial
evolution of resistance to antibiotics.
Misuse of Antibiotics and the Evolution of Resistance
As Nobel Laureate Joshua Lederberg said,
"The survival of the human species is not a preordained
evolutionary program. Abundant sources of genetic variation exist
for viruses to learn new tricks, not necessarily confined to what
happens routinely, or even frequently." (quoted in Garrett,
1995, p. 6). The current crisis in antibiotic resistance is
severe enough to lead another expert to question whether or not
humanity is entering a "post antimicrobial era" (Cohen,
1992). The primary source of the crisis is overuse of
antibiotics, not just for treating human disease, but also as a
feed supplement to speed the growth of animals being raised for
slaughter (Neu, 1992; Fisher, 1994).
Viruses, bacteria, fungi, and their human and
non-human hosts are engaged, neck-and-neck, in a coevolutionary
race, perpetually trying to devour, outcompete, or otherwise
defeat each other (Ehrlich and Raven, 1965; Anderson and May,
1979; Ehrlich, 1986, May, 1993). Bacteria had billions of years
of experience using antibiotics to battle each other, fungi, and
other microbes before Homo sapiens evolved. It is no wonder that
they show signs of defeating our antibiotic weapons a mere
half-century after they were first deployed on a large scale
(Anonymous, 1995b). Indeed, some evolutionists and medical
professionals have been very concerned about the evolutionary
consequences of antibiotic misuse, going all the way back to
Alexander Fleming himself (e.g., Ehrlich and Holm, 1963; Lappe,
1982; Slater, 1989; Cohen, 1992; Levy, 1992; Neu, 1992; Russell,
1993).
Bacteria have such rapid life cycles,
extraordinary abilities to swap genetic material (e.g., Davies,
1994; see also Conway et al., 1991 on the malarial parasite), and
intrinsic mechanisms of resistance derived from their
evolutionary experience (Nikaido, 1994) that the surprise really
is that they did not all become resistant to our puny efforts
sooner. The oft-heard lament that no antibiotics have been found
that control viruses would be humorous if it were not so tragic.
Viruses, especially RNA viruses (such as HIV) reproduce and
mutate even more rapidly than bacteria, and could be expected to
evolve resistance even faster.
Human beings, on the other hand, are condemned
by their long generation times (decades rather than minutes as in
microorganisms) to evolve genetic responses very slowly. But they
have a capacity for cultural evolution that can be much more
rapid, and that gives Homo sapiens the best chance of staying
even or getting ahead in the coevolutionary race (e.g., Alland,
1970; Inhorn and Brown, 1990).
Regrettably, human behavior with respect to the
use of antibiotics has been maladaptive since the start. These
"miracle drugs" are routinely misused in anticipation
of or in response to all manner of possible illnesses, without
deterring whether an antibiotic could even be effective (Lappe,
1982; Levy, 1992; Fisher, 1994). Even when taken to cure
infections against which they are effective, they are often taken
for far too short a period (due to ignorance and/or poverty),
thereby killing off the most susceptible bacteria while promoting
those that are resistant.
In developed nations, widespread ignorance of
evolutionary implications among medical professionals, false or
misleading information distributed by drug companies, inner-city
poverty, and the determination of misinformed patients to get
antibiotics by any means necessary have played major roles in the
rapid evolution of antibiotic resistance. In developing nations,
the principal factors at work include the inaccessibility of
professional health care, inability to afford the necessary full
course of antibiotic treatment, and the casual availability of
antibiotics through pharmacies and black markets. Poor health
policy, in general, is responsible in both regions of the world
(Lappe, 1982; Levy, 1992; Fisher, 1994; Erlich, 1995).
The particular case of a well-to-do Argentinian
businessman is indicative of what is going on worldwide. This
energetic individual led a busy life and did not like to be held
back by colds or other minor illnesses. Although he respected the
advice of his physician, for convenience he usually simply
treated himself with readily available drugs sold at the local
pharmacy. On one occasion, however, he developed a cough and
fever that would not go away, although he tried to treat it with
several different antibiotics. To make a long story short, he
eventually saw his doctor and was sent immediately to the United
States for treatment of acute leukemia, which can be caused by
the antibiotic chloramphenicol. Although the leukemia treatment
went well, the patient became infected with a strain of
Escherichia cold from his own intestinal tract that was resistant
to eight different antibiotics -- a level of resistance never
seen before by his doctors in the U.S. He died of massive
infection in a matter of a few weeks, succumbing to a usually
beneficial bacterium turned lethal due to his excessive
self-treatment with antibiotics (Levy, 1992).
Such multiply resistant bacterial strains can
easily be passed on to other people in hospitals or otherwise
spread rapidly. For example, public health officials have been
able to trace the initial source of penicillin-resistant bacteria
causing gonorrhea, now found worldwide, to brothels in Southeast
Asia (Levy, 1992).
Back in 1950, few, if any staphylococci
exhibited antibiotic resistance. Yet by 1960, about 80 percent of
the strains of staph showed resistance to penicillin,
tetracycline, and chloramphenicol. At the St. Joseph Hospital in
Paris, levels of resistance were up to 14 times higher than
reported in the United States. By 1980, penicillin was only
effective against 10 percent of the varieties of staph that it
used to control (Lappe, 1982). A similar story has unfolded in
the case of most pathogenic bacteria (Levy, 1992). Most recently,
bacteria have developed a complex strategy for protecting
themselves from vancomycin -- the "last ditch"
antibiotic for use agains enterococci (Lipsitch, 1995). The fear
now is that staph will acquire the resistance via plasmid
transfer from enterococci.
Overuse of antimalarial drugs has had similar
grim consequences, leading eventually to strains of the most
lethal malaria species, Plasmodium falciparum, that were
resistant to virtually all drugs (Looareesuwan et al., 1992; Ter
Kuile et al., 1993; Gay et al., 1994). Resistant malaria has led,
among other things, to increased AIDS transmission through the
use of transfusions to save children from death from
chloroquine-resistant Plasmodium falciparum (Bloland, et al.,
1993; Lackritz et al., 1992). Sadly, there are now signs that the
schistosomes (the blood flukes that cause Bilharzia) are becoming
resistant to praziquantel, the most important drug used to treat
the disease. Since some 200 million people are affected by the
disease, and some 200,000 die annually, this is bad news indeed
(Brown, 1994).
Another very serious problem has developed in
connection with the intensification of animal agriculture: the
massive use of antibiotics in farm animals. More than half of the
antibiotics produced in the United States -- in the vicinity of
8000 tons -- are fed annually to livestock alone, mostly in
sub-therapeutic doses which are ideal for the development of
resistance (Lappe, 1982; Holmberg et al., 1984; Fisher, 1994;
Levy, 1984, 1992; Wuethrich, 1994). Transmission of
antibiotic-resistant bacteria from livestock to humans can occur
through routes hardly imagined earlier. In 1991 in Massachusetts
an outbreak of a dangerous strain of Escherichia cold (0157:H7)
was traced to contaminated apple cider; the cider was made from
apples from trees that had been fertilized with livestock manure.
Subsequently, this strain of E. cold has been blamed for 6,000
food poisonings, sometimes lethal in small children, each year in
the United States (Garrett, 1994).
Moreover, antibiotics are given not just to
domestic livestock, but also to honeybees, fish, family pets, and
even to plants and trees (Levy, 1992). For example, various palms
are injected with oxytetracycline to delay or prevent
"lethal yellowing," and chrysanthemum cuttings are
placed directly into an antibiotic solution to deter disease.
Streptomycin is one of the two most commonly used antibiotics on
plants. Streptomycin resistance is now among the most prevalent
resistances found in bacterial strains associated with humans,
possibly tracing to its widespread use on plants. Although the
use of streptomycin in humans is now rare (because of its
toxicity), streptomycin resistance generally occurs in
conjunction with resistance to other antibiotics that are
important in human therapy.
GLOBAL CHANGE
Homo sapiens has been very successful in
developing industrial societies, although it has been very
unsuccessful at spreading the benefits of development equitably
(Ehrlich et al., 1995). But successful development has allowed
the scale of human enterprise to become so large that humanity is
now a global force -- rivalling natural processes in its ability
to modify climate, change landscapes, mobilize minerals, and so
forth (SCEP, 1970; Turner et al., 1990). As a result, the entire
biosphere is being altered in a process generally known as
"global change."
In many people's minds, "global
change" is virtually synonymous with global warming and
climate change. But it includes much more than changes in the
balance of gases in the atmosphere. The growth of the human
population to unprecedented size is itself an aspect of global
change. The modification of every square centimeter of Earth's
surface by human activities is an aspect of global change. So is
the extent of land degradation, which now afflicts over 40
percent of Earth's terrestrial vegetated surface and has caused
the loss of about 10 percent of the potential direct instrumental
value of productive land (Daily, 1995). And, perhaps least
appreciated of all, alteration of the epidemiological environment
is an aspect of global change (Epstein, 1992).
Land Conversion
The threat of "emergent viruses" --
such as HIV, Ebola, Marburg, and Lassa -- traces not just to the
recent dramatic increase in human population size. Rather, it is
that increase, coupled with mass migration into areas only
marginally suited, at best, to intensive agriculture and dense
human habitation, that so increases the chances for eruption of a
"new" disease. Larger and larger human populations,
pushed into contact with animal reservoirs of disease, both
increase the odds that a pathogen will invade human populations
and that the disease will become endemic. In small populations,
diseases would more likely quietly die out as death and immunity
exhausted the supply of susceptible individuals.
Population growth has been especially rapid in
Africa, which had only about 275 million people in 1960, now has
720 million, and may double that population size by 2025. Africa
is the homeland of humanity, and our closest living relatives,
the old-world monkeys and apes, are abundant there.
Evolutionarily, these are the animals most likely to be harboring
parasites, such as Marburg virus, that are capable of infecting
Homo sapiens (Smith et al., 1967; Kissling et al., 1968).
Forest clearance is one of the commonest
land-use changes wrought by Homo sapiens, usually occurring in
connection with agriculture, and it may exert positive or
negative effects on the epidemiological environment. On the
positive side (at least from an epidemiological viewpoint), it
can reduce contact of human populations with forest-dwelling
disease sources or reservoirs, including primates which are among
the most likely sources of emergent viruses.
On the negative side, forest clearance can
bring the Haemogogus mosquitoes that transmit yellow fever among
animal reservoirs in forest canopy into contact with human
beings. That can start yellow fever epidemics, with the disease
being propagated in the human population by the domestic mosquito
vector, Aedes aegypti (Brom, 1977). In Brazil, the most effective
Amazonian vector of malaria is Anopheles darling), a species of
the forest and forest edge. It makes malaria a major hazard for
farmers attempting to colonize the area (Bradley, 1993b).
Clearing primary forest in Tanzania has caused expansion of
malaria by increasing temperatures and creating sunny breeding
sites for the vector Anopheles gambiae. Forest clearance in Latin
America has exacerbated problems with leishmaniasis by increasing
populations of both its mammalian reservoirs and sandfly vectors
(Sutherst, 1993).
Land degradation, including deforestation and
desertification, also exerts a great impact on the
epidemiological environment by contributing to malnutrition
(e.g., Dasgupta, 1993; Daily, 1995; Ehrlich et al., 1995). In
addition, it may promote fungal diseases such as
coccidioidomycosis (valley fever), which is contracted by
breathing spore-laden dust (Sternberg, 1994).
Biodiversity Loss
Land conversion for agricultural purposes is
the paramount direct cause of the ongoing mass extinction
episode. As a matter of convenience, biodiversity loss is usually
quantified in terms of the rate of loss of species diversity. A
conservative estimate of the global rate of species loss is one
extinction per hour (Wilson, 1992), which exceeds by at least
four orders of magnitude the rate of evolution of novel species
(Lawson and May, 1995).
It is important to remember, however that
biodiversity refers to the diversity of life at all levels of
organization -- from the subcellular to the ecosystem level.
Dramatic as the rate of species loss is, the relevant rate here
-- that of the loss of population diversity -- is still orders of
magnitude higher (Daily and Ehrlich, 1995; unpublished analysis).
The benefits that biodiversity supplies to humanity are delivered
through populations of species (Daily and Ehrlich 1995; Daily,
1996). In the extreme, the preservation of just one population of
each of Earth's species in a zoo or park would do humanity little
good, since most people would not have access to it.
Moreover, the diversity of populations is
important for human health. Different populations of the same
species may produce different types or quantities of defensive
chemicals (potential pharmaceutical or pesticide compounds; e.g.,
Dolinger et al., 1973). For example, the development of
penicillin as a therapeutic antibiotic took a full 15 years after
Alexander Fleming's famous discovery of it in common bread mold.
This was in part because scientists had great difficulty
producing, extracting, and purifying needed quantities of it. In
1940, from 500 litres of broth culture scientists were not even
able to extract one-fourth of what was later established as a
single day's treatment of pneumococcal pneumonia. Yet, by 1944
production capabilities had improved so tremendously that all
seriously injured British and American troops could be treated.
One key to this improvement was the discovery, after a worldwide
search, of a variant of Fleming's mold that produced more
penicillin than the original (Dowling, 1977). Thus, population
diversity in the mold Penicillium notatum helped in saving many
lives.
Least appreciated is the impact of destroying
not other life forms themselves, but their interactions. For it
is in these interactions that many clues to the discovery of new
pharmaceuticals lie. It is hard to appraise a weapon of war, or
even recognize its existence, without observing it in use. The
discovery of penicillin by Fleming occurred largely by accident
when, upon returning from a weekend vacation, he noticed that the
mold that had contaminated one of his bacterial cultures was
actually killing the bacteria (Levy, 1992). That is, Fleming saw
the aftermath of the war being waged on his laboratory plates.
Only then did he realize that penicillin is a mold's weapon of
war and that humans might be able to wield it to great advantage,
too.
The magnitude of this problem is difficult to
overestimate. A recent study has shown that 118 out of 150 top
prescription drugs are based on chemical compounds from other
organisms, three quarters of them from plants. In the U.S. nine
of the ten top prescription drugs are based on natural plant
compounds (Dobson, 1995). Yet only slightly more than a thousand
of some 365,000 plant species have even been preliminarily
screened for medicinal compounds. It is impossible to know what
opportunities for pharmaceutical discovery are forever lost with
the destruction of biodiversity -- but the loss is akin to
emptying our armory.
Agricultural Intensification
Recent intensification of agriculture has had
manifold effects on the epidemiological environment. Expansion of
food supplies has had an enormous positive effect (even if
temporary; Ehrlich et al., 1995), but there have been negative
effects as well. Broadcast spraying of synthetic organic
insecticides against crop pests has induced resistance not only
in insects that attack our food supplies, but also in vectors of
disease. This problem was first foreseen by Rachel Carson (1962).
Agricultural spraying, especially on cotton and rice, has
contributed greatly to the evolution of pesticide resistance in
the Anopheles mosquitoes that transmit malaria and thus to the
resurgence of that disease (World Health Organization, 1976;
Chapin and Wasserstrom, 1981; Ehrlich, 1986; Georghiou, 1990).
"In effect, throughout southern India, the recrudescence of
malaria now represents a social cost of growing high-yielding
rice -- just as elsewhere in India and Central America it
represents a social cost of producing cotton" (Chapin and
Wasserstrom, 1981, p. 184).
The switch from subsistence agriculture to
cash-cropping of rice in the Demerara river estuary of Guyana
caused a related and similarly widely manifested deterioration of
the epidemiological environment. Flooded rice fields were ideal
breeding grounds for the local Anopheles vectors, while
mechanization reduced local populations of domestic animals, the
preferred source for the Anopheles's blood meals. The enlarged
population of vectors concentrated on Homo sapiens, and the
result was a malaria epidemic (Desowitz, 1981). In Honduras,
agricultural intensification and associated forest fragmentation
has led to the concentration of disease vectors and reservoirs in
periurban "misery belts", where the incidence of
malaria, leishmaniasis, dengue fever, and Chagas' disease has
increased dramatically (Almendras et al., 1993). Rodents, in
particular, are important consumers of agricultural crops and
players in the life cycle of many groups of diseases, including
bacterial and viral haemorrhagic fevers, tick-borne
encephalitides, Venezuelan equine encephalitis, the hantaviruses,
typhus, and spirochaetal and parasitic diseases. Agricultural
intensification typically promotes rodent populations through the
removal of predators and other natural enemies while
supplementing their food supply (Epstein and Chikwenhere, 1994).
Increases of bilharzia (schistosomaisis) with
the introduction of irrigation following the construction of the
Aswan, Volta Lake (Ghana), and other dams are another example
(Ehrlich and Ehrlich, 1970; Mobarak, 1982; Bradley, 1993b). So
was the epidemic of Rift Valley Fever that ravaged people in the
Aswan area in 1977 (Meegan, 1978). In the first case, perennial
irrigation and large impoundment lakes made possible by the dams
proved ideal breeding grounds for snails that served as
intermediate hosts for the blood flukes that cause bilharzia
(Ehrlich at al., 1977). Thus incidence of bilharzia in the
population along the Nile between Cairo and Aswan increased from
5 percent before the dam to 35 percent after (Van der Schalie,
1974). In the second, the mosquito vector (Aedes
pseudoscutellaris) of a virus causing a hemorrhagic disease
similar to yellow fever built up huge population sizes in newly
irrigated fields. That, possibly linked to the evolution of
increased virulence in the virus (Davies et al., 1981; Monath,
1993) caused a nasty epidemic which killed hundreds of people and
sickened hundreds of thousands.
Water management schemes can either encourage
or discourage the simuliid (blackfly) vectors of onchocerciasis
(river blindness). A dam may destroy the rapids required by
blackfly larvae, and substitute bilharzia (which is easier to
treat) for onchocerciasis (Bradley, 1993b).
Intensification of agriculture in the Pampas of
Argentina led to the introduction of herbicides after World War
II to fight weeds that competed with maize production. The
resultant change in the grass flora favored a mouse, Calomys
musculinus, which was the natural reservoir of the Junin virus,
the cause of Argentine hemorrhagic fever. The disease was
described in 1953 and is still expanding its range (Johnson,
1993). Another viral disease, Oropouche fever, emerged following
the agricultural colonization of the Amazon and the planting of
cacao as a cash crop. The latter makes excellent breeding
conditions for the vector, a biting gnat, Culicoides parasnsis
(Monath, 1993). In contrast, a shift from cattle raising to
subsistence agriculture encouraged another small mouse, Calomys
callosus, in eastern Bolivia, which was the reservoir of the
Machupo virus. The latter invaded the human population causing
Bolivian hemorraghic fever. The cautionary point is this: any
major land-use change is likely to alter the epidemiological
environment in ways that are often difficult to predict.
Ducks, other waterfowl, and shorebirds
(Webster, 1993) are major reservoirs of influenza viruses, and
some flu pandemics are thought to have their origin in integrated
pig-duck farming in China (Morse, 1993). Pigs can function as
"mixing vessels" for new flu strains able to infect
human beings; an agricultural system that puts the reservoir and
the mixing vessels in intimate contact seems bound to degrade the
epidemiological environment. The pig-duck system, in place in
China for several centuries and now being intensified,
constitutes a natural laboratory for generating new flu strains
(Scholtissek and Naylor, 1988) as viruses move back and forth
between human beings and swine and swine and ducks (Webster,
1993). It might have been responsible for the catastrophic
1918-1919 pandemic, possibly the worst single disease catastrophe
ever to afflict humanity in terms of numbers of lives lost in a
short period of time (Kiple, 1993). Even though many strains of
flu that infect birds are genetically attenuated in primate
systems (e.g., Murphy, 1993), such an event could transpire again
(Webster, 1993).
Ozone Depletion
Ozone depletion may also play a role in
reducing food supplies and in directly suppressing immune
responses (e.g., Jones and Wigley, 1989; McCalley and Cassel,
1990; Jeevan and Kripke, 1993). We hope that the steps being
taken to restore the ozone layer will be sufficient to cancel
this possible deleterious effect (e.g., Benedick, 1991).
Climate Change
The likelihood of human-induced, rapid climatic
warming is becoming increasingly clear. The possible magnitude of
the change over the next century could be as large as the change
from 18,000 years ago, when there was a mile of ice over New
York, to today. The regional consequences of global warming are,
at present, impossible to predict in detail. It is almost
certain, however, that such change will alter the geographic
distributions of pathogens, reservoirs, and vectors; the
competitive and predator-prey interactions among them; and the
probability of disease transmission (Smith and Tirpak, 1988;
Weihe and Mertens, 1991; Bradley, 1993a).
Many tropical diseases, whose distributions are
now restricted by climate, may move into the temperate zones
(Haines, 1990; Shope, 1991; Sutherst, 1993) where the majority of
human beings live. Such diseases kill 15-20 million people
annually at present (Gibbons, 1992). Recent modelling efforts
indicate, for instance, that malaria could extend its range by
tens of millions of square kilometers (Martin and Lefebvre, 1995;
Pearce, 1995). This is supported by extensive empirical
information on the coupling of malaria outbreaks and climatic
fluctuations, particularly those associated with the El
Nino-Southern oscillation (Bouma et al. 1994). In addition,
detailed analysis of the 1987 resurgence of malaria incidence in
Rwanda revealed that temperature and rainfall explained 80
percent of the variance in monthly malaria incidence (Loevinsohn,
1994). Climate change appears to have played a role in India's
recent bout with bubonic plague as well (e.g., Epstein, 1994).
This should not lead one to conclude that devastating epidemics
of now-tropical diseases are inevitable concomitants of global
warming. Rather, it should lead to the conclusion that such
epidemics are possible, should be guarded against, and could be
better anticipated by careful monitoring of climatic changes,
especially at the latitudinal and attitudinal limits of diseases
(Gillett, 1974; Rogers and Packer, 1993).
A more general lesson pertinent to the impacts
of both development and global change on the epidemiological
environment is that any large-scale change in an ecosystem can
greatly affect the health of human beings involved in that
ecosystem. Drainage of swamps, screening of houses, and general
improvements in sanitation and nutrition had yellow fever and
malaria on the retreat in the southern U.S. and malaria receeding
from southern Europe long before the etiologies of those diseases
were understood. On the other hand, an unusual weather sequence,
not clearly associated with any human activity, caused major
changes in the ecosystems of the southwestern United States in
1992 and 1993. Exceptionally wet weather broke a six-year drought
in the spring of 1992 and caused superabundant production of
pinyon-pine nuts, which in turn led to an outbreak of deer mice
(Peromyscus maniculatus). The abundant urine and feces of those
mice carried a previously unidentified strain of hantavirus,
which caused an outbreak of often-fatal respiratory disease in
1993, especially among those on Navajo reservations (Nichol et
al., 1993; Hughes et al., 1993).
Alterations of marine ecosystems accompanying
climatic change may also cause unpleasant changes in the
epidemiological environment (Epstein, 1992; Epstein et al.,
1993). We can only guess what warmer climate and rising sea level
might mean to the strains of Vibrio cholera e that live in the
bays and estuaries of the Gulf Coast of the United States that
serve as a reservoir for cholera (Shope, 1991).
Important as those changes may be, it is likely
that the impact of climate change on agricultural production will
constitute its most important influence on the epidemiological
environment. Rapid climatic change could very much reduce
humanity's ability to keep food supplies up with expanding
populations (Daily and Ehrlich, 1990; Ehrlich et al., 1995). More
widespread malnutrition would increase the proportion of the
population that is immune compromised, further worsening our
position in the coevolutionary race against pathogens.
WHAT ARE THE RISKS?
There is increasing evidence that the
epidemiological environment has played a major role in shaping
human history -- for example, allowing the easy conquest of the
western hemisphere by Europeans and preventing a similar sequence
of events in Africa (McNeill, 1976, 1993). If humanity does not
exercise more caution, diseases could reassert their historic
influence. The AIDS situation in Central African nations may
already be so bad that population growth there will be reversed
by AIDS mortality itself (Anderson et al., 1991). But one always
must be aware that direct mortality caused by a pathogen now may
only be the tip of the iceberg. Social breakdown has accompanied
epidemics in the past, and our limited experience with more
recent ones gives little reason to expect human behavior to be
different (e.g., Hudson, 1979). In highly centralized modern
societies, starvation could quickly follow plague if the latter
led to disruption of transport systems.
At the very least' disease is costly in
economic terms, and problems with the epidemiological environment
retard development processes which already face great
difficulties. For example, preventing deformity in India's
645,000 lepers would have increased the nation's 1985 GNP by some
$130 million, equivalent to about 10 percent of the external aid
the nation received at that time. Yet leprosy amounted to less
than 1 percent of India's disease burden (World Bank, 1993). The
global burden of disease, defined as the present value of the
future stream of disability-free life lost as a result of death,
disease, or injury, is already huge. For 1990 it was estimated at
1,362,000,000 disability adjusted life years (DALYs), 259 DALYs
per thousand in the population, or the equivalent of 42 million
infant deaths. Any substantial increase in the disease burden of
the global population would be an economic as well as a human
catastrophe.
It is easy to underestimate the danger of such
a catastrophe (Hudson, 1979). One could conceivably be caused
simply by an increase in the virulence of a common pathogen.
Webster (1993) describes a flu virus in chickens that suddenly
became highly lethal in Pennsylvania in 1983 -- wiping out all
the chickens in some rearing facilities. "The Agriculture
Department used the standard methods of eradication, killing the
infected chickens and the exposed neighboring birds and burying
the carcasses. But we can't help asking ourselves what we would
have done if this virus had occurred in humans. We can't dig
holes and bury all the people in the world" (p. 41). Webster
goes on to point out that when he tried the anti-viral drug
amantadine on chickens infected with the virus, the highly
mutable virus (Palese, 1993) became resistant within a week.
"Battery" chicken rearing facilities should be an ideal
environment for evolving highly lethal strains of diseases not
transmitted by vectors (Ewald, 1994), and (as we have pointed out
-- Daily et al., 1994) many people seem determined to move
humanity into a condition parallel to that of battery chickens.
WHAT SHOULD BE DONE ?
It has long been recognized that a fundamental
problem in health care in developing countries is that
"curative care is emphasized while prevention and early
treatment are neglected" (World Bank, 1980, p. 7). That
remains a critical problem, but not just in poor nations. While
much attention is paid in rich nations to prevention of cancer
(but not enough to suppress smoking, its most important known
cause), support of efforts to prevent infectious disease is
actually declining in the United States and perhaps elsewhere.
There are few barriers today between rich and
poor to stop the spread of epidemic disease. That Ebola, Marburg,
Lassa fever and a host of other "emergent" viruses have
not yet become established outside Africa may be primarily a
matter of luck. There has been no such luck with HIV. Similarly,
the evidence is abundant that pathogens evolving resistance to
the weapons humanity develops to counter them can share that
ability with other pathogen populations globally (Tauxe et al.,
1990; Cohen, 1992).
The situation with tuberculosis (TB), the
global leader among infectious diseases in causing death (almost
3 million annually, mostly in Asia and Africa), is alarming
(Bloom and Murray, 1992; Brown, 1992). Drug-resistant strains are
emerging that threaten to make it impossible to control the
disease; a third of New York City's cases in 1991 were resistant
to one or more drugs, and the fatality rate of those infected
with strains resistant to two or more major antibiotics is 40-60
percent, roughly that of untreated cases (Bloom and Murray,
1992). TB is resurgent for a number of reasons in addition to
drug resistance. It is a "sentinal disease" for AIDS
because a large portion (about one-third -- Brown, 1995) of the
human population is infected by Mycobacterium tuberculosis
asymptomatically, and TB commonly becomes patent when the immune
system is depressed (the annual risk of infected people
developing the disease if they are HIV positive is roughly the
same as the lifetime risk if they are not coinfected with HIV).
TB is primarily spread via droplets released in speaking and
coughing. Increased crowding, poverty, HIV infection, drug
resistance, the difficulties of doing research on the causitive
organism, and a decline of public health services (Bloom and
Murray, 1992) make it one of the major threats to health in both
rich and poor nations.
It therefore is in the interest of both rich
and poor to start altering the epidemiological environment to
give Homo sapiens as much of an edge as possible in its
coevolutionary race with pathogens. Some steps are obvious:
First and foremost, the medical community,
decision makers, and the general public must, as far as possible,
be made aware of the evolutionary and ecological dimensions of
the human health situation. In the short run, that requires media
cooperation, but in the long run it means much more attention
should be paid to evolution and ecology in schools -- especially
in medical schools. Unless there is general understanding of the
perpetual ability of microorganisms to evolve in response to
human biological and cultural evolution, people will continue to
seek "magic bullet" cures for infectious diseases. That
is a strategy usually doomed to eventual failure and it could
potentially be a recipe for catastrophe. Humanity will win its
coevolutionary race with some pathogens (the best example is the
smallpox virus), continue it with others, and enter into new
races with emerging pathogens. What must be avoided is losing
races.
Physicians by instinct and training focus on
the health of individuals; they must learn to pay more attention
to the health of whole societies and to deal with the difficult
conflicts of interest that often arise between the two. One
physician, Jeffrey Fisher (1994), recommends that physicians be
required to take periodic recertification exams in which they are
tested on antibiotic knowledge. If antibiotics had been used more
judiciously over the past few decades, there doubtless would have
been more deaths from bacterial infections misdiagnosed as viral,
and fewer deaths from allergic reactions to antibiotics. But a
small net increase in deaths would probably have been a
reasonable price to pay to avoid the present situation, which
portends a return to the pre-antibiotic era and much higher death
rates.
Public education is essential as well. Public
pressure in the United States and elsewhere has led to the
stigmatization of AIDS victims on one hand and (at least in the
U.S.) the treatment of the HIV pandemic as a civil rights rather
than a public health issue. Certainly there should be heavy
penalties for revealing publicly that an individual has AIDS, but
AIDS testing of all blood and making medical personnel alert to
seropositive patients is essential. Lack of data is a major
reason that it is extremely difficult to predict the course of
the AIDS epidemic (e.g., Chin, 1995). In general, much greater
emphasis should be placed on interdicting the spread of pathogens
rather than, as has been the case since World War II, treating
people after infection.
If humanity is to mount a coordinated
ecological-evolutionary response to infectious disease, it must
have the infrastructure necessary to implement it. We think this
means strengthening the Centers for Disease Control in the United
States and similar institutions in other nations, and finding
ways to minimize bureaucratic delays and turf wars within them
and within the global coordinating body, presumably the World
Health Organization.
The steps required on the front lines cannot be
exhaustively listed here, but some of the more obvious include:
1. Redoubling efforts to halt the growth of the
human population and eventually reduce it to an optimum size
(Daily et al., 1994). This is a very basic step, since
overpopulation makes substantial, diverse contributions to the
degradation of the epidemiological environment, in addition to
degrading other aspects of Earth's carrying capacity (Daily and
Ehrlich, 1992).
2. Establishing early warning networks
(including comprehensive monitoring and reporting systems) and
expert response teams to improve the chances of promptly
detecting and limiting potential viral epidemics (Henderson,
1993) and sharing information on drug resistance (Gibbons,
1992b). At the moment policies seem to be moving backwards.
Overconfidence, leading to funding cuts at federal, state, and
local levels, for example, has compromised infectious disease
surveillance in the United States (Barbour and Fish, 1993;
Altman, 1994; Berkelman et al., 1994).
3. Encouraging governments to develop
well-funded and well administered national vaccination programs
(e.g., Bloom, 1994; Fisher, 1994). Vaccines are the cheapest,
most efficient method of disease prevention (World Bank, 1993).
4. Finding workable methods of encouraging
governments and pharmaceutical companies to put more effort into
vaccine research (Cohen, 1994), to maintain a high level of
preparedness for producing vaccines, and to develop drugs for
dealing with tropical diseases and drug-resistant strains of all
pathogens. The situation today is not encouraging. Even in the
United States, government funding of research on antibiotics is
inadequate (e.g., Culotta, 1994). At present, pharmaceutical
houses are not anxious to do work on either vaccines or new
antibiotics (Gibbons, 1992a, b) for economic reasons. With the
possible exception of Mycobacteriumterium tuberculosis,
resistance problems are still most serious in developing nations
-- in rich countries, physicians usually can still find (at a
price) an antibiotic that still works (see, however, Altman,
1995).
The numbers tell the story. It costs a company
about $200 million to bring a new drug to market, and the drug
will not make a profit if it is of use primarily in poor
countries (Gibbons, 1992b). Japan spends over $400 per person
annually on drugs, and Germany and the United States about $200
each. The world average is about $40, but very poor countries
spend much less -- Kenya only $4 per person, India $3, Bangladesh
$2, and Mozambique $2 (Ballance et al., 1992). Contrast these
expenditures with the need for $13 per treatment to deal
effectively with a standard case of TB (Brown, 1995) or the
$25,000 worth of antibiotics that had to be prescribed for one
physician who was infected by a multidrug-resistant strain of the
TB Mycobacterium (Brown, 1992b).
A vaccine for malaria could restore to health
the roughly 5 percent of the human population currently afflicted
with that debilitating disease. The overall economic gains would
be enormous, creating a vaccine is clearly feasible (Nussenzweig
and Long, 1994), and effective control might be achieved at
levels of vaccination much lower than previously expected (recent
work suggests that malaria transmissibility, a primary
determinant in effective levels of vaccination, may be much lower
than inferred earlier; Gupta et al., 1994). But whether success
can be had at an acceptable price (which might involve the costs
of continuous vaccine modification to keep up with rapidly
evolving plasmodia) is an open question. On top of the problem of
ability to pay for drugs and vaccines is an extremely serious one
of liability of drug companies. Fear of gigantic awards by juries
dampens the enthusiasm of pharmaceutical houses for producing
novel products likely to become the subject of law suites.
How well cultural evolution, mediated by
molecular biologists, can keep us with the biological evolution
of resistance in bacteria, fungi, and protozoa is an open
question -- unless we choose to lose the coevolutionary race by
failing to devote adequate resources to it. The screening of
microorganisms, plants, and animals for new antibiotics should be
accelerated. So should research on "rational drug
design" in which understanding of the modes of acquiring
resistance is used to create or modify drugs to counter it (e.g.,
Taylor, 1993; Travis, 1994; Spratt, 1994; Amabile-Cuevas et al.,
1995) as well as other novel ways to eliminate or slow the spread
of resistance.
5. Developing global strategies of highly
targeted and minimal antibiotic and pesticide use, and the
imposition of moratoria, to slow the development of resistance
and thus extend the life of some of our most potent antimicrobial
and antivector weapons (e.g., Gerding et al., 1991; Haley et al.,
1985; Amabile-Cuevas et al., 1995). All nations should move to
restrict unsupervised access of people to antibiotics. In
addition, the U.S. and all other nations should follow Europe's
and ban all antibiotic use in animal feed (Levy, 1992). Indeed,
it would be very beneficial for human health if grain-feeding of
animals were greatly reduced, since the damage done by saturated
fats in the diets of the rich is becoming increasingly clear.
Basically the principles of integrated pest
management (IPM; e.g., Flint and van den Bosch, 1981) should be
extended to all enemies of Homo sapiens. In essence, IPM consists
of using a variable mix of measures tailored to specific
situations and modified as needed. IPM requires more knowledge
and better management than traditional "magic bullet"
approaches to pest control, but can be more successful in the
long run and produces fewer negative side effects. For example,
used in place of massive spraying of DDT and other pesticides in
rice and cotton agriculture, IPM can help reduce problems of
insecticide resistance in malaria vectors (Chapin and
Wasserstrom, 1981). Indeed, today the scientific community is
recommending what is basically IPM as the strategy for dealing
with resurgent malaria (Oaks et al., 1991). One promising method
of controlling malaria involves engineering and disseminating
strains of Anophel es that disable malaria parasites (Aldhous,
1993). Some Anopheles species might be controlled in that manner,
and others by habitat modification and judicious use of
pesticides when necessary (e.g., Oaks et al., 1991; Collins and
Besansky, 1994). In conjunction with such vector control,
increased sceening and bed nets, improved treatment of severe
cases (Miller et al., 1994), and a moderately successful
vaccination program might eliminate malaria as a public health
problem. IPM techniques show great promise for controlling many
parasitic diseases (Kolberg, 1994), but research programs in
parasitology to develop the needed techniques are in jeopardy
from the current financial drought (Aldhous, 1994).
Much more research is also needed on such
topics as the relationship of drug resistance to virulence and
the impacts of the use of antibiotics against resistant strains
on the competitors of those strains. The entire topic of the
evolution of virulence and transmissibility is just beginning to
be explored (e.g., Anderson and May, 1979; Dwyer et al., 1990;
Johnson, 1986; Lenski, 1988; Read and Harvey, 1993; Herre, 1993;
Ewald, 1988; 1994) and remains controversial (e.g., Bull and
Levin, 1994), although there can be little question that
virulence (or benignness) is often an evolved strategy of a
pathogen, although in some cases it is almost certainly
evolutionarily neutral (or close to it). More research on
virulence and transmissibility is required at levels ranging from
mathematical modeling of demographic and evolutionary dynamics of
diseases to investigation of the molecular mechanisms of
pathogenicity.
Why, for example, should pneumonic plague be so
much more deadly than bubonic (Mee, 1990) if Ewald's view of the
evolution of virulence is correct? This is but one of the
enduring mysteries about this disease (McEvedy, 1988). Might HIV
evolve towards droplet transmissibility, and if so would it still
cause AIDS (Ehrlich and Ehrlich, 1990, pp. 147-148)? What are the
chances that viruses such as Ebola and Marburgvirus might evolve
the ability to be transmitted by mosquitoes, ticks, or other
arthropods to end-run the transmission handicap of being so
virulent (Ewald, 1994)? If they did become arboviruses, would
that prevent a predicted evolution toward lower virulence? Why
are helminth parasites so readily able to evade or modulate the
immunological defenses of human beings (Maizels et al., 1993)?
6. Instituting worldwide campaigns designed
both the slow the spread and control the virulence of pathogens
(e.g., Ewald, 1994), especially those that are generally not
vector-borne. The prototypical campaign, already in place in some
areas, are campaigns against AIDS to promote condom use and
lessen the number of sexual contacts. In China and elsewhere,
integrated aquaculture systems should be modified to isolate
waterfowl from swine, in order to reduce the chances of evolution
of novel flu strains (Scholtissek and Naylor, 1988).
7. Instituting worldwide campaigns to emphasize
limiting the number of sexual partners, and to increase the use
of condoms and spermicides. Such changes would both to lower the
incidence of STDs and encourage the evolution of reduced
virulence in them (Ewald, 1994). Special attention should be paid
to methods that can be adopted by women (e.g., Rosenberg and
Gollub, 1992; Rosenberg et al., 1992; Rosenberg et al., 1993),
which should tie in neatly to related methods of improving the
epidemiological environment by limiting human population growth
(Ehrlich et al., 1995).
8. Designing cheap, disposable syringes that
self-destruct after one use for distribution to intravenous drug
abusers (while supporting programs to prevent such abused.
9. Upgrading facilities in hospitals worldwide
so that, for instance, no health worker is required to reuse an
unsterilized syringe. It is imperative that the frequency of
nosocomial infections be sharply reduced.
10. Making massive efforts worldwide, after
decades of talk, to provide adequate diets, pathogen-free
drinking water and sound sanitary facilities to everyone.
11. Providing international aid for the
upgrading of hospital buildings and dwellings in poor nations so
that access of arthropod vectors and rodents to infected persons
is greatly restricted. Screened homes will be more effective
(both epidemiologically and economically) against many serious
vector-borne diseases than bed-nets, antibiotics, or (in some
cases) vaccination. They are difficult defenses for vectors to
evolve around, and they are not heavily dependent on the behavior
of susceptible human beings for their effectiveness.
12. Persuading the leadership of both developed
and developing countries that infectious disease prevention and
treatment must have higher funding priority. Providing aid to
poor countries is essential. It has been estimated that the
expenditure of the required $13 per patient on tuberculosis could
save more than a million people per year over the next decade
(Brown, 1995; Economist, 1995).
The last few steps are so basic that it seems
almost foolish to reiterate them here. They are classic "no
regrets" strategies that humane people have long recommended
without knowledge of potentially serious degradation of the
global epidemiological environment. Well-educated people in
developed countries will realize that such steps are in their own
immediate self interest. But they will not be simple to take in
the face of continued expansion of the human enterprise in
general and population growth in particular.
There is no question that improved water
supplies and sanitation still have great potential for improving
the epidemiological environment; there is a question of how long
such improvement can be continued. It is likely that the quality
of water supplies is already declining in developed countries.
Half a century ago surface water could safely be consumed in most
sparsely inhabited areas of the United States. Now Giardia
presents a threat almost everywhere. Pathogens are becoming
increasingly resistant to chlorine (Russell, 1993; Levy, 1992;
Nikaido, 1994), and disease episodes traceable to treated but
still contaminated municipal supplies seem to be on the rise. In
1993 the Natural Resources Defense Council estimated that nearly
a million Americans were getting sick annually and some 900 dying
because of drinking water contamination (see summary in Garrett,
1994, pp. 428-430). A spread of chlorine resistance would be a
global public health disaster, since there seem to be no
economically viable substitutes on the horizon, and increasing
doses of chlorine would add more carcinogens to the water supply
via the chemical reactions of the chlorine with contaminants in
the water.
This nexus of tasks amounts to an unprecedented
opportunity for interdisciplinary cooperation. Important social
and economic issues regarding the efficient allocation of funds
among alternative disease-control strategies remain little
analyzed. At the most basic level, for example, how would the
benefits of concentrating spending on slowing population growth
or improving the water supply compare to benefits derived through
better funding of other public health measures, such as improving
a population's nutritional status, its female educational status,
or its access to maternal health care? These gruesome tradeoffs
are made all the time, but often without consideration of impacts
on the epidemiological environment, or analysis of the nexus of
interactions among possible interventions. Other key issues, such
as the economics of the complex of benefits and costs (especially
negative externalities) associated with the evolution of
antibiotic resistance, remain largely unaddressed by economists.
Doing the required analyses, and implementation of the
recommendations enumerated above, represent a gigantic challenge
to physicians, ecologists, epidemiologists, economists,
pharmacologists, molecular biologists, chemists, sanitary
engineers, political scientists, sociologists, and all others
professionally involved in the maintenance of public health.
CONCLUSION
Recently, the eminent historian of disease,
William H. McNeill stated: "The possibility of really
drastic epidemiological disaster bringing a halt to the modern
surge of human population seems to me something we all should
take very seriously... [In very short time], we have doubled in
number. A marvelous target for any organism that can adapt itself
to invading us" (1993, p. 33-34). We agree, although a
worldwide epidemic would be a most undesirable and inhumane way
to end the population explosion. But ending that explosion
humanely is a step that is absolutely necessary (but not
sufficient -- Ehrlich and Ehrlich, 1990) if the health of our
life-support systems and of ourselves is to be preserved.
Simultaneously, we should be taking all the other steps listed
above to improve the epidemiological environment. To solve all of
these problems, it is essential that equity of opportunity
between sexes, races, region, religions, and nations be increased
(Ehrlich et al., 1995). That is something that is in the vital
interest of both the rich and the poor.
ACKNOWLEDGEMENTS
We thank Angela Kalmer for substantial
help in searching the literature. Alan Campbell, Anne H. Ehrlich,
and Donald Kennedy (Department of Biological Sciences, Stanford),
Stanley Falkow (Department of Microbiology and Immunology,
Stanford), Peter Bing, MD (Los Angeles), and Charles Daily, MD
(San Rafael) were kind enough to read and criticize the
manuscript. This work has been supported in part by a grants from
the W. Alton Jones, Winslow, and Heinz Foundations and the
generosity of Peter and Helen Bing.
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