Chlorination,
Clean Water and the Public Health Progress that Changed
America
20th
Century Lessons-Learned for 21st Century Developing
Nations
At
the start of the twentieth century, high mortality
rates and substandard living conditions were commonplace
in urban America. Mortality rates in major cities
were substantially higher than in rural areas, a phenomenon
known as the "urban penalty". Yet by 1940, mortality
rates had declined by a full 40 percent, mostly due
to a reduction in infectious diseases. In addition,
the urban penalty had largely disappeared, with life
expectancy rising from 47 to 63 years.
What
fostered this rapid and revolutionary change, the
most dramatic reduction in mortality ever recorded
in the United States? There has been much debate on
this question, but to-date relatively little empirical
data to provide a verifiable answer. However, a new
study by two Harvard University researchers, David
Cutler of the Department of Economics and Grant Miller
of the Health Policy Program, finds the most compelling
root cause for the drop in U.S. mortality rates in
the twentieth century was the adoption of treatment
technologies for public drinking water supplies.
In their recent article, "The Role of Public Health
Improvements in Health Advances: The Twentieth Century
United States,"1 Cutler and Miller
conclude that clean water technologies, filtration
and chlorination, were responsible for nearly half
of the total mortality reduction in major cities
between 1900 and1936, with even greater impact on
infant and child mortality rates during that same
time period. Significantly, these technologies led
to the near-eradication of typhoid fever, the waterborne
disease that was one of the major scourges of that
era.
Considering
the cost of water infrastructure and the value of
reduced mortality, Cutler and Miller's analysis also
concludes that clean water technologies were not only
a boon to public health, but were tremendously cost
effective in doing so. Their data demonstrate that
these technologies, working together, yielded an estimated
$23.00 in benefits for every $1.00 invested.
Applying these findings to today's world, the authors
suggest a potential for tremendous public health and
individual wellness benefits from adopting inexpensive
water disinfection technologies in developing nations.
The
Adoption of Clean Water Technologies
In
the later half of 19th century, many large U.S. cities
had municipal water and sewer systems. As Cutler and
Miller note, however, these early systems did not
include treatment and did not prevent significant
outbreaks of waterborne diseases. In fact, drinking
water quality deteriorated, due to the dumping of
untreated sewage into rivers and lakes used as source
water. Often, primary sewer outfalls emptied upstream
or in close proximity to water intakes. Even the few
cities that addressed this problem early suffered
from the dumping of untreated sewage by upstream communities.
While
modern sewage treatment was not widely adopted until
the 1930's and 1940's, many major U.S. cities adopted
clean drinking water technologies by 1920. Two major
methods of filtration, slow sand and rapid (or mechanical),
emerged. Originally designed to reduce turbidity,
discoloration, and bad taste, these methods were also
found to improve the microbial quality of water. However,
it was clear that filtration did not remove all the
bacteria from public-use water. Complimentary disinfection
processes were evaluated to expand the effect of clean
water on urban populations. Found to be the least
costly option, chlorination was rapidly and widely
adopted. The first significant adoption of water chlorination
took place at the Boonton Reservoir of the Jersey
City, New Jersey waterworks in 1908, with most major
cities following suit in the ensuing decade.
Impact
of Clean Water on Public Health
To
measure how clean water affected mortality, Cutler
and Miller matched municipal-level mortality statistics
to knowledge of where and when filtration and chlorination
were adopted. By examining changes in mortality just
around the time that filtration and chlorination were
introduced in each city, they were able to distinguish
these impacts from other changes occurring during
the same time period (such as knowledge of appropriate
personal health practices). The final study sample
included thirteen cities where sufficiently complete
and reliable data were available: Baltimore, Chicago,
Cincinnati, Cleveland, Detroit, Jersey City, Louisville,
Memphis, Milwaukee, New Orleans, Philadelphia, Pittsburgh,
and St. Louis.
In
the absence of national death records prior to 1933,
Cutler and Miller utilized several research sources,
including data from both an official "death registration
area" comprised of 10 states and several "registration
cities" outside of those states. U.S. Census Bureau
monthly statistics, broken out by city, cause and
age, were also referenced as the base of their analysis.
While reported deaths from waterborne disease were
not a fixed statistic, as many died from variations
of diarrheal disease, the authors found that deaths
from typhoid fever were a recognized and consistently
registered cause of death during the era. Typhoid
fever then serves as a marker for other waterborne
and diarrheal diseases, which are estimated to account
for four times as many deaths as typhoid fever alone.
In the studied cities, major infectious disease and
childhood infectious disease rates plummeted in the
first decades of the century, including a massive
decline in tuberculosis and the near-eradication of
typhoid and malaria (see Table 1).
|
TABLE
1 -- Percentage of Deaths, by Cause, in Major
Cities
|
| Cause
of Death |
1900
|
1936
|
| Major
Infectious Diseases |
39.3
|
17.9
|
| Tuberculosis |
11.1
|
5.3
|
| Pneumonia |
9.6
|
9.3
|
| Diarrhea
and enteritis |
7.0
|
n/a
|
| Typhoid
Fever |
2.4
|
0.1
|
| Meningitis |
2.4
|
0.3
|
| Malaria |
1.2
|
0.1
|
| Smallpox |
0.7
|
0.0
|
| Influenza |
0.7
|
1.3
|
| Childhood
Infectious Diseases |
4.2
|
0.5
|
| Measles |
0.7
|
0.0
|
| Scarlet
Fever |
0.5
|
0.1
|
| Whooping
cough |
0.6
|
0.2
|
| Diptheria |
2.3
|
0.1
|
| Source:
U.S. Census Bureau's Mortality Statistics, 1900
and 1936. |
Cutler
and Miller found that filtration and chlorination
together reduced mortality by an average of 13%, infant
mortality by 46% and child mortality by 50% in major
U.S. cities. This accounts for about 43% of the total
reduction in mortality observed in these cities from
1900 to 1936. Even more striking, clean water appears
to have been responsible for 74% of the reduction
in infant mortality and 62% of the reduction in child
mortality (see Table 2).
|
TABLE
2 -- Effect of Filtration and Chlorination
on Mortality
|
| |
Total
Reduction in
Mortality Rate 1900-1936
|
Share
of Total Due
To Clean Water
|
| Typhoid
Mortality |
96%
|
91%*
|
| Total
Mortality |
30%
|
43%
|
| Infant
Mortality |
62%
|
74%
|
| Child
Mortality |
81%
|
62%
|
| *
Achieved five years after adoption of clean
water technologies |
Nearly
all of the mortality declines are accounted for by
reductions in infectious disease, which caused nearly
half of all deaths in 1900 but account for only a
small fraction of deaths today. Most notably, clean
water appears to have reduced typhoid fever deaths
by 26% initially and by another 65% after five years,
leading to the near-eradication of this killer disease
by 1936. Cutler and Miller suggest that clean water
reduced other infectious diseases, including pneumonia,
tuberculosis, and meningitis.
The
Economic Impacts of Clean Water
What
is the financial impact of providing clean water and
reducing disease to a society? As part of their study,
Cutler and Miller estimated the economic benefits
of these striking reductions in disease mortality.
To
do so, Cutler and Miller estimated the cost of a water
system serving 100,000 persons to be $30 million per
year (in 2003 dollars). Using the mortality reductions
indicated by their research, they also calculated
the annual number of deaths prevented by clean water
technologies (1,484), the number of person-years saved
(57,922), and the associated annual benefits ($679
million, in 2003 dollars).
The
result? Cutler and Miller demonstrate in their study
that the introduction of clean water technologies
produced an eye-popping estimated rate of return of
23:1. This means that the duel clean water technologies
of filtration and chlorination provide $23.00 in benefits
for every $1.00 invested in clean water. Significantly,
this statement of value does not tell the entire economic
impact story of clean water technologies. The additional
fact is that these estimates exclude the considerable
ancillary benefits of clean water for public use,
including overall reduced illnesses and productivity
gains in the general population.
Conclusions
Cutler
and Miller's analysis demonstrates the strikingly
large and cost-beneficial role of clean water technologies.
The period examined was the era of the most rapid
documented decline in mortality in American history,
and clean water appears to have played as large a
role as any force responsible for this rapid progress.
Although findings from the early twentieth century
in the United States cannot be compared directly to
the current circumstances of developing countries,
the results give some indication of the tremendous
health and economic gains achievable through clean
water technologies. Worldwide, roughly 1.1 billion
people lack access to safe water and 1.7 million people
die every year from diarrheal diseases. Applying results
from their analysis, and assuming that only 1% of
the annual deaths from diarrheal diseases could be
prevented by water disinfection, Cutler and Miller
estimate the corresponding social rate of return would
be about $160 billion annually.
End
Notes
1Cutler,
D. and Miller, G. (February, 2005). The Role of Public
Health Improvements in Health Advances: The Twentieth-Century
United States. Demography, vol. 42, no. 1,
1-22.