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Drinking
Water & Health Newsletter
Winter 1997
Table
of Contents
A Global Decline in Microbiological Safety of Water
Washington Update
Drinking Water Infrastructure Needs Survey - EPA Report to Congress
Chloroform: Research Findings Support Risk Reassessment
State of the States
Water Relief Network Helps Cuban Hurricane Recovery Effort
Jump In, the Water's Clean
A
Global Decline in Microbiological Safety of Water
by Timothy E. Ford, Ph.D.
In April 1995, the American Academy of Microbiology (AAM) convened an
international conference on water quality and safety in Guayaquil, Ecuador.
Attended by 65 scientists from 12 countries, the participants represented
a range of disciplines: public health microbiology, ecology, economics,
microbial (including molecular biology) methods, epidemiology and journalism.
The goal of the conference was to develop a report on needs, from policy
and scientific viewpoints, concerning microbial risks in drinking water.
I was privileged to chair the Steering Committee that organized the conference
and to join with Dr. Rita Colwell, chair of the AAM Board of Governors,
in preparing its final report, "A Global Decline in Microbiological Safety
of Water." The report's purpose was to raise awareness about the importance
of microbiological quality of water and the impact of waterborne disease
on society. This "Call to Action" is summarized below.
The spread of cholera in tropical nations and cryptosporidiosis outbreaks
in temperate regions are clear evidence of an increase in waterborne disease
worldwide. However, these represent only two of a multitude of waterborne
pathogens that are increasingly prevalent in both developing and developed
countries. These pathogens not only cause infectious disease, but many
have been linked to other health outcomes ranging from impaired development
to heart disease and cancer. We predict that the microbiological safety
of drinking water will be a major concern in the 21st century as much
of the world's population still lacks access to quality water supplies.
The severity of the problem is largely underestimated, not only by the
public but also by decision makers and the scientific community.
Pathogen
Control and Water Treatment
Waterborne transmission of pathogens can be reduced by watershed protection,
proper handling of wastewater, and drinking water treatment that removes
and/or inactivates pathogens.
Current water treatment methods for both wastewater and drinking water
are adequate, but are often not applied, are poorly applied or are not
sufficiently monitored and controlled. In developing countries, the use
of the simplest types of treatment will result in significant improvements
in human health.
In developed countries, the range of treatment options is generally more
diverse even though treatment processes must still be properly maintained,
monitored and operated. Inadequate, interrupted or intermittent treatment
has repeatedly been associated with waterborne disease outbreaks. There
is also increasing concern about pathogens that resist water treatment
and disinfection. The combined use of disinfectants -- for example, pre-ozonation
following by post-treatment chlorination -- may achieve better inactivation
of pathogens. The deteriorating conditions of our cities' distribution
systems make it critically important to maintain residual disinfection
to prevent recontamination. At present, chlorination provides the most
effective residual disinfection, although biofilms that sometimes form
in distribution pipes can protect pathogens from residual chlorine. There
is a clear need for further research on how to prevent pathogen survival
and proliferation in drinking water biofilms.
Competing
Health Risks
Health risks posed by microbial pathogens should receive the highest priority
in water treatment. Pathogens responsible for a large percentage of waterborne
disease are often of unknown origin and must be the focus of the search
for new knowledge about microbiological safety of water.
Toxicity of disinfection by-products (DBPs) in drinking water has recently
received considerable public attention. However, chlorine and other reactive
chemicals have been used successfully for more than 80 years to control
waterborne infectious diseases before it was recognized that they produce
a variety of by-products. Some by-products have been found to be associated
with a variety of toxicological effects when administered at high doses
to laboratory animals. While the collective epidemiological and toxicological
data suggest that there may be some risk to human health associated with
DBPs, the magnitude of these risks is very uncertain. It is important
to point out that there is no direct or conclusive evidence that DBPs
affect human health at concentrations found in drinking water.
Concerns over the toxicology of DBPs should not be allowed to compromise
successful disinfection of drinking water, at least without data to support
such decisions.
Public
Policy and Economics
In a time of increasing demands on public funds and resources, policymakers
in developed countries will be challenged to make decisions that ensure
safe drinking and source water. This raises the issue of how to quantify
the economic importance of good quality water. The recent outbreaks of
cryptosporidiosis in the United Kingdom, United States and Canada offer
good examples of the potential consequences of providing contaminated
water in a developed country.
For developing countries, the massive cholera epidemics in Latin America
and Southeast Asia constitute a significant increase in waterborne disease
outbreaks and fatalities, with devastating consequences in terms of human
suffering and both local and national economies. The growth in urban,
underserved and susceptible populations has outstripped sanitation and
water supply, resulting in further outbreaks.
Consistent economic underrating of the true value and costs of water has
been recognized as one of the root causes of the deplorable state of many
water supplies. The economic value of clean water needs to be recognized
as an important force to drive local governments and global associations
into action. Accurate valuation of clean water is necessary if costs and
benefits are to be correctly estimated.
Education
Improving human health requires a massive effort in public education and
raising awareness via the media and schools. In both developed and developing
countries, educational efforts should target government authorities, legislators,
administrators, industrialists, community leaders, teachers, journalists
and the general population.
The public must understand that water safety is important to the quality
of life. In developing countries, it is critical to educate the population
about good hygiene, maintenance of water delivery systems and safe storage
of water in the household.
The media are the main avenues for communication with the public, community
leaders and politicians. However, the media may be either generally ill-informed
or even misinformed. Authorities must be completely open and candid about
potential public health hazards and involve the press on a regular basis,
rather than occurred.
We are failing to educate individuals at the graduate level in waterrelated
disciplines. Research funding is insufficient to address the critical
questions of pathogen recognition and control that must be addressed if
we are to reduce the global burden of waterborne disease in a timely manner.
Research and training programs must be a priority for governmental, non-governmental
and international funding agencies, together with water-related industries.
Conclusion
Water is a requirement for life. Access to water must be viewed as a fundamental
human right, with important implications for national and international
policy. Water resources, distribution, allocation and safety will rise
to the top of the agenda of priorities for all nations as we approach
the 21st century.
It is a time for action, for response to the warning signals that are
occurring throughout the world. Microbiologically safe drinking water
can no longer be assumed, even in the United States and other developed
countries. Without early action at the national and international levels,
global epidemics of waterborne disease will become the rule, rather than
the exception.
Timothy
E. Ford, Ph.D., is an Associate Professor of Environmental Microbiology,
Department of Environmental Health of the Harvard School of Public Health.
In addition to other research into microbiological contaminants and waterborne
disease, Dr. Ford is developing an international program in water pollution
and drinking water quality.
Washington
Update
Environmental
Initiatives in the 105th Congress
The Clean Water Act and Superfund will be the two major environmental
initiatives slated for the 105th Congress's agenda. During the last Congress,
reauthorizing the Clean Water Act and reforming the Superfund law were
set aside in favor of completing amendments to the Safe Drinking Water
Act. With Congress and the White House now focused on budget, tax and
welfare matters, action to enact far-reaching environmental legislation
remains questionable.
Senator Bob Smith (R-NH) and 21 Republican cosponsors have introduced
the Superfund Cleanup Acceleration Act of 1997, which has been referred
to the Environment and Public Works Committee. The House Committee on
Transportation and Infrastructure, which has jurisdiction over the Clean
Water Act, is still being organized and has not begun drafting a bill.
Regulatory
Negotiations Continue on Drinking Water Rules
Work continues on several fronts relating to safe drinking water. The
Environmental Protection Agency (EPA) is engaged in formal Federal Advisory
Committee meetings to negotiate provisions of the rules -- due in November
1998 -- for controlling microbial contaminants and disinfection by-products.
The Chlorine Chemistry Council is a member of this advisory committee.
Technical working groups, with representatives from the EPA, the water
industry and the environmental community, are assessing new technical
information in an effort to reach consensus on the Stage I D/DBP and interim
enhanced surface water treatment rules. However, a key concern is that
delays in implementing the Information Collection Rule (ICR), intended
to provide the data on which to base the new DBP and water treatment rules,
may lead prematurely to regulatory requirements that cannot be supported
by the ICR results.
Driven by the congressional mandate contained in the SDWA amendments,
particular attention will be devoted to methods for controlling Cryptosporidium
and Giardia in drinking water supplies.
Safe
Drinking Water Act Implementation
Under provisions of the new Drinking Water State Revolving Fund (DWSRF),
$1.3 billion will be available to states this year for loans to help finance
infrastructure improvements in public water systems. In February, the
EPA reported to Congress the results of the first quadrennial drinking
water needs survey of public water systems (see sidebar). The survey data
will be a significant factor in determining how to allocate funds through
the DWSRF.
Most other provisions of the new Act, including the consumer awareness
and public notification requirements, will be phased in over three years
beginning in 1998.
Drinking
Water Infrastructure Needs Survey - EPA Report to Congress
The
nation's 55,000 community water systems must make significant investments
to install, upgrade or replace infrastructure to ensure the provision
of safe drinking to their 243 million customers. This first-ever national
survey estimates that these systems must invest a minimum of $138.4 billion
over the next 20 years. Of this total, $12.1 billion is needed now to
meet current Safe Drinking Water Act requirements.
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Treatment for microbiological contaminants under the SDWA accounts
for $10.2 billion -- about 84% of current SDWA need.
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Total
20-Year Need by System Size
(in billions of Jan. '95 dollars)
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System
Size
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Total
Need
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Large
Systems
(serving more than 50,000 people)
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$58.5
million
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Medium
Systems
(serving 3,301 to 50,000 people)
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$41.4
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Small
Systems
(serving 3,300 and fewer people)
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$37.2
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American
Indian and Alaska Native Systems
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$1.3
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Total
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$132.4
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Chloroform:
Research Findings Support Risk Reassessment
By
Robert G. Tardiff, Ph.D., A.T.S.
In 1996, the Environmental Protection Agency (EPA) announced a revised
approach to risk assessment for determining potential human health effects
from exposure to biological and chemical substances. Taking advantage
of new research tools developed for detecting changes in molecular and
cell biology, the agency now will rely more on cellular changes that integrate
dose-response reactions in human physiology rather than on simple descriptions
of toxicity in laboratory animals.
This new approach has proven valuable in the reconsideration of the risks
associated with chloroform. Over the past ten years, significant advances
in scientific research have shed new light on EPA's 1986 assessment of
chloroform as a potential human carcinogen.
This new data includes findings from over 20 epidemiological studies evaluating
the possibility of an association between chloroform and cancer. These
findings are supplemented by a vast collection of new data generated through
thousands of observations in humans and cancer studies in animals, providing
scientists with a greater foundation of knowledge about cancer risks in
general.
Following careful review of these studies, scientists now believe that
typical human exposures to chloroform -- in drinking water or showers
-- do not present an increased risk of cancer. Furthermore, EPA has acknowledged
that its 1986 assessment may have inadvertently exaggerated chloroform's
risk.
Low-Dose
Reassessment
There is a growing body of evidence that extrapolations from high-dose
animal studies can at times provide a misleading picture of the effects
of low-level exposure. In fact, many scientists now question the accuracy
of human cancer risk assessments that are based solely on such extrapolations.
A better understanding of how different compounds affect the human body
has led to this change in perspective. In particular, scientists now have
the research tools to understand how a chemical's structural features
might affect its toxicity and how potential poisons are absorbed, metabolized
and distributed in the body. Using these tools, researchers have found
that for many compounds the toxic effects of high doses often do not occur
at low doses.
This is particularly true for chloroform. Significant research has shown
that there is a dose range below which chloroform is not likely to be
carcinogenic to animals or humans. Typical human exposures are much lower
than this threshold dose range. Moreover, as shown in the chart, careful
assessment of current data also illustrates that a Virtually Safe Dose
(VSD) for chloroform exists at a far higher level than that specified
in the 1986 EPA assessment.
Important
Implications for Drinking Water Safety
Virtually all drinking water disinfectants produce disinfection by-products
(DBPs). Chloroform is a DBP of water chlorination, the primary drinking
water treatment in the United States. For nearly 100 years, chlorine disinfection
has played an essential role in preventing the waterborne transmission
of infectious diseases and achieving safe drinking water around the world.
Public health concerns about chloroform's carcinogenicity at human exposure
typically encountered in drinking water led EPA to propose rules to further
reduce the acceptable levels of chloroform and other DBPs in drinking
water. However, these draft rules have raised concerns that alteration
of water treatment may well increase microbially induced illness and death
from waterborne pathogens by reducing the efficacy of water disinfection.
Given the abundance of new data suggesting that EPA's current chloroform
risk is significantly overestimated, proposed rules to minimize human
exposure to chloroform must be revised.
Chloroform
as a Candidate for EPA Cancer Risk Reassessment
Formal EPA reassessment of chloroform's cancer potential will further
increase confidence in estimating public health impacts from exposure
to chloroform in water and air. Using EPA's revised approach to risk assessment
will result in a more scientifically rigorous assessment for chloroform.
In the end, chloroform risk estimates will be more defensible for decision-making
about trade-offs between competing risks such as those due to chlorination
DBPs and those due to microbial diseases from waterborne pathogens.
Conclusion
Scientists now have a wealth of information and research methodologies
for assessing the complex relationship between cancer and exposure to
chemical compounds. Using these tools, researchers now believe that exposure
to chloroform at levels typically found in drinking water and showers
does not present an increased risk of cancer in humans.
Robert
G. Tardiff, Ph.D., A.T.S., a risk analyst and toxicologist, is president
of The Sapphire Group, Inc. Dr. Tardiff previously worked for the U.S.
Environmental Protection Agency and managed the environmental health program
of the National Academy of Sciences. He is also former president of the
International Society for Risk Analysis.
State
of the States
States
Focus on Source Water Protection
New
York Watershed Protection
A final agreement for watershed protection regulations to protect the
quality of New York City's source waters was signed on January 21, 1997,
by the New York State Department of Health, Coalition of Watershed Towns,
U.S. Environmental Protection Agency and representatives of environmental
organizations. Gov. George Pataki has earmarked $2.1 million to implement
the watershed agreement, which includes provisions to control pollution
from wastewater treatment plants, septic systems, urban and rural stormwater
run-off, hazardous waste and petroleum storage facilities.
Other terms of the agreement include enhanced monitoring activities, incentives
for local watershed planning efforts and strategies, and a Watershed Protection
and Partnership Council to review water quality issues and recommend future
actions.
Under the federal Surface Water Treatment Rule (SWTR), all surface water
is required to be filtered unless certain criteria are met. New York water
meets SWTR conditions for a filtration waiver for the Catskill/ Delaware
watershed, the source of 90 percent of New York City's water. The new
agreement enables New York to continue providing unfiltered water to nearly
9 million people at least through 2002.
Maryland
Adopts Cryptosporidium Action Plan
In June 1996, health and water utility officials in Maryland finalized
a Cryptosporidium Action Plan to prevent waterborne cryptosporidiosis
and to educate the public. The plan focuses on watershed protection to
prevent pollution at the source, as well as proper maintenance of water
treatment plants.
The plan requires performance evaluations at each of the state's 52 water
treatment plants and monitoring the effectiveness of treatment processes.
To educate the public, the Maryland Department of Health and Mental Hygiene
(DHMH) and Maryland Department of the Environment (MDE) distributed information
about the illness to residents, water utilities, public health officials
and immunocompromised individuals. The action plan also includes a pilot
surveillance program for cryptosporidiosis cases and outbreaks and monthly
sales of anti-diarrheal medications.
Both DHMH and MDE have emergency response plans available to implement
when water quality is known or suspected to be below standard. The agencies
will hold discussions with water utilities and local health departments
when considering boil water advisories.
Water
Relief Network Helps Cuban Hurricane Recovery Effort
In
response to requests from the American and International Red Cross, the
chlorine industry's Water Relief Network donated chlorine-based water
disinfectants and hospital sanitizers (bleach) to help residents of Cuba
recover from Hurricane Lili which hit the western and central territory
of Cuba in October 1996.
Intense winds and rains damaged or destroyed 83,700 homes, 32 schools
and 15 hospitals, and resulting floods caused contamination of water supplies.
Disinfection of water supplies and hospitals following the hurricane placed
a large burden on already limited chlorine supplies. As a result, sanitation
and epidemic control have become a major cause for concern. Cuban Red
Cross and local public health officials fear contamination of water supplies
as the warmer months approach.
A shipment of 12 metric tons of calcium hypochlorite and one metric ton
of sodium hypochlorite arrived in Cuba in February 1997. These products
are being used to help restore safe drinking water supplies and proper
sanitation in hospitals.
Representatives from the American Red Cross and the Water Relief Network,
including Chlorine Chemistry Division of the American Chemistry Council
Managing Director Kip Howlett, traveled to Cuba to survey damage caused
by the hurricane and meet with International and Cuban Red Cross officials.
The mission provided an opportunity to view firsthand how the Network's
contribution to the American Red Cross will benefit residents of several
Cuban provinces and assist with continuing relief efforts.
This is the first major aid mission of the Water Relief Network since
its launch in June 1996. The donation is being made to the American Red
Cross Office of International Services to assist its cooperative effort
with the Cuban Red Cross.
The Water Relief Network is composed of more than 50 member companies
of the Chlorine Chemistry Division of the American Chemistry Council,
the Chlorine Institute and the Vinyl Institute. The Network provides the
American Red Cross with access to chlorine-based products necessary to
restore safe drinking water and other essential human needs following
a disaster.
JUMP
IN...THE WATER'S CLEAN
The
proper use of a chlorine sanitizer in pools and spas will ensure a safe
and healthy swim. For over a century, chlorine has been used to disinfect
pool and spa water. It destroys bacteria and germs introduced into the
water by swimmers and spa users and leaves a residual for continued cleaning.
A free brochure, "Chlorine: The Pool & Spa Sanitizer You Can Trust," that
answers questions about chlorine's use in swimming pools.
Drinking
Water & Health Newsletter is a Publication of the Public Health Advisory
Board to the Chlorine Chemistry Division of the American Chemistry Council
The
Public Health Advisory Board
Chair
Ralph Morris, M.D.
Galveston County
Health District
LaMarque, Texas
Vice
Chair
Joan B. Rose, Ph.D.
Department of Marine Science
University of South Florida
St. Petersburg, Florida
Bruce
Bernard, Ph.D.
SRA International
Washington, D.C.
Sanford
M. Brown, Jr., Ph.D.
Department of Health Sciences California State University
Fresno, California
Linda
Golodner
National Consumers League
Washington, D.C.
Jerod
Loeb, Ph.D.
Joint Commission on
Accreditation of Health
Care Organizations
Oakbrook Terrace, Illinois
Fred
Reiff, P.E.
Pan American Health
Organization (Retired)
Washington, D.C.
Chris
J. Wiant, Ph.D.
Tri-County Health Department
Englewood, Colorado
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