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sciencemag.org SCIENCE
By Yan Zheng
S
evere public health consequences of
worldwide geogenic arsenic occur-
rence in groundwater have been rec-
ognized since the late 1990s (1). The
population affected by groundwater
arsenic from domestic well supplies
has been frequently stated to exceed 100 mil-
lion. However, this compilation is fraught
with uncertainties due to incomplete and
unreliable records on domestic wells that
supply drinking water and incomplete test-
ing for arsenic. On page 845 of this issue,
Podgorski and Berg use statistical mod-
els to estimate that 94 million to 220 mil-
lion people, with 94% in Asia, are at risk of
drinking well water containing arsenic con-
centrations >10 mg/liter (2). In Bangladesh,
a 2009 national drinking-water quality sur-
vey found that about 20 million and 45 mil-
lion people were exposed to concentrations
greater than 50 and 10 mg/liter, respectively,
with an arsenic-related mortality rate of 1 in
every 18 adult deaths (3). This global threat
demands multisector solutions.
The 2017 edition of the World Health Or-
ganization’s Guidelines for Drinking-Water
Quality retained its provisional value of 10
mg/liter for inorganic arsenic, a recommen-
dation based on treatment performance
and analytical achievability. Many countries
have adopted this value as their drinking-
water quality standard over the past two
decades. Although the European Union has
set the standard at 10 mg/liter, Denmark’s
is more protective at 5 mg/liter. The Asso-
ciation of Dutch Drinking Water Companies
voluntarily agreed on a guideline of <1 mg/
liter in 2015 (4). The U.S. Environmental
Protection Agency adopted 10 mg/liter in
2001 for the federal maximum contaminant
level (MCL) on the basis of cost-benefit
analyses, effective 2006. However, the state
of New Jersey opted for 5 mg/liter effective
2006, and New Hampshire adopted 5 mg/li-
ter in 2020. The world’s two most populous
countries, China and India, lowered their
MCL, effective 2007 and 2012, respectively,
from 50 to 10 mg/liter. However, 50 mg/liter
is permissible in the absence of alternate
sources in India and remains the MCL for
Bangladesh and for small, dispersed rural
supplies in China. This order-of-magnitude
disparity in the MCL is concerning because
new health evidence suggests that even
10 mg/liter may not be protective enough,
especially during early, biologically vulner-
able stages of life.
PUBLIC HEALTH
Global solutions to a silent poison
Modeling arsenic in domestic well water highlights large data gaps in testing
PHOTO:
A.
M.
AHAD/AP
PHOTO
School of Environmental Science and Engineering,
Southern University of Science and Technology, Shenzhen
518055, China. Email: yan.zheng@sustech.edu.cn
PERSPECTIVES
INSIGHTS
A Bangladeshi woman collects
potable water from a hand pump.
The health toll from arsenic in
water justifies global solutions.
818 22 MAY 2020 • VOL 368 ISSUE 6493
Published by AAAS
on
May
21,
2020
http://science.sciencemag.org/
Downloaded
from
SCIENCE sciencemag.org
GRAPHIC:
X.
LIU/SCIENCE
FROM
(2)
The word arsenic originates from the
Greek arsenikon, which means valiant,
bold, or potent. Odorless and tasteless when
dissolved in water, this silent poison be-
came known as both “the king of poisons”
and “the poison of kings.” The acute toxicity
of inorganic arsenic, classified as a group I
carcinogen by the International Agency for
Research on Cancer, has been appreciated
since ancient times. Long-term exposure to
water containing high concentrations (>100
mg/liter) of inorganic arsenic (arsenate and
arsenite) is associated with nonmelanoma
skin, lung, and bladder cancers, as well as
noncancer outcomes. The Health Effects
of Arsenic Longitudinal Study (HEALS) in
Bangladesh showed dose-response relation-
ships between drinking-water arsenic and
skin lesions, respiratory symptoms, cardio-
vascular disease, and reduced intellectual
function in children (5). Long-term expo-
sure to moderate concentrations (<50 mg/
liter) has been associated with cardiovascu-
lar disease incidence and mortality in one of
the largest studies in the United States (6).
Epidemiologic evidence, consistent with ex-
perimental evidence, supports that arsenic
affects birth outcomes and impairs neuro-
development when exposure occurs during
early life, even at moderate concentrations
(<50 µg/liter) (5). In utero, arsenic exposure
has been associated with alterations in gene
expression pathways related to diabetes
(7), which may contribute to adult diabetes
risks. This supports the epigenome as a gen-
eral mechanism involved in arsenic toxicity,
consistent with evidence from a genome-
wide DNA methylation study of 396 HEALS
adults (8). Still, not enough is known about
the mode of action of inorganic arsenic for
extrapolating dose response to very low
concentrations (<5 mg/liter).
Because three-dimensional (longitude, lat-
itude, and depth) mapping of groundwater
arsenic concentration often lacks the spatial
resolution to characterize most aquifers, ex-
posure assessment has turned to “predictive”
models incorporating geo-environmental pre-
dictor variables. Podgorski and Berg utilized
58,555 aggregated well (<100-m depth) water
arsenic average values, mapped to 1-km2
grid
cells based on >200,000 tests from 67 coun-
tries, to develop a random forest machine-
learning model to globally quantify exposed
populations. This represents a culmination
of logistic regression (9, 10) and machine-
learning (11) modeling efforts (see the figure).
The authors’ efforts expose data gaps because
few countries have conducted a nationwide
groundwater arsenic survey. Testing data are
also clustered with uneven and incomplete
spatial coverage. More arsenic data and de-
tailed predictor datasets will reduce the large
and partially unknown uncertainties. Eleven
out of 52 spatially continuous predictor vari-
ables representing various climatic, geologic,
soil, and other parameters emerged through
recursive feature elimination to create the
simplest best model. Additional research is
required to explain why these are important.
Statistical models are not meant to predict
individual well water arsenic concentrations.
Their greatest value lies in identifying poten-
tial areas at risk that have not had testing.
This public health crisis leads to an ur-
gent call to test all domestic well water for
arsenic worldwide. Testing should prioritize
the high-risk areas identified by models.
Heterogeneous groundwater arsenic spa-
tial distribution (101
to 103
m) should make
wells that are close to known high-arsenic
wells testing priorities. The combination of
arsenic’s toxicity and its wide distribution
makes this task imperative. Disparities in
coverage of regulatory requirements in the
United States have left more than a million
rural Americans unknowingly exposed to
arsenic, with a high proportion belonging to
socioeconomically and behaviorally vulner-
able groups (10, 12). Development of sensi-
tive, reliable, inexpensive, and user-friendly
testing methods for inorganic arsenic in wa-
ter and urine, preferably with on-site rapid
measurement capability, can further improve
screening and identify exposed populations.
Whereas many countries have succeeded in
replacing noncompliant arsenic domestic
wells with alternative supplies or treatment
to reduce exposure, dispersed rural popula-
tions require sustained attention. Treatment
of arsenic is not cheap, burdening rural
households even in high-income countries.
Geogenic arsenic in well water is forever, but
our exposure to it should not be. j
REFERENCES AND NOTES
1. D.K.Nordstrom,Science296,2143(2002).
2. J.Podgorski,M.Berg,Science368,845(2020).
3. S.V.Flanagan,R.B.Johnston,Y.Zheng,Bull.World
HealthOrgan.90,839(2012).
4. A.Ahmadetal.,Environ.Int.134,105253(2020).
5. NationalResearchCouncil,“CriticalaspectsofEPA’s
IRISassessmentofinorganicarsenic:Interimreport”
(TheNationalAcademiesPress,Washington,DC,2013).
6. K.A.Moonetal.,Ann.Intern.Med.159,649(2013).
7. A.Navas-Acienetal.,Curr.Diab.Rep.19,147(2019).
8. K.Demanelisetal.,Environ.HealthPerspect.127,
057011(2019).
9. L.Winkeletal.,Nat.Geosci.1,536(2008).
10. J.D.Ayotteetal.,Environ.Sci.Technol.51,12443(2017).
11. J.D.Ayotteetal.,Environ.Sci.Technol.50,7555(2016).
12. Y.Zheng,S.V.Flanagan,Environ.HealthPerspect.125,
085002(2017).
ACKNOWLEDGMENTS
J.D.Ayotte,A.Navas-Acien,andD.K.Nordstromprovided
comments.FigurecourtesyofA.Bozack,Z.Tan,andB.Xu.Y.Z.
issupportedbyStrategicPriorityResearchProgramofthe
ChineseAcademyofSciences(XDA20060402),theNational
NaturalScienceFoundation(41831279),andtheU.S.National
InstituteofEnvironmentalHealthSciences,Superfund
ResearchProgram(P42ES010349).
10.1126/science.abb9746
Health effects in adults
General health effects
Mortality
DNA methylation
Gene expression
Nervous system
Movement and
motor function
Neuropathy
Immune system
Infections
Respiratory system
Bronchiectasis
Lung cancer
Cardiovascular system
Heart and vascular disease
High blood pressure
Stroke
Endocrine system
Diabetes
Soft organs
Kidney cancer
Bladder cancer
Liver cancer
Skin
Skin lesions
Skin cancer
Health effects in children
General health effects
Infant mortality
Reduced birth weight
DNA methylation
Gene expression
Nervous system
Neurological
impairment
>80% 60 to 80% 40 to 60% 20 to 40% <20%
0 6000
km
Model percent probability
of >5 mg/liter arsenic
concentration
A world model for groundwater arsenic risk
Lowering arsenic concentrations in drinking water helps avoid a range of adverse health outcomes. Modeling
the probability of groundwater arsenic with excess risks helps guide testing. Podgorski and Berg developed
global models for groundwater arsenic concentrations exceeding 5 and 10 mg/liter.
22 MAY 2020 • VOL 368 ISSUE 6493 819
Published by AAAS
on
May
21,
2020
http://science.sciencemag.org/
Downloaded
from
Global solutions to a silent poison
Yan Zheng
DOI: 10.1126/science.abb9746
(6493), 818-819.
368
Science
ARTICLE TOOLS http://science.sciencemag.org/content/368/6493/818
CONTENT
RELATED http://science.sciencemag.org/content/sci/368/6493/845.full
REFERENCES
http://science.sciencemag.org/content/368/6493/818#BIBL
This article cites 11 articles, 2 of which you can access for free
PERMISSIONS http://www.sciencemag.org/help/reprints-and-permissions
Terms of Service
Use of this article is subject to the
is a registered trademark of AAAS.
Science
Science, 1200 New York Avenue NW, Washington, DC 20005. The title
(print ISSN 0036-8075; online ISSN 1095-9203) is published by the American Association for the Advancement of
Science
Science. No claim to original U.S. Government Works
Copyright © 2020 The Authors, some rights reserved; exclusive licensee American Association for the Advancement of
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science.abb9746.pdf

  • 1. sciencemag.org SCIENCE By Yan Zheng S evere public health consequences of worldwide geogenic arsenic occur- rence in groundwater have been rec- ognized since the late 1990s (1). The population affected by groundwater arsenic from domestic well supplies has been frequently stated to exceed 100 mil- lion. However, this compilation is fraught with uncertainties due to incomplete and unreliable records on domestic wells that supply drinking water and incomplete test- ing for arsenic. On page 845 of this issue, Podgorski and Berg use statistical mod- els to estimate that 94 million to 220 mil- lion people, with 94% in Asia, are at risk of drinking well water containing arsenic con- centrations >10 mg/liter (2). In Bangladesh, a 2009 national drinking-water quality sur- vey found that about 20 million and 45 mil- lion people were exposed to concentrations greater than 50 and 10 mg/liter, respectively, with an arsenic-related mortality rate of 1 in every 18 adult deaths (3). This global threat demands multisector solutions. The 2017 edition of the World Health Or- ganization’s Guidelines for Drinking-Water Quality retained its provisional value of 10 mg/liter for inorganic arsenic, a recommen- dation based on treatment performance and analytical achievability. Many countries have adopted this value as their drinking- water quality standard over the past two decades. Although the European Union has set the standard at 10 mg/liter, Denmark’s is more protective at 5 mg/liter. The Asso- ciation of Dutch Drinking Water Companies voluntarily agreed on a guideline of <1 mg/ liter in 2015 (4). The U.S. Environmental Protection Agency adopted 10 mg/liter in 2001 for the federal maximum contaminant level (MCL) on the basis of cost-benefit analyses, effective 2006. However, the state of New Jersey opted for 5 mg/liter effective 2006, and New Hampshire adopted 5 mg/li- ter in 2020. The world’s two most populous countries, China and India, lowered their MCL, effective 2007 and 2012, respectively, from 50 to 10 mg/liter. However, 50 mg/liter is permissible in the absence of alternate sources in India and remains the MCL for Bangladesh and for small, dispersed rural supplies in China. This order-of-magnitude disparity in the MCL is concerning because new health evidence suggests that even 10 mg/liter may not be protective enough, especially during early, biologically vulner- able stages of life. PUBLIC HEALTH Global solutions to a silent poison Modeling arsenic in domestic well water highlights large data gaps in testing PHOTO: A. M. AHAD/AP PHOTO School of Environmental Science and Engineering, Southern University of Science and Technology, Shenzhen 518055, China. Email: yan.zheng@sustech.edu.cn PERSPECTIVES INSIGHTS A Bangladeshi woman collects potable water from a hand pump. The health toll from arsenic in water justifies global solutions. 818 22 MAY 2020 • VOL 368 ISSUE 6493 Published by AAAS on May 21, 2020 http://science.sciencemag.org/ Downloaded from
  • 2. SCIENCE sciencemag.org GRAPHIC: X. LIU/SCIENCE FROM (2) The word arsenic originates from the Greek arsenikon, which means valiant, bold, or potent. Odorless and tasteless when dissolved in water, this silent poison be- came known as both “the king of poisons” and “the poison of kings.” The acute toxicity of inorganic arsenic, classified as a group I carcinogen by the International Agency for Research on Cancer, has been appreciated since ancient times. Long-term exposure to water containing high concentrations (>100 mg/liter) of inorganic arsenic (arsenate and arsenite) is associated with nonmelanoma skin, lung, and bladder cancers, as well as noncancer outcomes. The Health Effects of Arsenic Longitudinal Study (HEALS) in Bangladesh showed dose-response relation- ships between drinking-water arsenic and skin lesions, respiratory symptoms, cardio- vascular disease, and reduced intellectual function in children (5). Long-term expo- sure to moderate concentrations (<50 mg/ liter) has been associated with cardiovascu- lar disease incidence and mortality in one of the largest studies in the United States (6). Epidemiologic evidence, consistent with ex- perimental evidence, supports that arsenic affects birth outcomes and impairs neuro- development when exposure occurs during early life, even at moderate concentrations (<50 µg/liter) (5). In utero, arsenic exposure has been associated with alterations in gene expression pathways related to diabetes (7), which may contribute to adult diabetes risks. This supports the epigenome as a gen- eral mechanism involved in arsenic toxicity, consistent with evidence from a genome- wide DNA methylation study of 396 HEALS adults (8). Still, not enough is known about the mode of action of inorganic arsenic for extrapolating dose response to very low concentrations (<5 mg/liter). Because three-dimensional (longitude, lat- itude, and depth) mapping of groundwater arsenic concentration often lacks the spatial resolution to characterize most aquifers, ex- posure assessment has turned to “predictive” models incorporating geo-environmental pre- dictor variables. Podgorski and Berg utilized 58,555 aggregated well (<100-m depth) water arsenic average values, mapped to 1-km2 grid cells based on >200,000 tests from 67 coun- tries, to develop a random forest machine- learning model to globally quantify exposed populations. This represents a culmination of logistic regression (9, 10) and machine- learning (11) modeling efforts (see the figure). The authors’ efforts expose data gaps because few countries have conducted a nationwide groundwater arsenic survey. Testing data are also clustered with uneven and incomplete spatial coverage. More arsenic data and de- tailed predictor datasets will reduce the large and partially unknown uncertainties. Eleven out of 52 spatially continuous predictor vari- ables representing various climatic, geologic, soil, and other parameters emerged through recursive feature elimination to create the simplest best model. Additional research is required to explain why these are important. Statistical models are not meant to predict individual well water arsenic concentrations. Their greatest value lies in identifying poten- tial areas at risk that have not had testing. This public health crisis leads to an ur- gent call to test all domestic well water for arsenic worldwide. Testing should prioritize the high-risk areas identified by models. Heterogeneous groundwater arsenic spa- tial distribution (101 to 103 m) should make wells that are close to known high-arsenic wells testing priorities. The combination of arsenic’s toxicity and its wide distribution makes this task imperative. Disparities in coverage of regulatory requirements in the United States have left more than a million rural Americans unknowingly exposed to arsenic, with a high proportion belonging to socioeconomically and behaviorally vulner- able groups (10, 12). Development of sensi- tive, reliable, inexpensive, and user-friendly testing methods for inorganic arsenic in wa- ter and urine, preferably with on-site rapid measurement capability, can further improve screening and identify exposed populations. Whereas many countries have succeeded in replacing noncompliant arsenic domestic wells with alternative supplies or treatment to reduce exposure, dispersed rural popula- tions require sustained attention. Treatment of arsenic is not cheap, burdening rural households even in high-income countries. Geogenic arsenic in well water is forever, but our exposure to it should not be. j REFERENCES AND NOTES 1. D.K.Nordstrom,Science296,2143(2002). 2. J.Podgorski,M.Berg,Science368,845(2020). 3. S.V.Flanagan,R.B.Johnston,Y.Zheng,Bull.World HealthOrgan.90,839(2012). 4. A.Ahmadetal.,Environ.Int.134,105253(2020). 5. NationalResearchCouncil,“CriticalaspectsofEPA’s IRISassessmentofinorganicarsenic:Interimreport” (TheNationalAcademiesPress,Washington,DC,2013). 6. K.A.Moonetal.,Ann.Intern.Med.159,649(2013). 7. A.Navas-Acienetal.,Curr.Diab.Rep.19,147(2019). 8. K.Demanelisetal.,Environ.HealthPerspect.127, 057011(2019). 9. L.Winkeletal.,Nat.Geosci.1,536(2008). 10. J.D.Ayotteetal.,Environ.Sci.Technol.51,12443(2017). 11. J.D.Ayotteetal.,Environ.Sci.Technol.50,7555(2016). 12. Y.Zheng,S.V.Flanagan,Environ.HealthPerspect.125, 085002(2017). ACKNOWLEDGMENTS J.D.Ayotte,A.Navas-Acien,andD.K.Nordstromprovided comments.FigurecourtesyofA.Bozack,Z.Tan,andB.Xu.Y.Z. issupportedbyStrategicPriorityResearchProgramofthe ChineseAcademyofSciences(XDA20060402),theNational NaturalScienceFoundation(41831279),andtheU.S.National InstituteofEnvironmentalHealthSciences,Superfund ResearchProgram(P42ES010349). 10.1126/science.abb9746 Health effects in adults General health effects Mortality DNA methylation Gene expression Nervous system Movement and motor function Neuropathy Immune system Infections Respiratory system Bronchiectasis Lung cancer Cardiovascular system Heart and vascular disease High blood pressure Stroke Endocrine system Diabetes Soft organs Kidney cancer Bladder cancer Liver cancer Skin Skin lesions Skin cancer Health effects in children General health effects Infant mortality Reduced birth weight DNA methylation Gene expression Nervous system Neurological impairment >80% 60 to 80% 40 to 60% 20 to 40% <20% 0 6000 km Model percent probability of >5 mg/liter arsenic concentration A world model for groundwater arsenic risk Lowering arsenic concentrations in drinking water helps avoid a range of adverse health outcomes. Modeling the probability of groundwater arsenic with excess risks helps guide testing. Podgorski and Berg developed global models for groundwater arsenic concentrations exceeding 5 and 10 mg/liter. 22 MAY 2020 • VOL 368 ISSUE 6493 819 Published by AAAS on May 21, 2020 http://science.sciencemag.org/ Downloaded from
  • 3. Global solutions to a silent poison Yan Zheng DOI: 10.1126/science.abb9746 (6493), 818-819. 368 Science ARTICLE TOOLS http://science.sciencemag.org/content/368/6493/818 CONTENT RELATED http://science.sciencemag.org/content/sci/368/6493/845.full REFERENCES http://science.sciencemag.org/content/368/6493/818#BIBL This article cites 11 articles, 2 of which you can access for free PERMISSIONS http://www.sciencemag.org/help/reprints-and-permissions Terms of Service Use of this article is subject to the is a registered trademark of AAAS. Science Science, 1200 New York Avenue NW, Washington, DC 20005. The title (print ISSN 0036-8075; online ISSN 1095-9203) is published by the American Association for the Advancement of Science Science. No claim to original U.S. Government Works Copyright © 2020 The Authors, some rights reserved; exclusive licensee American Association for the Advancement of on May 21, 2020 http://science.sciencemag.org/ Downloaded from