Standard Guide for Using Publicly Available Data to Identify Schools and Vulnerable Communities at High Risk for Elevated Lead in Drinking Water

SIGNIFICANCE AND USE
4.1 Lead can enter drinking water when service lines or plumbing fixtures that contain lead corrode, especially where the water has high acidity or low mineral content. According to the EPA, lead typically enters school drinking water as a result of interaction with lead-containing plumbing materials and fixtures within the building (EPA 2019 EPA 2018, (5)). Although lead pipes and lead solder were not commonly used after 1986, water fountains and other fixtures were allowed to have up to 8 percent lead until 2014 (GAO, 2018 (2)). Consequently, both older and newer school buildings can have lead in drinking water at concentrations that exceed the NPDWR.  
4.2 Following the reports in 2015 of elevated lead levels in the water in Flint, Michigan, Congress passed the Water Infrastructure Improvements for the Nation Act in 2016 (Public Law 114-322), which, among other things, amended the SDWA, to establish a grant program for states to assist school districts in voluntary testing for lead contamination in drinking water at schools. As a condition of receiving funds, school districts are required to test for lead using standards that are at least as stringent as those in federal guidance for schools.  
4.3 California’s State Water Resources Control Board’s Division of Drinking Water initiated an aggressive program of sampling and public water systems supplying water to schools in 2018. California Assembly Bill 746 published on October 12, 2017, effective January 1, 2018, requires community water systems to test lead levels, by July 1, 2019, in drinking water at all California public, K-12 school sites that were constructed before January 1, 2010.  
4.4 Lobo (2021) (6) reports that two factors predominantly control lead leaching into the drinking water: (1) the presence or absence of lead-bearing plumbing materials, and (2) water quality that promotes the formation of soluble or insoluble lead corrosion products. This guide provides a method of using publicly-available...
SCOPE
1.1 As the General Accountability Office (GAO) reported in 2018 (2), the discovery of toxic levels of lead in drinking water in Flint, Michigan in 2015 renewed awareness about the risks that lead poses to public health. Exposure to lead can result in elevated blood lead levels and negative health effects. Children are at particular risk, because their growing bodies absorb more lead than adults, so protecting them from lead is important to lifelong good health. According to the Centers for Disease Control and Prevention (CDC), elevated blood lead levels have been linked to anemia, kidney and brain damage, learning disabilities, and decreased growth. As a result of widespread human use, lead is prevalent in the environment; for example, it can be found in paint (lead in paint was banned in the United States in 1978)4 and soil, and can leach into drinking water from lead-containing plumbing materials, such as faucets and drinking fountains.  
1.2 Lead in school drinking water is a concern because it is a daily source of water for over 50 million children enrolled in public schools. The pattern of school schedules—including time off over weekends, holidays, and extended breaks—can contribute to standing water in the school’s plumbing system. If there is lead in the plumbing system, the potential for it to leach into water can increase the longer the water remains in contact with the plumbing. Estimating the risk of lead contamination of schools' drinking water at the State level is a complex and important challenge. Variable water quality among water systems and changes in water chemistry during distribution affect lead dissolution rates from pipes and fittings. In addition, the locations of lead-bearing plumbing materials are uncertain. EPA, 2002 (3), Triantafyllidou and Edwards, 2012 (4).  
1.3 The US EPA is responsible for enforcement of the Safe Drinking Water Act (SDWA) on Tribal land; there is no delegation of this ...

General Information

Status
Published
Publication Date
30-Apr-2023

Relations

Effective Date
01-Dec-2015

Overview

ASTM E3366-23 is the standard guide developed by ASTM International for using publicly available data to identify schools and vulnerable communities at high risk for elevated lead in drinking water. The standard empowers stakeholders-including governments, school districts, and water utilities-to leverage data and geographic information systems (GIS) to rapidly assess the risk of lead exposure in drinking water supplies without costly inspections.

Lead is a persistent health concern, particularly for children, due to its potential to leach from aging infrastructure and plumbing materials into potable water. This standard is closely aligned with US EPA policies and federal funding programs, responding to significant public health events and regulations such as the Lead and Copper Rule Revision and the Safe Drinking Water Act (SDWA).

Key Topics

  • Lead Contamination in Drinking Water
    Lead most commonly enters drinking water through corrosion of service lines or fixtures containing lead, especially in older buildings or where water exhibits high acidity or low mineral content. Both older and relatively newer school buildings can have lead concentrations exceeding regulatory limits.

  • Vulnerable Populations
    Children, especially in schools, are at greater risk because their bodies absorb more lead. Vulnerable communities often experience disproportionate exposure due to older infrastructure, lower income, and systemic inequities.

  • Data-Driven Risk Identification
    The standard details a step-by-step procedure for gathering and analyzing:

    • Demographic data (e.g., income, race, and unemployment, often from US Census Bureau and American Community Survey)
    • Water quality data and average lead concentrations from public water system reports (such as Annual Consumer Confidence Reports and the EPA Safe Drinking Water Information System)
    • Infrastructure age and materials known to be associated with lead risk
    • Geographic cluster analysis using GIS tools
  • Compliance and Regulatory Context
    The approach outlined aligns with requirements in the Infrastructure Investment and Jobs Act, EPA’s Lead and Copper Rule Revisions, and associated guidance for service line inventories and replacements. The standard encourages full lead service line replacement and discourages partial measures.

Applications

  • Rapid Screening for Lead Risk
    Schools and community organizations can use the guide to prioritize testing and remediation where risk is highest, based on the intersection of infrastructure, water chemistry, and demographic vulnerability.

  • Resource Allocation and Planning
    State agencies and school districts may leverage the methodology to inform grant applications, allocate remediation funds, and meet federal or state regulatory requirements.

  • Supporting Regulatory Compliance
    By following this standard, water utilities and school managers can ensure that their testing and remediation programs adhere to the latest federal guidance and standards, minimizing public health risks and legal liabilities.

  • GIS and Predictive Modeling
    The standard's use of geographic information systems enables precise mapping of at-risk areas, supporting targeted interventions and efficient use of resources.

Related Standards

  • ASTM E3032 - Guide for Climate Resiliency Planning and Strategy, which includes relevant approaches to environmental risk assessment and planning.
  • EPA 816-B-22-001 - Guidance for Developing and Maintaining a Service Line Inventory.
  • EPA 810-R-19-003 - Strategies to Achieve Full Lead Service Line Replacement.
  • Lead and Copper Rule Revisions - Federal regulations establishing stricter limits and monitoring requirements for lead in drinking water.

Keywords

Lead in drinking water, ASTM E3366, schools, vulnerable communities, GIS, public health, water quality, lead service line, EPA, Safe Drinking Water Act, risk assessment, infrastructure, environmental standards, lead remediation, data-driven analysis.

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Frequently Asked Questions

ASTM E3366-23 is a guide published by ASTM International. Its full title is "Standard Guide for Using Publicly Available Data to Identify Schools and Vulnerable Communities at High Risk for Elevated Lead in Drinking Water". This standard covers: SIGNIFICANCE AND USE 4.1 Lead can enter drinking water when service lines or plumbing fixtures that contain lead corrode, especially where the water has high acidity or low mineral content. According to the EPA, lead typically enters school drinking water as a result of interaction with lead-containing plumbing materials and fixtures within the building (EPA 2019 EPA 2018, (5)). Although lead pipes and lead solder were not commonly used after 1986, water fountains and other fixtures were allowed to have up to 8 percent lead until 2014 (GAO, 2018 (2)). Consequently, both older and newer school buildings can have lead in drinking water at concentrations that exceed the NPDWR. 4.2 Following the reports in 2015 of elevated lead levels in the water in Flint, Michigan, Congress passed the Water Infrastructure Improvements for the Nation Act in 2016 (Public Law 114-322), which, among other things, amended the SDWA, to establish a grant program for states to assist school districts in voluntary testing for lead contamination in drinking water at schools. As a condition of receiving funds, school districts are required to test for lead using standards that are at least as stringent as those in federal guidance for schools. 4.3 California’s State Water Resources Control Board’s Division of Drinking Water initiated an aggressive program of sampling and public water systems supplying water to schools in 2018. California Assembly Bill 746 published on October 12, 2017, effective January 1, 2018, requires community water systems to test lead levels, by July 1, 2019, in drinking water at all California public, K-12 school sites that were constructed before January 1, 2010. 4.4 Lobo (2021) (6) reports that two factors predominantly control lead leaching into the drinking water: (1) the presence or absence of lead-bearing plumbing materials, and (2) water quality that promotes the formation of soluble or insoluble lead corrosion products. This guide provides a method of using publicly-available... SCOPE 1.1 As the General Accountability Office (GAO) reported in 2018 (2), the discovery of toxic levels of lead in drinking water in Flint, Michigan in 2015 renewed awareness about the risks that lead poses to public health. Exposure to lead can result in elevated blood lead levels and negative health effects. Children are at particular risk, because their growing bodies absorb more lead than adults, so protecting them from lead is important to lifelong good health. According to the Centers for Disease Control and Prevention (CDC), elevated blood lead levels have been linked to anemia, kidney and brain damage, learning disabilities, and decreased growth. As a result of widespread human use, lead is prevalent in the environment; for example, it can be found in paint (lead in paint was banned in the United States in 1978)4 and soil, and can leach into drinking water from lead-containing plumbing materials, such as faucets and drinking fountains. 1.2 Lead in school drinking water is a concern because it is a daily source of water for over 50 million children enrolled in public schools. The pattern of school schedules—including time off over weekends, holidays, and extended breaks—can contribute to standing water in the school’s plumbing system. If there is lead in the plumbing system, the potential for it to leach into water can increase the longer the water remains in contact with the plumbing. Estimating the risk of lead contamination of schools' drinking water at the State level is a complex and important challenge. Variable water quality among water systems and changes in water chemistry during distribution affect lead dissolution rates from pipes and fittings. In addition, the locations of lead-bearing plumbing materials are uncertain. EPA, 2002 (3), Triantafyllidou and Edwards, 2012 (4). 1.3 The US EPA is responsible for enforcement of the Safe Drinking Water Act (SDWA) on Tribal land; there is no delegation of this ...

SIGNIFICANCE AND USE 4.1 Lead can enter drinking water when service lines or plumbing fixtures that contain lead corrode, especially where the water has high acidity or low mineral content. According to the EPA, lead typically enters school drinking water as a result of interaction with lead-containing plumbing materials and fixtures within the building (EPA 2019 EPA 2018, (5)). Although lead pipes and lead solder were not commonly used after 1986, water fountains and other fixtures were allowed to have up to 8 percent lead until 2014 (GAO, 2018 (2)). Consequently, both older and newer school buildings can have lead in drinking water at concentrations that exceed the NPDWR. 4.2 Following the reports in 2015 of elevated lead levels in the water in Flint, Michigan, Congress passed the Water Infrastructure Improvements for the Nation Act in 2016 (Public Law 114-322), which, among other things, amended the SDWA, to establish a grant program for states to assist school districts in voluntary testing for lead contamination in drinking water at schools. As a condition of receiving funds, school districts are required to test for lead using standards that are at least as stringent as those in federal guidance for schools. 4.3 California’s State Water Resources Control Board’s Division of Drinking Water initiated an aggressive program of sampling and public water systems supplying water to schools in 2018. California Assembly Bill 746 published on October 12, 2017, effective January 1, 2018, requires community water systems to test lead levels, by July 1, 2019, in drinking water at all California public, K-12 school sites that were constructed before January 1, 2010. 4.4 Lobo (2021) (6) reports that two factors predominantly control lead leaching into the drinking water: (1) the presence or absence of lead-bearing plumbing materials, and (2) water quality that promotes the formation of soluble or insoluble lead corrosion products. This guide provides a method of using publicly-available... SCOPE 1.1 As the General Accountability Office (GAO) reported in 2018 (2), the discovery of toxic levels of lead in drinking water in Flint, Michigan in 2015 renewed awareness about the risks that lead poses to public health. Exposure to lead can result in elevated blood lead levels and negative health effects. Children are at particular risk, because their growing bodies absorb more lead than adults, so protecting them from lead is important to lifelong good health. According to the Centers for Disease Control and Prevention (CDC), elevated blood lead levels have been linked to anemia, kidney and brain damage, learning disabilities, and decreased growth. As a result of widespread human use, lead is prevalent in the environment; for example, it can be found in paint (lead in paint was banned in the United States in 1978)4 and soil, and can leach into drinking water from lead-containing plumbing materials, such as faucets and drinking fountains. 1.2 Lead in school drinking water is a concern because it is a daily source of water for over 50 million children enrolled in public schools. The pattern of school schedules—including time off over weekends, holidays, and extended breaks—can contribute to standing water in the school’s plumbing system. If there is lead in the plumbing system, the potential for it to leach into water can increase the longer the water remains in contact with the plumbing. Estimating the risk of lead contamination of schools' drinking water at the State level is a complex and important challenge. Variable water quality among water systems and changes in water chemistry during distribution affect lead dissolution rates from pipes and fittings. In addition, the locations of lead-bearing plumbing materials are uncertain. EPA, 2002 (3), Triantafyllidou and Edwards, 2012 (4). 1.3 The US EPA is responsible for enforcement of the Safe Drinking Water Act (SDWA) on Tribal land; there is no delegation of this ...

ASTM E3366-23 is classified under the following ICS (International Classification for Standards) categories: 13.060.20 - Drinking water. The ICS classification helps identify the subject area and facilitates finding related standards.

ASTM E3366-23 has the following relationships with other standards: It is inter standard links to ASTM E3032-15. Understanding these relationships helps ensure you are using the most current and applicable version of the standard.

ASTM E3366-23 is available in PDF format for immediate download after purchase. The document can be added to your cart and obtained through the secure checkout process. Digital delivery ensures instant access to the complete standard document.

Standards Content (Sample)


This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the
Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
Designation: E3366 − 23
Standard Guide for
Using Publicly Available Data to Identify Schools and
Vulnerable Communities at High Risk for Elevated Lead in
1,2
Drinking Water
This standard is issued under the fixed designation E3366; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
INTRODUCTION
Sections 50105 and 50110 of the Infrastructure Investment and Jobs Act (1) direct the US EPA to
identify schools and housing in vulnerable communities at high risk to lead exposure from water
supply infrastructure. The Agency has responded with its Guidance for Developing and Maintaining
a Service Line Inventory EPA 816-B-22-001 (August 2022) and the January 2021 Lead and Copper
Rule Revision. The Lead and Copper Rule Revision establishes new limits for lead and copper in
drinking water. This guide describes a series of steps to effectively identify schools and vulnerable
communities at risk of high lead levels in drinking water using only publicly-available information and
robust geographic information systems software and is consistent with the Predictive Modeling
approach described in Section 5.5 of Guidance for Developing and Maintaining a Service Line
Inventory. This guide complements the records review activities described in EPA’s lead service line
replacement guidance. Stakeholders can use the procedures described in this guide to rapidly assess
the likelihood of lead in water exceeding the limits in federal regulations (40 CFR 141 et seq.) without
the costs associated with inspecting water service lines and water service line connections at schools
and in vulnerable communities.
According to EPA:
Service line inventories are the foundation from which water systems take action to address a
significant source of lead in drinking water - lead service lines (LSLs). Establishing an inventory of
service line materials and identifying the location of LSLs is a key step in getting them replaced and
protecting public health. Lead service line replacement (LSLR) is not dependent on knowing the
location of all LSLs; in fact, simultaneously developing an inventory while conducting LSLR can have
many benefits. For example, systems can save costs by replacing LSLs when crews find them onsite
during service line investigations. Systems can also leverage the opportunity for LSLR by seeking
customer consent and private property access during service line investigation. Replacing LSLs in a
safe and prompt manner while crews are in the field for inventory development provides an
opportunity for public health benefits for consumers by more quickly eliminating this potential source
of lead exposure from drinking water. (EPA August 2022)
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
E3366 − 23
1. Scope of lead concentrations exceeding the maximum contaminant
level (MCL), using publicly available data. These steps aug-
1.1 As the General Accountability Office (GAO) reported in
ment and complement the records review activities that the US
2018 (2), the discovery of toxic levels of lead in drinking water
EPA encourages as part of the LSLR program.
in Flint, Michigan in 2015 renewed awareness about the risks
1.6 This standard does not purport to address all of the
that lead poses to public health. Exposure to lead can result in
safety concerns, if any, associated with its use. It is the
elevated blood lead levels and negative health effects. Children
responsibility of the user of this standard to establish appro-
are at particular risk, because their growing bodies absorb more
priate safety, health, and environmental practices and deter-
lead than adults, so protecting them from lead is important to
mine the applicability of regulatory limitations prior to use.
lifelong good health. According to the Centers for Disease
1.7 This international standard was developed in accor-
Control and Prevention (CDC), elevated blood lead levels have
dance with internationally recognized principles on standard-
been linked to anemia, kidney and brain damage, learning
ization established in the Decision on Principles for the
disabilities, and decreased growth. As a result of widespread
Development of International Standards, Guides and Recom-
human use, lead is prevalent in the environment; for example,
mendations issued by the World Trade Organization Technical
it can be found in paint (lead in paint was banned in the United
Barriers to Trade (TBT) Committee.
States in 1978) and soil, and can leach into drinking water
from lead-containing plumbing materials, such as faucets and
2. Referenced Documents
drinking fountains.
2.1 ASTM Standards:
1.2 Lead in school drinking water is a concern because it is
E3032 Guide for Climate Resiliency Planning and Strategy
a daily source of water for over 50 million children enrolled in
public schools. The pattern of school schedules—including
2.2 EPA References:
time off over weekends, holidays, and extended breaks—can
EPA 810-R-19-003 EPA. Strategies to Achieve Full Lead
contribute to standing water in the school’s plumbing system.
Service Line Replacement. October 2019
If there is lead in the plumbing system, the potential for it to
EPA 816-B-22-001 EPA Guidance for Developing and
leach into water can increase the longer the water remains in
Maintaining a Service Line Inventory. August 2022
contact with the plumbing. Estimating the risk of lead con-
tamination of schools’ drinking water at the State level is a
3. Terminology
complex and important challenge. Variable water quality
3.1 Definitions of Terms Specific to This Standard:
among water systems and changes in water chemistry during
3.1.1 community water system, CWS, n—as defined in the
distribution affect lead dissolution rates from pipes and fittings.
Safe Drinking Water Act, a water system that supplies water to
In addition, the locations of lead-bearing plumbing materials
the same population year-round.
are uncertain. EPA, 2002 (3), Triantafyllidou and Edwards,
3.1.1.1 Discussion—A community water system serves at
2012 (4).
least 25 people at their primary residences or at least 15
1.3 The US EPA is responsible for enforcement of the Safe
residences that are primary residences (for example,
Drinking Water Act (SDWA) on Tribal land; there is no
municipalities, mobile home park, subdivisions).
delegation of this authority to the States.
3.1.2 maximum contaminant level (MCL), n—The highest
1.4 Sections 50105 and 50110 of the Infrastructure Invest- level of a contaminant that is allowed in drinking water.
ment and Jobs Act (Public Law 117–58) (1) provides funding
3.1.2.1 Discussion—MCLs are set as close to MCLGs as
and directs the US EPA and the Department of Interior to feasible using the best available treatment technology and
address lead in drinking water systems that provide potable
taking cost into consideration. MCLs are enforceable stan-
water to schools and on Tribal land. EPA has announced that in dards.
accordance with this statute, the Agency discourages partial
3.1.3 maximum contaminant level goal (MCLG), n—The
lead service line replacements and encourages full replacement
level of a contaminant in drinking water below which there is
of deficient service lines. The legislation provided the US EPA
no known or expected risk to health.
with approximately $15 billion over a 5-year period to achieve
3.1.3.1 Discussion—MCLGs allow for a margin of safety
this goal.
and are non-enforceable public health goals.
1.5 This guide describes steps to rapidly identify commu-
3.1.4 national primary drinking water regulations
nity and public water systems, as defined in the SDWA, at risk
(NPDWRs), n—the National Primary Drinking Water Regula-
tions (NPDWR) are legally enforceable primary standards and
This guide is under the jurisdiction of ASTM Committee E50 on Environmental treatment techniques that apply to public water systems.
Assessment, Risk Management and Corrective Action and is the direct responsibil-
ity of Subcommittee E50.05 on Environmental Risk Management.
Current edition approved May 1, 2023. Published July 2023. DOI: 10.1520/
E3366–23 For referenced ASTM standards, visit the ASTM website, www.astm.org, or
Adapted from “Identifying Schools at High Risk for Elevated Lead in Drinking contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
Water Using Only Publicly Available Data. Science of the Total Environment Standards volume information, refer to the standard’s Document Summary page on
The boldface numbers in parentheses refer to a list of references at the end of the ASTM website.
this standard. Available from United States Environmental Protection Agency (EPA), William
Lead in Paint. Centers for Disease Control and Prevention. https:// Jefferson Clinton Bldg., 1200 Pennsylvania Ave., NW, Washington, DC 20460,
www.cdc.gov/nceh/lead/prevention/sources/paint.htm http://www.epa.gov.
E3366 − 23
3.1.4.1 Discussion—Primary standards and treatment tech- 4.3 California’s State Water Resources Control Board’s
niques protect public health by limiting the levels of contami- Division of Drinking Water initiated an aggressive program of
nants in drinking water. sampling and public water systems supplying water to schools
in 2018. California Assembly Bill 746 published on October
3.1.5 public water system, n—As defined in the Safe Drink-
12, 2017, effective January 1, 2018, requires community water
ing Water Act, a public water system provides water for human
systems to test lead levels, by July 1, 2019, in drinking water
consumption through pipes or other constructed conveyances
at all California public, K-12 school sites that were constructed
to at least 15 service connections or serves an average of at
before January 1, 2010.
least 25 people for at least 60 days a year.
4.4 Lobo (2021) (6) reports that two factors predominantly
3.1.5.1 Discussion—A public water system may be publicly
or privately owned. control lead leaching into the drinking water: (1) the presence
or absence of lead-bearing plumbing materials, and (2) water
3.1.6 vulnerable communities, n—are groups and commu-
quality that promotes the formation of soluble or insoluble lead
nities at a higher risk for poor health as a result of the barriers
corrosion products. This guide provides a method of using
they experience to social, economic, political and environmen-
publicly-available information to determine if the water sup-
tal resources, as well as limitations due to illness or disability.
plied to schools presents an unacceptable lead exposure hazard.
3.2 Abbreviations and Acronyms:
4.5 The procedures described in the guide are consistent
3.2.1 CCR—Consumer Confidence Report
with Sections 4, 5, and 6 of Guide E3032.
3.2.2 CWS—Community Water System
5. Procedure
3.2.3 EPA—U.S. Environmental Protection Agency
5.1 Data Collection:
3.2.4 GAO—General Accountability Office
5.1.1 The data requirements for this guide include
3.2.5 GIS—Geographic Information System
demographics, water quality, age of the water supply pipes and
associated infrastructure, and school capture area (boundar-
3.2.6 LSL—Lead Service Line
ies) . The data requirements are based upon the research
3.2.7 LSLR—Lead Service Line Replacement
conducted at the University of California, Berkeley (Lobo,
3.2.8 MCL—Maximum Contaminant Level
2021 (7).
3.2.9 MCLG—Maximum Contaminant Level Goal
5.2 Demographic Data:
5.2.1 Use the US Census Bureau’s data portal ()to obtain the
3.2.10 NPDWR—National Primary Drinking Water Regula-
socioeconomic information for the students attending each
tions
school by assigning data from individual census tracts to
3.2.11 SDWA—Safe Drinking Water Act (42 USC 300f et
schools drawing students from those census tracts. Social data
seq. 1974; §612 as implemented by Public Law No: 114-322.
from American Community Survey (8) should be used to
2016)
estimate social conditions within census tracts. Select socio-
3.2.12 SDWIS —Safe Drinking Water Information System economic features that correspond to race, poverty levels and
unemployment. State annual school census reports, that include
4. Significance and Use information on race/ethnicity, by grade level, are another
source of demographic data that is publicly available.
4.1 Lead can enter drinking water when service lines or
5.2.1.1 Low-income minority groups have been reported to
plumbing fixtures that contain lead corrode, especially where
be at a disproportionately larger risk of lead exposure from old
the water has high acidity or low mineral content. According to
and poorly maintained water infrastructure in Flint, MI and the
the EPA, lead typically enters school d
...

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