Document headings vary by document type but may contain the following:
See the Document Drafting Handbook for more details.
AGENCY:
Environmental Protection Agency (EPA).
ACTION:
Final rule.
SUMMARY:
In December 2023, the U.S. Environmental Protection Agency (EPA) requested comment on the proposed the Lead and Copper Rule Improvements (LCRI), which informed the revisions to the National Primary Drinking Water Regulation (NPDWR) for lead and copper. After consideration of public comment on the LCRI, and consistent with the provisions set forth under the Safe Drinking Water Act (SDWA), the EPA is finalizing revisions to the NPDWR for lead and copper. In this rule, the agency is finalizing requirements for drinking water systems to replace lead and certain galvanized service lines. The final rule also removes the lead trigger level, reduces the lead action level to 0.010 mg/L, and strengthens tap sampling procedures to improve public health protection and simplify implementation relative to the 2021 Lead and Copper Rule Revisions (LCRR). Further, this final rule strengthens corrosion control treatment, public education and consumer awareness, requirements for small systems, and sampling in schools and child care facilities. The final rule will significantly reduce the adverse human health impacts of exposure to toxic lead in drinking water.
DATES:
Effective date: This final rule is effective on December 30, 2024.
Judicial review: For judicial review purposes, this final rule is promulgated as of October 30, 2024.
Compliance dates: The compliance date for the revisions to 40 CFR part 141, subpart I, is set forth in § 141.80(a). The compliance date for the revisions to 40 CFR 141.2 and 141.31 is November 1, 2027. The compliance date for the changes made to 40 CFR part 141, subpart O, is set forth in § 141.152(a). The compliance date for the changes to 40 CFR part 141, subpart Q (§ 141.202 and appendices A and B) is November 1, 2027.
ADDRESSES:
The EPA has established a docket for this action under Docket ID No. EPA-HQ-OW-2022-0801. All documents in the docket are listed on the https://www.regulations.gov website. Although listed in the index, some information is not publicly available, e.g., Confidential Business Information or other information whose disclosure is restricted by statute. Certain other material, such as copyrighted material, is not placed on the internet and will be publicly available only in hard copy form. Publicly available docket materials are available electronically through https://www.regulations.gov.
FOR FURTHER INFORMATION CONTACT:
Michael Goldberg, Office of Ground Water and Drinking Water, Standards and Risk Management Division (Mail Code 4607M), Environmental Protection Agency, 1200 Pennsylvania Ave. NW, Washington, DC 20460; telephone number: 202-564-1379; email address: LCRI@epa.gov.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Executive Summary
II. General Information
A. What does the final LCRI require?
B. Does this action apply to me?
C. Dates for Compliance
III. Background
A. Overview of Lead and Lead Exposures Through Drinking Water
B. Human Health Effects of Lead and Copper
C. Regulatory History
D. Statutory Authority
E. Anti-backsliding Analysis of LCRI Relative to LCR and LCRR
F. White House Lead Pipe and Paint Action Plan and EPA's Strategy To Reduce Lead Exposures and Disparities in U.S. Communities
G. Bipartisan Infrastructure Law and Other Financial Resources
H. Lead Exposure and Environmental Justice, Equity, and Federal Civil Rights
IV. Final Revisions to 40 CFR Part 141, Subpart I, Control of Lead and Copper
A. Regulatory Approach
B. Service Line Replacement
C. Service Line Replacement Plan
D. Service Line Inventory
E. Tap Sampling for Lead and Copper
F. Corrosion Control Treatment
G. Water Quality Parameter Monitoring
H. Distribution System and Site Assessment
I. Compliance Alternatives for a Lead Action Level Exceedance for Small Community Water Systems and Non-Transient Non-Community Water Systems
J. Public Education
K. Additional Requirements for Systems With Multiple Lead Action Level Exceedances
L. Lead Sampling at Schools and Child Care Facilities
M. Copper
N. System Reporting and Recordkeeping Requirements
O. Other Proposed Revisions to 40 CFR Part 141
V. Rule Implementation and Enforcement
A. General
B. What are the rule compliance dates?
C. State Primacy and Special Primacy Requirements
D. State Reporting and Recordkeeping Requirements
VI. Economic Analysis
A. Summary of Public Comments and the EPA's Response
B. Affected Entities and Major Data Sources Used To Develop the Baseline
C. Overview of the Cost-Benefit Model
D. Cost Analysis
E. Benefits Analysis
F. Cost-Benefit Comparison
G. Alternative Regulatory Options Considered
VII. Statutory and Executive Order Reviews
A. Executive Order 12866 (Regulatory Planning and Review) and Executive Order 14094 (Modernizing Regulatory Review)
B. Paperwork Reduction Act (PRA)
C. Regulatory Flexibility Act (RFA)
D. The Unfunded Mandates Reform Act (UMRA)
E. Executive Order 13132 (Federalism)
F. Executive Order 13175 (Consultation and Coordination With Indian Tribal Governments)
G. Executive Order 13045 (Protection of Children From Environmental Health and Safety Risks)
H. Executive Order 13211 (Actions That Significantly Affect Energy Supply, Distribution, or Use)
I. National Technology Transfer and Advancement Act of 1995
J. Executive Order 12898 (Federal Actions To Address Environmental Justice in Minority Populations and Low-Income Populations) and Executive Order 14096 (Revitalizing Our Nation's Commitment to Environmental Justice for All)
K. Consultations With the Science Advisory Board (SAB) and the National Drinking Water Advisory Council (NDWAC)
L. Consultation With the Department of Health and Human Services Under SDWA Section 1412(d)
M. Congressional Review Act (CRA)
VIII. Severability
IX. References
I. Executive Summary
The United States Environmental Protection Agency's (EPA) mission is to protect human health and the environment. The EPA is finalizing the Lead and Copper Rule Improvements (LCRI) to significantly reduce the risk of exposure to lead through drinking water. There is no known safe level of lead in drinking water. Exposure to drinking water contaminated with lead can cause serious human health impacts including neurodevelopmental problems in children and heart disease in adults. Young children and pregnant people are especially susceptible to the impacts of lead exposure. Reducing lead in drinking water will reduce the risk of negative neurodevelopmental outcomes for children as well as reduce a range of health risks to adults. This final rule builds on the 2021 Lead and Copper Rule Revisions (LCRR) and the pre-2021 Lead and Copper Rule (LCR), originally promulgated in 1991.
The EPA conducted a review of the 2021 LCRR in accordance with Executive Order 13990 and announced its intention to strengthen the 2021 LCRR with this new rulemaking, the LCRI, to address key issues and opportunities identified in the review. This final LCRI addresses the priorities the EPA identified in the 2021 LCRR review, including the equitable replacement of lead service lines (LSLs) in the nation, improving identification of where LSLs are located, and triggering action in communities most at risk of lead exposure, and streamlined and improved implementation of the rule relative to the 2021 LCRR. This final LCRI is the culmination of numerous meaningful consultations with stakeholders and the public during the 2021 LCRR review, engagements and consultations held to support the development of the LCRI, and public comments received on the proposed LCRI.
Protecting Public Health and the Environment and Restoring Science to Tackle the Climate Crisis (86 FR 7037, January 20, 2021).
The LCRI makes important advancements in protecting children and adults from the significant and irreversible health effects of exposure to lead in drinking water. These advancements are scientifically based and incorporate drinking water system best practices. The final rule strengthens the lead and copper rule in five focus areas: (1) achieving lead pipe replacement within 10 years, (2) locating legacy lead pipes, (3) improving tap sampling, (4) lowering the lead action level, and (5) strengthening protections to reduce exposure. The final rule also includes compliance dates and an updated benefits and costs analysis. Each of these topics is summarized below, in sequential order.
Achieving Lead Pipe Replacement Within 10 Years
This final rule provides a fundamental shift to a more preventive approach to lead in drinking water. This is based on the EPA's experience in implementing the lead rule for many years. Specifically, based on over 30 years of implementing the 1991 LCR, the EPA has determined that requiring lead service line replacement (LSLR) based on tap sampling and 90th percentile lead levels alone is insufficient to protect public health. LSLs are a source of lead exposure in drinking water, even when systems are optimized at or below the lead action level.
The science is clear that there is no known safe level of lead in drinking water, especially for children. Among other effects, lead exposure can cause damage to the brain and kidneys and can interfere with the production of red blood cells that carry oxygen to all parts of the body. In children, even low levels of lead exposure can cause cognitive health effects like lower intelligence quotient (IQ) as well as learning and behavioral problems. In adults, health effects include elevated risk of heart disease, high blood pressure, kidney or nervous system problems, and cancer.
In the LCRI, the EPA is requiring water systems to replace all lead and certain galvanized service lines (specifically, galvanized requiring replacement (GRR) service lines) under their control no later than 10 years after the compliance date. The LCRI provides, in limited circumstances, additional time for some systems to complete systemwide full service line replacement. Water systems must replace lead and GRR service lines under their control regardless of the lead levels occurring in tap or other drinking water samples. Replacing lead and GRR service lines will significantly reduce lead releases into drinking water. In addition, while consistently well-operated and optimized corrosion control treatment (CCT) is generally effective at reducing lead to low levels, elimination of lead and GRR service lines will result in even greater public health protection by eliminating a significant lead exposure source and will minimize the impacts of CCT implementation errors that have been documented over the years.
Historically, lead service lines, as well as lead-bearing fixtures and solder, were commonly used in water distribution systems as well as in home plumbing. While replacing LSLs does not eliminate all lead exposures from tap water because plumbing systems inside homes and buildings ( i.e., premise plumbing) can also contain lead components, replacing LSLs removes a key source of lead in drinking water. Where present, LSLs represent the greatest lead exposure source through drinking water (Sandvig et al., 2008). Buildings and homes built before 1986 often have LSLs connecting their plumbing system to the main water supply line under the street. These LSLs can deteriorate or corrode, releasing lead particles into the drinking water (Sandvig et al., 2008). Modeling done as part of the LCRI economic analysis confirms that LSL presence significantly contributes to drinking water lead levels (USEPA, 2024a).
The EPA does not believe that there are lead water mains in the United States and, if they do occur, it is extremely rare. The poor structural integrity of lead pipes that are more than two inches in diameter means that lead was primarily used in pipes of smaller diameter such as service lines. Conversely, the water mains that distribute water throughout a city or town tend to be six inches or larger in diameter. The common water main materials include ductile iron, PVC, asbestos cement, high-density polyethylene (HDPE), and concrete steel. The oldest water mains are cast iron and asbestos cement (Folkman, 2018).
Sandvig et al. (2008) found that LSLs contributed an average of approximately 50 to 75 percent of the total lead mass measured at the tap, while premise piping and the faucet contributed approximately 20 to 35 percent and 1 to 3 percent, respectively. At sites with no LSL, premise piping and the faucet contributed a greater percentage of lead mass to the total lead mass measured at the tap (approximately 55 percent and 12 percent, respectively), while main samples ranged from approximately 3 to 15 percent.
Locating Legacy Lead Pipes
Knowing where lead pipes are located is critical to replacing them efficiently and equitably, as well as for informing consumers ( i.e., persons served) so they can take actions to reduce their exposure to lead. The LCRI builds upon the 2021 LCRR's requirement for water systems to create an initial inventory, to regularly update their inventory, and to identify the material of all service lines by the mandatory service line replacement deadline. Under the final LCRI, all water systems are required to make their service line inventories publicly available. Water systems must use a validation process to ensure the service line inventory is accurate. Water systems are also required to track lead connectors in their inventories and replace them as they are encountered.
Improving Tap Sampling
The final LCRI makes key changes to the required protocol for tap sampling informed by best practices already being deployed at the local and State level. Under the LCRI, water systems are required to collect first- and fifth-liter tap samples at sites with LSLs and use the higher of the two values when determining compliance. This method will better represent water that has been stagnant both within the LSL and the premise plumbing. This will help water systems better understand the effectiveness of their CCT.
Lowering the Lead Action Level
The final LCRI lowers the lead action level from 0.015 mg/L to 0.010 mg/L. When a water system exceeds the lead action level, it is required to inform the public, take actions associated with CCT, and employ public education measures to reduce lead exposure. For example, a system may be required to install or adjust CCT to reduce lead that leaches into drinking water. Actions resulting from a lowered lead action level will improve public health benefits because they will require systems to take actions to reduce lead exposure sooner. The EPA also emphasizes the many final rule requirements that will result in additional public health benefits irrespective of systemwide lead levels, recognizing there is no safe level of lead in drinking water. For example, the final rule requires full service line replacement and public education provisions independent of a system's 90th percentile lead level.
Strengthening Protections To Reduce Exposure
The final LCRI requires water systems with continually high lead levels to conduct additional outreach to consumers and make filters certified to reduce lead in drinking water available to all consumers. These additional actions can reduce consumer exposure to higher levels of lead in drinking water while the water system works to reduce systemwide lead levels ( e.g., achieving 100 percent replacement of lead and GRR service lines, installing or re-optimizing optimal corrosion control treatment (OCCT)), which may take years to fully implement.
Benefits and Costs Analysis
As part of its Health Risk Reduction and Cost Analysis (HRRCA), the EPA evaluated quantifiable and nonquantifiable health risk reduction benefits and costs associated with the final LCRI. At a two percent discount rate, the EPA estimates the quantifiable annual benefits of the final rule will be $13.49 to $25.14 billion and the quantifiable annual costs of the rule will be $1.47 to $1.95 billion in 2022 dollars. The EPA Administrator confirms the determination made at proposal that the quantified and nonquantifiable benefits of the final LCRI justify the quantified and nonquantifiable costs.
To evaluate these benefits and costs, the EPA determined which entities would be affected by the LCRI, quantified costs using available data, and described nonquantifiable costs. The EPA quantified benefits by estimating and monetizing avoided reductions in IQ, cases of attention-deficit/hyperactivity disorder (ADHD) in children, lower birth weights in children, and cases of cardiovascular disease premature mortality in adults associated with lead and GRR service line replacement, CCT installation and re-optimization, the use of point-of-use devices as a small system compliance option, and the temporary use of point-of-use devices and water filters in systems with multiple lead action level exceedances. Prior efforts to quantify benefits associated with reducing lead in drinking water have focused on neurodevelopmental outcomes in children because of the lifelong impact on their ability to thrive. The current benefits assessment also incorporates recent scientific analyses that allow better quantification of benefits to adults associated with reductions in lead exposure.
There are many additional benefits of the LCRI that the EPA assessed qualitatively. For example, the requirements for water systems to issue public education (including using languages of the communities where systems serve a large proportion of consumers with limited English proficiency), to make the inventory of service line and connector materials publicly available, and to make the service line replacement plan publicly available will promote the public's behaviors to reduce their exposure to lead in drinking water. Health benefits qualitatively evaluated include reduced incidence of renal effects, reproductive and developmental effects (apart from ADHD), immunological effects, neurological effects (apart from children's IQ), and cancer.
In addition, persons served by systems required to install or re-optimize OCCT under the final LCRI and living in homes with premise plumbing containing lead will receive health benefits from reduced lead exposure that were not quantified in the analysis of the final rule. Increased use of CCT resulting from the final LCRI's lower lead action level and improved tap sampling may have a beneficial secondary effect of reducing copper levels and avoiding certain negative health impacts of copper, such as acute gastrointestinal conditions and health effects associated with Wilson's Disease. Other nonquantifiable co-benefits associated with the increased use of corrosion inhibitors resulting from the LCRI's lower lead action level and improved tap sampling include extending the useful life of plumbing components and appliances ( e.g., water heaters), reduced plumbing maintenance costs, reduced treated water loss from the distribution system due to leaks, and reduced potential liability and damages from broken pipes in buildings.
To support eliminating LSLs, the Infrastructure Investment and Jobs Act (Pub. L. 117-58), also referred to as the Bipartisan Infrastructure Law (BIL), included $15 billion specifically appropriated for LSLR projects and associated activities directly connected to the identification and replacement of LSLs. The BIL also included over $11.7 billion for the Drinking Water State Revolving Fund General Supplemental, which can also be used for lead service line replacement as well as other drinking water projects. The agency notes the costs cited above do not take into account this available funding source. The EPA is also providing significant technical assistance to communities through efforts such as the “Get the Lead Out Initiative” and “Lead Service Line Replacement Accelerators,” which assist efforts to conduct service line replacement.
Compliance and Public Process
Water systems must comply with the requirements of the LCRI starting three years after promulgation of this final rule. The EPA is requiring water systems to comply with select requirements introduced in the 2021 LCRR that the agency did not propose to change in the LCRI, starting on October 16, 2024. This includes the 2021 LCRR initial LSL inventory, notification of service line material, and associated reporting requirements. Water systems must also comply with the Tier 1 public notification (PN) requirement for a lead action level exceedance that was introduced under the 2021 LCRR starting October 16, 2024. Please see section V.B.3 of this preamble for a full discussion of the provisions with a compliance date of October 16, 2024. The final LCRI otherwise requires water systems to comply with the pre-2021 LCR (and not the 2021 LCRR) between October 16, 2024, and the LCRI compliance date so that water systems can directly transition from the regulatory scheme of the LCR to the LCRI.
II. General Information
The final Lead and Copper Rule Improvements (LCRI) builds upon the previous lead and copper rules. The LCRI revises the most recent lead and copper rule, the 2021 Lead and Copper Rule Revisions (LCRR), which was promulgated on January 15, 2021 (86 FR 4198, USEPA, 2021a). Key revisions in the LCRI address the opportunities for improvement identified in the “Review of the National Primary Drinking Water Regulation: Lead and Copper Rule Revisions” (or LCRR review) including proactively and equitably replacing all lead service lines (LSLs), strengthening compliance with tap sampling to better identify communities most at risk of elevated lead in drinking water to better compel actions to reduce health risks, reducing the complexity of the regulation, and ensuring that the rule is more understandable (86 FR 71574, USEPA, 2021b). The United States Environmental Protection Agency (EPA) developed the LCRI considering the input received in numerous meaningful consultations and engagements over several years, including during the LCRR review and in stakeholder outreach conducted to inform the development of the proposed and final LCRI, along with almost 200,000 public comments submitted to the docket as well as oral comments provided to the EPA during the public hearing held January 16, 2024, for the proposed LCRI.
A. What does the final LCRI require?
The LCRI requires full service line replacement of lead and galvanized requiring replacement (GRR) service lines under the control of the water system, regardless of the system's 90th percentile lead level. Water systems are required to complete replacements within 10 years of the LCRI compliance date. There is a limited exception for systems with a high proportion of service lines requiring replacement: they are eligible for a deferred deadline if they meet a specified threshold and receive State approval. Systems with deferred deadlines and States must regularly assess whether they can complete the replacement at a faster rate. Water systems must identify all service lines of unknown composition (“unknown service lines”) to replace all lead and GRR service lines by the replacement deadline. Systems must also track lead connectors in their inventories and replace them whenever encountered during normal operations. All water systems with non-lead service lines in their inventories must validate the methods used to categorize those service lines as non-lead with some exceptions. All water systems with known or potential lead or GRR service lines must prepare and make publicly accessible a service line replacement plan which can facilitate the equitable replacement of all lead or GRR service lines by the replacement deadline.
The final LCRI reduces the lead action level from 0.015 mg/L to 0.010 mg/L, which will result in more water systems installing and re-optimizing optimal corrosion control treatment (OCCT) and providing public education to reduce drinking water lead exposure. Systems that exceed the lead action level three or more times in a five-year period must take additional actions to provide public education and make filters available.
The rule updates the tap sampling protocol by requiring systems to collect a first-liter sample (in addition to the fifth-liter sample required by the 2021 LCRR) at structures with LSLs and then use the higher of the first- or fifth-liter sample values at the LSL sites when calculating the 90th percentile. The first- and fifth-liter sample values represent water that has been stagnant in premise plumbing (plumbing within buildings) and within the service line, respectively, and therefore, more accurately identify where higher lead levels might be present compared to sampling the first liter or the fifth liter alone. Systems must prioritize sampling at sites most likely to contain lead and use this data to calculate the 90th percentile. The LCRI requires most systems with lead and GRR service lines to start (or continue) standard monitoring. Additionally, any system with a 90th percentile lead level above the LCRI lead action level, based on the system's results from the most recent tap monitoring period prior to the compliance date, will need to start (or continue) standard monitoring. The EPA updated the requirements for systems with insufficient Tier 1 and Tier 2 sites to meet their minimum required number of samples to use the highest sample results from Tiers 1, 2, and the next highest available tiers (equal to the minimum required number of samples) to calculate the 90th percentile. Sample site tiers are used to prioritize sampling locations and were first introduced in the 1991 LCR.
The LCRI requires States to set optimal water quality parameters (OWQPs) for medium systems (serving greater than 10,000 persons and fewer than or equal to 50,000 persons) that are required to optimize or re-optimize corrosion control treatment (CCT). These systems must meet those parameters to demonstrate that OCCT is being maintained. The rule allows all systems to defer OCCT or re-optimized OCCT (but maintain any existing CCT) if they can replace all lead and GRR service lines at a minimum percent annual rate within five years or less. Water systems with lead and GRR services lines and OCCT that are meeting their OWQPs are not required to re-optimize their OCCT more than once following a lead action level exceedance after the compliance date. After systems remove all of their lead and GRR service lines, they must re-optimize again if they exceed the lead action level. In addition, water systems may be required to re-optimize by the State at any time. Systems not required to re-optimize under the final rule still have to meet other requirements, including for public education if there are multiple action level exceedances (see sections IV.J and IV.K of this preamble).
The LCRI updates public education requirements, instituting changes to content and delivery frequency for more proactive messaging about lead in drinking water and actions individuals can take to reduce their exposure. It includes requirements to make information about lead in drinking water more accessible to consumers including individuals with limited English proficiency. The LCRI also introduces new public education requirements for lead and copper.
The LCRI revises the small system compliance flexibility provision to eliminate LSLR as a compliance option, as all systems must conduct mandatory service line replacement regardless of their 90th percentile lead level. The eligibility threshold for the flexibility for community water systems (CWSs) is lowered to those serving 3,300 or fewer persons.
The LCRI retains the requirements from the 2021 LCRR for CWSs to conduct sampling and public education in schools and child care facilities but expands the available waivers to include sampling efforts conducted prior to the rule compliance date, including sampling conducted through the Water Infrastructure Improvements for the Nation (WIIN) Act grant program. The LCRI also restructures and clarifies areas of the rule that did not change to make the rule more implementable.
Exhibit 1 compares the major differences among the pre-2021 Lead and Copper Rule (LCR), 2021 LCRR, and the final LCRI. Asterisks (*) in the pre-2021 LCR and 2021 LCRR column denote requirements that are retained in the final LCRI, and these requirements are, therefore, not repeated in the final LCRI column.
Exhibit 1—Comparison of the 2021 LCRR, Proposed LCRI, and Final LCRI Requirements
Category | Examples of potentially affected entities |
---|---|
Public water systems | CWSs; NTNCWSs. |
State and Tribal government agencies | Agencies responsible for developing, ensuring compliance with, and enforcing National Primary Drinking Water Regulations (NPDWRs). |
Exhibit 2—Percent of Systems by LSL and CCT Status With Lead Levels at or Below Potential Lead Action Levels Adjusted for the Final LCRI Sampling Protocol
[2012-2020]
Exhibit 3—Requirements Introduced in the 2021 LCRR That Water Systems Must Comply With Between October 16, 2024, and the LCRI Compliance Date
Citation (CFR codified July 1, 2023) | Description |
---|---|
§ 141.84(a)(1) through (10) (excluding paragraphs (a)(6) and (7)) | Initial public service line inventory development. |
§ 141.90(e)(1) | Submission of initial inventory to the State. |
§ 141.85(e) | Initial and annual notification of known or potential service line containing lead. |
§ 141.85(a)(1)(ii) | Revised lead health effects language. |
§ 141.90(e)(13) and (f)(4) | Annual reporting and certification of the notifications in § 141.85(e) to the State. |
§ 141.90(h)(3) | State provides results of the 90th percentile lead calculations, in writing, to the water system within 15 days of the end of the tap sampling period (if applicable). |
§§ 141.201(a)(3)(vi) and 141.202(a)(10) | Tier 1 PN for exceedance of the lead action level as specified in § 141.80(c). |
§§ 141.201(c)(3) and 141.31(d)(2) | Submit copy of Tier 1 PN for a lead action level exceedance to the head of the primacy agency and the EPA administrator no later than 24 hours after the system learns of the exceedance. |
40 CFR part 141, appendix A to subpart Q, section I.C.1 (excluding § 141.90, except paragraphs (e)(1) and (13) and (f)(4)) | Tier 3 PN required for: failure to notify persons served at service connections of a known or potential service line containing lead and failure to submit initial inventory to the State by October 16, 2024. |
40 CFR part 141, appendix B to subpart Q, section D.23 | Revised lead health effects language for required PN. |
As codified on July 1, 2020. |
Exhibit 4—Data Sources Used To Develop the Baseline for the Final LCRI
Exhibit 5—PWS Cost Components, Subcomponents, and Activities Organized by Section
Exhibit 6—Estimated National Total Monetized Annualized PWS Rule Costs—2 Percent Discount Rate
[Millions of 2022 USD]
PWS annual costs | Low estimate | High estimate | ||||
---|---|---|---|---|---|---|
Rule component | Baseline | LCRI | Incremental | Baseline | LCRI | Incremental |
Sampling | $134.0 | $166.0 | $32.0 | $143.6 | $176.2 | $32.6 |
PWS Service Line Replacement * | 84.6 | 1,259.0 | 1,174.4 | 124.5 | 1,763.9 | 1,639.4 |
Corrosion Control Technology | 552.0 | 591.1 | 39.1 | 647.8 | 692.9 | 45.1 |
Point-of Use Device Installation and Maintenance | 2.4 | 5.1 | 2.7 | 5.9 | 9.6 | 3.7 |
Public Education and Outreach | 69.6 | 267.3 | 197.7 | 72.1 | 302.2 | 230.1 |
Rule Implementation and Administration | 0.1 | 3.4 | 3.3 | 0.2 | 3.4 | 3.2 |
Total Annual PWS Costs | 842.7 | 2,291.9 | 1,449.2 | 994.1 | 2,948.2 | 1,954.1 |
* Service line replacement includes full and partial lead and GRR service line replacements. | ||||||
Previous Baseline costs are projected over the 35-year period of analysis and are affected by the EPA's assumptions on three uncertain variables that vary between the low- and high-cost scenarios. For the LCRR Economic Analysis (USEPA, 2020d), the EPA assumed that the cost of customer-side service line replacements made under the goal-based replacement rate would be paid for by households. The agency also assumed that system-side service line replacements under the goal-based replacement rate and all service line replacements (both customer-side and systems-side) would be paid by the PWS under the three percent mandatory replacement rate. The EPA made these modeling assumptions based on the different levels of regulatory responsibility systems faced operating under a goal-based replacement rate versus a mandatory replacement rate. While systems would not be subject to a potential violation for not meeting the target replacement rate under the goal-based replacement requirement, under the three percent mandatory replacement rate, the possibility of a violation could motivate more systems to meet the target replacement rate even if they had to adopt customer incentive programs that would shift the cost of replacing customer-side service lines from customers to the system. To be consistent with these LCRR modeling assumptions, under the LCRI, the EPA assumed that mandatory replacement costs would fall only on systems. Therefore, the negative incremental values reported for the “Household Service Line Replacement Costs” category do not represent a net cost savings to households. They represent an assumed shift of the estimated service line replacement costs from households to systems. The EPA has insufficient information to estimate the actual service line replacement cost-sharing relationship between customers and systems at a national level for this analysis. |
Exhibit 7—Estimated Annualized Incremental Cost per Household by Community Water System Category—Low Scenario
[2022 USD]
Ownership | Source water | Size | Mean | 10th percentile | 25th percentile | 50th percentile | 75th percentile | 90th percentile |
---|---|---|---|---|---|---|---|---|
Private | Ground | Less than 100 | $67.10 | $28.10 | $39.80 | $57.80 | $89.00 | $117.00 |
Private | Ground | 101 to 500 | 22.50 | 6.40 | 11.40 | 19.40 | 28.10 | 43.50 |
Private | Ground | 501 to 1,000 | 4.60 | 1.20 | 1.60 | 3.00 | 6.10 | 8.50 |
Private | Ground | 1,001 to 3,300 | 2.70 | 0.60 | 0.90 | 1.60 | 3.60 | 4.80 |
Private | Ground | 3,301 to 10,000 | 8.50 | −0.20 | 0.60 | 5.00 | 14.50 | 25.00 |
Private | Ground | 10,001 to 50,000 | 6.50 | 0.10 | 0.60 | 6.40 | 11.20 | 14.30 |
Private | Ground | 50,001 to 100,000 | 7.50 | 0.00 | 0.30 | 8.70 | 11.70 | 13.90 |
Private | Ground | 100,001 to 1,000,000 | 4.70 | 0.00 | 0.20 | 3.80 | 8.50 | 9.70 |
Private | Surface | Less than 100 | 59.20 | 23.40 | 32.80 | 50.90 | 78.60 | 106.40 |
Private | Surface | 101 to 500 | 17.70 | 5.60 | 8.40 | 15.00 | 22.40 | 33.70 |
Private | Surface | 501 to 1,000 | 4.30 | 1.50 | 1.90 | 2.80 | 5.20 | 8.70 |
Private | Surface | 1,001 to 3,300 | 2.60 | 0.60 | 0.70 | 1.40 | 3.20 | 4.60 |
Private | Surface | 3,301 to 10,000 | 9.70 | 0.30 | 0.80 | 6.40 | 15.30 | 26.20 |
Private | Surface | 10,001 to 50,000 | 5.50 | 0.20 | 0.50 | 4.70 | 9.60 | 13.00 |
Private | Surface | 50,001 to 100,000 | 7.00 | 0.00 | 2.00 | 7.90 | 10.90 | 13.80 |
Private | Surface | 100,001 to 1,000,000 | 5.70 | 0.00 | 0.20 | 6.10 | 9.70 | 12.10 |
Private | Surface | Greater than 1,000,000 | 1.90 | 1.30 | 1.30 | 2.40 | 2.40 | 2.60 |
Public | Ground | Less than 100 | 52.20 | 23.40 | 31.60 | 43.50 | 69.50 | 93.90 |
Public | Ground | 101 to 500 | 14.80 | 4.90 | 7.40 | 11.80 | 18.60 | 28.10 |
Public | Ground | 501 to 1,000 | 3.70 | 1.20 | 1.60 | 2.50 | 4.40 | 6.70 |
Public | Ground | 1,001 to 3,300 | 2.00 | 0.50 | 0.70 | 1.30 | 2.50 | 3.50 |
Public | Ground | 3,301 to 10,000 | 7.10 | 0.20 | 0.60 | 4.30 | 11.30 | 19.30 |
Public | Ground | 10,001 to 50,000 | 4.50 | 0.10 | 0.50 | 4.00 | 7.30 | 10.20 |
Public | Ground | 50,001 to 100,000 | 5.20 | 0.00 | 0.90 | 6.00 | 8.20 | 9.90 |
Public | Ground | 100,001 to 1,000,000 | 5.20 | 0.00 | 1.20 | 6.30 | 8.00 | 9.60 |
Public | Ground | Greater than 1,000,000 | 0.60 | 0.30 | 0.30 | 0.80 | 0.80 | 0.90 |
Public | Surface | Less than 100 | 54.30 | 21.00 | 29.70 | 52.50 | 72.20 | 90.30 |
Public | Surface | 101 to 500 | 12.60 | 4.40 | 6.30 | 10.20 | 15.50 | 23.60 |
Public | Surface | 501 to 1,000 | 3.50 | 1.30 | 1.60 | 2.40 | 4.20 | 6.40 |
Public | Surface | 1,001 to 3,300 | 2.00 | 0.50 | 0.70 | 1.20 | 2.30 | 3.40 |
Public | Surface | 3,301 to 10,000 | 7.90 | 0.50 | 0.80 | 5.30 | 12.90 | 20.60 |
Public | Surface | 10,001 to 50,000 | 5.00 | 0.20 | 0.60 | 4.60 | 8.40 | 11.10 |
Public | Surface | 50,001 to 100,000 | 5.90 | 0.00 | 0.40 | 6.50 | 9.50 | 11.80 |
Public | Surface | 100,001 to 1,000,000 | 6.50 | 0.10 | 0.50 | 7.60 | 10.00 | 12.10 |
Public | Surface | Greater than 1,000,000 | 2.40 | 0.30 | 0.60 | 2.00 | 2.40 | 5.00 |
Notes: Rows are not included for system categories that contain zero systems. Detailed rows may not add exactly to the total due to independent rounding. | ||||||||
When evaluating the economic impacts on PWSs, the EPA uses the estimated PWS cost of capital to discount future costs (not the 2 percent discount rate used to evaluate social costs and benefit) because this best represents the actual costs of compliance that water systems would incur over time. For more information on cost of capital, see the final LCRI Economic Analysis chapter 4, section 4.2.3.3. |
Exhibit 8—Estimated Annualized Incremental Cost per Household by Community Water System Category—High Scenario
[2022 USD]
Funding | Source Water | Size | Mean | 10th percentile | 25th percentile | 50th percentile | 75th percentile | 90th percentile |
---|---|---|---|---|---|---|---|---|
Private | Ground | Less than 100 | $64.60 | $25.50 | $35.50 | $55.40 | $87.40 | $115.80 |
Private | Ground | 101 to 500 | 22.00 | 4.60 | 9.40 | 18.70 | 27.70 | 46.80 |
Private | Ground | 501 to 1,000 | 4.80 | 1.00 | 1.50 | 2.90 | 6.50 | 11.00 |
Private | Ground | 1,001 to 3,300 | 2.80 | 0.50 | 0.80 | 1.50 | 3.70 | 5.20 |
Private | Ground | 3,301 to 10,000 | 11.20 | −1.70 | 0.60 | 6.20 | 19.50 | 34.00 |
Private | Ground | 10,001 to 50,000 | 8.90 | 0.10 | 0.50 | 8.00 | 15.40 | 20.40 |
Private | Ground | 50,001 to 100,000 | 10.60 | 0.00 | 0.10 | 12.00 | 16.70 | 20.10 |
Private | Ground | 100,001 to 1,000,000 | 6.50 | 0.00 | 0.20 | 6.10 | 11.70 | 13.80 |
Private | Surface | Less than 100 | 57.20 | 20.90 | 29.90 | 49.30 | 79.90 | 108.10 |
Private | Surface | 101 to 500 | 16.70 | 2.60 | 6.90 | 13.30 | 21.20 | 35.10 |
Private | Surface | 501 to 1,000 | 4.40 | 1.20 | 1.80 | 2.70 | 5.60 | 9.70 |
Private | Surface | 1,001 to 3,300 | 2.80 | 0.50 | 0.70 | 1.20 | 3.40 | 5.20 |
Private | Surface | 3,301 to 10,000 | 12.50 | −0.50 | 0.70 | 7.10 | 20.30 | 36.60 |
Private | Surface | 10,001 to 50,000 | 7.50 | 0.10 | 0.60 | 4.90 | 13.10 | 18.20 |
Private | Surface | 50,001 to 100,000 | 9.80 | 0.00 | 2.20 | 10.90 | 15.30 | 19.40 |
Private | Surface | 100,001 to 1,000,000 | 8.00 | 0.00 | 0.10 | 8.50 | 14.00 | 16.90 |
Private | Surface | Greater than 1,000,000 | 2.50 | 1.60 | 1.60 | 3.20 | 3.20 | 3.40 |
Public | Ground | Less than 100 | 51.70 | 22.20 | 29.40 | 44.40 | 71.70 | 92.10 |
Public | Ground | 101 to 500 | 15.00 | 4.40 | 6.40 | 11.50 | 18.80 | 30.60 |
Public | Ground | 501 to 1,000 | 4.00 | 1.20 | 1.50 | 2.50 | 4.80 | 8.20 |
Public | Ground | 1,001 to 3,300 | 2.30 | 0.40 | 0.70 | 1.20 | 2.70 | 4.30 |
Public | Ground | 3,301 to 10,000 | 8.70 | −0.60 | 0.50 | 4.40 | 15.00 | 26.30 |
Public | Ground | 10,001 to 50,000 | 6.20 | 0.10 | 0.50 | 5.70 | 10.50 | 14.40 |
Public | Ground | 50,001 to 100,000 | 7.30 | 0.00 | 1.50 | 8.40 | 11.70 | 14.20 |
Public | Ground | 100,001 to 1,000,000 | 7.20 | 0.00 | 2.00 | 8.60 | 11.00 | 13.50 |
Public | Ground | Greater than 1,000,000 | 0.80 | 0.30 | 0.30 | 1.10 | 1.10 | 1.20 |
Public | Surface | Less than 100 | 52.90 | 19.40 | 28.50 | 50.30 | 71.00 | 90.50 |
Public | Surface | 101 to 500 | 12.60 | 3.80 | 5.40 | 9.80 | 15.80 | 25.50 |
Public | Surface | 501 to 1,000 | 3.60 | 1.10 | 1.50 | 2.30 | 4.60 | 7.60 |
Public | Surface | 1,001 to 3,300 | 2.20 | 0.40 | 0.60 | 1.20 | 2.60 | 4.00 |
Public | Surface | 3,301 to 10,000 | 9.90 | 0.10 | 0.70 | 5.80 | 17.00 | 27.90 |
Public | Surface | 10,001 to 50,000 | 7.00 | 0.20 | 0.60 | 6.20 | 11.70 | 16.00 |
Public | Surface | 50,001 to 100,000 | 8.20 | 0.00 | 0.40 | 9.00 | 13.50 | 16.70 |
Public | Surface | 100,001 to 1,000,000 | 9.10 | 0.00 | 0.60 | 10.50 | 14.10 | 17.00 |
Public | Surface | Greater than 1,000,000 | 3.20 | 0.30 | 0.80 | 2.60 | 3.30 | 6.90 |
Notes: Rows are not included for system categories that contain zero systems. Detailed rows may not add exactly to the total due to independent rounding. | ||||||||
When evaluating the economic impacts on PWSs, the EPA uses the estimated PWS cost of capital to discount future costs (not the two percent discount rate used to evaluate social costs and benefit) because this best represents the actual costs of compliance that water systems would incur over time. For more information on cost of capital, see the final LCRI Economic Analysis chapter 4, section 4.2.3.3. |
Exhibit 9—State Cost Components, Subcomponents, and Activities Organized by Section
Exhibit 10—Estimated National Monetized Annualized Rule Costs—2 Percent Discount Rate
[Millions of 2022 USD]
PWS annual costs | Low estimate | High estimate | ||||
---|---|---|---|---|---|---|
Rule component | Baseline | LCRI | Incremental | Baseline | LCRI | Incremental |
Sampling | $134.0 | $166.0 | $32.0 | $143.6 | $176.2 | $32.6 |
PWS Service Line Replacement * | 84.6 | 1,259.0 | 1,174.4 | 124.5 | 1,763.9 | 1,639.4 |
Corrosion Control Technology | 552.0 | 591.1 | 39.1 | 647.8 | 692.9 | 45.1 |
Point-of Use Installation and Maintenance | 2.4 | 5.1 | 2.7 | 5.9 | 9.6 | 3.7 |
Public Education and Outreach | 69.6 | 267.3 | 197.7 | 72.1 | 302.2 | 230.1 |
Rule Implementation and Administration | 0.1 | 3.4 | 3.3 | 0.2 | 3.4 | 3.2 |
Total Annual PWS Costs | 842.7 | 2,291.9 | 1,449.2 | 994.1 | 2,948.2 | 1,954.1 |
Household Service Line Replacement Costs ** | 8.1 | 0.0 | −8.1 | 26.4 | 0.0 | −26.4 |
State Rule Implementation and Administration | 38.4 | 66.1 | 27.7 | 41.8 | 67.6 | 25.8 |
Wastewater Treatment Plant Costs *** | 3.0 | 3.0 | 0.0 | 4.8 | 5.1 | 0.3 |
Total Annual Rule Costs | 892.2 | 2,361.0 | 1,468.8 | 1,067.1 | 3,020.9 | 1,953.8 |
Note: Previous Baseline costs are projected over the 35-year period of analysis and are affected by the EPA's assumptions on three uncertain variables which vary between the low- and high-cost scenarios. | ||||||
* Service line replacement includes full and partial lead and GRR service line replacements. | ||||||
** The EPA in the LCRR Economic Analysis (USEPA, 2020d) assumed that the cost of customer-side service line replacements made under the goal-based replacement rate would be paid for by households. The agency also assumed that system-side service line replacements under the goal-based replacement rate and all service line replacements (both customer-side and systems-side) would be paid by the PWS under the 3 percent mandatory replacement rate. The EPA made these modeling assumptions based on the different levels of regulatory responsibility systems faced operating under a goal-based replacement rate versus a mandatory replacement rate. While systems would not be subject to a potential violation for not meeting the target replacement rate under the goal-based replacement requirement, under the 3 percent mandatory replacement rate, the possibility of a violation could motivate more systems to meet the target replacement rate even if they had to adopt customer incentive programs that would shift the cost of replacing customer-side service lines from customers to the system. To be consistent with these LCRR modeling assumptions, under the LCRI, the EPA assumed that mandatory replacement costs would fall only on systems. Therefore, the negative incremental values reported for the “Household Service Line Replacement Costs” category do not represent a net cost savings to households. They represent an assumed shift of the estimated service line replacement costs from households to systems. The EPA has insufficient information to estimate the actual service line replacement cost-sharing relationship between customers and systems at a national level for this analysis. | ||||||
*** Due to many water systems operating both the wastewater and drinking water systems, the EPA is evaluating the costs of additional phosphate usage for informational purposes. Because these costs are not incurred by the public water system, these costs are not “likely to occur solely as a result of compliance” with the LCRI, and, therefore, are not costs considered as part of HRRCA under SDWA section 1412(b)(3)(C)(i)(III). | ||||||
Acronyms: LCRI = Lead and Copper Rule Improvements; PWS = public water system. |
Exhibit 11—LSL and CCT Scenarios and Simulated Geometric Mean Tap Water Lead Concentrations and Standard Deviations for the First Ten Liters Drawn After Stagnation for Each Combination of LSL and CCT Status (Exhibit Includes Assumed GRR, POU, and Pitcher Filter Water Lead Concentrations)
Exhibit 12—Modeled SHEDS-P b Geometric Mean Blood Lead Levels in Children for Each Possible Drinking Water Lead Exposure Scenario for Each Year of Life
Exhibit 13—Estimates of Geometric Mean Blood Lead Levels in Older Children and Adults (Ages 8-79) for Each Possible Drinking Water Lead Exposure Scenario
Exhibit 14—Estimated National Monetized Annual Benefits—2 Percent Discount Rate
[millions of 2022 USD]
Low estimate | High estimate | |||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Annual IQ Benefits | $1,208.5 | $6,831.3 | $5,622.8 | $3,279.0 | $10,963.0 | $7,684.0 |
Annual Low-Birth Weight Benefits | 1.0 | 5.4 | 4.4 | 1.8 | 5.7 | 3.9 |
Annual ADHD Benefits | 33.6 | 196.3 | 162.7 | 179.9 | 599.5 | 419.6 |
Annual Adult CVD Premature Mortality Benefits | 1,750.7 | 9,454.3 | 7,703.6 | 8,174.9 | 25,210.0 | 17,035.1 |
Total Annual Benefits | 2,993.8 | 16,487.3 | 13,493.5 | 11,635.6 | 36,778.2 | 25,142.6 |
Acronyms: LCRI = Lead and Copper Rule Improvements; IQ = intelligence quotient; ADHD = attention-deficit/hyperactivity disorder; CVD = cardiovascular disease. |
Exhibit 15—Comparison of Estimated Monetized National Annualized Incremental Costs to Benefits of the LCRI—2 Percent Discount Rate
[millions 2022 USD]
PWS annual costs | Low scenario | High scenario |
---|---|---|
Annualized Incremental Costs | $1,468.8 | $1,953.8 |
Annualized Incremental Benefits | 13,493.5 | 25,142.6 |
Annual Net Benefits | 12,024.7 | 23,188.8 |
Exhibit 16—Summary of Alternative Options Considered for the Final LCRI
Area | Alternative option considered | Final LCRI |
---|---|---|
Lead Action Level | 1. Lead Action Level of ≤0.015 mg/L 2. Lead Action Level of ≤0.005 mg/L | Lead AL of ≤0.010 mg/L (proposed rule). |
Service Line Replacement Rate | Service lines are replaced at an annual rate of 7% | Service lines are replaced at an annual rate of 10% (proposed rule). |
Definition of Lead Content to be Replaced | Systems must replace lead service lines and galvanized lines previously downstream of lead lines or unknown lead content lines, and lead connectors and galvanized lines previously downstream of lead connectors | Systems must replace lead service lines and galvanized lines previously downstream of lead lines or unknown lead content lines. Lead connectors are replaced when encountered (proposed rule). |
SLR Deferred Deadline | 1. Systems may be given a deferred deadline for finishing all LSL and GRR replacements resulting in a maximum rate which is the lower of 10,000 lines per year or 39 replacements per 1,000 connections per year (proposed rule—with change to connections per year from households per year) 2. Systems may be given a deferred deadline for finishing all LSL and GRR replacements resulting in a maximum rate which is the lower of 8,000 lines per year or 39 replacements per 1,000 connections per year | Systems may be given a deferred deadline for finishing all lead and GRR service line replacements resulting in a maximum rate of 39 replacements per 1,000 connections. |
Lead Tap Sampling | All systems return to standard 6-month monitoring with an ALE. Systems with lead, GRR, and/or unknown service lines at the compliance date conduct standard 6-month monitoring at the compliance date and non-lead service line systems remain on LCR monitoring schedule until new LCRI protocol sampling may change P90. When (and if) a non-lead system finds a lead or GRR service line they return to 6-month monitoring. (proposed rule). Systems that sampled using the new protocol and are below the LCRI action level prior to the compliance date may qualify to retain their current schedule | All systems return to standard 6-month monitoring with an ALE. Systems with lead and GRR service lines return to standard 6-month monitoring at compliance date. Unknown and non-lead service line systems remain on LCR monitoring schedule until new LCRI protocol sampling may change P90. When (and if) a non-lead/all unknown system finds a lead or GRR service line they return to 6-month monitoring. Systems with lead and GRR service lines that sampled using the new protocol and are below the LCRI action level prior to the compliance date may qualify to retain their current schedule. |
Multiple ALE Filter Programs | Systems with at least 2 lead ALEs in a rolling 5-year period must prepare and submit a filter plan to State. Systems with at least 3 lead ALEs in a rolling 5-year period must: 1. Make filters available to all customers with lead, GRR, and unknown lead content service lines 2. Deliver filters directly to all customers. | Systems with at least 2 lead ALEs in a rolling 5-year period must prepare and submit a filter plan to State. Systems with at least 3 lead ALEs in a rolling 5-year period must make filters available to all customers (proposed rule—with filter plan being required after 2 ALEs instead of 3 ALEs for the final rule). |
Small System Flexibility | CWSs that serve 10,000 or fewer persons, and all NTNCWSs, are provided compliance flexibility when they exceed the action level | CWSs that serve 3,300 or fewer persons, and all NTNCWSs, are provided compliance flexibility when they exceed the action level (proposed rule). |
Acronyms: LCRI = Lead and Copper Rule Improvements; GRR = galvanized requiring replacement; ALE = action level exceedance; CWS = community water system; NTNCWS = non-transient, non-community water system; LSL = lead service line; GRR = galvanized requiring replacement service line; P90 = calculated 90th percentile lead tap sample. | ||
Note: (Proposed Rule) indicates if a final rule component or alternative option were originally considered as part of the proposed LCRI. |
Exhibit 17—Estimated National Annualized Rule Cost Comparison Between the Final LCRI and Alternative Lead Action Level Option (AL ≤0.015 mg /L)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
PWS annual costs | Final rule | Alternative option (AL ≤0.015 mg/L) | ||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Sampling | $143.6 | $176.2 | $32.6 | $143.6 | $168.1 | $24.5 |
PWS SLR | 124.5 | 1,763.9 | 1,639.4 | 124.5 | 1,765.2 | 1,640.7 |
Corrosion Control Technology | 647.8 | 692.9 | 45.1 | 647.8 | 621.1 | −26.7 |
Point-of Use Installation and Maintenance | 5.9 | 9.6 | 3.7 | 5.9 | 5.6 | −0.3 |
Public Education and Outreach | 72.1 | 302.2 | 230.1 | 72.1 | 274.7 | 202.6 |
Rule Implementation and Administration | 0.2 | 3.4 | 3.2 | 0.2 | 3.4 | 3.2 |
Total Annual PWS Costs | 994.1 | 2,948.2 | 1,954.1 | 994.1 | 2,838.1 | 1,844.0 |
Household SLR Costs | 26.4 | 0.0 | −26.4 | 26.4 | 0.0 | −26.4 |
State Rule Implementation and Administration | 41.8 | 67.6 | 25.8 | 41.8 | 66.2 | 24.4 |
Wastewater Treatment Plant Costs | 4.8 | 5.1 | 0.3 | 4.8 | 3.3 | −1.5 |
Total Annual Rule Costs | 1,067.1 | 3,020.9 | 1,953.8 | 1,067.1 | 2,907.6 | 1,840.5 |
Acronyms: AL = action level; LCRI = Lead and Copper Rule Improvements; PWS = public water system; SLR = lead service line replacement; USD = United States dollar. | ||||||
Notes: | ||||||
(1) Previous Baseline costs are projected over the 35-year period of analysis and are affected by the EPA's assumptions on three uncertain variables which vary between the low and high cost scenarios. | ||||||
(2) Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 18—Estimated National Annual Benefit Comparison Between the Final LCRI and Alternative Lead Action Level Option (AL ≤0.015 mg /L)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
Final rule | Alternative option (AL ≤0.015 mg/L) | |||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Annual IQ Benefits | $3,279.0 | $10,963.0 | $7,684.0 | $3,279.0 | $10,586.0 | $7,307.0 |
Annual Low-Birth Weight Benefits | 1.8 | 5.7 | 3.9 | 1.8 | 5.5 | 3.7 |
Annual ADHD Benefits | 179.9 | 599.5 | 419.6 | 179.9 | 580.4 | 400.5 |
Annual Adult CVD Premature Mortality Benefits | 8,174.9 | 25,210.0 | 17,035.1 | 8,174.9 | 24,203.4 | 16,028.5 |
Total Annual Benefits | 11,635.6 | 36,778.2 | 25,142.6 | 11,635.6 | 35,375.3 | 23,739.7 |
Acronyms: ADHD = attention-deficit/hyperactivity disorder; AL = action level; CVD = cardiovascular disease; IQ = intelligence quotient; LCRI = Lead and Copper Rule Improvements; USD = United States dollar. | ||||||
Note: Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 19—Estimated National Annualized Rule Cost Comparison Between the Final LCRI and Alternative Lead Action Level Option (AL ≤0.005 mg /L)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
PWS annual costs | Final rule | Alternative option (AL ≤0.005 mg/L) | ||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Sampling | $143.6 | $176.2 | $32.6 | $143.6 | $198.7 | $55.1 |
PWS SLR | 124.5 | 1,763.9 | 1,639.4 | 124.5 | 1,762.4 | 1,637.9 |
Corrosion Control Technology | 647.8 | 692.9 | 45.1 | 647.8 | 819.4 | 171.6 |
Point-of Use Installation and Maintenance | 5.9 | 9.6 | 3.7 | 5.9 | 15.7 | 9.8 |
Public Education and Outreach | 72.1 | 302.2 | 230.1 | 72.1 | 374.2 | 302.1 |
Rule Implementation and Administration | 0.2 | 3.4 | 3.2 | 0.2 | 3.6 | 3.4 |
Total Annual PWS Costs | 994.1 | 2,948.2 | 1,954.1 | 994.1 | 3,174.0 | 2,179.9 |
Household SLR Costs | 26.4 | 0.0 | −26.4 | 26.4 | 0.0 | −26.4 |
State Rule Implementation and Administration | 41.8 | 67.6 | 25.8 | 41.8 | 71.7 | 29.9 |
Wastewater Treatment Plant Costs | 4.8 | 5.1 | 0.3 | 4.8 | 8.2 | 3.4 |
Total Annual Rule Costs | 1,067.1 | 3,020.9 | 1,953.8 | 1,067.1 | 3,253.9 | 2,186.8 |
Acronyms: AL = action level; LCRI = Lead and Copper Rule Improvements; PWS = public water system; SLR = lead service line replacement; USD = United States dollar. | ||||||
Notes: | ||||||
(1) Previous Baseline costs are projected over the 35-year period of analysis and are affected by EPA's assumptions on three uncertain variables which vary between the low and high cost scenarios. | ||||||
(2) Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 20—Estimated National Annual Benefit Comparison Between the Final LCRI and Alternative Lead Action Level Option (AL ≤0.005 mg /L)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
Final rule | Alternative option (AL ≤0.005 mg/L) | |||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Annual IQ Benefits | $3,279.0 | $10,963.0 | $7,684.0 | $3,279.0 | $11,651.2 | $8,372.2 |
Annual Low-Birth Weight Benefits | 1.8 | 5.7 | 3.9 | 1.8 | 6.0 | 4.2 |
Annual ADHD Benefits | 179.9 | 599.5 | 419.6 | 179.9 | 634.9 | 455.0 |
Annual Adult CVD Premature Mortality Benefits | 8,174.9 | 25,210.0 | 17,035.1 | 8,174.9 | 27,044.4 | 18,869.5 |
Total Annual Benefits | 11,635.6 | 36,778.2 | 25,142.6 | 11,635.6 | 39,336.5 | 27,700.9 |
Acronyms: ADHD = attention-deficit/hyperactivity disorder; AL = action level; CVD = cardiovascular disease; IQ = intelligence quotient; LCRI = Lead and Copper Rule Improvements; SLR = lead service line replacement; USD = United States dollar. | ||||||
Note: Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 21—Estimated National Annualized Rule Cost Comparison Between the Final LCRI and Alternative Service Line Replacement Option (SLR Rate = 7%)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
PWS Annual Costs | Final rule | Alternative option (SLR Rate = 7%) | ||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Sampling | $143.6 | $176.2 | $32.6 | $143.6 | $176.1 | $32.5 |
PWS SLR | 124.5 | 1,763.9 | 1,639.4 | 124.5 | 1,672.2 | 1,547.7 |
Corrosion Control Technology | 647.8 | 692.9 | 45.1 | 647.8 | 696.0 | 48.2 |
Point-of Use Installation and Maintenance | 5.9 | 9.6 | 3.7 | 5.9 | 10.2 | 4.3 |
Public Education and Outreach | 72.1 | 302.2 | 230.1 | 72.1 | 341.0 | 268.9 |
Rule Implementation and Administration | 0.2 | 3.4 | 3.2 | 0.2 | 3.4 | 3.2 |
Total Annual PWS Costs | 994.1 | 2,948.2 | 1,954.1 | 994.1 | 2,898.9 | 1,904.8 |
Household SLR Costs | 26.4 | 0.0 | −26.4 | 26.4 | 0.0 | −26.4 |
State Rule Implementation and Administration | 41.8 | 67.6 | 25.8 | 41.8 | 67.7 | 25.9 |
Wastewater Treatment Plant Costs | 4.8 | 5.1 | 0.3 | 4.8 | 5.2 | 0.4 |
Total Annual Rule Costs | 1,067.1 | 3,020.9 | 1,953.8 | 1,067.1 | 2,971.8 | 1,904.7 |
Acronyms: LCRI = Lead and Copper Rule Improvements; PWS = public water system; SLR = lead service line replacement; USD = United States dollar. | ||||||
Notes: (1) Previous Baseline costs are projected over the 35-year period of analysis and are affected by the EPA's assumptions on three uncertain variables which vary between the low- and high-cost scenarios. | ||||||
(2) Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 22—Estimated National Annual Benefit Comparison Between the Final LCRI and Alternative Service Line Replacement Option (SLR Rate = 7%)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
Final rule | Alternative option (SLR Rate = 7%) | |||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Annual IQ Benefits | $3,279.0 | $10,963.0 | $7,684.0 | $3,279.0 | $9,994.8 | $6,715.8 |
Annual Low-Birth Weight Benefits | 1.8 | 5.7 | 3.9 | 1.8 | 5.2 | 3.4 |
Annual ADHD Benefits | 179.9 | 599.5 | 419.6 | 179.9 | 540.5 | 360.6 |
Annual Adult CVD Premature Mortality Benefits | 8,174.9 | 25,210.0 | 17,035.1 | 8,174.9 | 22,997.8 | 14,822.9 |
Total Annual Benefits | 11,635.6 | 36,778.2 | 25,142.6 | 11,635.6 | 33,538.3 | 21,902.7 |
Acronyms: ADHD = attention-deficit/hyperactivity disorder; CVD = cardiovascular disease; IQ = intelligence quotient; LCRI = Lead and Copper Rule Improvements; SLR = lead service line replacement USD = United States dollar. | ||||||
Note: Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 23—Estimated National Annualized Rule Cost Comparison Between the Final LCRI and Alternative Option Including Lead Connectors in Definition of Service Lines To Be Replaced—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
Final rule | Alternative option (lead connectors and galvanized lines previously downstream of lead connectors must be replaced) | |||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
PWS Annual Costs | ||||||
Sampling | $143.6 | $176.2 | $32.6 | $143.6 | $176.4 | $32.8 |
PWS SLR | 124.5 | 1,763.9 | 1,639.4 | 124.5 | 1,921.7 | 1,797.2 |
Corrosion Control Technology | 647.8 | 692.9 | 45.1 | 647.8 | 701.3 | 53.5 |
Point-of Use Installation and Maintenance | 5.9 | 9.6 | 3.7 | 5.9 | 9.7 | 3.8 |
Public Education and Outreach | 72.1 | 302.2 | 230.1 | 72.1 | 306.6 | 234.5 |
Rule Implementation and Administration | 0.2 | 3.4 | 3.2 | 0.2 | 3.4 | 3.2 |
Total Annual PWS Costs | 994.1 | 2,948.2 | 1,954.1 | 994.1 | 3,119.1 | 2,125.0 |
Household SLR Costs | 26.4 | 0.0 | −26.4 | 26.4 | 0.0 | −26.4 |
State Rule Implementation and Administration | 41.8 | 67.6 | 25.8 | 41.8 | 67.9 | 26.1 |
Wastewater Treatment Plant Costs | 4.8 | 5.1 | 0.3 | 4.8 | 5.3 | 0.5 |
Total Annual Rule Costs | 1,067.1 | 3,020.9 | 1,953.8 | 1,067.1 | 3,192.3 | 2,125.2 |
Acronyms: LCRI = Lead and Copper Rule Improvements; SLR = lead service line replacement; PWS = public water system; USD = United States dollar. | ||||||
Notes: (1) Previous Baseline costs are projected over the 35-year period of analysis and are affected by the EPA's assumptions on three uncertain variables which vary between the low and high cost scenarios. | ||||||
(2) Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 24—Estimated National Annual Benefit Comparison Between the Final LCRI and Alternative Option Including Lead Connectors in Definition of Service Lines To Be Replaced—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
Final rule | Alternative option (lead connectors and galvanized lines previously downstream of lead connectors must be replaced) | |||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Annual IQ Benefits | $3,279.0 | $10,963.0 | $7,684.0 | $3,279.0 | $12,646.8 | $9,367.8 |
Annual Low-Birth Weight Benefits | 1.8 | 5.7 | 3.9 | 1.8 | 6.4 | 4.6 |
Annual ADHD Benefits | 179.9 | 599.5 | 419.6 | 179.9 | 684.8 | 504.9 |
Annual Adult CVD Premature Mortality Benefits | 8,174.9 | 25,210.0 | 17,035.1 | 8,174.9 | 28,943.5 | 20,768.6 |
Total Annual Benefits | 11,635.6 | 36,778.2 | 25,142.6 | 11,635.6 | 42,281.5 | 30,645.9 |
Acronyms: ADHD = attention-deficit/hyperactivity disorder; CVD = cardiovascular disease; IQ = intelligence quotient; LCRI = Lead and Copper Rule Improvements; USD = United States dollar. | ||||||
Note: Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 25—Estimated National Annualized Rule Cost Comparison Between the Final LCRI and Alternative Deferred Deadline Option (Adding Max Rate of 10,000 SL Per Year)—High Scenario—2 Percent Discount Rate
[millions of 2022 USD]
PWS Annual Costs | Final rule | Alternative option (SL replacement deferred deadline with additional potential maximum rate of 10,000 SL per year) | ||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Sampling | $143.6 | $176.2 | $32.6 | $143.6 | $176.0 | $32.4 |
PWS SLR | 124.5 | 1,763.9 | 1,639.4 | 124.5 | 1,763.1 | 1,638.6 |
Corrosion Control Technology | 647.8 | 692.9 | 45.1 | 647.8 | 692.8 | 45.0 |
Point-of Use Installation and Maintenance | 5.9 | 9.6 | 3.7 | 5.9 | 9.7 | 3.8 |
Public Education and Outreach | 72.1 | 302.2 | 230.1 | 72.1 | 302.4 | 230.3 |
Rule Implementation and Administration | 0.2 | 3.4 | 3.2 | 0.2 | 3.4 | 3.2 |
Total Annual PWS Costs | 994.1 | 2,948.2 | 1,954.1 | 994.1 | 2,947.4 | 1,953.3 |
Household SLR Costs | 26.4 | 0.0 | −26.4 | 26.4 | 0.0 | −26.4 |
State Rule Implementation and Administration | 41.8 | 67.6 | 25.8 | 41.8 | 67.6 | 25.8 |
Wastewater Treatment Plant Costs | 4.8 | 5.1 | 0.3 | 4.8 | 5.0 | 0.2 |
Total Annual Rule Costs | 1,067.1 | 3,020.9 | 1,953.8 | 1,067.1 | 3,020.0 | 1,952.9 |
Acronyms: LCRI = Lead and Copper Rule Improvements; PWS = public water system; SL = service line; SLR = lead service line replacement; USD = United Stated dollar. | ||||||
Notes: (1) Previous Baseline costs are projected over the 35-year period of analysis and are affected by the EPA's assumptions on three uncertain variables which vary between the low and high cost scenarios. | ||||||
(2) Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 26—Estimated National Annual Benefit Comparison Between the Final LCRI and Alternative Deferred Deadline Option (Adding Max Rate of 10,000 SL Per Year)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
Final rule | Alternative option (SL replacement deferred deadline with additional potential maximum rate of 10,000 SL per year) | |||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Annual IQ Benefits | $3,279.0 | $10,963.0 | $7,684.0 | $3,279.0 | $10,960.3 | $7,681.3 |
Annual Low-Birth Weight Benefits | 1.8 | 5.7 | 3.9 | 1.8 | 5.7 | 3.9 |
Annual ADHD Benefits | 179.9 | 599.5 | 419.6 | 179.9 | 599.3 | 419.4 |
Annual Adult CVD Premature Mortality Benefits | 8,174.9 | 25,210.0 | 17,035.1 | 8,174.9 | 25,203.7 | 17,028.8 |
Total Annual Benefits | 11,635.6 | 36,778.2 | 25,142.6 | 11,635.6 | 36,769.0 | 25,133.4 |
Acronyms: ADHD = attention-deficit/hyperactivity disorder; CVD = cardiovascular disease; IQ = intelligence quotient; LCRI = Lead and Copper Rule Improvements; SL = service line; USD = United States dollar. | ||||||
Note: Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 27—Estimated National Annualized Rule Cost Comparison Between the Final LCRI and Alternative Deferred Deadline Option (Adding Max Rate of 8,000 SL Per Year)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
PWS Annual Costs | Final rule | Alternative option (SL replacement deferred deadline with additional potential maximum rate of 8,000 SL per year) | ||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Sampling | $143.6 | $176.2 | $32.6 | $143.6 | $176.0 | $32.4 |
PWS SLR | 124.5 | 1,763.9 | 1,639.4 | 124.5 | 1,761.8 | 1,637.3 |
Corrosion Control Technology | 647.8 | 692.9 | 45.1 | 647.8 | 692.8 | 45.0 |
Point-of Use Installation and Maintenance | 5.9 | 9.6 | 3.7 | 5.9 | 9.7 | 3.8 |
Public Education and Outreach | 72.1 | 302.2 | 230.1 | 72.1 | 302.7 | 230.6 |
Rule Implementation and Administration | 0.2 | 3.4 | 3.2 | 0.2 | 3.4 | 3.2 |
Total Annual PWS Costs | 994.1 | 2,948.2 | 1,954.1 | 994.1 | 2,946.4 | 1,952.3 |
Household SLR Costs | 26.4 | 0.0 | −26.4 | 26.4 | 0.0 | −26.4 |
State Rule Implementation and Administration | 41.8 | 67.6 | 25.8 | 41.8 | 67.6 | 25.8 |
Wastewater Treatment Plant Costs | 4.8 | 5.1 | 0.3 | 4.8 | 5.0 | 0.2 |
Total Annual Rule Costs | 1,067.1 | 3,020.9 | 1,953.8 | 1,067.1 | 3,019.0 | 1,951.9 |
Acronyms: LCRI = Lead and Copper Rule Improvements; PWS = public water system; SL = service line; SLR = lead service line replacement; USD = United Stated dollar. | ||||||
Notes: (1) Previous Baseline costs are projected over the 35-year period of analysis and are affected by the EPA's assumptions on three uncertain variables which vary between the low and high cost scenarios. | ||||||
(2) Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 28—Estimated National Annual Benefit Comparison Between the Final LCRI and Alternative Deferred Deadline Option (Adding Max Rate of 8,000 SL per Year)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
Final rule | Alternative option (SL replacement deferred deadline with additional potential maximum rate of 8,000 SL per year) | |||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Annual IQ Benefits | $3,279.0 | $10,963.0 | $7,684.0 | $3,279.0 | $10,943.3 | $7,664.3 |
Annual Low-Birth Weight Benefits | 1.8 | 5.7 | 3.9 | 1.8 | 5.7 | 3.9 |
Annual ADHD Benefits | 179.9 | 599.5 | 419.6 | 179.9 | 598.3 | 418.4 |
Annual Adult CVD Premature Mortality Benefits | 8,174.9 | 25,210.0 | 17,035.1 | 8,174.9 | 25,164.0 | 16,989.1 |
Total Annual Benefits | 11,635.6 | 36,778.2 | 25,142.6 | 11,635.6 | 36,711.3 | 25,075.7 |
Acronyms: ADHD = attention-deficit/hyperactivity disorder; CVD = cardiovascular disease; IQ = intelligence quotient; LCRI = Lead and Copper Rule Improvements; SL = service line; USD = United States dollar. | ||||||
Note: Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 29—Estimated National Annualized Rule Cost Comparison Between the Final LCRI and Alternative Temporary Filters Program for Multiple ALE Systems Option (Filters Made Available to Lead, GRR, and Unknown Service Line Customers Only)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
PWS Annual Costs | Final rule | Alternative option (temporary filters made available to lead, GRR, and unknown lead content service line customers only in systems meeting multiple ALE criteria) | ||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Sampling | $143.6 | $176.2 | $32.6 | $143.6 | $176.1 | $32.5 |
PWS SLR | 124.5 | 1,763.9 | 1,639.4 | 124.5 | 1,763.9 | 1,639.4 |
Corrosion Control Technology | 647.8 | 692.9 | 45.1 | 647.8 | 692.9 | 45.1 |
Point-of Use Installation and Maintenance | 5.9 | 9.6 | 3.7 | 5.9 | 9.6 | 3.7 |
Public Education and Outreach | 72.1 | 302.2 | 230.1 | 72.1 | 274.8 | 202.7 |
Rule Implementation and Administration | 0.2 | 3.4 | 3.2 | 0.2 | 3.4 | 3.2 |
Total Annual PWS Costs | 994.1 | 2,948.2 | 1,954.1 | 994.1 | 2,920.7 | 1,926.6 |
Household SLR Costs | 26.4 | 0.0 | −26.4 | 26.4 | 0.0 | −26.4 |
State Rule Implementation and Administration | 41.8 | 67.6 | 25.8 | 41.8 | 67.6 | 25.8 |
Wastewater Treatment Plant Costs | 4.8 | 5.1 | 0.3 | 4.8 | 5.1 | 0.3 |
Total Annual Rule Costs | 1,067.1 | 3,020.9 | 1,953.8 | 1,067.1 | 2,993.4 | 1,926.3 |
Acronyms: ALE = action level exceedance; LCRI = Lead and Copper Rule Improvements; PWS = public water system; LSL = lead service line; GRR = galvanized requiring replacement service line; SLR = lead service line replacement; United States dollar. | ||||||
Notes: (1) Previous Baseline costs are projected over the 35-year period of analysis and are affected by the EPA's assumptions on three uncertain variables which vary between the low and high cost scenarios. | ||||||
(2) Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 30—Estimated National Annualized Rule Cost Comparison Between the Final LCRI and Alternative Temporary Filters Program for Multiple ALE Systems Option (Deliver Filters to All Customers)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
PWS Annual Costs | Final rule | Alternative option (deliver temporary filters directly to all customers in systems meeting multiple ALE criteria) | ||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Sampling | $143.6 | $176.2 | $32.6 | $143.6 | $176.1 | $32.5 |
PWS SLR | 124.5 | 1,763.9 | 1,639.4 | 124.5 | 1,763.9 | 1,639.4 |
Corrosion Control Technology | 647.8 | 692.9 | 45.1 | 647.8 | 692.9 | 45.1 |
Point-of Use Installation and Maintenance | 5.9 | 9.6 | 3.7 | 5.9 | 9.6 | 3.7 |
Public Education and Outreach | 72.1 | 302.2 | 230.1 | 72.1 | 308.1 | 236.0 |
Rule Implementation and Administration | 0.2 | 3.4 | 3.2 | 0.2 | 3.4 | 3.2 |
Total Annual PWS Costs | 994.1 | 2,948.2 | 1,954.1 | 994.1 | 2,954.0 | 1,959.9 |
Household SLR Costs | 26.4 | 0.0 | −26.4 | 26.4 | 0.0 | −26.4 |
State Rule Implementation and Administration | 41.8 | 67.6 | 25.8 | 41.8 | 67.6 | 25.8 |
Wastewater Treatment Plant Costs | 4.8 | 5.1 | 0.3 | 4.8 | 5.1 | 0.3 |
Total Annual Rule Costs | 1,067.1 | 3,020.9 | 1,953.8 | 1,067.1 | 3,026.7 | 1,959.6 |
Acronyms: ALE = action level exceedance; LCRI = Lead and Copper Rule Improvements; PWS = public water system; SL = service line; SLR = lead service line replacement; United States dollar. | ||||||
Notes: (1) Previous Baseline costs are projected over the 35-year period of analysis and are affected by the EPA's assumptions on three uncertain variables which vary between the low and high cost scenarios. | ||||||
(2) Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 31—Estimated National Annualized Rule Cost Comparison Between the Final LCRI and Alternative Small System Flexibility Option (Flexibility for CWSs Serving Up to 10,000 Persons)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
PWS Annual Costs | Final rule | Alternative option (small system flexibility for CWSs serving up to 10,000 persons) | ||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Sampling | $143.6 | $176.2 | $32.6 | $143.6 | $176.0 | $32.4 |
PWS SLR | 124.5 | 1,763.9 | 1,639.4 | 124.5 | 1,763.9 | 1,639.4 |
Corrosion Control Technology | 647.8 | 692.9 | 45.1 | 647.8 | 692.7 | 44.9 |
Point-of Use Installation and Maintenance | 5.9 | 9.6 | 3.7 | 5.9 | 9.6 | 3.7 |
Public Education and Outreach | 72.1 | 302.2 | 230.1 | 72.1 | 302.0 | 229.9 |
Rule Implementation and Administration | 0.2 | 3.4 | 3.2 | 0.2 | 3.4 | 3.2 |
Total Annual PWS Costs | 994.1 | 2,948.2 | 1,954.1 | 994.1 | 2,947.6 | 1,953.5 |
Household SLR Costs | 26.4 | 0.0 | −26.4 | 26.4 | 0.0 | −26.4 |
State Rule Implementation and Administration | 41.8 | 67.6 | 25.8 | 41.8 | 67.6 | 25.8 |
Wastewater Treatment Plant Costs | 4.8 | 5.1 | 0.3 | 4.8 | 5.2 | 0.4 |
Total Annual Rule Costs | 1,067.1 | 3,020.9 | 1,953.8 | 1,067.1 | 3,020.4 | 1,953.3 |
Acronyms: CWS = community water system; LCRI = Lead and Copper Rule Improvements; SLR = lead service line replacement; PWS = public water system; United States dollar. | ||||||
Notes: (1) Previous Baseline costs are projected over the 35-year period of analysis and are affected by the EPA's assumptions on three uncertain variables which vary between the low and high cost scenarios. | ||||||
(2) Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Exhibit 32—Estimated National Annual Benefit Comparison Between the Final LCRI and Alternative Small System Flexibility Option (Flexibility for CWSs Serving Up to 10,000 Persons)—High Scenario—2 Percent Discount Rate
[Millions of 2022 USD]
Final rule | Alternative option (small system flexibility for CWSs serving up to 10,000 persons) | |||||
---|---|---|---|---|---|---|
Baseline | LCRI | Incremental | Baseline | LCRI | Incremental | |
Annual IQ Benefits | $3,279.0 | $10,963.0 | $7,684.0 | $3,279.0 | $10,963.1 | $7,684.1 |
Annual Low-Birth Weight Benefits | 1.8 | 5.7 | 3.9 | 1.8 | 5.7 | 3.9 |
Annual ADHD Benefits | 179.9 | 599.5 | 419.6 | 179.9 | 599.5 | 419.6 |
Annual Adult CVD Premature Mortality Benefits | 8,174.9 | 25,210.0 | 17,035.1 | 8,174.9 | 25,210.5 | 17,035.6 |
Total Annual Benefits | 11,635.6 | 36,778.2 | 25,142.6 | 11,635.6 | 36,778.8 | 25,143.2 |
Acronyms: ADHD = attention-deficit/hyperactivity disorder; CVD = cardiovascular disease; CWS = community water system; IQ = intelligence quotient; LCRI = Lead and Copper Rule Improvements; USD = United States dollar. | ||||||
Note: Very small differences in results between the final rule and the regulatory option are due to inter-run variability in the SafeWater LCR model, and/or rounding, and should not be interpreted at true differences between the costs and benefits of the final rule and the alternative option. |
Table 1 to Paragraph (b)(5)(ii)
Size of validation pool | Number of validations required |
---|---|
<1,500 | 20 percent of validation pool. |
1,500 to 2,000 | 322. |
2,001 to 3,000 | 341. |
3,001 to 4,000 | 351. |
4,001 to 6,000 | 361. |
6,001 to 10,000 | 371. |
10,001 to 50,000 | 381. |
>50,000 | 384. |
Table 2 to Paragraph (d)(6)(iii) (A)
System-owned portion | Customer-owned portion | Categorization for entire service line |
---|---|---|
Lead | Lead | Lead. |
Lead | Galvanized Requiring Replacement | Lead. |
Lead | Non-lead | Lead. |
Lead | Lead Status Unknown | Lead. |
Non-lead | Lead | Lead. |
Non-lead and never previously lead | Non-lead, specifically galvanized pipe material | Non-lead. |
Non-lead | Non-lead, material other than galvanized pipe material | Non-lead. |
Non-lead | Lead Status Unknown | Lead Status Unknown. |
Non-lead, but system is unable to demonstrate it was not previously Lead | Galvanized Requiring Replacement | Galvanized Requiring Replacement. |
Lead Status Unknown | Lead | Lead. |
Lead Status Unknown | Galvanized Requiring Replacement | Galvanized Requiring Replacement. |
Lead Status Unknown | Non-lead | Lead Status Unknown. |
Lead Status Unknown | Lead Status Unknown | Lead Status Unknown. |
Table 1 to Paragraph ( c )(1)
System size (number of people served) | Standard number of sites for lead and copper sampling |
---|---|
>100,000 | 100 |
10,001 to 100,000 | 60 |
3,301 to 10,000 | 40 |
501 to 3,300 | 20 |
101 to 500 | 10 |
≤100 | 5 |
Table 2 to Paragraph ( d )(1)
System size (number of people served) | Reduced minimum number of sites for lead and copper sampling |
---|---|
>100,000 | 50 |
10,001 to 100,000 | 30 |
3,301 to 10,000 | 20 |
501 to 3,300 | 10 |
101 to 500 | 5 |
≤100 | 5 |
Table 1 to Paragraph ( b )(1)( i )
System size (number of people served) | Minimum number of sites for water quality parameters |
---|---|
>100,000 | 25 |
10,001 to 100,000 | 10 |
3,301 to 10,000 | 3 |
501 to 3,300 | 2 |
101 to 500 | 1 |
≤100 | 1 |
Table 2 to Paragraph ( c )(1)
System size (number of people served) | Reduced minimum number of sites for water quality parameters |
---|---|
>100,000 | 10 |
10,001 to 100,000 | 7 |
3,301 to 10,000 | 3 |
501 to 3,300 | 2 |
101 to 500 | 1 |
≤100 | 1 |
Contaminant (units) | Traditional MCL in mg/L | To convert for CCR, multiply by | MCL in CCR units | MCLG | Major sources in drinking water | Health effects language |
---|---|---|---|---|---|---|
* * * * * * * | ||||||
Inorganic contaminants | ||||||
* * * * * * * | ||||||
Lead (mg/L) | AL = 0.010 | 1,000 | AL = 10 | 0 | Corrosion of household plumbing systems and service lines connecting buildings to water mains, erosion of natural deposits | There is no safe level of lead in drinking water. Exposure to lead in drinking water can cause serious health effects in all age groups, especially pregnant people, infants (both formula-fed and breastfed), and young children. Some of the health effects to infants and children include decreases in IQ and attention span. Lead exposure can also result in new or worsened learning and behavior problems. The children of persons who are exposed to lead before or during pregnancy may be at increased risk of these harmful health effects. Adults have increased risks of heart disease, high blood pressure, kidney or nervous system problems. Contact your health care provider for more information about your risks. |
* * * * * * * |