LEAD 6543 Module 1 Policy Problem Definition and Context Example

Twenty-Eight Thousand Lead Pipes: Defining the Policy Problem of Lead Service Lines in an Ohio City

Student Name

American College of Education

LEAD6543: Policy and Governance

Module 1 Assignment

Instructor Name

July 7, 2031

Introduction

How a policy problem is defined shapes which solutions seem reasonable and whose interests count. This paper defines a problem facing Riverford, a composite Ohio city of about 280,000 people whose details combine several cities and have been altered. About 28,000 homes in Riverford receive drinking water through lead service lines, the pipes that connect water mains to buildings. A new federal rule requires most of these lines to be replaced within about a decade, and the city must decide how to do it. The paper states the problem carefully, measures it, sets out its context and identifies the stakeholders and values involved.

Defining Without Prescribing

Bardach and Patashnik (2020) advised analysts to define a problem in terms of deficits or excesses that can be measured and to avoid embedding a solution in the definition. Saying the problem is that the city lacks a lead line replacement fund, for example, assumes the answer. Stone (2012) added that problem definitions are never neutral; they carry stories about causes and blame that favor some responses over others. With both warnings in mind, the problem is defined here as follows: about 28,000 Riverford households, concentrated in older neighborhoods with lower incomes, receive water through lead pipes that can release lead into drinking water, exposing residents, especially young children and pregnant women, to a preventable health risk.

Scale and Distribution

The city's service line inventory, completed under federal requirements, identifies about 28,000 lead lines and about 9,000 lines of unknown material, out of roughly 105,000 connections. Mapping the inventory against census data shows that lead lines are heavily concentrated in neighborhoods built before 1940, where median household income is about 40 percent below the city median and a majority of residents rent. In eleven of these census tracts, more than half of homes have lead lines. The problem is therefore not only large but unequally distributed, falling most heavily on residents with the fewest resources to address it themselves.

Health Context

No safe level of lead exposure in children has been identified, and exposure is associated with lasting effects on cognitive development. The Flint water crisis showed how quickly risk can become harm. Hanna-Attisha et al. (2016) found that after Flint switched its water source in 2014 without adequate corrosion control, a markedly larger proportion of young children tested above the blood lead reference value, and the jump was steepest in the wards where tap water carried the most lead. Riverford treats its water to reduce corrosion, and most tap samples meet current standards, but treatment can fail and disturbances during construction can release lead.

Legal Context

In 2024, the U.S. Environmental Protection Agency finalized improvements to its lead and copper regulations that require most community water systems to identify and replace lead service lines, generally within ten years, and that lower the level of lead that triggers additional action (Environmental Protection Agency, 2024). Ohio law and the state environmental agency's rules govern how the federal requirements are applied to the city's water system. For Riverford, the federal rule converts a long-recognized risk into a legal obligation with a deadline, which changes the policy question from whether to act to how.

Ownership and Cost

A complication shapes every option. Each service line has two segments: the public side, from the main to the curb, owned by the city's water utility, and the private side, from the curb to the house, owned by the property owner. Replacing only the public side can disturb the remaining lead and temporarily increase lead levels, so full replacement is preferred. The city's engineers estimate an average full replacement cost of about $11,000, roughly $4,000 for the public side and $7,000 for the private side, for a total near $310 million for known lead lines. Many owners, particularly landlords and low-income homeowners, are unlikely to pay for the private side voluntarily.

Funding Context

Federal infrastructure legislation enacted in 2021 dedicated substantial funding to lead service line replacement through state revolving loan funds, with a share available as grants or forgivable loans for disadvantaged communities. Riverford has received an initial allocation that covers a fraction of the total cost. Other sources include water rates, which fall on all customers, local general funds and state programs. Each funding choice has distributional consequences: higher water bills take the biggest bite from poorer families, while relying on owners to pay for private sides leaves the poorest neighborhoods with the most lead.

Stakeholders

Many parties have a stake. Residents of affected neighborhoods, including renters who cannot authorize work on property they do not own, face the health risk most directly. Property owners, including landlords, face costs and disruption. All ratepayers face possible rate increases. The water utility must comply with the rule and manage construction. The city council and mayor make funding and policy decisions. The state environmental agency enforces the rules and administers the loan fund. Community organizations and health advocates press for urgency and equity, while contractors and labor groups have interests in how work is procured.

Values in Tension

The problem involves values that pull in different directions. Health protection argues for speed and full replacement. Equity argues for prioritizing the neighborhoods and households with the least capacity to pay. Fiscal responsibility argues for limiting the burden on ratepayers and the city's budget. Respect for property rights complicates mandatory access to private property. Efficiency argues for replacing lines block by block regardless of income, which reduces cost per line but may delay help to the most exposed. These tensions explain why the policy choice is contested even though everyone agrees lead lines should go.

What Is Known and Unknown

Some facts are firm and others uncertain. The number of known lead lines is reliable, but the 9,000 lines of unknown material may include several thousand more lead lines. Cost estimates may rise with inflation and contractor availability. Tap sampling shows lead levels mostly below current action levels, but sampling captures only some homes at some times. A careful definition states these uncertainties, because later decisions about pace and funding depend on them.

A Wicked Problem

Rittel and Webber (1973) described wicked problems as those in public policy that lack a definitive formulation, have no stopping rule, allow no correct solution but only better or worse ones and are each essentially unique, with every attempted solution having consequences that cannot be undone. Lead service line replacement is partly tame, since the engineering is well understood, but it has wicked features: how to weigh equity against cost, how to secure access to private property and how to fund the work have no single right answer and involve trade-offs among stakeholders' values. Recognizing these features suggests that process and legitimacy will matter as much as technical design.

Conclusion

Riverford's problem is that about 28,000 households, concentrated in lower-income older neighborhoods, receive water through lead pipes that pose a preventable health risk, a risk the Flint experience shows can turn into harm. A 2024 federal rule requires replacement within about a decade, but split ownership, a total cost near $310 million and limited funding create hard choices. Stakeholders and values conflict, and the problem has wicked features that make governance and process central. The next paper will examine who has authority to decide and how governance structures shape the choices.

References

Bardach, E., & Patashnik, E. M. (2020). A practical guide for policy analysis: The eightfold path to more effective problem solving (6th ed.). CQ Press.

Environmental Protection Agency. (2024). National primary drinking water regulations for lead and copper: Improvements (LCRI). Federal Register, 89, 86418-86716.

Hanna-Attisha, M., LaChance, J., Sadler, R. C., & Champney Schnepp, A. (2016). Elevated blood lead levels in children associated with the Flint drinking water crisis: A spatial analysis of risk and public health response. American Journal of Public Health, 106(2), 283-290. https://doi.org/10.2105/AJPH.2015.303003

Rittel, H. W. J., & Webber, M. M. (1973). Dilemmas in a general theory of planning. Policy Sciences, 4(2), 155-169. https://doi.org/10.1007/BF01405730

Stone, D. (2012). Policy paradox: The art of political decision making (3rd ed.). W. W. Norton.