May 2008

Know Your Way

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By Prabha Kumar, Anna White

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Over a period of three decades, stormwater management has evolved from localized flood control to an integrated and comprehensive natural resource management and sustainable development approach. With such a paradigm shift in stormwater management vision and mission, the need for dedicated and reliable financing has become more urgent.

Is your community in need of a viable user fee–funded stormwater utility? Are you wondering where to begin and which of the myriad of issues you need to address first? Are you looking for some kind of a roadmap to follow? If you answered yes to any of these questions, you are not alone—you are indeed part of a growing community of utility managers who are proactively examining alternative sources of funding for sustainable stormwater management.

Background
The Natural Resources Defense Council examined 100 case studies and found that the use of dedicated funding sources, such as stormwater user fees or dedicated environmental fees, “help ensure that stormwater programs are stable over time and help gain public support” (NRDC 1999). The number of municipal utilities implementing a stormwater user fee has steadily increased from around 300 utilities in 1996 to more than 600 at the present time. Recognizing the benefits of a user fee–funded stormwater enterprise, in some states such agencies as the Department of Environmental Protection offer grants to municipalities to conduct utility-development feasibility studies.

With user fee–funded stormwater utilities gradually increasing in number nationwide, so too is the need for well-defined business policies and processes increasing. With the availability of sophisticated technology and skilled resources, customers and decision makers now expect greater “due diligence” in the planning and implementation of stormwater-user-fee programs. Utility managers tasked with the challenge of establishing user fee–funded stormwater programs often find the task of navigating the complex maze of policy issues rather daunting.

To help mitigate this policy development challenge, this article provides insights into key policy issues that need to be identified and adequately brainstormed before finalizing and implementing a stormwater-user-fee program. In emphasizing the key policy issues, this article also references, where appropriate, the latest findings from the Black & Veatch 2007 Stormwater Utility Survey. This seventh national survey provides information on nine key areas based on data gathered from a survey of 71 utilities that have implemented stormwater user fees.

Why Dwell on Policy Issues?
It is important to first understand why it is worthwhile to invest the time and effort in identifying and addressing policy issues. The key principles that guide the design of a stormwater user fee are that the fee should bear a reasonable nexus, or relationship, to the demand a property places on the community’s stormwater system and that it should provide for equitable recovery of costs. The demand a property places on the system is usually attributed to some measure of development that has occurred on the property—often referred to as a parcel’s impervious area. As there is no direct way to measure the volume of runoff that occurs from a property, surrogate measures, such as impervious area, are used as a basis for assessing stormwater user fees.

In such a situation, numerous questions may arise, such as the following:

  • How should the impervious area be determined—through actual measurement or some other method of estimation?
  • Should a charge be assessed from parcels that remain as vacant land?
  • Who should pay for the streets, medians, and other rights of way in a community?

The inherent challenge lies not in addressing the questions but in anticipating the issues and questions that may be unique to the community. Each community has unique situations and needs, and therefore a one-size-fits-all approach cannot be used when developing policies. For example, the policies needed for allocating impervious area in a highly urbanized skyscraper environment will be significantly different from those for a suburban community with vast swaths of agricultural land.

Therefore, policy development should focus on identifying the challenges specific to the community and on developing defensible policies to address these various issues. However, because many utilities have successfully developed the required policies for stormwater-user-fee implementation, it is not necessary to reinvent the wheel. Utility managers can leverage lessons learned and develop their own tailored policies in an efficient manner. The time spent up front in defining well-thought-out policies and in obtaining consensus for the policies will ultimately determine the success in implementing a stormwater user fee.

Policy Issues in Stormwater-User-Fee Implementation
Utility managers who have successfully implemented a stormwater user fee will readily agree that such an undertaking can be an arduous process—especially if it is handled without a well-thought-out business plan. Understanding what the key policy issues are, and defining those policy issues, will provide utility managers with a solid foundation for implementing their utility’s stormwater user fee. The key policy issues that need to be addressed span the following areas:

  • User-fee methodology
  • Customer classification
  • Stormwater exemptions
  • Stormwater credits
  • Payment responsibility
  • Enforcement
  • Billing system selection
  • Ongoing maintenance

User-Fee Methodology
The fundamental policy decision a utility needs to make is what basis will be used for assessing a stormwater user fee. Some of the common user-fee options include the following:

  • Total gross area
  • Impervious area
  • Average impervious area for single-family residences
  • Effective impervious area for single-family residences
  • Gross area with level of development
  • Billable hydraulic area

In evaluating the best-fit option or combination of options, factors such as data availability, ease of understanding, ability to recognize runoff from pervious and impervious areas, equity, and database maintenance requirements have to be considered. For example, the use of gross parcel area may be an attractive option as it ranks high with respect to ease of understanding and the data are relatively easy to obtain from tax-assessment systems. However, this method ranks low when it comes to equity because it does not distinguish between a parcel that is fully developed with an impervious structure, consequently contributing a high volume of runoff, and a parcel that has very little impervious structure and contributes a relatively low volume of runoff. On the other hand, when compared with the total-gross-area method, the impervious area method ranks higher in terms of equity, is on par in terms of ease of understanding, but is more complex with respect to database maintenance requirements.

Each method has certain advantages and constraints, and hence it is often valuable to review the pros and cons of each method and develop a user-fee option matrix that can facilitate effective decision making. The user-fee method evaluation matrix in Figure 1 shows a ranking of the methods with respect to the five evaluation factors.

Sometimes, a single method may not adequately address distinctive characteristics among customer classes and data availability limitations. Therefore, many utilities that have implemented a stormwater user fee employ a combination of one or more methods to define the basis of their stormwater user fees. The 2007 Black & Veatch Survey indicates that 65% of the respondents base their charges directly on impervious area determinations, while 12% base their charges on gross area in conjunction with a runoff or intensity-of-development factor. Nine percent of respondents use a combination of impervious area and gross area as the basis for their user fees, with the remaining 14% using such other factors as the number of rooms, water usage, or a fixed flat fee.

Customer Classification
Customer classification provides an effective mechanism to recognize the relative differences in land-use characteristics. The potential runoff that can occur from a single-family residential parcel differs significantly from the runoff from a parcel that has an industrial or commercial use. The number and type of customer classes that need to be defined are dictated largely by selected user-fee methodologies and data availability.

If actual impervious area is to be selected as the user-fee basis, and if these data are consistently available for all the parcels in a municipality, one could argue that there is no need for any customer classification—in effect, each individual parcel becomes a customer class in its own right. However, if impervious area is estimated based on gross parcel area multiplied by a land-use-type-based runoff coefficient, customer classes are important. Defining customer classes—such as single-family residential, commercial, industrial, institutional, and vacant land—based on land-use types enables the utility to assign a reasonable runoff coefficient value to each customer class to develop estimates of impervious area.

Although there is no rule of thumb as to what the customer classifications should be, the 2007 Black & Veatch Survey indicates that the most commonly recognized customer classes include residential (89% of respondents), commercial (57% of respondents), industrial (23% of respondents), or a combination of the above classes (26% of respondents). Only 10% of respondents reported having no customer classifications. Next Page >

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