Abstract
This article uses a system of Poisson demand equations to examine the revenue potential associated with uniform, site-differentiated, and income-differentiated recreational access fees for more than 130 lakes in the state of Iowa. We also consider optimal fees in the spirit of Ramsey (1927) and demonstrate how the new insights from Banzhaf and Smith (2022) can empirically inform discussions of user fees. We find that user fees could be used to raise revenue for the maintenance of recreation infrastructure, but that they are generally regressive. Fees differentiated by income groups can attenuate (but not eliminate) this regressivity.
1. Introduction
Public outdoor recreation sites provide millions of people with access to outdoor activities and are a primary way through which people interact with the environment. Visitor infrastructure and site quality conditions are major determinants of the benefits that visitors receive from recreation sites; their maintenance is therefore critical to ensuring a sustainable flow of economic value from recreation resources. However, securing adequate funding to support recreation infrastructure has been a perpetual challenge at the federal level and in many states and localities. For example, the U.S. Congressional Research Service estimated that in 2018, the four major federal land management agencies—Bureau of Land Management, Fish and Wildlife Service, Forest Service, and National Park Service—together faced over $19 billion in deferred maintenance (Vincent 2019). These types of backlogs as well as the fiscal challenges all levels of government are facing have generated interest in alternative ways of raising revenue to support outdoor recreation. One possibility is expanded user fees. In this article, we use the tools of recreation demand analysis to examine the performance of site entry fees as a means of securing revenue to finance outdoor recreation.
Recreation demand has a unique history among empirical microeconomic demand modeling in at least two dimensions. First, from early in its history, researchers using the method collected primary household-level data to fit models. The need to do so arose because the cost of accessing a site is the primary component of the price of the good. Therefore, it was critical to identify the location of the household’s primary residence, which could best be achieved with household-level surveys. Primary surveys generated a breadth of additional household-level detail that allowed researchers to study heterogeneity in behavior and preferences at a finer scale than aggregate data allowed. Second, a key motivation in environmental economics for recreation demand modeling has been to estimate consumer surplus changes associated with site access or environmental quality changes for use in benefit-cost analysis or damage assessment. Examples abound and include Burt and Brewer (1971), Smith, Desvousges, and McGivney (1983), Bockstael, Hanemann, and Kling (1987), English et al. (2018), and Parsons et al. (2021), and there are many review and textbook treatments (Freeman, Herriges, and Kling 2014; Phaneuf and Requate 2016; Mendelsohn 2019; Lupi, Phaneuf, and von Haefen 2020). In these studies, accurately predicting changes in visitation patterns and levels via estimation of price or income elasticities generally receives less attention than the development of utility theoretic specifications to recover consumer surplus estimates.
This article builds on the literature in recreation demand modeling by considering these models when the endpoint of interest is to raise revenue to support local infrastructure. Specifically, we use a demand system model to evaluate alternative fee structures to understand how hypothetical site user fees would affect site visitation and consumer surplus and generate government revenue. State and local parks and recreation areas generally charge nothing (or a nominal fee) for entry. Even parks of national and iconic importance often charge quite small fees for access. Despite the recent passage of a major public lands bill (Karlson 2020), there remains continued discussion of how state and local governments can best fund the many recreational sites in their borders and under their jurisdictions. To study these issues, we exploit the Iowa Lakes data set, which contains information on outdoor recreation opportunities at over 130 public lakes in Iowa. These lakes are examples of the type of local amenities for which state and local jurisdictions often struggle to fund infrastructure and maintain environmental quality. This data set has been used in many contexts to learn about household behavior with respect to local recreation sites (Herriges and Phaneuf 2002; Egan et al. 2009; Phaneuf, Carbone, and Herriges 2009; Hogue, Herriges, and Kling 2020; Ji, Keiser, and Kling 2020), providing a solid basis of knowledge on which to build. The data were collected over nearly 15 years and provide a unique panel database for analysis. In addition to recreation behavior, we observe information on a range of household incomes, education levels, family sizes, and employment levels.
We begin with a brief discussion of relevant literature, followed by a summary of the Iowa lakes recreation data. We discuss a demand system model as the starting point for our empirical analysis and draw from the optimal taxation literature to consider efficient fee structures based on the well-known Ramsey (1927) result that minimizes deadweight loss from a set of differentiated commodity taxes. We contrast the distributional and welfare effects of these fees. Finally, we draw from the insights of Banzhaf and Smith (2022), who study the combined welfare effects of a use fee that is recycled to fund site quality improvements. We provide an empirical example of their approach by solving for the size of the quality change needed for a given fee to improve consumer welfare.
2. Literature Context
Recreation demand models feature prominently in at least two distinct research areas— environmental and resource economics and leisure sciences—and these have influenced policy in different ways. As noted, researchers in resource economics have focused on estimating nonmarket values from changes in environmental quality and site availability. Applications by environmental economists have been influential in benefit-cost analysis, damage assessment, and environmental policy generally. In a thorough review, Hunt et al. (2019) identified 118 sport fishing studies published from 1988 to 2017 and found that while the cost of access and catch-related quality metrics were common, many studies omitted other dimensions of quality, even though, when included, they were commonly important predictors.
Researchers in leisure science and its subfields have also contributed to this literature and, in some cases, address different issues. A good example is Powers et al. (2020), who assess the socioeconomic status of recreational users. Other work in this vein includes Schroeder and Louviere (1999), More and Stevens (2000), Kyle, Graefe, and Absher (2002), and Chung et al. (2011), with topics addressing the efficiency, equity, and attitudinal aspects of user fees. Watson and Herath (1999) summarize findings from two early special issues on recreation fees and note that economic efficiency is only one of several goals a fee system might address, which also include equity and acceptability by the public.1
Several studies have targeted an understanding of the responsiveness of use to fees. For example, Englin, Boxall, and Watson (1998) examine price responsiveness to measure the welfare effects of international exchange rate changes, and Herriges and Phaneuf (2002) emphasize own- and cross-price elasticities as the building blocks for understanding different models’ welfare predictions. In other cases, researchers have used predicted trip responses as a metric to gauge model performance (e.g., von Haefen and Phaneuf 2003). A specific topic in this space is optimal rationing of recreation access, including characterizing optimal fees (e.g., Wilman 1988; Walsh, Peterson, and McKean 1989; Sibly 2001; Alpizar 2006) and the optimal taxation literature that began with Ramsey (1927), who characterized efficient commodity taxes to achieve a revenue target. Importantly for our purposes, two studies have directly addressed the ability of fees to raise revenue and their distributional consequences: Adams et al. (1989) and Kim, Shaw, and Woodward (2007).
Another key literature topic is the concept of weak complementarity (Mäler 1974; Smith and Banzhaf 2004, 2007) and the contribution from Banzhaf and Smith (2022) in this issue, who build on the weak complementarity literature to identify the conditions for an unambiguously positive welfare change from a user fee that is used to improve the quality of the affected site. Their work provides important insights by focusing on the potential welfare improvements from the combination of an increase in fees and an adequate site quality improvement.
3. Iowa Lakes Data
The data used in this study come from the Iowa Lake Project, a multiple-year household survey initiative conducted by the Center for Agricultural and Rural Development at Iowa State University. Surveys were conducted in 2002, 2003, 2004, 2005, 2009, and 2014.2 For each survey year, trip records were collected for recreation visits by Iowa residents to over 130 lakes in the state, using identical solicitation questions in each iteration. To construct an unbalanced panel, in 2002 and 2003, approximately 8,000 randomly selected households were sent a survey packet. During each subsequent iteration, the original respondents were once again contacted, and a new set of randomly selected households was added to refresh the sample due to nonresponse loss. For 2002-2009, the same set of lakes was included in the survey. A new set of urban lakes close to population centers was added in 2014. Appendix Figure B1 shows the map used with the 2014 survey to display the location of lakes. Each annual cross section contains approximately 3,000-5,000 usable household samples, representing almost 9,000 unique households, with 5,327 households contributing at least two years of data and nearly 400 completing all years.3
Table 1 shows summary statistics for several main variables, broken out by survey years. Iowa households reported taking an average of 6.59 annual trips to lakes in the state. The annual number of reported trips is quite stable across years, with the lowest trip counts in 2009 at 6.25 and the highest trip counts in 2003 at 6.94. Conditional on taking a trip, residents of the state report avid use, with visitors taking approximately 11 trips a year.
Table 1 also shows summary statistics for travel costs, defined to include out-of-pocket costs and the opportunity cost of time. We define travel cost tcijy for each household i to each lake j during year y using the following formula:
[1]
where cy is the marginal cost per mile reported in the year y by the American Automotive Association (AAA),4dij is the one-way distance in miles to lake j from the household’s home, and timeij is the one-way travel time in hours. The variable wageiy is the average household wage, obtained by dividing household income by the number of adults in the household then by 2,000, an approximation for annual work hours. Following convention, we use one-third of the average wage as the opportunity cost of an hour’s travel time. All travel costs are expressed in 2002 dollars. Household-lake pairwise travel costs vary moderately, ranging from $97 in 2014 to a high of $143 in 2005. The range of travel costs for trips taken varies from $36 to about $66. The average household size was around 2.5 people, and about two-thirds of the respondents were male. We construct the average weekend temperature and precipitation in the home county during the year, using data from the PRISM Climate Group.5
4. Demand System Model and Optimal User Fees
Empirical Model
We use a demand system model based on Poisson-distributed trip counts (Englin, Boxall, and Watson 1998; von Haefen and Phaneuf 2003) to study the effects of counterfactual fee increases using the Iowa lakes data. Specifically, we assume that the expected demand for trips by household i during year y to lake j is given by
[2]
Our specification includes a full set of time-by-site alternative specific constants αjy, which control for all characteristics of recreation sites (e.g., water quality, visitor facilities, surface area, depth of the lake) that are constant over people for that site-year pair. For consistency with integrability conditions (von Haefen 2002), we allow the own-travel cost parameter βj to vary across sites, restrict the coefficient γon annual income Yiy to be constant across sites, and restrict all cross-travel cost parameters to zero. This last restriction has important ramifications for how the model accommodates substitution across sites. The variable Xiy is a set of household demographics, including age, gender, educational attainment of the respondent, and the average weekend weather variables (temperature and precipitation) at the household’s home county. The functional form of the demand system in equation [2] gives rise to an expected indirect utility function of the form
[3]
To estimate the parameters in equation [3], we assume that tripsijy has a univariate Poisson distribution so that
[4]
where the first moment of the distribution is equal to expected trips:
[5]
With this assumption, the contribution to the log-likelihood for household i in year y is
[6]
We use equation [6] to derive the sample log-likelihood for all households and years and estimate the demand equation parameters using maximum likelihood.
Raising Revenue
Our primary interest is studying how alternative revenue-raising schemes perform using this trip demand structure. We assume it is possible to impose a lake-specific per visit user fee tj for each lake j = 1,…,J. With this, the expected revenue from household i during year y is
[7]
The fee system also reduces visitors’ welfare. Based on the indirect utility function in equation [3], the welfare loss from the fee system without any feedback to improved site quality is
[8]
The compensating variation (CV) from the fee system is a willingness to accept. It is the income transfer the person would need to receive to restore baseline utility. Computationally for our utility function, CV is the increase in income under the fee system that makes V0 = V1 in equation [8], which we solve as
[9]
Optimal User Fees without Revenue Recycling for a Quality Improvement
We use equations [7] and [9] to predict the individual and population revenue and welfare consequences of an arbitrary set of site user fees. We are also interested in the optimal user fees when there is a specific revenue goal. For this, we apply the Ramsey (1927) logic to derive user fees that minimize the welfare cost of obtaining a revenue goal. Specifically, in the case of a single household, we select user fees t1,…,tJ to minimize equation [8] subject to a revenue constraint based on equation [7]. Because the first three terms in equation [8] are constant with respect to the user fees, the formal problem can be written as
[10]
where R is the revenue target and λis the Lagrange multiplier on the revenue constraint. In Appendix A, we examine the first-order conditions for this problem and show that the optimal user fees are characterized by
[11]
This result matches the standard Ramsey intuition that an optimal tax system should reduce the quantity demanded for all taxed commodities by the same proportion. Here, βj is the proportionate reduction in trips to site j from a one-unit change in the fee, and so tj · βj is the overall proportionate reduction from the fee level tj.
The formulas for revenue, welfare loss, and optimal user fees are derived in reference to a single household. In our empirical analysis, we are also interested in understanding aggregate outcomes. The predictions for household revenue and welfare losses in equations [7] and [9] can be directly aggregated using the properties of our sample. The population analog to the optimal user fees, however, requires a separate calculation when households are not identical. We show in Appendix A that equation [11] holds approximately in our context when income effects are small.
Optimal User Fees with Revenue Recycling for a Quality Improvement
Banzhaf and Smith (2022) derive two relationships conditioned on weak complementarity that determine whether a user fee accompanied by a site quality improvement is welfare enhancing. First, if weak complementarity holds and the combined effect of the user fee and the resulting site quality improvement leads to an increase in trip demand, consumer surplus is positive (this is exact for Hicksian demand and holds for Marshallian demand if the Willig condition also holds).
To examine this situation in our context, we need a way for site quality to enter our system of demand equations. Fortunately, the alternative specific constant, αjy, can be interpreted as a site quality index that nonparametrically captures all nonprice and household-constant determinants of demand for site j during year y. Similar to Murdock (2006) and Phaneuf, Carbone, and Herriges (2009), we assume the quality index is a function of observable, policy-relevant quality variables qjy (e.g., ambient water quality) as well as unmeasured or unobservable (to the researcher) attributes ξjy, so that
[12]
We consider changes in the quality index αjy that could be brought about by an unspecified change in an element of qjy, given the structure in equation [12]. With this addition to our basic model in equation [2], we can analyze the effects of a simultaneous site user fee and quality change.
If we posit a set of user fees t1,…,tJ and an increase in site quality of Δαj, Banzhaf and Smith’s (2022) condition that welfare is improved if site demand increases can be written as
[13]
where we have dropped the time subscripts to reduce clutter.
Their second insight relevant for our work is that if the cost structure of the quality improvement is unknown, it is still possible to solve for the welfare-enhancing change in site quality. The break-even quality change falls out naturally from equation [13] and can be written as
[14]
or equivalently as
[15]
The second form of this break-even condition corresponds to equation [6] in Banzhaf and Smith (2022), which shows that the break-even tax is a product of the change in quality and the marginal willingness to pay for a trip, since the per trip consumer surplus in the semi-log model is simply
. Thus equation [15] provides a prediction for the change in the site quality index that is required to offset the trip-reducing impact of a site fee.
5. Results
Parameter Estimates
Table 2 displays selected parameter estimates for two versions of our demand system model. Both models include a full set of site-by-year fixed effects (the αjy terms in equation [2]) that are not shown. Model 1 corresponds to a standard specification: we estimate 139 own-travel cost parameters, 139 parameters for each of 12 demand-shifting variables, and a single income coefficient. Model 2 generalizes the specification to allow the travel cost and income coefficients to vary with household membership in one of five income categories. Specifically, we estimate separate parameters and γa for the a = 1,…,5 income categories defined in Table 1. That is, we estimate 139 own-travel cost parameters for each income category and five separate income parameters while maintaining homogeneity in the demand-shifting parameters. The table of results shows median and interquartile ranges for the travel cost and demand shift parameters across the range of values for the recreation sites. Point estimates and z-statistics constructed using robust standard errors are displayed for the income coefficients.
Our estimates are generally as expected. The travel cost parameters are in $100 units and are negative across their interquartile ranges (and are, in fact, negative for all sites). The distance between the 25th and 75th percentiles for these parameters shows that there is substantial heterogeneity across sites in the responsiveness of trip demand to travel cost. In model 1, the log-linear functional form and travel cost units imply the demand for trips at the median value of βj decreases 5.7% from a $1 increase in travel cost; this changes to 7.3% and 4.3% at the endpoints of the interquartile range. In model 2, we see similar variation for the βjs in the income categories and find that the median and interquartile endpoints are smaller in absolute value for households in the upper income categories. This suggests higher-income households are less sensitive to travel costs than are households in the lower-income categories. These findings are similar in spirit to Kim, Shaw, and Woodward (2007), who allow the travel cost parameters in a random utility model to differ with income levels.
The income parameters are positive in general, with model 2 showing smaller income responsiveness for higher-income households. The direction of heterogeneity in travel cost and income effects in model 2 suggests that important distributional aspects may be masked when the simpler specification from model 1 is used, a point to which we return below. The demand shift variables show substantial heterogeneity across sites in how they affect demand, with the interquartile range going from negative to positive for nearly all variables. This heterogeneity implies it is difficult to draw general conclusions about the household, precipitation, and temperature variables, so we treat them mainly as controls and do not discuss them further.
In Table 3, we explore the behavioral implications of the different models by examining how aggregate trip demand responds to marginal price and income changes. Specially, we construct total trip price arc elasticities by increasing the travel cost to each site for each respondent in the 2014 cross section by 1%. With this, we predict the change in total trips for each respondent. The change is divided by expected baseline trips and multiplied by 100. We similarly construct total trip income arc elasticities by predicting the change in trips to all sites from a 1% increase in income. The sample averages for these calculations are reported in Table 3. Two observations are clear from the predictions. First, total trip demand is elastic with respect to travel cost for all income categories, so site entry fees may generate a comparatively large decrease in visits. Model 1 by construction captures little variation in price responsiveness across income categories, whereas for model 2, higher-income households are moderately less price elastic. Second, total trip demand is inelastic with respect to income. The log-linear functional form that we use implies that the income elasticity of trip demand for all sites is the product of income and the coefficient on income. The heterogeneity in income elasticities across income categories in model 1 is therefore mechanical. The heterogeneity in model 2 is based on differences in coefficients and income levels, so it is a more genuine representation of differential elasticities. We find that the lowest and highest income households’ total trip demand is the least responsive to a change in income, while the middle three categories are similar and somewhat more responsive.
Uniform User Fees
To further investigate the behavioral responses implied by the model specifications, we consider three different uniform fee structures and their consequences for changes in trip-taking behavior, revenue collected, and consumer welfare. The scenarios include:
■ Scenario 1: entry fee of $20 per trip at all lake sites in the model (Fees All $20).
■ Scenario 2: entry fee of $20 per trip at all lakes sites that have a boat ramp (Fees Boat $20, 105 sites).
■ Scenario 3: entry fee of $20 per trip at all lakes sites that are designated as state parks (Fees Park $20, 47 sites).
■ Scenario 4: entry fee of $5 per trip at all lake sites in the model (Fees All $5).
Table 4 provides point estimates of the average household responses to the four price change scenarios for the two model specifications. For these average effects, there is little difference between the homogeneous (model 1) and heterogeneous (model 2) specifications. In all cases, the estimates illustrate that entry fees decrease recreation visits and private consumer welfare (defined as deadweight loss plus the transfer payment). The predicted change in trips to lakes with a fee is equivalent to the overall change in trips. This absence of substitution toward nonfee lakes is a direct consequence of the limited cross-site substitution patterns captured by the log-linear functional form and is a disadvantage of this modeling approach. Nonetheless, our estimates suggest that entry fees can provide revenue to support recreation infrastructure. For the Fees All $20 scenario, for example, the per household total fee payment ranges from $49 to $52 across the two models. The per household revenue amounts are smaller for the boat ramp and park site scenarios, in that fewer lakes have a fee. Likewise, the $5 fee generate correspondingly less revenue. The $20 fee scenario revenue figures come at a relatively high private welfare cost. For the Fees All scenario, for example, the private welfare loss to revenue ratio is 1.67 and 1.61 for models 1 and 2, respectively. For both models and all the $20 scenarios, the ratio is larger than 1.5, implying that uniform fees of this size are a relatively inefficient means of raising revenue for recreation infrastructure. We note, however, that a $20 fee represents an average tax rate of 33%, based on the average travel cost of $60 for trips taken (see Table 1). For the more modest $5 entry fee—an 8.3% rate—the ratio of welfare loss to revenue raised is 1.16 for both models. This suggests that modest uniform fees can generate (smaller) revenue amounts at relatively smaller welfare loss ratios.
Table 5 presents aggregate annual estimates scaled up to the population of Iowa, assuming that our unit of observation is a household and there are 1.267 million households in the state. In aggregate, the two models once again imply similar conclusions. For the most extensive Fees All $20 scenario, the fee program would reduce trips by over 5 million visits, generate $62-$65 million in new revenue, and reduce visitors’ welfare by over $100 million annually. The predictions are similar for the Fees Boat $20 scenario. While lakes with boat ramps make up around 80% of lakes in our data, these sites are popular destinations, thus yielding similar revenue and welfare effects as the more expansive scheme. The less expansive Fees Park $20 scheme generates correspondingly less revenue at a smaller welfare cost. Finally, the Fees All $5 scheme can provide $32 million per year in revenue with comparatively modest aggregate welfare loss.
The average effects shown in Tables 4 and 5 are likely to mask heterogeneity in the incidence of user fees. To examine distributional aspects, Table 6 breaks out household-level averages for the five income categories in our models (see Table 1). Appendix Figure B2 shows the income share of fees paid for each income category across the two models and four fee scenarios. For all fee scenarios and both models, the revenue raised and welfare lost increase with higher income levels, meaning that higher-income households contribute more to overall revenue. Appendix Figure B2 shows, however, that the fee structures are regressive in the sense that households in lower-income categories pay a higher proportion of their income in fees. Comparing panels A and B shows that the extent of regressivity is smaller when we construct predictions using the income-differentiated travel cost coefficient model (model 2). A second way of looking at incidence is to examine heterogeneity in the ratio of private welfare loss to revenue. For model 1, these ratios are largely constant across income categories for any fee scenario. For model 2, this ratio falls with movements to higher-income categories. Thus, our most general specification illustrates two ways that user fees may be regressive: lower-income groups pay higher fees as a percentage of income while also experiencing higher welfare loss per dollar raised.
Optimal User Fees
Here we consider the efficiency properties of uniform versus differentiated fees for raising a fixed amount of revenue. For illustration, we fix a revenue goal of $60 million per year to raise via user fees at all of the lakes in our model. This is our Fees All scenario. For this goal, we consider three possible revenue schemes:
■ Uniform: a fixed entry fee for all visitors at all sites.
■ Income Group: fixed entry fees at all sites that are differentiated by five income categories.
■ Ramsey: site-differentiated entry fees.
The Income Group scheme is a hybrid that we include to consider revenue raising that optimally differentiates user fees (in terms of minimizing welfare loss) for a population based on income categories. Its relevance is illustrated by common price discrimination fee structures, such as senior citizen and student discounts. We examine each revenue scheme for our models and compare the resulting user fees, per household revenue and private welfare loss, and the efficiency ratio, defined as the ratio of welfare loss to revenue raised. We consider average effects and distributional elements.
The analytical characteristics of the Ramsey scheme are described above and in Appendix A. Actual computation for the Uniform, Income Group, and Ramsey schemes for the Iowa population relies on numerical search algorithms. For the Uniform scheme, an iterative approach is used whereby the single entry fee is incrementally changed up or down until a fee is located that results in $60 million in revenue from the Iowa population of households. For the Ramsey scheme, we use a minimization algorithm in Matlab. The objective function in Appendix A equation [A5] is coded with AR = $60 million and scaling up our sample to represent the population. The search algorithm locates the user fees by minimizing aggregate welfare loss subject to the revenue constraint. A similar algorithm is used for the Income Group, but instead of searching for site-differentiated users fees, it searches for five income category-differentiated fees.
Table 7 shows average results for the three schemes and two models, which each raise the $60 million in targeted revenue. In all cases, households contribute on average $47 per year, but there are substantial differences in how the different schemes accomplish this. For model 1, a uniform fee of nearly $16.50 per visit generates an average welfare loss per household of $72 per year. Differentiating the fees based on income leads to modest differences across income groups and similar aggregate welfare losses.6 In contrast to the Uniform and Income Group schemes, optimally site-differentiated user fees reduce the welfare loss to $63 on average—a 12.5% reduction for the same revenue outcome. This is accomplished using a wide range of user fees with median, 5th, and 95th percentiles of $9.30, $4.40, and $25, respectively. These predictions are qualitatively similar for model 2, with the main difference arising for the income-differentiated scheme. Here we see that parameterizing demand based on income category generates more substantial differences in the optimal income category fees. Nonetheless, the average welfare consequences of the non-Ramsey revenue-raising schemes are qualitatively similar to model 1. Specifically, for model 2, the ratio of average private welfare loss to average revenue per household falls from 1.43 for the Uniform and Income Group schemes to 1.29 for the Ramsey scheme.
The distributional properties of the three schemes are shown in Table 8 and Appendix Figure B3. Because model 2 provides income-differentiated estimates, we focus our discussion on the results for this specification. We once again find evidence of regressivity for the Uniform and Ramsey fee schemes in that higher-income households pay a smaller percentage of income and have lower welfare loss to revenue ratios. This regressivity is partially mitigated by the Income Group scheme. Although lower-income households still pay a higher percentage of income in total fees, the magnitude is smaller relative to the other schemes. In addition, the welfare loss to revenue ratio is smaller for the lowest income group (1.36) than for the highest income group (1.53). These findings suggest there is a trade-off between the efficiency gains from optimally differentiated site fees and the distributional benefits from differentiating based on income categories.
User Fees and Quality Changes
Our empirical analysis of user fees has thus far abstracted from the primary motivation for implementing a fee system: to raise revenue to improve recreation infrastructure and site quality. In this section, we consider the magnitude of quality changes necessary to offset the welfare losses implied by specific revenue goals and fee structures following Banzhaf and Smith (2022). Because we do not have access to reliable estimates of the costs required to increase site quality, we consider how overall site quality would need to change to achieve specific revenue targets while structuring welfare-neutral site fees as described in equation [16].
We examine the distribution of these quality changes for a suite of aggregate revenue goals and fee structures. Since the quality index αj does not have meaningful units, we summarize our results using the percentage change in quality relative to average site quality in the landscape:
[16]
where
is the average of the ASCs for the reference year.
Focusing on the results in model 1, we consider revenue targets of $60, $40, and $20 million and examine the quality-change equivalents necessary to make uniform and optimal user fees welfare neutral. Table 9 summarizes the distribution of for each revenue target/fee structure pair. Two patterns are apparent. First, the comparatively inefficient uniform fee approach to raising revenue requires substantially greater site quality improvements to generate welfare gains from a given revenue target. This is especially so for larger revenue targets: for a $60 million target with uniform fees, the average site requires a 94% quality improvement to be welfare neutral; this falls to 54% for the optimal fee structure. Second, the size of site quality improvements needed for welfare neutrality decreases nonlinearly with the aggregate revenue goal. Although this pattern is likely functional-form dependent, it is noteworthy that relatively modest quality improvements (10% and 16% at the average site for Ramsey and uniform fee, respectively) would justify a program targeting $20 million in revenue raised from visitors to lakes in Iowa. That the approximately 135 estimated ASCs have a mean of −1.07 and a standard deviation of 1.7 (far exceeding a 16% difference) suggests that this magnitude of quality improvement may be realistic.
6. Discussion and Conclusions
The focus in applications of recreation demand modeling in environmental economics has long been on measuring the willingness to pay for access and site quality changes. For this reason, research has emphasized methods and specifications that facilitate prediction of theoretically consistent models and welfare measures. We considered a somewhat different problem that has been a focus in areas outside of environmental economics: using recreation demand models to understand the revenue-raising potential and efficiency properties of user fees to provide funds to support recreation infrastructure on public lands. Using the Iowa Lakes data set and a demand system model for illustration, we draw four main conclusions.
First, we find that there is substantial heterogeneity across destinations in the responsiveness of trip demand to travel cost. Nonetheless, demand is generally elastic: a 1% increase in price at all sites would decrease aggregate demand by more than 1.5%. This suggests that large user fees could lead to a notable reduction in visits to lakes. For example, we predict that households will take four fewer trips per year on average in response to a $20 per trip user fee at all sites. This is relative to baseline averages of nearly seven trips a year for all households, 11 trips per year for household that take any trips, and an average travel cost for trips taken of $60. For a more modest $5 per trip fee, we predict a decrease of around 1.5 trips.
Second, we find that there are efficiency trade-offs in designing user fees. A system of uniform user fees designed to raise $60 million from visitors to Iowa lakes results in the average household experiencing a 1.43 ratio of welfare loss to revenue contributed for our most general model. This ratio can be thought of in terms of a marginal cost of public funds (MCPF) in the sense that the uniform fee has a private welfare cost of $1.43 for each $1 raised to support recreation infrastructure. Two recent reviews suggest that the magnitude of the MCPF from income and other taxes in the United States ranges from 1.08 to 1.47 (Auriol and Warlters 2012; Saez, Slemrod, and Giertz 2012). Our estimate for uniform fees is within this range, albeit at the upper end. Furthermore, the ratio falls to 1.29 when the fee system is optimally differentiated across sites. These findings indicate that, even in the absence of the welfare gains from recycling the tax revenues to improve site quality (thereby compensating in part for the welfare loss from the taxation scheme), this form of financing public goods is no more inefficient than the use of general revenues. In this vein, user fees are roughly an equivalent second-best policy for revenue as the use of general revenues raised via income and other distortionary taxes.
Third, like much of the leisure sciences research (e.g., More and Stevens 2000), we find that user fees are likely to be regressive. Across model specifications and revenue-raising scenarios, we find that lower-income households pay a higher proportion of total income in user fees, relative to higher-income households. For uniform and optimally differentiated fees, we also find that lower-income households experience a larger ratio of welfare loss to revenue contributed, illustrating an additional dimension along which user fees may be regressive. We find that income-differentiated users fees can partially mitigate the regressivity of uniform and Ramsey-type fees but at the expense of efficiency gains generated by the latter. Importantly, uniform fees do not provide notable distributional benefits vis-à-vis Ramsey-type fees, so equity considerations do not suggest favoring a less efficient uniform fee system.
Finally, through our analysis of simultaneous fee and quality changes, we provide an application of the Banzhaf and Smith (2022) framework for assessing the welfare consequences of relying on user fees to generate revenue for improving site quality. Our approach produced a distribution of quality changes that would be needed for a range of possible aggregate revenue goals and site fee systems to be welfare neutral. Through this analysis, we show that the theoretical possibility of welfare-improving fee and quality-change combinations may have practical potential in our application. For our Iowa lakes application, an average quality improvement of 10% at each site would be sufficient to justify $20 million in new revenue/expenditure raised from an optimal set of user fees; this increases to 16% for a comparatively inefficient uniform fee structure. While assembling the cost information is beyond the scope of this research, our sense from this exercise is that modest efforts in Iowa to improve lake site quality by collecting user fees could generate positive net welfare effects.
We close with some caveats and suggestions for further research. First, all our findings are conditional on the assumption that people respond to explicit user costs in the same way they respond to implicit travel costs. Although this is a foundational assumption in travel cost modeling, there is little evidence on its validity. For example, if visitors are more responsive to actual money fees than implicit travel costs, our analysis will underpredict trip changes and overpredict revenue potential. Similarly, our analysis does not consider the potential for short-term backlash to user fees as a dramatic departure from established norms. Second, the findings we report are specific to the Iowa lakes contexts. It will be useful to examine the heterogeneity that may exist across geography and recreation resources.
Further research should examine these questions using a broader set of modeling frameworks. This seems especially important given that the system approach used here imposes strong restrictions on the extent of cross-site substitution possibilities. Research focusing on the merits of different modeling approaches has mainly emphasized welfare comparisons. Including more explicit considerations of revenue raising, income-based heterogeneity and distributional elements, changes in trip-taking patterns, and optimal user fees may be useful and provide additional dimensions for gauging the merits of competing approaches.
Acknowledgments
We appreciate that many useful comments provided by Spencer Banzhaf, an anonymous reviewer, and participants at the Property and Environment Research Center’s workshop “What Price to Play? The Future of Outdoor Recreation and Public Land Funding” in Bozeman, Montana, on November 7–9, 2019. Partial financial support was provided by grant 2019-67023-29637 from the National Institute of Food and Agriculture.
Footnotes
Appendix materials are freely available at http://le.uwpress.org and via the links in the electronic version of this article.
↵1 They also identified seven key research themes as quoted in Buckley (2003, 57): “trade-offs between collective and consumer perspectives; roles of visitor and agency; when to charge fees and what to do with the revenue; public support for fees; who is most affected by fees; how managers can access effects of policy on visitors; and how to integrate science into policy formation.”
↵2 A seventh survey has been recently completed, but data are not yet available.
↵3 If 2014 is not included, there are nearly 1,000 households completing all five years of the survey.
↵4 These costs are: 2002, 29.6 cents; 2003, 31.2 cents; 2004, 31.1 cents; 2005, 32.6 cents; 2009, 34.32 cents; 2014, 40.73 cents. These marginal driving costs include operational costs like gas, maintenance, and tires, plus the marginal depreciation cost.
↵5 See the PRISM Climate Group (monthly data), available at http://prism.oregonstate.edu/.
↵6 The algorithm used to optimally determine the five income group fees was confirmed to have produced smaller aggregate utility losses than the nonoptimized uniform fee, even though the unform fee results in marginally higher average household welfare loss in model 1.