Valuing the Endangered Silvery Minnow
and the Protection of Minimum Instream Flows in New Mexico
Robert P. Berrens
Philip Ganderton
Department of Economics
University of New Mexico
Carol Silva
Institute for Public Policy
University of New Mexico
Address correspondence to R. Berrens, 1915 Roma NE, Economics Building, Albuquerque
NM 87131-1101; 505-***-****; ********@***.***. Helpful research assistance was
provided by Paul Leonis and Tim Cone. Scott Goold of the Survey Research Center, Institute
for Public Policy, (SRC-IPP) at the University of New Mexico provided valuable assistance in
survey implementation. The authors are solely responsible for any errors.
ABSTRACT: The survey-based contingent valuation (CV) method is used to value the
protection of the endangered silvery minnow (Hybnognathus amarus), and minimum instream
flows in New Mexico s rivers. Instream flows are not a recognized category of be neficial use
under New Mexico water law. All other western states recognize some degree of benefits
accruing from provision of instream flow. The CV survey uses a dichotomous choice format
for eliciting valuation responses, and includes split sample treatments for tests of: (1)
sensitivity to changes in the scope of the good, and (2) response effects from a reminder of
group size supporting the public good. Results show that there are significant positive values
for the maintenance of minimum instream flows, and the preservation of flows associated with
the silvery minnow s habitat. The evidence rejects the hypothesis of insensitivity to changes
in scope, and shows no response effects to the group size reminder. Together, these tests
provide evidence against the recent hypothesis that CV results are dominated by a
"contribution model" of valuation responses. While the degree of acceptable precision of CV
results remains hotly debated for legal proceedings, our purpose is targeted to investigating the
prima facia case for important benefits associated with protecting minimum instream flows in New
Mexico.
KEY WORDS: instream flows, endangered species, contingent valuation, contribution model.
1
I. INTRODUCTION
The protection of instream flows has emerged as a serious issue in western states.
While the prior appropriation doctrine is the common denominator in western water law,
individual states differ substantially in the mechanisms available for the protection of instream
flows. New Mexico trails the other western states in not providing a mechanism or avenue for
the protection of instream flows, and has been historically resistant to change (DeYoung,
1993; Nelson et al., 1978). Across the west, there is accumulating evidence on the nonmarket
benefits (e.g., recreation, fish and wildlife habitat) of protecting instream flows. In New
Mexico, minimum instream flows and associated riparian habitats are critical to the
preservation of a number of endangered native fresh water fish species, including the
recently-listed silvery minnow (Hybnognathus amarus) in the middle Rio Grande (Bestgen
and Platania, 1991). A change in the status quo requires that a prima facia case be made for
the public benefits of maintaining instream flows for the protection of at-risk fish species.
This study uses the survey-based contingent valuation (CV) method to estimate nonmarket
values for protecting the silvery minnow and minimum instream flows in New Mexico. Asking
respondents to a New Mexico telephone survey whether they would contribute to a trust fund
set up to protect minimum instream flows, we use econometric techniques to test the
predictions of competing theoretical models and ultimately obtain an estimate of the
aggregate value of maintainin instream flows in New Mexico rivers.
The CV method is a valuable tool for measuring the economic value of nonmarket
environmental goods, and can provide important quantitative information in the larger
decision making system. While controversial in some settings, applications of CV are
increasing rapidly. Application of the CV method to measure nonuse or passive use values,
not associated with any direct in situ use of the resource, has recently received the qualified
endorsement of a blue -ribbon panel that included several Nobel Laureate economists (Arrow
et al., 1993). Nevertheless, debate over the method remains polemic (e.g., Diamond and
Hausman, 1994; Hanemann, 1994).
Continued refinement of the CV method requires formal hypothesis testing and the
accumulation of evidence; this implies the mapping of performance characteristics for selected
survey instruments and experimental designs. The survey instrument used here includes a
dichotomous choice format for eliciting valuation responses, and split sample treatments for
tests of: (1) sensitivity to changes in the scope of the good, and (2) reminder effects on group
size supporting the public good. Both tests are designed to respond directly to specific
concerns raised recently over the validity of CV results, and in particular the hypothesis that
CV surveys are dominated by a contribution model of valuation responses (e.g., Green et al.,
1994; Kahneman and Knetsch, 1992; Kahneman et al., 1993; Kahneman and Ritov, 1994).
II. BACKGROUND ON INSTREAM FLOW PROTECTION AND VALUES
A rapidly growing population in an arid climate has placed increasing demands on New
Mexico's limited water supply. The struggle over water allocation and management has led to
careful scrutiny of the provisions and principles of New Mexico water law. Throughout the
2
west there is growing concern for the protection of instream flows (Bokum et al., 1992;
MacDonnell and Rice, 1993). Instream flow can be defined as the flow of water in its natural
channels without diversion. There is little dispute that maintaining some degree of instream
flow is desirable to protect and enhance recreation, water quality, and biodiversity. What is
disputed is the degree to which maintenance of instream flows inhibits existing consumptive
uses of water, and what additional actions, if any, are implied by a minimum instream flow
regime.
Like all western states, the basic tenet of New Mexico water law is the prior
appropriation doctrine.1 The four main features of the prior appropriation doctrine are: (i)
early claimants hold senior rights, latter claimants hold junior rights; (ii) rights are
usufructory, and water must be put to beneficial use, (iii) an extended period (e.g., three to
four years) of nonuse is cause for the revocation of water rights; and (iv) water rights can be
transferred from one party to another. New Mexico does not recognize instream flows as a
beneficial use of water, and has been politically resistant to any disruption in the status quo
(DeYoung, 1993). In the past, New Mexico has been singled out for its successful prior
1
Article XVI of the Constitution of the State of New Mexico includes provisions for allocating
water: (1) All existing rights to the use of any waters in this state for any useful or beneficial purpose
are hereby recognized and confirmed; (2) The unappropriated water of every natural stream,
perennial or torrential, within the State of New Mexico, is hereby declared to belong to the public and
to be subject to appropriation for beneficial use, in accordance with the laws of the State. Priority of
appropriation shall give the better right; (3) Beneficial use shall be the basis, the measure and the
limit of the right to use water (Bokum et al. 1992). In contrast to some other western states (e.g.,
Arizona), the New Mexico Constitution does not explicitly mention diversion. Although, longstanding
historical interpretation makes this requirement clear in New Mexico (Bahr and Perman, 1984;
DeYoung, 1993). Similarly, while undefined, beneficial use has traditionally been legally interpreted
3
appropriation system, and in particular its avoidance of any politically formulated preference
categories of beneficial use (e.g., Williams, 1985). However, there has always been an implicit
political preference against instream flow protection, and explicit legal preference in state
case law to impose a diversionary requirement on beneficial use.
as agricultural, municipal, and industrial.
4
Given that beneficial use typically requires that water be diverted from the streambed,
voluntary private market transfers to provide instream flows are still generally unavailable or
heavily restricted in most western states. In response, a variety of alternative protection
actions have been explored. These include applications of the common law public trust
doctrine, and explicit "public interest" or "public welfare" clauses in state statutes.2 Further,
in some states, a single public agency may purchase water rights to protect instream flows,
and typically restricted to some minimum requirement. It has long been argued that operation
of the New Mexico water rights system provides sufficient de facto protection of instream
flows (Reynolds, 1977; DeYoung, 1993). Such an system is open to abuse and stands in direct
contrast to accumulating ecological evidence of degraded and dewatered riparian ecosystems
(Bestgen and Platania, 1991; Bokum et al., 1992; Platania, 1991). Protecting minimum
2
Griffin and Hsu (1993) derive the theoretical conditions for an efficient water market that
accommodates both traditional diversionary and instream interests. Necessary conditions are complex
and include a public agency for facilitating transfers, recognizing the presence of instream flow
interests, and full identification of return flow coefficients for all diversion and consumption uses.
Achieving efficiency is also complicated by the public good characteristics (nonrivalness and
nonexclusiveness) of instream flow protection (Colby, 1993). There are also distributional concerns.
In New Mexico, there is longstanding concern that opening voluntary market transactions to
instream flows would negatively affect traditional communal water use systems (acequias). See
DeYoung (1993) and references therein.
5
instream flows has been identified as critical to the maintenance of riparian ecosystems and
fish and wildlife habitats.
In August 1994, the silvery minnow (Hybnognathus amarus) was officially added to the
list of endangered species by the U.S. Fish and Wildlife Service (USFWS). This tiny fish
(approximately 3 1/2" length) was once abundant throughout the Rio Grande system, but now
lives in five percent of its original habitat - relegated to a 170 mile stretch in the middle Rio
Grande. Maintenance of this habitat depends on some level, as yet to be determined, of
instream flows (Bestgen and Platania 1991; Winter, 1994). The silvery minnow is one of
eleven threatened or endangered freshwater fish species in New Mexico, approximately half
of the total number of freshwater fish species in New Mexico. Perfunctory arguments that the
current state system provides de facto protection of instream flows are incre asingly matched
against federal regulatory requirements to protect listed species (Potter, 1993). Thus, there is
a federal nexus; e.g., the failure by New Mexico to provide any avenue for the protection of
instream flows may necessitate future costly fede ral ESA actions.
Any future federal ESA actions to protect instream flows will not come without
warning. In response to the problem of diminished instream flows, the USFWS has long
argued that the use of instream flows for the maintenance of habitat for flora and fauna,
maintenance of fisheries and recreation, and maintenance of streambeds for controlling
erosion and flooding should be recognized in New Mexico as beneficial uses of water (e.g.,
Nelson, 1978). Federal agencies such as the U.S. Forest Service (USFS) have also sought,
6
unsuccessfully, to use the public trust doctrine to obtain New Mexico water rights for the
maintenance of instream flows (Ranquist, 1980).3
3
In a key interpretation of the implied reserved right principle, a 1978 Supreme Court ruling
(U.S. vs. New Mexico, 438 U.S. 696) determined that the federal government agencies cannot
generally appropriate water for instream flows, unless the state agrees or establishes an instream
flow act or provision (Ranquist, 1980). Because New Mexico does not recognize the maintenance of
minimum instream flow as a beneficial use of water, federal agencies have been hampered from
appropriating water rights to maintain the flows necessary for habitat preservation.
7
In New Mexico, the State Engineer has broad authority over water appropriations
(DuMars, 1982). Although not specifically directed to instream flows, state water statutes
were amended in 1985 so that all new appropriations and transfers of both ground and surface
water are subject to conservation and public welfare considerations. Protest of any
appropriation or transfer is allowed for "legitimate" public welfare concerns (Bokum et al.,
1992). Based on this public welfare clause, the State Engineer could deny an application that
would result in a depletion of instream flows required for fish, or that threatened riparian
habitats. Like beneficial use, the concept of public welfare remains undefined, and has not
been employed to protect instream flows (Bokum et al. 1992; Gomez, 1993).4
The legacy of disregard in New Mexico stands in contrast to evidence on the
nonmarket benefits of protecting instream flows in the west. This empirical evidence comes in
a variety of forms; it has been thoroughly reviewed elsewhere, and is discussed only in brief
here. In a methodological and empirical review, Loomis (1987) argues that dollar values for
instream flows can be reasonably estimated using nonmarket valuation techniques, and often
compare favorably against the value of water in traditional beneficial uses. Colby (1990,
1993) also finds strong economic arguments for providing instream flow levels that enhance
recreation and wildlife habitat. Both Loomis (1987) and Colby (1990, 1993) recognize the
4
Gomez (1993) cites the State Engineer's chief water lawyer as questioning whether public
welfare can be quantified in any objective manner, and whether social factors should even be
considered in public welfare deliberations on transfer permits.
8
importance of both use and nonuse values associated with instream flows. Nonuse values may
be especially important when unique environments or endangered species are involved.
Published studies on recreational values associated with instream flows continue to
accumulate. Ward et al. (1991) use a regional travel cost model linked to a biophysical mode l
(including flow) to estimate values for recreational angling in New Mexico. Using a discrete
choice random utility model for a study of California households, Loomis and Creel (1992) find
that increasing summer flows in the San Joaquin Valley provide re creation benefits
competitive with agricultural values. Using dichotomous choice CV, Duffield et al. (1992) and
Harpman et al. (1993) estimate values of recreational angling in Montana and Colorado
rivers, respectively.5
This valuation study investigates the prima facia case for public preferences for
instream flow protection in New Mexico. It is expected that the nonmarket values
investigated in this study will be significantly composed of non-use, or passive use values not
directly related to any in situ use of the resource. Our focus is on the protection of minimum
instream flows (not recreational optimal flows), and endangered and threatened fish species
that are not typically targeted by anglers. We make no attempt to decompose value
estimates, which may in part reflect current or expected future onsite use of the instream
5
In an unpublished CV study of licensed anglers, Duffield and Patterson (1992) find evidence
of positive willingness to contribute to a hypothetical trust fund to protect flows in several Montana
rivers. While there is suggestive evidence that hypothetical values may overestimate relative to
actual contributed values from a control group, the mail survey results are affected by sample
selection and low response rates.
9
flows. While often showing relatively large nonuse values (e.g., Loomis et al., 1993), such
decompositions are of questionable theoretical validity, and are not a fundamental
requirement.
III. SURVEY INSTRUMENT AND EXPERIMENTAL DESIGN
The CV survey was part of a regular quarterly-profile telephone survey of New
Mexico. It was designed and administered in February 1995 by the Survey Research Center
of the Institute for Public Policy (SRC-IPP) at the University of New Mexico. The survey used
random digit dialing and was based on a probability-based sample, and included attitudinal and
perception questions on topics about New Mexico institutions and politics, as well as
numerous socio-economic questions.
In their prescriptive review of CV, Arrow et al. (1993) advocate the use of in-person
surveys, large samples and the avoidance of mail surveys. Telephone surveys are viewed as
a middle alternative. Telephone surveys are significantly cheaper than in-person interviews,
and may reduce the occurrence of response effects such as social desirability bias. The case
for preferring in-person over telephone surveys is unclear, and additional research has been
advocated by a number of sources. However, the use of telephone surveys in CV studies
remains relatively rare. In response, we adopt a formal hypothesis-testing approach, and
evaluate whether complex valuation information can conferred in a carefully administered
telephone survey.
10
The survey instrument includes reminders of household income, budget constraints
and available substitutes, and uses a dichotomous choice elicitation format. The CV section of
the survey was pretested using two focus groups of approximately 20 respondents each. The
SRC-IPP staff of 12 trained interviewers also provided a reading and discussion of the CV
section. Wording of the instrument was refined after each focus group.
The payment vehicle for the hypothetical market is a special trust fund used to buy or
lease water for the purpose of maintaining instream flows. The trust fund payment vehicle was
chosen to match those actually implemented by some western states (e.g., Montana in 1989),
and a river trust that is in initial development in New Mexico (Winter, 1994). The trust fund
would span a period of five years. Respondents are asked for their willingness to pay an
annual contribution into the trust fund to purchase water rights to maintain instream flows. An
explicit feature of the experimental de sign is to phrase the dichotomous choice valuation
question as a willingness to "contribute" a specified dollar amount ?, which is varied across
the sample. The voluntary contribution format is commonly used in CV studies of
nonexclusive environmental goods, including the protection of instream flows (Duffield and
Patterson, 1992), and endangered species (Stevens et al., 1991).
While McConnell (1994) notes an absence of testable models of how people answer
CV-style questions, Kahneman and colleagues argue in a series of recent papers that there
are, in fact, two competing models for how individuals answer valuation questions: the
11
purchase model and the contribution model.6
6
The distinction between the purchase and contribution model can be found in Green et al.,
(1994), Kahneman et al. (1993), and Kahneman and Ritov (1994), and stems from earlier work by
Kahneman and Knetsch (1992). The purchase and contribution model are consistent with the
Stevens et al. (1994) distinction between a utilitarian model and a duty-based Kantian model,
respectively, for how respondents may be interpreting nonuse value questions for wildlife.
12
The "purchase" or exchange model that underlies much of the historical CV literature
constructs a hypothetical (private good or political) market. Within this constructed market
the individual is asked to compare two states of the world and provide the Hicksian income
adjustment that makes her indifferent to a posited change in an environmental good or
service. Willingness to pay (or be paid) responses are interpreted as exchange values, and
expressions of valid measures of welfare change. A general measure of support for the
purchase model is the ubiquitous finding of significant price (or "bid") responsiveness in
referendum-style dichotomous choice models (McConnell, 1994). The purchase model may
also best apply to use values for familiar or near-market commodities (e.g., outdoor
recreation), where general sensitivity to changes in the scope of the good are regularly
observed (e.g., Harpman et al., 1993). The purchase model emphasizes the acquisition of a
precisely demarcated commodity.7
The contribution, or donation, model posits that individuals view public goods provision
as good causes that need/require support (Kahneman and Knetsch, 1992; Kahneman et al.,
1993). Under the contribution model, WTP expresses an attitude to a public good or general
cause. As such, the contribution model entails generally low sensitivity to changes in the
scope of the environmental good or service. Recent evidence of embedding effects in CV
responses are often interpreted as supporting the contribution model. Contributions that
7
Carson and Mitchell (1995) review and provide evidence that a well-defined CV survey
instrument will commonly show sensitivity to changes in the scope of the good for elicited values,
including passive use values. Contrary evidence from a variety of "embedding" tests is attributed to
ill-defined commodities and poor survey design in general.
13
express attitudes may be the source of intrinsic satisfaction, and thus may be the source of
social desirability bias and "warm glow" effects. The contribution model may also be
particularly applicable to nonuse or passive use values (Kahneman and Ritov, 1994).
In order to advance CV research, the standard constructed market exchange model
and the more recent challenger, the contribution model, must produce competing hypotheses.
Discussion has centered around several CV studies that have shown insensitivity to changes
in the scope of the good. However, it is unclear what exactly was tested in some cases,
whether any violation of the standard exchange model actually occurred, or whether the
results were simply anomalies from poorly administered surveys (Carson and Mitchell, 1995).
More recently, CV critics have argued that the exchange model should be invariant to a
reminder of the number of potentially contributing households, whereas the contribution model
posits that such a reminder may be influential. In the initial empirical test of this hypothesis,
Green et al. (1994) identify highly significant reminder effects that lowered valuations for
several public goods by 50 percent or more.
Our telephone survey instrument uses a 2 x 2 experimental design for hypothesis
testing. The two specific hypotheses to be tested are: (1) sensitivity to changes in the scope
of the good, and (2) reminder effects on group size supporting the public good.
The valuation section of the survey begins by asking some general awareness
questions on New Mexico water issues and defining instream flows. Respondents are then
provided with some information concerning instream flows and water law. This text is shown
14
below:
Instream flows support fish and wildlife, vegetation and habitat, recreation and viewing opportunities.
Minimum instream flows can also protect water quality by diluting pollution. Maintaining instream flows
may prevent costly federal government actions to protect endangered species and water quality.
At present New Mexico does not recognize instream as a beneficial use of water. If New Mexico were to
recognize instream flows as a beneficial use, private individuals and groups, and government agencies
could buy or lease water to be left in rivers and streams. It is possible that the price of some agricultural
commodities and municipal water rates could increase, and some development could be restricted.
The experimental treatment used to test the sensitivity of a change in scope is given
by the bracketed material in the text below. There are a range of nesting and sequencing
phenomenon that have been loosely referred to as "embedding effects." Following Carson
and Mitchell's (1995) categorization, we conduct an external (split-sample) test of component
sensitivity for nested goods.8
By federal law the critical habitat of endangered fish species must be protected, and this may require
maintaining minimum instream flows. In New Mexico, endangered fish species are found in a number of
the major rivers including the Gila, Pecos, Rio Grande and the San Juan. [The Silvery Minnow is a small
fish found in the Middle Rio Grande and is currently listed as an endangered species. ]
Now I would like to ask you several questions about the dollar value your household puts on protecting
minimum instream flows [specifically to protect the silvery minnow].There are no right or wrong answers.
Before answering, remember your household income and budget, and decide what you could realistically
afford. Money spent on protecting instream flows is money not available for other goods, public programs,
or other environmental programs. The establishment of a special trust fund for buying or leasing water is
used in some states to protect fish species.
The treatment for the group size reminder directly preceded the valuation question, and was
chosen to closely follow that used in Green et al. (1994):
If such a special trust fund was set up in New Mexico, and requests were made statewide, up to a half
million households could contribute. So each dollar of average household contribution produces a half
million dollars for the special trust fund.
8
This test corresponds to Kahneman and Knetsch's (1992) concept of perfect embedding,
applied in a split-sample context.
15
For modeling, the presence of the group size reminder is hereafter indicated by the dummy
variable, RM (RM=1, reminder treatment, RM=0, control group, no reminder).
The text of the dichotomous choice valuation question for the maintenance of minimum
instream flows specifically for the silvery minnow, the nested good, was:
Would your household contribute $ ? dollars each year for five years to a special trust fund used
to buy or lease water from willing parties to maintain minimum instream flows for the silvery
minnow in the Middle Rio Grande?
The text of the dichotomous choice valuation question for instream flow protection in the
major rivers of New Mexico, the inclusive good, was:
Would your household contribute $ ? dollars each year for five years to a special trust fund used
to buy or lease water from willing parties to maintain minimum instream flows in the major
rivers of New Mexico?
For modeling, the test of scope is hereafter indicated by the dummy variable, SM (SM=1
indicates the silvery minnow question, SM=0 indicates general instream flow question).
An important element of the experimental design in a dichotomous choice CV survey is
the number and size of the offered payment amounts, ?, that are allocated across the sample.
A large literature has developed around this topic, and no consensus has emerged. The
pragmatic approach chosen here was to allocate 8-10 separate amounts across the expected
quarterly profile sample size of 675-700 completed observations, with iterative updating to fill
out the probability of acceptance curve, while keeping excess weight out of the upper and
lower 15 percentiles (Kanninen, 1995). Using the dichotomous choice pre -test results for $5,
$10, and $20, a single initial payment amount ($20) was selected, and the observed probability
16
of acceptance calculated for approximately the first 50 observations. Subsequent additional
payment amounts were added several at a time, with some filling across the mid-range of the
probability of acceptance distribution. Using the CATI (computer-assisted telephone
interview) lab facilities, acceptance rates were observed and updated on a daily basis for the
seven day sampling period. The set of nine separate payment amounts was A = {5, 20, 30,
40, 50, 75, 100, 150, 200}.
Additionally, the structure of the payment amounts had to be coordinated with the 2 x 2
experimental design. Table 1 shows the observed acceptance rates to the dichotomous choice
valuation question broken down by elements of the experimental design (structure of the
contribution amounts, test of the reminder effect, and test of scope).
IV. THEORETICAL CONSIDERATIONS AND MODEL SPECIFICATION
The household's maximum willingness to pay into the special trust to provide
protection of minimum instream flows can be defined as the Hicksian compensating variation
(HCV) measure of the welfare change:
where e is the household's expenditure function, p is a vector of prices for market goods, Q
is the level of instream flow protection, and U is the level of utility or well-being of the
household. A minimum protection level for instream flows is represented by Q1, against an
17
initial lack of protection, Q0. Thus, WTPHCV is an income adjustment that represents the
maximum amount of money the household is willing to pay to acquire the change in instream
flow protection from Q0 to Q1 (Q1 >Q0), while maintaining utility at the initial level, U0. It also
implies that the property right is not currently held by those valuing instream flows.
In the specific case of minimum instream flows, the protection outcome Q1 can be
thought of as a vector of geographic locations (different rivers or river stretches) or
components qj1, Q1 = {q11, q21 qj1 qn1}. As a theoretical condition, imposing weak
monotonicity on the valuation of any nested geographic component implies:
This says that increasing the scope of minimum instream flow protection should not decrease
the valuation. Imposing strong monotonicity would imply the strict inequality. Monotonicity
conditions on nonmarket values are testable hypotheses (Carson and Mitchell, 1995).
In practice the welfare measure WTPHCV, or hereafter just WTP, is a stochastic
variable, and may be conditioned a number of determinants. Further, in the dichotomous
choice elicitation format, WTP is an unobservable variable and must be statistically inferred
though the yes and no responses to the given dollar payment amount, A, which is varied
across the sample. In estimation we follow Cameron's (1988) censored logistic regression
approach, which emphasizes the determinants of WTP, and facilitates hypothesis testing
18
(Cameron, 1991).9
B egin by assuming that underlying, latent, willingness to pay into the trust fund is a
linear function of a vector of explanatory variables, X, which may include respondent
characteristics and elements of the experimental design:
where is a vector of coefficients to be estimated, and ei is an error term assumed to be
distributed logistically with mean 0 and standard deviation b. The logistic distribution is
further characterized by the additional scale parameter ?, where ? =b 3/p (Park and Loomis,
1992).
To estimate the latent WTP, we introduce a binary indicator variable of yes (Wi=1) and
9
This valuation approach has been applied in recent studies on water resources (Duffield et
al., 1992; Whitehead and Blomquist, 1991), and endangered species (Hagen et al., 1991).
19
no (Wi=0) responses to the dichotomous choice valuation question as follows:
The probability of a yes response in the logistic model is represented as:
where ? is the coefficient on the censoring threshold, ?, and ? is the vector of coefficients on
the explanatory variables, X. The equation to be estimated can be represented as the linear-
in-the-parameters "logit" or log of the odds ratio, ln[Pi/(1-Pi)] = a ? i + ? Xi. Given that the
WTP scale parameter, ?, is equal to the negative of the inverse of the estimated coefficient on
the payment amount (? =-1/a ), the coefficients of the logit model can be used to recover the
underlying, latent WTP, or "variation function" (Cameron, 1988; Park and Loomis, 1992):
Thus, dividing through by the coefficient on the payment amount, yields the vector of
coefficients on the latent WTP equation ( =-? /a ). Equation (6) can be interpreted as the result
of an ordinary least squares regression, where expected WTP is conditional on the fitted
values for the coefficients.
Further, using Cameron's censored logistic approach and maximum likelihood
techniques, the scale parameter ?, the vector of coefficients, and associated standard errors
can be estimated directly for the WTP function. For the sample of individual observations, n,
20
the simplified log-likelihood for the censored logistic approach is:
Estimates from both logit and WTP models are presented in the empirical results below.
V. EMPIRICAL RESULTS
Estimates from selected valuation models can be used to test the two component
hypotheses that together provide evidence for, or against, the contribution model. In this
section we test these hypotheses using three distinct, but related, me thods. We describe a
non-parametric test, and a set of parametric tests based on statistics from logit and maximum
likelihood (Cameron) models.
The results of conducting nonparametric tests of scope and reminder effects using the
observed acceptance rates P(Wi=1) are shown in Table 1. Wilcoxson Signed Rank Tests for
Paired Difference Experiments, were conducted with pairings at each payment level, ?,
forming the probability distributions (McLave and Deitrich, 1985:496). For the test of scope
(SM=1 versus SM=0), the evidence rejects the null hypothesis that the probability
distributions are identical (at a less than 0.02 significance level for the two-tailed test, and
0.01 for the one -tailed test). Thus, there is initial evidence of sensitivity to a change in the
scope of the good. For the test of the reminder effect (RM=1 versus RM=0), the evidence
supports the null hypothesis that the probability distributions are the same. These tests have
21
limited appeal as they do not control for respondent characteristics. We use the valuation
models developed in section IV above to estimate treatment effects within a regression
framework.
The telephone survey included a wide variety of attitudinal and socio-economic
questions. Descriptive statistics with response rates for selected variables are shown in Table
2, which also includes the expected effect each variable will have on the probability of
responding yes to the contribution question.
Probability models were estimated incorporating treatment indicators and variables
suggested by economic theory and previous CV studies.10 Table 3 presents the results of
estimating three separate logit models (I, II, III). Logit-I is a linear-in-the-parameters model
with 10 explanatory variables, and the censoring threshold, ? . Logit-II is an extended linear
model that tests for the effect of an additional five explanatory variables.
Comparing the first two logit specifications, there is little to separate them in terms of
overall goodness-of-fit statistics. The evidence from separate likelihood ratio tests (LRT)
rejects the null hypothesis that all model coefficients are zero, and shows that both models are
highly significant overall at the 0.01 level. Both models have McFadden R2 values of 0.15 and
10
A variety of linear and log-linear probit and logit models were estimated. Model diagnostics
were quite similar when using the same set of explanatory variables, with logit models typically
outperforming the probit models slightly. Results from Box-Cox transformations on the bid variable
were indeterminate between the linear and log-linear models. In contrast to the linear models, the
log-linear models do not allow for negative value predictions; something we were unwilling to rule out
for the controversial protection of instream flows. Given that estimated coefficients on the log-linear
logit models were also often in a range producing undefined estimates of the mean, we focus on the
linear logit models.
22
just less than 70 percent correct predictions. As a check on model specification, Logit-III is a
parsimonious specification with only the features of the experimental de sign (?, SM, RM)
included. This model is statistically significant at a level of less than 0.01 with a McFadden R2
of 0.06, and gives 63 percent correct predictions.
All model specifications are consistent with basic economic theory. The estimated
coefficients on the offered contribution amount, ? are statistically significant at the 0.01 level
and negative. In models (I,II), which include income levels, protection of instream flow is
found to be a normal good. The estimated coefficients are positive and significant at less than
the 0.05 level for each of the four income category variables (INC2, INC3, INC4, INC5).11
In the models (I, II) conditioned on respondent characteristics, the estimated
coefficients on age (AGE) and an index of self-reported political ideology (POL-IDEO) are
negative and significant at the 0.05 level. Younger and more liberal respondents are more
likely to contribute a given amount. Additionally, the estimated coefficients for an index of
11
As is common, income responses were obtained for intervals (See Table 2). A variety of
income category groupings were used in preliminary specifications, with the final set chosen on the basis
of statistical efficiency. None of the primary hypotheses tests results for scope and reminder effects
were sensitive to the choice of income groupings.
23
perceived importance of protecting instream flows (IMPORT), and a binary indicator
(RECOG) of whether individuals feel instream flows should be legally recognized as a
beneficial use, are positive and highly significant at the 0.01 level.
The primary hypotheses in this study are tested within the logit model using the
estimated coefficients on the treatment indicators SM (silvery minnow habitat versus all
major rivers) and RM (reminder of group size). The coefficient on SM is highly significant at
the 0.01 level and negative in each specification. We reject the null hypothesis that the
probability of agreeing to contribute a positive amount is insensitive to a change in the scope
of the good (H0:? SM = 0, versus Ha:? SM 0). Moreover, the negative sign supports, within a
one-tail test, the strong monotonicity hypothesis that the implied value of the inclusive good
(instream flows in all New Mexico rivers) is greater than the value of the nested, or included
good (instream flows to protect the silvery minnow in the middle Rio Grande). The coefficient
on RM is not significantly different from zero in any model. We cannot reject the null
hypothesis that the group size reminder has no effect on expressed values (H0:? RM = 0, versus
Ha:? RM 0). Together, these two test results provide evidence contrary to the implications of
the contribution model.
The specification logit-II provides a check on the robustness of the treatment effects
across a larger set of explanatory variables. Additional variables include an interaction term
(INTERACT) between the dummy variables testing sensitivity to scope (SM) and the group
size reminder effect (RM) and binary indicators for awareness of the endangered status of the
24
protected fish in each sample treatment (AWARE), membership in an environmental
organization (ENV-ORG), current or recent ownership of a NM fishing license by any
household member (FSH-LIC), and residential status in Bernalillo County (BERN-CO), which
includes the primary urban area of Albuquerque. The model estimates show that the
coefficients on all five additional explanatory variables are not significantly different from
zero. Further, the signs and general significance of all other explanatory variables remain
stable. Thus, specific hypotheses test results concerning the contribution model are robust
across a wider set of additional explanatory variables, including the interaction between the
experimental treatments.
Table 4 presents the results of estimating the underlying WTP functions directly using
Cameron's (1988) maximum likelihood approach. Three alternative WTP specifications are
again used to test the primary hypotheses, although only WTP-1 corresponds directly to one
of the logit models (I). Specification WTP-1 shows that the signs and significance of the
estimated logit coefficients are maintained. In particular, the estimated coefficient on RM is
insignificant; the evidence supports the null hypothesis of no group size reminder effect
(H0: RM = 0, versus Ha: RM 0). Further, the estimated coefficient on SM is negative and
significant at the 0.01 level; the evidence supports the alternative hypothesis of sensitivity to
a change in the scope of instream flow protection (H0: SM = 0, versus Ha: SM 0).
Specifications WTP-2 and WTP-3 allow a set of nested hypotheses tests to be
conducted using likelihood ratio tests. Specification WTP-3 is a joint model that allows the
25
parameters on each explanatory variable to differ across the test of scope treatment (SM),
and tests for the consistency of the insignificant reminder effect (RM) across the scope
treatment. The model WTP-2 represents the extreme restriction that there is no SM
treatment, and provides a reference for the joint model WTP-3. It also shows that the signs
and significance of all other variables are maintained when the significant SM dummy is
dropped.
Using the joint model (WTP-3) results, the evidence from a likelihood ratio test
supports the alternative hypothesis of a significant difference at the 0.01 level in the sets of
estimated coefficients for the SM treatment groups, against the null of no difference. The
joint model shows that there is a behavioral difference in valuation responses under the test of
scope. Specifically, for the larger inclusive good (general instream flow protection on all
major rivers in NM), all income group coefficients remain significant at less then the 0.05
level and there is a larger bid responsiveness (implicit in the estimated coefficient on ? ). Age
and political ideology are now insignificant. The nested good (instream flow protection for the
silvery minnow) shows reduced income effects and responsiveness to the bid level, while older
and more conservative respondents remain significantly less willing to contribute. However,
in both SM treatment groups the estimated coefficient for the RM dummy is insignificantly
different from zero.12
12
While not presented here, an additional joint model was estimated that incorporated the
restriction that the coefficient on the reminder (RM) is the same for both SM treatment groups.
Evidence from a likelihood ratio test shows no significant difference between this specification and
WTP-3.
26
In summary, across these WTP specifications, the findings with respect to the primary
hypotheses that emerged from the nonparametric Wilcoxson test and the logit models
continue to appear. There is significant sensitivity in valuation responses to a change in the
scope of instream flow protection. The direction of this sensitivity satisfies the strong
monotonicity hypothesis with respect to the valuation of nested goods. There is no statistical
evidence of any response effect due to a group size reminder; this holds across two
significantly different levels of instream flow protection. Table 5 summarizes many of the
diverse hypothesis test results (nonparametric, logit, and WTP models).
With no evidence that valuation responses are consistent with the contribution model
framework, we turn to estimating the expected value of instream flows consistent with the
exchange model interpretation of stated values. Using specification WTP-1 and the sample
means for all variables, except SM, we obtain the function, WTP = 83.54 - 58.32 (SM).13
Using the joint model specification WTP-3, mean predicted annual household willingness to
pay for protection of instream flows specifically for the silvery minnow on the middle Rio
Grande is $28 (standard error of $3.79), versus $92 (standard error of $5.88) for the
protection of minimum instream flows on all major NM rivers and the 11 total listed fish
species. These estimates of annual household willingness to pay are comparable with
13
The mean predicted annual household willingness to pay for the split samples using
specification WTP-1 is $30 (standard error of $4.68; n=287) for the nested good, protection of
minimum instream flows specifically for the silvery minnow on the middle Rio Grande, versus $79
(standard error of $4.93; n=280) for the inclusive good, protection of minimum instream flows on all
major NM rivers and the 11 total listed fish species.
27
estimated values identified in previous nonuse value studies of western instream flows; Colby
(1993) cites a range of annual household values from $40 to $80.
While not the specific focus of this study, estimates of annual household values can
also be aggregated. Using the results from specification WTP-3 and a conservative figure of
500,000 households, estimates of annual statewide values are $14 million for the nested good,
and $46 million for the inclusive good. Further, using these results and a conservative
discount rate of 10 percent, aggregating over the five years of the hypothetical trust fund
program gives a present value of $58 million for minimum instream flow protection in the
middle Rio Grande, and $1.9 billion for minimum instream flow protection on all major New
Mexico rivers.
Estimated values are clearly subject to specification error, statistical error, the choice
of discount rate, etc. Further, the nature of the experiment does not provide marginal values
that can easily be converted into a Mm3 or cfs basis for comparison with alternative uses of
water. However, such considerations do not negate the prima facia evidence that significant
positive values exist for the protection of minimum instream flows in New Mexico. Even
accepting arguments that all CV estimates should be calibrated downward (e.g., dividing by
two in legal damage assessments), the resultant values would still wa rrant important
consideration in public policy debates.
V. DISCUSSION AND CONCLUSIONS
28
In their recent review of CV, Brookshire and McKee (1994) argue that there are two
grounds from which a valuation technique may be criticized: (i) the theoretical basis is flawed,
and (ii) the empirical estimates lack the necessary robustness for their intended purposes. In
this study, the first ground for criticism is addressed by jointly testing two hypotheses from the
contribution model . The second ground for criticism is addressed through the primia facia
argument and the specific context of minimum instream flow values in New Mexico.
Much of the recent debate surrounding CV centers on acceptable levels of precision
for use in natural resource damage assessments and liability cases. However, when using CV
for a wide variety of ex ante policy, and methodological research issues, the same burden of
proof as legal proceedings may not be necessary (e.g., in-person interviews and suggested n >
1000 for each sample treatment (Arrow et al., 1993) ). Our primary objective was in
investigating the prima facia case for nonmarket benefits associated with protecting minimum
instream flows. Such evidence is important in establishing whether instream flow concerns
warrant consideration, or even have legitimate standing in future New Mexico deliberations
over water resources management (e.g., determining allowable beneficial use or public
welfare).
Application of a carefully administered CV telephone survey shows that New Mexico
households place a positive expected value on the maintenance of instream flows, and the
preservation of habitat for endangered and threatened fish species. Valuation responses are
shown to be sensitive to a change in the scope of the good, and insensitive to a reminder of
29
group size, evidence against the contribution model of valuation responses.
These expressed preferences of New Mexico residents strengthen the case for the revision
of the longstanding status quo in New Mexico. Given the right impetus, the prior appropriation
doctrine has been shown to be responsive elsewhere in the West to changing public preferences
(MacDonnel and Rice, 1993). Economists and other social scientists can continue to contribute to
this research by investigating the relative merits of alternative mechanisms for instream flow
protection (e.g. water markets or public welfare intervention). Prudence and pragmatism require
that such analyses be done in the context of potentially irreversible losses of native fish species.
30
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T able 1. Acceptance Rates by Payment Amount and Experimental Treatment
S M=1 and SM=1 and SM=0 and SM=0 and
P ayment, RM=1 RM=0 RM=1 RM=0 T otals
33
$5 16/25 12/21 9/14 16/23 53/83
(.64) [1] (.57) (.64) [2] (.70) (.64) [3]
$20 18/21 12/17 18/21 9/19 57/78
(.86) (.71) [3] (.86) (.47) [1] (.73) [4]
$30 6/24 9/28 13/29 12/16 40/97
(.25) [1] (.32) [1] (.45) (.75) [1] (.41) [3]
$40 7/18 6/17 8/19 15/21 36/75
(.39) [2] (.35) [1] (.42)