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IS THERE A MARKET FOR BRANDED GULF OF MEXICO OYSTERS?

Published online by Cambridge University Press:  16 January 2017

DANIEL R. PETROLIA*
Affiliation:
Department of Agricultural Economics, Mississippi State University, Mississippi State, Mississippi
WILLIAM C. WALTON
Affiliation:
School of Fisheries, Aquaculture, and Aquatic Sciences, Auburn University, Auburn, Alabama
LAURIANE YEHOUENOU
Affiliation:
Food and Resource Economics Department, University of Florida, Gainesville, Florida
*
*Corresponding author's e-mail: d.petrolia@msstate.edu

Abstract

We administered an online choice experiment to a sample of U.S. raw-oyster consumers to identify factors influencing preferences for Gulf of Mexico oysters, determined the extent of preference heterogeneity, and estimated marginal willingness to pay for specific varieties and other key attributes. Results indicate significant preference heterogeneity among select varieties, with non-Gulf respondents estimated to require a price discount on Gulf oyster varieties on the order of $3–$6/half dozen. Gulf respondents were found to be less sensitive to oyster variety, and estimated to be willing to pay a price premium only for select Gulf varieties on the order of $0–$3/half dozen.

Type
Research Article
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution, and reproduction in any medium, provided the original work is properly cited.
Copyright
Copyright © The Author(s) 2017

1. Introduction

The U.S. Gulf states of Alabama, Florida, Louisiana, Mississippi, and Texas harvested 8,731 metric tons of the eastern oyster (Crassostrea virginica) in 2013, accounting for more than 75% of total production for the United States (National Marine Fisheries Service [NMFS], 2014). Yet the value of the Gulf states’ harvest represents only 53% of the total market value because Gulf oysters sell at significantly lower prices relative to those produced in Atlantic and Pacific states (NMFS, 2014). Although many factors affect these prices, the extensive, on-bottom method of oyster farming practiced in Louisiana and other Gulf states has primarily targeted production of large quantities of affordable oysters, which are sold by the sack to processors and typically sold as shucked meats, in sharp contrast to the sales by piece along the northeast Atlantic and Pacific coasts for the live shellstock market. Furthermore, the condition and appearance of extensively cultured oysters is highly dependent on season and harvest location, which can lead to large variation in the quality of the product on the half-shell market.

Although they are the same species, oysters marketed along the Atlantic coast, for example, sell under regional names, such as Wellfleets (from Cape Cod), Blue Points (Long Island), and Chincoteagues (Virginia), and often at a premium. Gulf oysters, on the other hand, are usually sold as cheaper, generic oysters, as Jacobsen (2011) says, “indicative of a region that pays less attention to the nuances of different raw oysters than to their culinary possibilities.” The major exceptions on the Gulf coast are Apalachicolas (Florida), which comprise the bulk of Florida's oyster harvest. Although there is no clear evidence that they sell at a premium, there is anecdotal evidence to suggest that a market has developed for these branded oysters and that additional opportunities may exist.

An alternative source of oyster production is off-bottom farm-raised oysters. Although they currently make up only a very small portion of production in the Gulf, they tend to sell at a premium in high-end restaurants because of their superior aesthetic qualities. Since 2009, nearly two dozen off-bottom oyster farms have been established in the Gulf of Mexico region. This alternative production method allows for greater control of aesthetic characteristics, yielding a potentially higher-value product. The potential for geographic branding and a relative shift in focus from quantity to quality provides an opportunity for Gulf oyster producers to reach new markets, increase existing market share, and/or increase market value.

Although previous work has investigated consumer opinions regarding oysters, most studies have provided more general, qualitative findings (Bishop and Peterson, Reference Bishop and Peterson2005; Grabowski et al., Reference Grabowski, Powers, Peterson, Powers and Green2003; House, Hanson, and Sureshwaran, Reference House, Hanson and Sureshwaran2003; Kow et al., Reference Kow, Yu, FitzGerald and Grewal2008; Martínez-Cordero, Fong, and Haws, Reference Martínez-Cordero, Fong and Haws2009; Nell, O'Riordan, and Ogburn, Reference Nell, O'Riordan and Ogburn2006). Several that have taken a more quantitative approach and reported welfare estimates have focused on the effects of postharvest processing and related risk-reduction initiatives on preferences (Bruner et al., Reference Bruner, Huth, McEvoy and Morgan2011; Lin and Milon, Reference Lin and Milon1993; Morgan et al., Reference Morgan, Whitehead, Huth, Martin and Sjolander2013; Morgan, Martin, and Huth, Reference Morgan, Martin and Huth2009; Morgan, Whitehead, and Huth, 2015; Whitehead et al., Reference Whitehead, Morgan, Huth, Martin and Sjolander2012) or preferences as a function of ecosystem services provided (Kecinski, Messer, and Peo, Reference Kecinski, Messer and Peo2016). Manalo and Gempesaw (Reference Manalo and Gempesaw1997) come closest to the present study in that they utilized a choice experiment to identify preferences over specific attributes, with their focus on price, production method (wild caught vs. farm raised), and inspection agency (U.S. Food and Drug Administration vs. U.S. Department of Agriculture).Footnote 1

We are aware of no studies that have addressed consumer preferences for oysters over specific harvest locations/brands, size, and taste (saltiness), and only the one aforementioned study has focused on production method. To our knowledge, this is also the only study that does so on a national scale, including derivation of marginal willingness-to-pay (WTP) estimates for the specific locations/brands and other attributes. We designed and administered an online choice experiment to a panel of U.S. oyster consumers to identify factors influencing preferences for Gulf oysters, to determine the extent of preference heterogeneity among oyster varieties, and to estimate marginal WTP for specific oyster attributes, including harvest location or brand, size, taste (saltiness), and cultivation method (wild vs. farm raised). Methodologically, this study also represents one of very few analyses to utilize best–worst scaling (BWS) as the preference elicitation method within the choice experiment, particularly with an experiment that includes tasting as part of the panelist's evaluation of the alternatives. This approach allows for more efficient preference information extraction per choice set relative to the typical “first-best” choice approach. Because consumers along the Atlantic and Pacific coasts are generally accustomed to choosing from a variety of oysters from a variety of individual producers and locations, which excludes Gulf coast varieties, whereas Gulf coast consumers are accustomed to purchasing cheaper, generic “Gulf” oysters, the experimental design accounts for regional marketing differences by tailoring the choice sets to mimic the choices that a given consumer would make in their respective market.

2. Experimental Design

The preference elicitation mechanism for this study was a discrete-choice experiment embedded in an online survey instrument (see Louviere, Hensher, and Swait, Reference Louviere, Hensher and Swait2000; McFadden, 1986; McFadden and Train, Reference McFadden and Train2000). The survey instrument had four sections. The first section focused on raw-oyster consumption patterns of respondents. It first screened for raw-oyster consumers using the question, “Do you eat raw oysters on the half shell at least once per year?” Those that responded yes were then asked about raw-oyster consumption frequency, quantity consumed per meal, and source of oysters (e.g., restaurant, seafood market). Of those that responded no, 107 were randomly selected to answer a brief set of alternative questions. These latter respondents were not included in the present analysis. The second section was the choice experiment. Prior to the choice sets, respondents were introduced to the objective of the choice experiment and were given explanations and examples of each attribute. To aid in the size attribute, a photo was provided of a typical small, medium, and large oyster that included an oyster fork for size reference. Respondents were provided an explanation of the alternatives that would be available in each choice set and the available response options. They were informed that they would be asked to evaluate six different choice sets. Then the six choice sets followed.Footnote 2 The third section elicited respondents’ perceived food safety and seafood quality ratings for individual water bodies throughout the United States where oysters are harvested. Specifically, we asked respondents: “Please rate what you perceive to be the overall quality of raw oysters on the half shell from the following places, where a 1 is poor and a 10 is excellent.” We also asked respondents: “Please rate what you perceive to be the overall level of food safety of seafood in general from the following places, where a 1 is poor and a 10 is excellent.” The fourth and final section was a risk-preference exercise (not treated in the present analysis; for details, see Petrolia, Reference Petrolia2016).

The experimental design for the choice experiment was a four-alternative (three oyster alternatives plus a “none of the above” optionFootnote 3 ), 24-row, four-block design (so that each respondent evaluated six choice sets), generated using Ngene software, and was optimized according to S-efficiency (ChoiceMetrics, 2012).Footnote 4 There were two separate designs based on whether a generic Gulf oyster was included as one of the alternatives. Because cheaper, generic Gulf oysters are the typical type of oysters sold in the Gulf region, a survey was designed that included a lower-priced generic Gulf oyster as a fixed third alternative. The design was constrained so that the generic Gulf oyster price was always less than the other branded alternatives offered in a given choice set. To account for this price differential, we specify the price variable as the price difference of the branded oyster alternatives relative to the base generic oyster (i.e., the generic oyster alternative's price is normalized to zero). This survey design was administered to Gulf households only. An alternative survey design was administered that did not include the generic Gulf alternative, but rather included only branded oysters. This design was administered primarily to non-Gulf (i.e., Atlantic coast, Pacific coast, and inland) respondents, although a small number of these were administered to Gulf respondents as well. Although it would have been feasible to administer the design that included generic Gulf oysters to non-Gulf consumers, we decided to administer a design that most closely mimicked the actual market in which a given respondent would purchase oysters.

Attributes included oyster brand/name, price per half dozen, size, saltiness level, and production method (wild or cultivated). All nonprice attribute levels were specified as discrete (i.e., binary) variables, and price was specified as continuous, in units of dollars per half dozen oysters. A total of 13 oyster varieties were included in the design: 7 Gulf varieties, including the “generic” Gulf oyster; 3 Atlantic varieties; and 3 Pacific varieties.Footnote 5 For the generic Gulf oyster only, size was described as “sizes vary,” and saltiness was described as “saltiness varies” to reflect the true variation in size and saltiness found in a typical order of generic Gulf oysters.Footnote 6 All other oyster varieties took on one of the specific levels (i.e., “small”, “medium”, or “large”; “sweet”, “mildly salty”, or “salty”).Footnote 7 Table 1 contains a summary of the attributes and their levels used in the online survey.

Table 1. Attributes and Their Levels Used in the Online Survey Experimental Design (the “low-information” treatment included only the oyster variety and price per half dozen, whereas the “high-information” treatment included all of the attributes listed)

Notes: Asterisk (*) applies to generic Gulf oyster only.

Choice set responses were elicited using the BWS format (Louviere, Flynn, and Marley, Reference Louviere, Flynn and Marley2015). BWS has emerged of late as an alternative to the format of having respondents indicate only their first-best choice (Flynn and Marley, Reference Flynn, Marley, Hess and Daly2014; Flynn et al., Reference Flynn, Louviere, Peters and Coast2007; Marley and Louviere, Reference Marley and Louviere2005; Potoglou et al., Reference Potoglou, Burge, Flynn, Netten, Malley, Forder and Brazier2011; Rigby, Burton, and Lusk, Reference Rigby, Burton and Lusk2015; Scarpa et al., Reference Scarpa, Notaro, Louviere and Raffaelli2011). The BWS format asks respondents to indicate the “best” alternative and then to indicate the “worst” alternative, and of the remaining alternatives, they are asked to indicate the “best” of those remaining and then the “worst,” and so forth, until a full ranking is achieved. The argument is made that choosing “bests” and “worsts” is a relatively easy task for respondents and yields more information per choice set than the standard question format. Thus, it represents a further extension of the discrete-choice experiment format with the potential to increase survey administration cost efficiency even further.

The present format is an application of “case III” BWS (the multiprofile case; see Flynn and Marley, Reference Flynn, Marley, Hess and Daly2014), included a single question with three alternatives, and elicited the “best” and “worst” choice of the three alternatives, thus yielding a full ranking. This ranking was then decomposed following the method of rank-order explosion proposed by Chapman and Staelin (Reference Chapman and Staelin1982), which, in this case, yields two choice observations for each choice set evaluated: a three-alternative observation (first-best case) and a two-alternative observation (second-best case).Footnote 8 In this particular context, respondents were asked to indicate which of the three alternatives they were “Most Likely to Buy” at the posted prices (i.e., “best”) and which of the three alternatives there were “Least Likely to Buy” at the posted prices (i.e., “worst”) (Figure 1).

Figure 1. Example Choice Sets for Online Survey (top: high-information including generic Gulf oyster; bottom: low-information not including generic Gulf oyster)

The GfK Group (formerly Knowledge Networks) administered the survey instrument online to a sample of households participating in their Knowledge Panel, a nationally representative and probability-based online panel. The target population was consumers of raw oysters on the half shell. Specifically, it consisted of general population English-speaking adults (age 18+) who reside in one of the U.S. metropolitan statistical areas (MSAs; as defined by the U.S. Census) identified by the authors as being key markets for raw-oyster consumption and who responded yes to the screening question.Footnote 9

Survey design was informed by three previously conducted in-person choice experiments that included oyster tasting (conducted on December 7, 2012; February 13, 2013; and November 11, 2013) consisting of 169 total participants. The draft instrument was then reviewed by an advisory panel consisting of subject matter expertsFootnote 10 and revised according to their feedback. A penultimate version of the survey instrument was then pretested on 18 panelists on April 9–10, 2013, and the final version administered, in two waves, on April 16–May 2 and November 7–18, 2013. A total of 6,879 panelists were sampled from GfK's Knowledge Panel, and of these, 3,807 agreed to be interviewed. A total of 730 responded yes to the screening question, for a 19% incidence rate (i.e., the rate of those that eat raw oysters at least once per year), and continued to complete the main survey.

2.1. Empirical Models

It is assumed that respondent i chooses oyster alternative j if and only if the level of utility associated with alternative j is greater than the level of utility associated with the remaining alternatives ~j. We adopt a random-utility framework (see Lancaster, Reference Lancaster1966; Marschak, Reference Marschak and Arrow1960; McFadden, Reference McFadden and Zarembka1974; Thurstone, Reference Thurstone1927) wherein utility is composed of two components: observables, which in this case are the attribute levels of the given oyster alternatives, and unobservables, which are those factors known to the respondent that affect utility but unknown to the researcher. Because each respondent evaluated multiple choice sets, it is necessary to adopt an empirical model that accounts for the panel nature of the data. Furthermore, it is hypothesized that preferences over the oyster varieties are not fixed throughout the sample, but rather are heterogeneous. To account for both of these issues, we adopt a random coefficients logit model and specify oyster variety coefficients to follow a normal distribution. Thus, distinct coefficient values are estimated for each respondent (note that the panel specification constrains these coefficients to be equal across observations for the same respondent). Following Carson and Czajkowski (Reference Carson and Czajkowski2013), the coefficient on price is exponentiated, the effect of which is that the support of the price parameter is restricted to be in the positive domain and the resulting ratios of attribute parameters and the price parameter will have well-defined moments. The coefficients on the remaining attributes are fixed across the sample; these attributes include size (small, medium, or large), saltiness level (sweet, mildly salty, or salty), and production method (wild caught or cultivated).

Collecting all of the aforementioned issues discussed previously, utility may be specified empirically as ${U_{ij}} = {( {{{{\bm \beta }}_j} + {{{\bm \sigma }}_{ij}}} )^\prime }{{{\bm x}}_{ij}}$ , where ${{{\bm \beta }}_j}$ is a vector of fixed coefficients associated with alternative-specific attributes x ij , andσ ij is a random term capturing preference heterogeneity over the oyster brand/location attributes only. Price was specified as a continuous variable, whereas all others were specified as discrete indicator variables. All regression models for the online survey data were estimated using NLOGIT's “rplogit” routine with panel specification (Greene, Reference Greene2012).

3. Results

3.1. Sample Overview

A total of 730 respondents indicated that they eat raw oysters on the half shell at least once per year. Of these, 455 respondents are classified as Gulf respondents and 275 are classified as non-Gulf respondents (see footnote 9). Table 2 contains a summary of descriptive statistics for the sample, broken down by Gulf and non-Gulf respondents, and includes both oyster eaters (i.e., those who responded yes to the screening question and the small comparison sample of non–oyster eaters that responded no to the screening question). Two sets of tests of differences were conducted across samples: comparing oyster eaters with non–oyster eaters for both Gulf and non-Gulf respondents, and comparing Gulf oyster eaters with non-Gulf oyster eaters. Significant differences (based on t-tests for persons per household and income category, and proportion tests for all others, using P = 0.05 as cutoff) were found between Gulf and non-Gulf oyster eaters with regard to percent males, percent college graduates, and income category. Also, a significant difference was found between Gulf oyster eaters and non–oyster eaters with regard to percent males. A rigorous statistical comparison of the sample to the population of interest is challenging. First, the population of interest is the set of individuals that eat raw oysters, but we are not aware of any set of statistics describing the composition of this population, and it is not known if or how this population differs from the general population. Second, our sample is composed of respondents from 20 different U.S. MSAs with vastly differing demographic compositions. Thus, we have no definitive indicators of the composition of our population of interest, and our best proxy for it—the composition of the general population of our study MSAs—varies widely. The best we can do, then, is to compare our sample statistics with the range of census statistics reported across the 20 MSAs. Table 2 reports these ranges, broken down into Gulf and non-Gulf subgroups (U.S. Census Bureau, 2016). We find that our sample statistics fall within the range for persons per household, percent college graduates, and income category, but outside of the range for percent persons aged 65+, percent males, percent whites (outside the range for Gulf only), and percent high school graduates.

Table 2. Comparison of Sample Descriptive Statistics to Census Data for Study Markets

Notes: Asterisk (*) indicates significant difference between sample Gulf and non-Gulf oyster eaters. Dagger (†) indicates significant difference between sample Gulf oyster eaters and noneaters.

Source: U.S. Census Bureau (2016).

Respondents were asked to indicate the frequency of raw-oyster consumption. Forty-one percent indicated one to two times per year, 40% indicated three to four times per year, and 19% indicated more than four times per year. Responses were similar between Gulf and non-Gulf respondents. Respondents were then asked to indicate the quantity of raw oysters consumed in a typical meal. Among Gulf respondents, 44% indicated a dozen, 35% indicated a half dozen, 11% indicated more than a dozen, and 10% indicated less than a half dozen. Among non-Gulf respondents, 44% indicated a half dozen, 32% indicated a dozen, 18% indicated less than a half dozen, and 6% indicated more than a dozen.

3.2. Quality and Seafood Safety Ratings

Table 3 contains the mean oyster quality and seafood safety ratings and proportion of “Don't Know” responses among Gulf and non-Gulf respondents, respectively. Regarding oyster quality ratings, Gulf respondents tended to give the highest ratings to Apalachicola Bay, Florida; coastal Louisiana; Cape Cod, Massachusetts; and Chesapeake Bay, Virginia (based on pairwise t-tests with a P = 0.05 cutoff, the ratings of these four were statistically equivalent and, with few exceptions, significantly higher than the ratings of all others). Long Island Sound was rated lower than all other locations (and this finding was statistically significant), although Gulf respondents rated all other Atlantic locations higher than Pacific locations. Gulf respondents rated all other Atlantic locations higher than Pacific locations (although the differences were not statistically significant). Regarding the proportion of “Don't Know” responses, those of Long Island Sound and the Pacific coast locations were significantly higher than the remaining locations (based on pairwise tests of proportions), that of Gulf of Mexico was significantly higher than all others, and that of coastal Louisiana was significantly higher than all except Apalachicola Bay. Turning to seafood safety, Gulf respondents tended to rate Atlantic locations highest (Cape Code was significantly higher than all other locations, followed by Chesapeake Bay, whose mean rating was significantly higher than the remaining ones). Gulf respondents tended to rate the seafood safety of Atlantic locations highest (with the exception of Long Island Sound) and rated Pacific locations as high as or higher than Gulf locations. As with the quality ratings, Apalachicola Bay and coastal Louisiana fared better relative to other Gulf locations (the ratings of Apalachicola Bay, coastal Louisiana, and the Pacific coast locations were statistically equivalent, but significantly higher than other Gulf locations and Long Island Sound). Significant differences across proportions of “Don't Know” responses were consistent with those of oyster quality reported previously.

Table 3. Mean Ratings of Perceived Oyster Quality and Seafood Safety of Oyster-Harvest Bodies of Water

Notes: Ratings are from 1 (poor) to 10 (excellent). Proportion of “Don't Know” responses also reported.

Non-Gulf respondents tended to rate the quality of oysters from Cape Cod the highest and those from all Gulf locations (except for coastal Louisiana) the lowest. The mean quality rating of Cape Cod was significantly greater than all other locations. Chesapeake Bay, coastal Oregon, and Puget Sound were statistically equivalent, and, with a few exceptions, significantly higher than all others. Coastal Louisiana was statistically equivalent to Northern California and Long Island Sound, and rated significantly higher than all other Gulf locations. Mean ratings for Gulf of Mexico and Galveston Bay were generally significantly lower than all others. The proportion of “Don't Know” responses was significantly different for the Atlantic coast locations and coastal Louisiana compared with Apalachicola Bay and Galveston Bay, whereas those with intermediate proportions were not significantly different from each other.

Turning to seafood safety, non-Gulf respondents tended to rate Cape Cod and Puget Sound, Washington, highest, followed by other Atlantic and Pacific locations (the mean ratings for Cape Cod, Chesapeake Bay, and the Pacific coast locations were generally statistically equivalent and significantly higher than all others), with Gulf locations receiving the lowest ratings. Again, Apalachicola Bay and coastal Louisiana fared better than the other Gulf locations (the ratings of Apalachicola Bay and coastal Louisiana were statistically equivalent and significantly greater than all other Gulf coast locations). Significant differences across proportions of “Don't Know” responses were consistent with those of oyster quality reported previously.Footnote 11

3.3. Regression Results

Table 4 contains the results of the random parameters logit regression models. A two-step approach was followed to arrive at the final reported models. First, each model was estimated with all coefficients on Gulf oyster varieties (and, for the generic treatment model, the non-Gulf oyster varieties coefficient as well) specified as random, all normally distributed. Those for which no evidence of preference heterogeneity was found (i.e., the standard deviation of the random coefficient was not significantly different from zero) were respecified as fixed, and the was model reestimated.Footnote 12 Both first- and second-step model results were tested for sensitivity to the number of Halton draws used during estimation; results stabilized at about 400–500 draws. Reported results are those corresponding to 500 Halton draws.

Table 4. Random Parameters Logit Regression Estimates

Note: Asterisks (***, **, *) indicate significance at the 1%, 5%, and 10% levels, respectively.

Under the nongeneric treatments, we specified the base as containing all non–Gulf coast oyster varieties, and for the other attributes, the base levels were medium-sized, mildly salty, and cultivated oysters. The reported coefficients indicate relative preferences for all other oyster varieties and attribute levels relative to these base levels.

The first two columns of Table 4 contain the results for the nongeneric treatment over the sample of non-Gulf respondents. Initial model results indicated significant preference heterogeneity for Apalachicola Bay (Florida) and Champagne Bay (Louisiana) oyster varieties only. Thus, only these varieties were specified as having random coefficients in the final model reported. The random coefficients logit model allows for estimation of respondent-specific preference parameters. Parsing these individualized parameters into two groups, those with positive coefficients and those with negative coefficients, indicates that 97% had a negative coefficient for Apalachicola Bay oysters, whereas 3% had a positive coefficient; 86% had a negative coefficient for Champagne Bay oysters, whereas 14% had a positive coefficient. In other words, although there was significant heterogeneity across respondents with regard to their preferences for these two oyster varieties, most respondents had negative preferences for them relative to the base (non-Gulf) oyster varieties. As expected, then, the means of the coefficients for these two varieties were found to be significant and negative. For the remaining Gulf oyster varieties, the coefficients were significant and negative as well, indicating that these varieties were significantly less likely to be chosen relative to the base. Regarding the coefficients on taste, size, and production method, results indicate that small-sized and salty oysters were significantly less likely to be chosen, whereas wild-caught oysters were significantly more likely to be chosen.

The third and fourth columns of Table 4 contain the results for the nongeneric treatment over the sample of Gulf respondents. Results indicate significant preference heterogeneity for all Gulf oyster varieties except for Portersville Bay (Alabama). The breakdown of individual respondent coefficients is 65% with a positive coefficient and 35% with a negative coefficient for Apalachicola Bay; 73% positive and 27% negative for Bay St. Louis (Mississippi); 83% positive and 17% negative for Champagne Bay; 80% positive and 20% negative for Lonesome Reef (Texas); and 67% positive and 33% negative for Point aux Pins (Alabama). The mean of the coefficients on Apalachicola Bay and Point aux Pins were not statistically different from zero, and those of Bay St. Louis and Lonesome Reef are only marginally significant, leaving Champagne Bay as the only variety specified with a random coefficient as having a highly significant positive mean effect. Also, the coefficient on Portersville Bay was not statistically different from zero.

Under the generic treatment, each choice set included a fixed third alternative representing a generic (i.e., commodity) Gulf of Mexico oyster. All non–Gulf coast oyster varieties were pooled into a single category under the “non-Gulf varieties” attribute. As before, for the other attributes, the base levels were medium-sized, mildly salty, and cultivated oysters. The reported coefficients indicate relative preferences for all other oyster varieties relative to the base. For the other attributes, the reported coefficients indicate relative preferences for other branded oysters with the base attribute levels.

The last two columns of Table 4 contain the results for the generic treatment over the sample of Gulf respondents. Initial model results indicated significant preference heterogeneity for all oyster varieties except for Bay St. Louis and Portersville Bay. Thus, all varieties except these two were specified as having random coefficients in the final model reported. The breakdown of individual respondent coefficients was 72% with positive preferences (i.e., a positive coefficient) and 28% with negative preferences for Apalachicola Bay; 79% with positive preferences and 21% with negative preferences for Champagne Bay oysters; 30% with positive preferences and 70% with negative preferences for Lonesome Reef oysters; 14% with positive preferences and 86% with negative preferences for Point aux Pins oysters. The mean of the coefficient for Apalachicola Bay was found to be highly significant and positive, whereas that of Champagne Bay was found to be positive as well but only marginally significant. Although a large majority of respondent coefficients were estimated to be negative, the means of the coefficients on Lonesome Reef and Point aux Pins were not significantly different from zero. The (fixed) coefficients on Bay St. Louis and Portersville Bay were not significantly different from zero either. Regarding the coefficients on taste, size, and production method, results indicate that small-sized oysters were significantly less likely to be chosen, whereas wild-caught oysters were significantly more likely to be chosen.

3.4. Welfare Estimates

Mean WTP a premium for a given oyster alternative is defined as the ratio of the associated coefficient and the exponential of the price coefficient. Confidence intervals were calculated using the Delta method following Bliemer and Rose (Reference Bliemer and Rose2013). For reference, oyster varieties averaged $13 per half dozen in the survey, so the reported dollar values can be interpreted as premia (or discounts) added to this price.

Table 5 contains the mean maximum WTP a premium for a given oyster variety over and above the price of the base oyster varieties, as well as 95% confidence intervals around those means, based on the random coefficients regression results. The welfare estimates for attributes with significant preference heterogeneity tend to have very wide confidence intervals. Attributes whose regression coefficients were significantly different from zero are marked with an asterisk in Table 5, implying WTP estimates significantly different from zero. Those without asterisks are treated in the discussion as statistically equal to zero (i.e., fetching neither a price premium nor discount).

Table 5. Marginal Willingness-to-Pay Estimates Based on Random Coefficients Logit Results, Amounts Represent Dollar Premium per Half Dozen Oysters over and above Price of Base Oyster (for nongeneric treatments, non-Gulf varieties; for generic treatment, generic Gulf oyster)

Notes: Asterisk (*) indicates attributes whose (mean) coefficients reported in Table 3 were significantly different from zero, implying that the mean WTP estimates reported here are significantly different from zero. Dagger (†) indicates that for these attributes only, the reported value should be interpreted as the willingness to pay a premium over and above the price of an alternative oyster having the base attribute level (i.e., medium size, mildly salty, or cultivated, respectively). For the generic treatment, it is relative to an alternative branded oyster having the base attribute level. CI, confidence interval.

Under the nongeneric treatment administered to non-Gulf respondents, all Gulf varieties are estimated to require a price discount relative to base non-Gulf varieties. Champagne Bay oysters require the smallest discount, whereas the remaining Gulf varieties require substantially larger discounts. Note, however, that because of the significant preference heterogeneity found for Apalachicola Bay and Champagne Bay oysters, the confidence intervals on these varieties are very wide, whereas the confidence intervals on the remaining Gulf varieties span a few dollars on either side of the mean. Results also indicate that small oysters, as well as salty oysters, come at a price discount. Wild-caught oysters are found to fetch a price premium over the base cultivated oysters.

Among Gulf respondents, Bay St. Louis, Champagne Bay, and Lonesome Reef varieties are estimated to fetch a mean price premium relative to non-Gulf varieties, although given the significant preference heterogeneity, the confidence intervals are very wide and span both sides of zero. Results also indicate that small oysters come at a price discount. No other varieties or attributes were found to significantly affect price among Gulf respondents under the nongeneric treatment.

Under the generic treatment, administered to Gulf respondents only, Apalachicola Bay and Champagne Bay varieties are estimated to fetch a mean price premium relative to generic Gulf oysters but, given the significant preference heterogeneity, have very wide confidence intervals spanning both sides of zero. Results also indicate that small oysters come at a price discount, whereas wild-caught oysters come at a price premium.

4. Discussion and Conclusions

Here we summarize the key findings based on our sample of how consumers are likely to respond to branded Gulf oysters. Responses to questions regarding perceptions indicate that Gulf consumers tend to perceive the quality of oysters and overall safety of seafood from Apalachicola Bay and coastal Louisiana higher than that of other Gulf, Atlantic, and Pacific water bodies. Consumers in non-Gulf markets on the other hand tend to perceive the quality of oysters and safety of seafood from Gulf water bodies as worse than that of Atlantic and Pacific locations, although Apalachicola Bay and coastal Louisiana appear to rate higher than other Gulf locations. At the same time, we observed more “I don't know” responses to these questions by respondents in non-Gulf markets, indicating that consumers from these markets are more likely to have no or less well-formed opinions on Gulf oysters.

The nongeneric treatment of the choice experiment attempted to capture the potential effects of introducing branded Gulf oysters into non-Gulf markets, such as those along the Atlantic and Pacific coasts. Results indicate that consumers in non-Gulf markets are less likely to choose Gulf oysters relative to non-Gulf varieties. However, results also indicate significant preference heterogeneity for Champagne Bay (Louisiana) and Apalachicola Bay (Florida) oysters, indicating that although most non-Gulf consumers are likely to hold negative preferences for these two varieties, at least some proportion are likely to hold positive preferences for them. This finding is consistent with the perception responses discussed previously, where these two varieties rated higher than other Gulf varieties. Additionally, small-sized oysters appear less likely to be chosen and wild-caught oysters appear more likely to be chosen by consumers in non-Gulf markets.

Results for the nongeneric treatment administered to respondents in Gulf markets indicate widespread preference heterogeneity across Gulf oyster varieties, meaning that preferences for each variety are likely to vary widely from person to person. Champagne Bay oysters performed best of all Gulf varieties, although significant positive preferences were found for Bay St. Louis (Mississippi) and Lonesome Reef (Galveston Bay, Texas) varieties. As before, small-sized oysters were less preferred, and wild-caught oysters were more preferred.

The generic treatment administered to respondents in Gulf markets attempts to capture the potential of Gulf consumers to pay a premium for branded Gulf oysters over the common generic (i.e., commodity) Gulf oysters. Results indicate significant preference heterogeneity among most Gulf varieties. However, significant positive preferences were found for Apalachicola Bay (Florida) and Champagne Bay (Louisiana) varieties. Also, as before, it appears that consumers in Gulf markets are likely to have a strong distaste for small-sized oysters and a strong preference for wild-caught oysters. Comparing results for Gulf consumers between nongeneric and generic treatments, we see fairly consistent results, especially regarding strong performance of Champagne Bay, although Bay Saint Louis and Lonesome Reef performed relatively better under the nongeneric treatment, whereas Apalachicola Bay performed better under the generic treatment.

In terms of WTP a premium for branded Gulf varieties, the results from our sample indicate that consumers are likely to require a price discount relative to non-Gulf varieties, on the order of $3–$6 per half dozen. Using the mean branded variety price of $13 per half dozen used during the choice experiment, this implies that Gulf varieties might sell retail at $7–$10 per half dozen in non-Gulf markets, depending on the specific variety and other factors.Footnote 13 For example, results indicate that wild-caught oysters may fetch a premium of $2 per half dozen over farm-raised oysters independent of the brand. It is important to stress, however, the fairly wide confidence intervals on some of these estimates, indicating that the true price premia may lie far outside the levels indicated by the means here.

Among Gulf respondents, we estimate positive price premia for branded varieties on the order of $0–$8 per half dozen ($0–$3 per half dozen if the outlying Apalachicola Bay estimate is omitted). Using the mean price of $9 per half dozen for generic Gulf oysters as used in the choice experiment, there is implied a retail price of $9–$17 per half dozen ($9–$12 if Apalachicola Bay is omitted) for branded Gulf varieties.Footnote 14 The same caveat about taking into account the wide confidence intervals around these means applies here as well.

Overall, results are indicative of a universal preference for oysters originating from one's own region, as evidenced by the almost complete reversal of model coefficients and welfare estimates for Gulf varieties from non-Gulf to Gulf samples. Although interesting, this finding is not particularly surprising and not really the point of this study. Rather, the point is to understand the relative preferences of Gulf oysters, and to identify any specific Gulf varieties and/or attributes that perform relatively better (or worse) among the different set of consumers, in order to identify the most likely avenues for market development. In this regard, we find that among Gulf varieties, Champagne Bay (Louisiana) and Apalachicola Bay (Florida) stood out as relatively preferred over the other Gulf varieties tested, small-sized oysters were significantly less preferred, and wild-caught oysters were significantly more preferred. Thus, if market opportunities do exist for branded Gulf oysters, the present results indicate that the greatest promise may lie with Florida and Louisiana oysters. This finding may be at least partially explained, however, by the fact that Florida and Louisiana are more widely recognized for their seafood than the other Gulf states. Thus, our results are not meant to discount the market potential of the oysters from Alabama, Mississippi, and Texas, but rather to imply that the successful marketing of oysters from these states may require a more nuanced marketing and branding strategy. For example, Gulf oysters tend to grow larger than non-Gulf oysters, and Gulf oyster production is predominated by wild-caught oysters in contrast to non-Gulf oyster production, which is predominated by farm-raised oysters. Given that our results show strong preferences for wild-caught and relatively larger oysters, marketing strategies could highlight these two attributes. Furthermore, given that a substantial share of respondents in non-Gulf markets indicated no clear opinions on the quality and safety of Gulf waters (i.e., they responded “I don't know” to such questions), there may be some opportunity to sway currently uninformed consumer opinion.

Footnotes

This research was sponsored by the U.S. Department of Commerce's National Oceanic and Atmospheric Administration (NOAA) under NOAA Award NA10OAR4170078 and the Mississippi-Alabama Sea Grant Consortium, as well as by the U.S. Department of Agriculture National Institute of Food and Agriculture, Multistate Project W-3133 “Benefits and Costs of Natural Resources Policies Affecting Ecosystem Services on Public and Private Lands” (Hatch Project MIS-033140). We extend special thanks to Jim Gossen, Michael Herzog, Rowan Jacobsen, Chris Nelson, Jon Rowley, Robb Walsh, Steve Crockett, Steve LaHaie, and Brian Caswell for their guidance and support throughout the research process.

1 Overall, research on oyster markets appears to be limited. Beside the studies cited previously that focus on consumer preferences, Dedah, Keithly, and Kazmierczak (Reference Dedah, Keithly and Kazmierczak2011); Lipton (Reference Lipton2008); and Keithly and Diop (Reference Keithly and Diop2001) analyze various shocks to oyster markets using market data.

2 We did not use any of the typical strategies for mitigating hypothetical bias, such as a cheap talk script or a reminder about budget, so we readily acknowledge the potential for hypothetical bias.

3 It turned out that very few respondents chose the opt-out alternative, so for the econometric analysis, we dropped the observations of the few that did this and modeled only the three oyster alternatives.

4 To generate an S-efficient design, it is necessary to assume prior parameter estimates. The priors used in the present study were based on the results of a conditional logit regression model estimated over choice data collected during pretesting of the survey.

5 One of the major advantages of branded oysters over the commodity oysters typically marketed in the Gulf region is their uniformity in size, shape, and/or taste. Thus, it was necessary that we highlight this distinction between the generic and the branded oysters.

6 One of the major advantages of branded oysters over the commodity oysters typically marketed in the Gulf region is their uniformity in size, shape, and/or taste. Thus, it was necessary that we highlight this distinction between the generic and the branded oysters.

7 Exceptions to this were to reflect the true constraints on the characteristics of particular oyster varieties: the production method of Point aux Pins was fixed at “cultivated,” and the saltiness level of Hood Canal oysters was constrained to be either “mildly salty” or “salty.”

8 Let A and B represent a pair of alternatives in a choice set. The second-best case operates under the assumption that the probability of A being chosen as “worst” is equal to the probability of B being chosen as “best.”

9 Non-Gulf respondents were sampled from the following MSAs: Baltimore–Towson, MD; Boston–Cambridge–Quincy, MA-NH; Charleston–North Charleston, SC; Chicago–Naperville–Joliet, IL-IN-WI; Las Vegas–Paradise, NV; New York–Newark–Edison, NY-NJ-PA; Portland–South Portland, ME; St. Louis, MO-IL; San Francisco–Oakland–Fremont, CA; Seattle–Tacoma–Bellevue, WA; and Washington–Arlington–Alexandria, DC-VA. Gulf respondents were sampled from Atlanta–Sandy Springs–Marietta, GA; Baton Rouge, LA; Houston–Baytown–Sugar Land, TX; Jacksonville, FL; Miami–Ft. Lauderdale–Miami Beach, FL; Mobile, AL; New Orleans–Metairie–Kenner, LA; Tallahassee, FL; and Tampa–St. Petersburg–Clearwater, FL.

10 Our advisory panel included Jim Gossen (distributor, Louisiana Foods), Michael Herzog (director of food and beverage, Grand Hotel Marriott Resort, Point Clear, AL), Rowan Jacobsen (author of A Geography of Oysters: The Connoisseur's Guide to Oyster Eating in North America), Chris Nelson (oyster processor and distributor, Bon Secour Fisheries), Jon Rowley (noted food critic and a leader of the “oyster revival”), and Robb Walsh (food critic and author of Sex, Death & Oysters).

11 We wish to speak briefly about two issues specific to Gulf oysters that may have influenced responses. These are any perceived effects regarding of the 2010 Deepwater Horizon oil spill and that of Vibrio vulnificus. Although we did not elicit any responses specific to these two issues, we did include an open-ended question immediately following the choice experiment, food safety ratings, and quality ratings questions that asked, “While answering the previous questions, did you have any particular concerns about any of the oysters that had a big influence on your choices?” Although most respondents typically opt out of leaving comments (in the present survey, 46% of all respondents left it completely blank and another 14% said some variant of no), we conducted a keyword search for the following terms: “oil,” “BP,” “spill,” “Deepwater,” “Vibrio,” and “bacteria.” One of the oil-related terms appeared 40 times (23 times among Gulf respondents and 17 times among non-Gulf respondents), and a Vibrio-related term appeared 5 times (4 times among Gulf respondents and once among non-Gulf respondents). It is an open question as to whether the frequency of oil-related comments is of concern. Forty is just over 5% of the total number of respondents, but 14% when limited to those respondents who left a comment of some kind.

12 Respecifying the model as described had no substantial effects on other model results and yielded more efficient welfare estimates (i.e., smaller variances) for those variables respecified.

13 As of September 2, 2015, branded oyster varieties were selling at the following prices per half dozen at the following Atlantic and Pacific coast restaurants: Island Creek Oyster Bar (Boston), $15–$21; Grand Central Oyster Bar (New York), $12.90–$22.50; Shaw's Crab House (Chicago), $18; and Elliott's Oyster House (Seattle), $16.50–$21.

14 As of September 2, 2015, (generic) Gulf oysters were selling at the following prices per half dozen at the following Gulf coast restaurants: Liberty Kitchen & Oyster Bar (Houston), $10.25; Felix's (New Orleans), $8.75; Wintzell's Oyster House (Mobile), $9.99; Atlas Oyster House (Pensacola), $6.95; and The Oyster Bar (Tampa Bay), $9.

References

Bishop, M.J., and Peterson, C.H.. “Consumer Rating of the Suminoe Oyster, Crassostrea Ariakensis, during Home Cooking.” Journal of Shellfish Research 24,2(2005):497502.Google Scholar
Bliemer, M.C.J., and Rose, J.M.. “Confidence Intervals of Willingness-to-Pay for Random Coefficient Logit Models.” Transportation Research Part B: Methodological 58(December 2013):199214.Google Scholar
Bruner, D., Huth, W., McEvoy, D.M., and Morgan, O.A.. “Accounting for Tastes: A Valuation of Risk Reduction in Raw Seafood Consumption.” Department of Economics Working Paper No. 11-09, Boone, NC: Department of Economics, Appalachian State University, 2011.Google Scholar
Carson, R.T., and Czajkowski, M.. “A New Baseline Model for Estimating Willingness to Pay from Discrete Choice Models.” Paper presented at the 2013 International Choice Modelling Conference, Sydney, Australia, July 3–5, 2013. Internet site: http://www.icmconference.org.uk/index.php/icmc/ICMC2013/paper/view/730 (Accessed December 9, 2014).Google Scholar
Chapman, R.G., and Staelin, R.. “Exploiting Rank Ordered Choice Set Data within the Stochastic Utility Model.” Journal of Marketing Research 19(August 1982):288301.Google Scholar
ChoiceMetrics. Ngene 1.1.1 User Manual & Reference Guide. Sydney, Australia: ChoiceMetrics, 2012.Google Scholar
Dedah, C., Keithly, W.R. Jr., and Kazmierczak, R.F. Jr.An Analysis of US Oyster Demand and the Influence of Labeling Requirements.” Marine Resource Economics 26,1(2011): 1733.Google Scholar
Flynn, T.N., Louviere, J.J., Peters, T.J., and Coast, J.. “Best–Worst Scaling: What It Can Do for Health Care Research and How to Do It.” Journal of Health Economics 26,1(2007):171–89.Google Scholar
Flynn, T.N., and Marley, A.A.J.. “Best-Worst Scaling: Theory and Methods.” Handbook of Choice Modelling. Hess, S. and Daly, A., eds. Cheltenham, UK: Edward Elgar, 2014, pp. 178201.Google Scholar
Grabowski, J.H., Powers, S.P., Peterson, C.H., Powers, M.J., and Green, D.P.. “Consumer Ratings of Non-Native (Crassostrea gigas and Crassostrea ariakensis) vs. Native (Crassostrea virginica) Oysters.” Journal of Shellfish Research 22,1(2003):2130.Google Scholar
Greene, W.H. Reference Guide: NLOGIT Version 5.0. Plainview, NY: Econometric Software Inc., 2012.Google Scholar
House, L., Hanson, T.R., and Sureshwaran, S.. “U.S. Consumers: Examining the Decision to Consume Oysters and the Decision of How Frequently to Consume Oysters.” Journal of Shellfish Research 22,1(2003):5159.Google Scholar
Jacobsen, R. “The Oyster Guide.” 2016. Internet site: http://www.oysterguide.com/maps/gulf-coast (Accessed February 17, 2011).Google Scholar
Kecinski, M., Messer, K.D., and Peo, A.J.. Consumer Preferences for the Provision of Water Quality Services by Oysters. Newark: Department of Applied Economics and Statistics (APEC), College of Agriculture and Natural Resources, University of Delaware, APEC Research Report RR16-02, March 2016.Google Scholar
Keithly, W.R., and Diop, H.. “The Demand for Eastern Oysters, Crassostrea virginica, from the Gulf of Mexico in the Presence of Vibrio vulnificus .” Marine Fisheries Review 63,1(2001):4753.Google Scholar
Kow, F., Yu, L., FitzGerald, D., and Grewal, D.. “Understanding the Factors Related to the Consumers’ Choices of Oysters in Australia: An Empirical Study.” Journal of Food Service 19,4(2008):245–53.Google Scholar
Lancaster, K.J. “ A New Approach to Consumer Theory.” Journal of Political Economy 74,2(1966):132–57.Google Scholar
Lin, C.-T.J., and Milon, J.W.. “Attitudes and Safety Perception in a Double-Hurdle Model of Shellfish Consumption.” American Journal of Agricultural Economics 75,3(1993):724–29.Google Scholar
Lipton, D.Economic Benefits of a Restored Oyster Fishery in Chesapeake Bay.” Journal of Shellfish Research 27,3(2008):619–23.Google Scholar
Louviere, J.J., Flynn, T.N., and Marley, A.A.J.. Best-Worst Scaling: Theory, Methods and Applications. Cambridge: Cambridge University Press, 2015.Google Scholar
Louviere, J.J., Hensher, D.A., and Swait, J.. Stated choice methods: analysis and application. Cambridge, UK: Cambridge University Press, 2000.Google Scholar
Manalo, A.B., and Gempesaw, C.M. , II.Preferences for Oyster Attributes by Consumers in the U.S. Northeast.” Journal of Food Distribution Research 28,2(1997):5563.Google Scholar
Marley, A.A.J., and Louviere, J.J.. “Some Probabilistic Models of Best, Worst, and Best–Worst Choices.” Journal of Mathematical Psychology 49,6(2005):464–80.Google Scholar
Marschak, J.Binary Choice Constraints on Random Utility Indications.” Stanford Symposium on Mathematical Methods in the Social Sciences. Arrow, K., ed. Stanford, CA: Stanford University Press, 1960, pp. 312–29.Google Scholar
Martínez-Cordero, F.J., Fong, Q.S.W., and Haws, M.C.. “Marketing Extension and Outreach in Sinaloa, Mexico: A Preliminary Analysis of Preferences for Oysters.” Marine Resource Economics 24,1(2009):8995.Google Scholar
McFadden, D.Conditional Logit Analysis of Qualitative Choice Behavior.” Frontiers in Econometrics. Zarembka, P., ed. New York: Academic Press, 1974, pp. 105–42.Google Scholar
McFadden, D.The Choice Theory Approach to Market Research.” Marketing Science 5,4(1986):275–97.Google Scholar
McFadden, D., and Train, K.. “Mixed MNL Models for Discrete Response.” Journal of Applied Econometrics 15,5(2000):447–70.3.0.CO;2-1>CrossRefGoogle Scholar
Morgan, O.A., Martin, G.S., and Huth, W.L.. “Oyster Demand Adjustments to Counter-Information and Source Treatments in Response to Vibrio vulnificus .” Journal of Agricultural and Applied Economics 41,3(2009):683–96.Google Scholar
Morgan, O.A., Whitehead, J.C., and Huth, W.L.. “Accounting for Heterogeneity in Behavioural Responses to Health-Risk Information Treatments.” Journal of Environmental Economics and Policy 5,3(2016):283–97.Google Scholar
Morgan, O.A., Whitehead, J.C., Huth, W.L., Martin, G.S., and Sjolander, R.. “A Split-Sample Revealed and Stated Preference Demand Model to Examine Homogeneous Subgroup Consumer Behavior Responses to Information and Food Safety Technology Treatments.” Environmental and Resource Economics 54,4(2013):593611.Google Scholar
National Marine Fisheries Service (NMFS). “Annual Commercial Landings Statistics: Eastern Oyster, 2013” [online database]. NMFS, Fisheries Statistics and Economics Division, 2014. Internet site: http://www.st.nmfs.noaa.gov/commercial-fisheries/commercial-landings/annual-landings/index (Accessed August 12, 2015).Google Scholar
Nell, J.A., O'Riordan, P.J., and Ogburn, D.M.. “Consumer Evaluation of Diploid and Triploid Pacific Oysters Subjected to High Pressure Treatment.” Journal of Shellfish Research 25,3(2006):1101–4.Google Scholar
Petrolia, D.R.Risk Preferences, Risk Perceptions, and Risky Food.” Food Policy 64(2016):3748.Google Scholar
Potoglou, D., Burge, P., Flynn, T., Netten, A., Malley, J., Forder, J., and Brazier, J.E.. “Best–Worst Scaling vs. Discrete Choice Experiments: An Empirical Comparison Using Social Care Data.” Social Science & Medicine 72,10(2011):1717–27.Google Scholar
Rigby, D., Burton, M., and Lusk, J.L.. “Journals, Preferences, and Publishing in Agricultural and Environmental Economics.” American Journal of Agricultural Economics 97,2(2015):490509.Google Scholar
Scarpa, R., Notaro, S., Louviere, J., and Raffaelli, R.. “Exploring Scale Effects of Best/Worst Rank Ordered Choice Data to Estimate Benefits of Tourism in Alpine Grazing Commons.” American Journal of Agricultural Economics 93,3(2011):813–28.Google Scholar
Thurstone, L.L.A Law of Comparative Judgement.” Psychological Review 34,4(1927):273–86.Google Scholar
U.S. Census Bureau. “QuickFacts” [various cities]. Internet site: http://www.census.gov/quickfacts/table/PST045215/00 (December 1, 2016).Google Scholar
Whitehead, J.C., Morgan, O.A., Huth, W.L., Martin, G.S., and Sjolander, R.. “Willingness-to-Pay for Oyster Consumption Mortality Risk Reductions.” Department of Economics Working Paper No. 12-07, Boone, NC: Department of Economics, Appalachian State University, 2012.Google Scholar
Figure 0

Table 1. Attributes and Their Levels Used in the Online Survey Experimental Design (the “low-information” treatment included only the oyster variety and price per half dozen, whereas the “high-information” treatment included all of the attributes listed)

Figure 1

Figure 1. Example Choice Sets for Online Survey (top: high-information including generic Gulf oyster; bottom: low-information not including generic Gulf oyster)

Figure 2

Table 2. Comparison of Sample Descriptive Statistics to Census Data for Study Markets

Figure 3

Table 3. Mean Ratings of Perceived Oyster Quality and Seafood Safety of Oyster-Harvest Bodies of Water

Figure 4

Table 4. Random Parameters Logit Regression Estimates

Figure 5

Table 5. Marginal Willingness-to-Pay Estimates Based on Random Coefficients Logit Results, Amounts Represent Dollar Premium per Half Dozen Oysters over and above Price of Base Oyster (for nongeneric treatments, non-Gulf varieties; for generic treatment, generic Gulf oyster)