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been widely applied to estimate non-market benefits of improved 
            
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ecological status, assuming that respondents declare their true 
            
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preferences that are stable over time. However, evidence on preference 
            
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stability is mixed in the literature. The objective of this paper is 
            
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to study preference stability towards water bodies improvement. As the 
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to study preference stability towards water bodies improvement. As the 
            
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WFD implementation has been delayed and have proven to be a greater 
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WFD implementation has been delayed and have proven to be a greater 
            
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challenge than expected, we focus on the effects of policy 
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challenge than expected, we focus on the effects of policy 
            
103
implementation failures on preference stability. We analyse two 
113
implementation failures on preference stability. We analyse two 
            
104
contingent valuation surveys to assess environmental values for the 
114
contingent valuation surveys to assess environmental values for the 
            
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case of the Mar Menor (SE Spain) in years 2010 and 2017. We find 
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case of the Mar Menor (SE Spain) in years 2010 and 2017. We find 
            
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higher protest response rate, changing indirect utility functions 
            
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towards good ecological status and decreased WTPs in 2017. It 
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towards good ecological status and decreased WTPs in 2017. It 
            
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indicates that public valuation might fail to adhere to rational 
            
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economic premises when public authorities fail to reach environmental 
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economic premises when public authorities fail to reach environmental 
            
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objectives and/ or PoMs are not correctly implemented. Decision making 
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objectives and/ or PoMs are not correctly implemented. Decision making 
            
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based on stated preferences should carefully consider potential biases 
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based on stated preferences should carefully consider potential biases 
            
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emerging from management performance.",
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    "es": "The Water Framework Directive (WFD) establishes that 
            
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assessed to determine whether the benefits obtained from the good 
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assessed to determine whether the benefits obtained from the good 
            
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ecological status outweigh the costs. Stated preference methods have 
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ecological status outweigh the costs. Stated preference methods have 
            
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been widely applied to estimate non-market benefits of improved 
            
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ecological status, assuming that respondents declare their true 
            
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preferences that are stable over time. However, evidence on preference 
            
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stability is mixed in the literature. The objective of this paper is 
            
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to study preference stability towards water bodies improvement. As the 
132
to study preference stability towards water bodies improvement. As the 
            
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WFD implementation has been delayed and have proven to be a greater 
133
WFD implementation has been delayed and have proven to be a greater 
            
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challenge than expected, we focus on the effects of policy 
134
challenge than expected, we focus on the effects of policy 
            
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implementation failures on preference stability. We analyse two 
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implementation failures on preference stability. We analyse two 
            
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contingent valuation surveys to assess environmental values for the 
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contingent valuation surveys to assess environmental values for the 
            
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case of the Mar Menor (SE Spain) in years 2010 and 2017. We find 
137
case of the Mar Menor (SE Spain) in years 2010 and 2017. We find 
            
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higher protest response rate, changing indirect utility functions 
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higher protest response rate, changing indirect utility functions 
            
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towards good ecological status and decreased WTPs in 2017. It 
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towards good ecological status and decreased WTPs in 2017. It 
            
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indicates that public valuation might fail to adhere to rational 
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indicates that public valuation might fail to adhere to rational 
            
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economic premises when public authorities fail to reach environmental 
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economic premises when public authorities fail to reach environmental 
            
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