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Consumer misperception of eco-labels, green market structure and welfare

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Abstract

Eco-labels are essential for informing consumers about products’ environmental characteristics. However, the many different labels consumers encounter can be confusing, which makes assessing environmental quality associated with each label difficult. How does consumer misperception of competing eco-labels affect market structure and welfare? This article provides theoretical insight into this issue by using a double-differentiation model in which three products compete: an unlabeled product and two distinctly eco-labeled products, one with a medium and one with a high level of environmental quality. The study investigates the effects of consumers’ imperfect information when they perceive all eco-labels as a sign of the same high environmental quality and consider each label as a unique product. This misperception can weaken the firm that provides the greenest product, though paradoxically this situation is not always detrimental to social welfare. However, depending on the certifying organizations, consumer misperception can induce firms to use a greenwashing strategy and encourage nongovernmental organizations and regulators to introduce less stringent standards.

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Notes

  1. European Commission’s definition of ‘eco-label’ (see http://ec.europa.eu/environment/ecolabel/index_en.htm (accessed 2014/05/09).

  2. See the Environmental Protection Agency web page on ‘Greener Products’, http://www.epa.gov/greenerproducts/index.html (accessed 2016/12/15).

  3. www.ecolabelindex.com (accessed 2015/11/17).

  4. Studies most often adopt a vertical (Arora and Gangopadhyay 1995; Amacher et al. 2004; Ben Youssef and Lahmandi-Ayed 2008; Bottega and de Freitas 2009; Bottega et al. 2009) or horizontal (Eriksson 2004; Boyer et al. 2006; Clemenz 2010) differentiation model framework. They emphasize the conditions under which eco-labeling may be an efficient policy, depending on cost structure and abatement method of firms and on environmental consciousness, information and altruism of consumers.

  5. Note that a single eco-label may also be imperfect, as when the label imperfectly informs consumers on the environmental quality of the high-quality product. Bonroy and Constantatos (2008) show that when consumers have heterogeneous beliefs that a firm provides a high-quality product (and that its competitor provides a low-quality product), introducing a perfect label enhances welfare; however, they note that sometimes such a label should be made mandatory and an imperfect label may be damaging.

  6. Baksi et al. (2016) investigate a related issue in a vertical differentiation model with three competing products. However, rather than assuming consumer misperception of eco-labels, they assume that consumers overestimate intermediate environmental quality and perfectly assess the low and high quality. Moreover, they assume that qualities only result from firm strategies and that firms know that consumers overestimate the intermediate-quality product. Finally, they assume that environmental externalities do not affect social welfare. In such a specific framework, Baksi et al. show that overestimation benefits the intermediate-quality firm and enhances social welfare when firms compete on price but harms social welfare when they compete on quantity.

  7. Brécard’s (2014) model cannot be analytically solved, except in the specific case of uniform standard, and does not allow comparison between perfect and imperfect information cases.

  8. In Daughety and Reinganum’s (2008) model, product quality is private information of each firm and therefore is unknown to both the consumer and the firm’s competitors. However, consumers know that the quality may be either high or low.

  9. In Ben Youssef and Abderrazak’s (2009) model, the prices do reveal information on environmental quality because consumers face two eco-labels and know that the eco-labeled products are vertically differentiated. This departs from the assumptions in the current study that consumers do not know differences in environmental quality of (imperfect) eco-labeled products and that these products are horizontally differentiated.

  10. In particular, imperfect disclosure can come from ‘noisy certification’, due to the limited reliability of product testing (De and Nabar 1991; Mason and Sterbenz 1994; Mason 2011), or from the incentive of certification intermediaries with market power to manipulate information to capture the informational surplus in the market (Lizzeri 1999).

  11. The current research’s assumptions differ from those of Brécard (2014), who considers heterogeneous WTP for environmental quality and assumes no interplay between WTP for the perceived environmental quality and WTP for a specific eco-label.

  12. Assuming that \(\theta \) is identical for all consumers allows analytical resolution of the game, which would not be achievable with a more conventional assumption of uniform distribution of parameters \(\theta \) as in Brécard (2014).

  13. Assume that r is large enough to ensure that the market is covered.

  14. This assumption differs from Brécard (2014), who assumes additivity of WTP for environmental quality and WTP for a given label. It is close to Degryse and Irmen’s (2001) assumption, which states that the indirect utility depends on the product quality not only through the quality level itself but also through the transportation cost towards the product, proportional to the quality level: \(u_i \left( \lambda \right) =r+q_i -\left( {1+\delta q_i } \right) \lambda -p_i \), with \(\delta \) the interaction parameter.

  15. The main results are not affected by this assumption: The brown product would be favored by undervaluation of eco-labeled products when \(\tilde{q}_L \in [q_{NL} ,q_{LM} ]\) and penalized by overvaluation of eco-labeled products when \(\tilde{q}_L \in [q_{LH} ,\bar{{q}}]\). In both cases, the blue product would benefit from a competitive advantage over the green product, as in the case in which \(\tilde{q}_L \in \left[ {q_{LM} ,q_{LH} } \right] \).

  16. Moreover, firms choosing the medium and the high environmental quality always want to disclose quality though an eco-label, according to the ‘unraveling result’ (Dranove and Jin 2010).

  17. “ Appendix 1” details the marginal WTP \(\theta _{NL} \), \(\theta _{LM} \) and \(\theta _{LH} \). Assuming a quadratic production-cost function \(c\left( {q_i } \right) ={q_i^2 }/2\), it is straightforward to show that \(\theta _{LM} \le \theta _{LH} \le \theta _{NL} \).

  18. “Appendix 1” defines the marginal WTP \(\tilde{\theta }_{NL} \), \(\tilde{\theta }_{LM} \) and \(\tilde{\theta }_{LH} \). Assuming a quadratic production cost function\(c\left( {q_i } \right) ={q_i^2 }/2\), the model shows that \(\tilde{\theta }_{LM} \le \tilde{\theta }_{LH} \le \tilde{\theta }_{NL} \), \(\tilde{\theta }_{NL} \ge \theta _{NL} \), \(\tilde{\theta }_{LM} \le \theta _{LM} \) and \(\tilde{\theta }_{LH} \ge \theta _{LH} \) for all values of \(q_{LM} \), \(q_{LH} \) and \(\tilde{q}_L \).

  19. “Appendix 2” provides demonstrations.

  20. See footnotes 22, 23 and 28 for some results of welfare analysis with a populist regulator.

  21. In Fig. 5, \(\theta =1\), \(\underline{q}=1\), \(q_{LM} =1.7\), \(q_{LH} =2\), fixed costs are equal to 0, and a quadratic cost function is assumed. Because the large number of involved parameters prevents an analytical demonstration of the effects of perceived quality \(\tilde{q}_L\) on consumer surplus and profits, it was necessary to perform numerical simulations with a large set of relevant values of parameters to check the robustness of the results.

  22. Variations in perceived consumer surplus are greater than changes in the real consumer surplus because consumers directly benefit from higher perceived quality of eco-labeled products.

  23. However, the global real surplus is always damaged by imperfect information when the differentiation between the brown and the blue products is too low (for a given quality of the green product). Conversely, the global perceived consumer surplus is favored by imperfect information when consumers attach a high environmental quality to both labeled products because increasing perceived quality directly improves perceived surplus.

  24. Unfortunately, no analytical solution exists for any case using first-order conditions. With regard to a numerical solution, the system of equations has many candidates for the equilibrium, but only one solution fulfills the existence condition for triopoly, namely, \(q_{Lj} \le 4\theta \) (j = H, M), the second-order conditions and the non-deviation conditions. Numerical simulations using various suitable values of \(\theta \),\(\underline{q}\) and \(\delta \) are used to test the robustness of the results. First-order conditions and simulations are available upon request from the author.

  25. Replacing \(q_{LM}\) and \(q_{LH}\) by \(q_L \) in one of the first-order conditions, the symmetric standard can be defined as \(q_L^*=\frac{1}{4}\left( {3\theta +\sqrt{9\theta ^{2}+8\theta -4}} \right) \).

  26. The greater the \(\delta \), the more stringent the public label, but \(q_{LH}^{pc} \) is lower than \(q_{LH}^{nc} \) of the NGO regardless of the value of \(\delta \),

  27. Brécard (2014) assumes that \(q_L =\mu q_{LH} +\left( {1-\mu } \right) q_{LM} \), with \(\mu \in \left[ {0,1} \right] \). The term \(\mu \) \((1 - \mu )\) can be interpreted as the degree of influence of the green (blue) firm on consumers’ beliefs. Setting \(\mu \) to 1/2 avoids the situation in which a firm benefits more than its rival from the way consumers form their beliefs.

  28. In the case of a populist regulator, accounting for perceived surplus of consumers, the standard would be equal to \(\overline{q} \), though such a standard is likely to trigger the disappearance of the green product (for \(q_{LH}\) higher than 2.55). Such a puzzling result arises from the positive effect of \(q_{LH}\) on perceived quality of the blue product, which artificially increases perceived surplus of consumers.

  29. http://www.pinocchio-awards.org/ (accessed 2015/12/16).

  30. In the line with Gabszewicz and Thisse (1980), only a limited number of eco-labels can coexist in a differentiated industry because of the vertical aspect of production differentiation.

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Correspondence to Dorothée Brécard.

Additional information

I am grateful to the audience at FAERE meetings 2014 and 2015 and EAERE meeting 2015 and two anonymous referees for helpful comments. The usual disclaimer applies.

Appendices

Appendix 1: Price equilibrium

1.1 Case of perfect eco-labels

From Eqs. (11) to (13) and definitions of demand functions, the following market shares of the three firms are deduced:

$$\begin{aligned} d_{LM}^*= & {} \frac{c\left( {\underline{q}} \right) -\theta \underline{q}}{3\theta q_{LM} }+\frac{c\left( {q_{LH} } \right) q_{LM} +\left( {2\theta q_{LM} -c\left( {q_{LM} } \right) } \right) \left( {2q_{LH} +3q_{LM} } \right) }{6\theta q_{LM} \left( {q_{LH} +q_{LM} } \right) }\qquad \quad \end{aligned}$$
(17)
$$\begin{aligned} d_{LH}^*= & {} \frac{c\left( {\underline{q}} \right) -\theta \underline{q}}{3\theta q_{LH} }+\frac{c\left( {q_{LM} } \right) q_{LH} +\left( {2\theta q_{LH} -c\left( {q_{LH} } \right) } \right) \left( {3q_{LH} +2q_{LM} } \right) }{6\theta q_{LH} \left( {q_{LM} +q_{LH} } \right) },\qquad \quad \end{aligned}$$
(18)

and \(d_{NL}^*=1-d_{LM}^*-d_{LH}^*\). Profits are \(\uppi _{NL}^*=\frac{\theta q_{LM} q_{LH} }{q_{LM} +q_{LH} }d_{NL}^{*\,{2}}\), \(\uppi _{LM}^*=\theta q_{LM} d_{LM}^{*\,{2}}-k_{LM} \) and \(\uppi _{LH}^*=\theta q_{LH} d_{LH}^{*\,{2}}-k_{LH} \).

The three conditions for triopoly, \(d_{NL}^*\ge 0\), \(d_{LM}^*\ge 0\) and \(d_{LH}^*\ge 0\), can be translated into the conditions \(\theta \le \theta _{NL} \), \(\theta \ge \theta _{LM} \) and \(\theta \ge \theta _{LH} \), where the thresholds are defined as follows:

$$\begin{aligned} \theta _{NL}\equiv & {} \frac{c\left( {q_{LH} } \right) q_{LM} +c\left( {q_{LM} } \right) q_{LH} -\left( {q_{LM} +q_{LH} } \right) c\left( {\underline{q}} \right) }{2q_{LM} q_{LH} -\left( {q_{LM} +q_{LH} } \right) \underline{q}} \end{aligned}$$
(19)
$$\begin{aligned} \theta _{LM}\equiv & {} \frac{-c\left( {q_{LH} } \right) q_{LM} +c\left( {q_{LM} } \right) \left( {2q_{LH} +3q_{LM} } \right) -2\left( {q_{LM} +q_{LH} } \right) c\left( {\underline{q}} \right) }{6q_{LM}^2 +4q_{LM} q_{LH} -2\left( {q_{LM} +q_{LH} } \right) \underline{q}} \qquad \qquad \end{aligned}$$
(20)
$$\begin{aligned} \theta _{LH}\equiv & {} \frac{c\left( {q_{LH} } \right) \left( {3q_{LH} +2q_{LM} } \right) -c\left( {q_{LM} } \right) q_{LH} -2\left( {q_{LM} +q_{LH} } \right) c\left( {\underline{q}} \right) }{6q_{LH}^2 +4q_{LM} q_{LH} -2\left( {q_{LM} +q_{LH} } \right) \underline{q}}.\qquad \qquad \end{aligned}$$
(21)

1.2 Case of imperfect eco-labels

From Eqs. (14) to (16) and definitions of demand functions, the following market shares of the three firms can be deduced:

$$\begin{aligned} \tilde{d}_{NL}^*= & {} \frac{c\left( {q_{LM} } \right) +c\left( {q_{LH} } \right) -2c\left( {\underline{q}} \right) -2\theta \left( {q_L -\underline{q}} \right) }{12\theta q_L } \end{aligned}$$
(22)
$$\begin{aligned} \tilde{d}_{LM}^*= & {} \frac{4c\left( {\underline{q}} \right) -5c\left( {q_{LM} } \right) +c\left( {q_{LH} } \right) +2\theta \left( {5q_L -4\underline{q}} \right) }{12\theta q_L } \end{aligned}$$
(23)
$$\begin{aligned} \tilde{d}_{LH}^*= & {} \frac{4c\left( {\underline{q}} \right) +c\left( {q_{LM} } \right) -5c\left( {q_{LH} } \right) +2\theta \left( {5q_L -4\underline{q}} \right) }{12\theta q_L }. \end{aligned}$$
(24)

The existence conditions for triopoly are characterized by marginal WTP \(\tilde{\theta }_{NL} \), \(\tilde{\theta }_{LM} \) and \(\tilde{\theta }_{LH} \) such as \(\tilde{d}_{NL}^*\ge 0\) when \(\theta \le \tilde{\theta }_{NL} \), \(\tilde{d}_{LM}^*\ge 0\) when \(\theta \ge \tilde{\theta }_{LM} \) and \(\tilde{d}_{LH}^*\ge 0\) when \(\theta \ge \tilde{\theta }_{LH} \):

$$\begin{aligned} \tilde{\theta }_{NL}\equiv & {} \frac{c\left( {q_{LH} } \right) +c\left( {q_{LM} } \right) -2c\left( {\underline{q}} \right) }{2\left( {q_L -\underline{q}} \right) } \end{aligned}$$
(25)
$$\begin{aligned} \tilde{\theta }_{LM}\equiv & {} \frac{-c\left( {q_{LH} } \right) +5c\left( {q_{LM} } \right) -4c\left( {\underline{q}} \right) }{10q_L -4\underline{q}} \end{aligned}$$
(26)
$$\begin{aligned} \tilde{\theta }_{LH}\equiv & {} \frac{5c\left( {q_{LH} } \right) -c\left( {q_{LM} } \right) -4c\left( {\underline{q}} \right) }{10q_L -4\underline{q}}. \end{aligned}$$
(27)

Appendix 2: Effects of consumer misperception on market equilibrium

1.1 The green product

From Eq. (16), it is evident that price \(\tilde{p}_{LH}^*\) is an increasing function of \(q_{L}\). Thus, to prove that \(p_{LH}^*\ge \tilde{p}_{LH}^*\), it is sufficient to demonstrate that this inequality is true for \(q_L =q_{LH} \). Because \(\left. {p_{LH}^*-\tilde{p}_{LH}^*} \right| _{q_L =q_{LH} } =\frac{\left( {q_{LH} -q_{LM} } \right) \left( {2\theta q_{LH} -c\left( {q_{LH} } \right) +c\left( {q_{LM} } \right) } \right) }{12\left( {q_{LM} +q_{LH} } \right) }\) and \(c\left( {q_{LH} } \right) \le 2\theta q_{LH} \), \(p_{LH}^*\ge \tilde{p}_{LH}^*\) is always fulfilled.

Similarly, it is evident that \(\tilde{d}_{LH}^*\) is an increasing function of \(q_{L}\) and that \(d_{LH}^*\ge \tilde{d}_{LH}^*\) for \(q_L =q_{LH} \), as \(d_{LH}^*-\left. {\tilde{d}_{LH}^*} \right| _{q_L =q_{LH} } =\frac{\left( {q_{LH} -q_{LM} } \right) \left( {2\theta q_{LH} -c\left( {q_{LH} } \right) +c\left( {q_{LM} } \right) } \right) }{12\theta q_{LH} \left( {q_{LH} +q_{LM} } \right) }\ge 0\), and thus for all \(q_L \le q_{LH} \). Finally, because consumer misperception decreases both the price and the market share of the green product, it also lowers the profit of the green firm.

1.2 The blue product

From Eq. (15), it follows that \(\tilde{p}_{LM}^*\) declines with \(q_{L}\). Moreover \(p_{LM}^*\le \tilde{p}_{LM}^*\) when \(q_L =q_{LM} \) because \(\left. {p_{LM}^*-\tilde{p}_{LM}^*} \right| _{q_L =q_{LM} } =\frac{-\left( {q_{LH} -q_{LM} } \right) \left( {c\left( {q_{LH} } \right) -c\left( {q_{LM} } \right) +2\theta q_{LM} } \right) }{12\left( {q_{LM} +q_{LH} } \right) }\le 0\). Consequently, \(p_{LM}^*\le \tilde{p}_{LM}^*\) for all \(q_L \ge q_{LM} \).

From Eq. (23), \(\frac{\partial \tilde{d}_{LM}^*}{\partial q_L }=\frac{5}{6q_L }-\frac{\tilde{d}_{LM} }{q_L }\), which is positive when the blue product captures less than five sixths of the market. Furthermore, \(d_{LM}^*\le \tilde{d}_{LM}^*\) for \(q_L =q_{LM} \), as \(d_{LM}^*-\left. {\tilde{d}_{LM}^*} \right| _{q_L =q_{LM} } =\frac{-\left( {q_{LH} -q_{LM} } \right) \left( {2\theta q_{LM} +c\left( {q_{LH} } \right) -c\left( {q_{LM} } \right) } \right) }{12\theta q_{LM} \left( {q_{LH} +q_{LM} } \right) }\le 0\), and thus for all \(q_L \ge q_{LM} \). In summary, the profit of the firm producing the blue product is increased by consumer misperception about the perfect information case.

1.2.1 The brown product

From Eq. (14), it appears that \(\tilde{p}_{NL}^*\) is a decreasing function of \(q_{L}\). In addition,

$$\begin{aligned}&p_{NL}^*-\left. {\tilde{p}_{NL}^*} \right| _{q_L =q_{LM} } =\frac{-\left( {q_{LH} -q_{LM} } \right) \left( {2\theta q_{LM} +c\left( {q_{LH} } \right) -c\left( {q_{LM} } \right) } \right) }{6\left( {q_{LH} +q_{LM} } \right) }\le 0,\\&p_{NL}^*-\left. {\tilde{p}_{NL}^*} \right| _{q_L =q_{LH} } =\frac{\left( {q_{LH} -q_{LM} } \right) \left( {2\theta q_{LH} -c\left( {q_{LH} } \right) +c\left( {q_{LM} } \right) } \right) }{6\left( {q_{LH} +q_{LM} } \right) }\ge 0. \end{aligned}$$

Therefore, there is a threshold \(\hat{{q}}_L \) such that \(\tilde{p}_{NL} >p_{NL} \) when \(q_L \le \hat{{q}}_L \), and \(\tilde{p}_{NL} <p_{NL} \) otherwise. This threshold is defined as \(\hat{{q}}_L =\frac{2\theta q_{LM} q_{LH} +\left( {q_{LH} -q_{LM} } \right) \left( {c\left( {q_{LH} } \right) -c\left( {q_{LM} } \right) } \right) }{2\theta \left( {q_{LM} +q_{LH} } \right) }\).

From Eq. (22), it follows that \(\frac{\partial \tilde{d}_{NL}^*}{\partial q_L }=\frac{-c\left( {q_{LH} } \right) -c\left( {q_{LM} } \right) +2c\left( {\underline{q}} \right) -2\theta \underline{q}}{3\theta q_L^2 }\le 0\). Moreover,

$$\begin{aligned} \left. {d_{NL}^*-\tilde{d}_{NL}^*} \right| _{q_L =q_{LM} }= & {} \frac{-\left( {q_{LH} -q_{LM} } \right) \left( {c\left( {q_{LH} } \right) -c\left( {\underline{q}} \right) +\theta \underline{q}} \right) }{3\theta q_{LM} q_{LH} }\le 0\\ \left. {d_{NL}^*-\tilde{d}_{NL}^*} \right| _{q_L =q_{LH} }= & {} \frac{\left( {q_{LH} -q_{LM} } \right) \left( {c\left( {q_{LM} } \right) -c\left( {\underline{q}} \right) +\theta \underline{q}} \right) }{3\theta q_{LM} q_{LH} }\ge 0. \end{aligned}$$

Consequently, there is a threshold \(\hat{{\hat{{q}}}}_L \) such that \(\tilde{d}_{NL} >d_{NL} \) when \(q_L \le \hat{{\hat{{q}}}}_L \), and \(\tilde{d}_{NL} <d_{NL} \) otherwise. The profit of the brown firm follows the same development, which translates to better performance when \(q_{L}\) is close to \(q_{LM} \) and worse performance when \(q_{L}\) is close to \(q_{LH} \).

Appendix 3: Effects of consumer misperception on the quality of the environment

The derivative of global environmental quality in the imperfect information case is characterized by

$$\begin{aligned} \frac{\partial \tilde{Q}}{\partial q_L }=\frac{\left( {5q_{LH} -q_{LM} -4\underline{q}} \right) c\left( {q_{LH} } \right) -\left( {q_{LH} -5q_{LM} -4\underline{q}} \right) c\left( {q_{LM} } \right) +4\left( {q_{LH} +q_{LM} -2\underline{q}} \right) \left( {\theta q_{NL} -c\left( {\underline{q}} \right) } \right) }{12\theta q_L^2 } \end{aligned}$$

Because the second term of the numerator is necessarily lower than the first term and the third term is positive, the global environmental quality rises with perceived quality \(q_{L}\). Furthermore, using the fully coverage property, it is possible to characterize \(Q^{*}-\tilde{Q}^{*}\) in two ways:

$$\begin{aligned} Q^{*}-\tilde{Q}^{*}= & {} \left( {q_{LM} -q_{LH} } \right) \left( {d_{LM}^*-\tilde{d}_{LM}^*} \right) \nonumber \\&+\,\left( {\underline{q}-q_{LH} } \right) \left( {d_{NL}^*-\tilde{d}_{NL}^*} \right) \ge 0\quad \hbox { if }\quad q_L \le \hat{{\hat{{q}}}}_L ,\hbox { and}\\ Q^{*}-\tilde{Q}^{*}= & {} \left( {q_{LH} -q_{LM} } \right) \left( {d_{LH}^*-\tilde{d}_{LH}^*} \right) \nonumber \\&+\,\left( {\underline{q}-q_{LM} } \right) \left( {d_{NL}^*-\tilde{d}_{NL}^*} \right) \le 0\quad \hbox { if }\quad q_L \ge \hat{{\hat{{q}}}}_L . \end{aligned}$$

Therefore, when the perceived quality is low (high), the global environmental quality is lower (greater) than that occurring in the perfect information case.

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Brécard, D. Consumer misperception of eco-labels, green market structure and welfare. J Regul Econ 51, 340–364 (2017). https://doi.org/10.1007/s11149-017-9328-8

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