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Master thesis Green retailing: the spillover-effect of organic products on the perceived eco-friendliness of supermarkets Guus van den Munckhof 4816773 August 9th, 2021 Supervisor: Dr. Holger J. Schmidt

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Page 1: Master thesis Green retailing: the spillover-effect of

Master thesis

Green retailing: the spillover-effect of organic products on the

perceived eco-friendliness of supermarkets

Guus van den Munckhof

4816773

August 9th, 2021

Supervisor:

Dr. Holger J. Schmidt

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Abstract

Over past years, the already present attention for the environment has been increasing. With

consumers feeling insignificant in bringing climate change to a halt, consumers are

increasingly looking at corporations like supermarket chains to take responsibility, by

choosing to buy at companies that are actively environmentally friendly. Nonetheless, not

much research has been done on the actions that supermarkets can take to improve the extent

to which consumers perceive them to be environmentally-friendly. Past research has

nonetheless shown that pro-environmental products, in this case organic products, can cause a

spillover of the environmental-friendly connotations to the image of the entire supermarket.

Making use of an experiment, respondents were divided into six groups, each exposed

to a different manipulation, showing different supermarket shelves containing either no

organic products, organic private label brand products, or organic national brand products.

Furthermore, the shelves contained either hedonic or utilitarian products. As a covariate, the

organic involvement of participants was tested.

Results showed no effects of the types of brands in the assortment on the extent to

which participants saw a supermarket as environmentally friendly, even in comparison to the

situation not containing organic products. Interestingly, an effect was found of the extent to

which participants were involved with organic products, showing that higher involvement

leads to lower perceived eco-friendliness. Furthermore, there was a direct effect of product

category, with participants who were exposed to the utilitarian shelves seeing the supermarket

as more environmentally friendly than the participants who saw the hedonic shelves.

This provides supermarket managers with insights into how to influence their

environmentally-friendly image.

Keywords: Organic products, private label brand, environmental friendliness, spillover effect,

hedonic, utilitarian

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Table of contents

1. Introduction ......................................................................................................................... 5

2. Literature review ................................................................................................................. 8

2.1 Organic products ............................................................................................................... 8

2.2 Perceived eco-friendliness ................................................................................................ 9

2.3 Type of brand (Organic private label brands vs. organic national brands) .................... 11

2.4 Spillover effect ............................................................................................................... 12

2.5 Product category (hedonic vs. utilitarian products) ........................................................ 14

2.6 Organic involvement ...................................................................................................... 15

2.7 Demographic variables ................................................................................................... 17

2.8 Conceptual model ........................................................................................................... 18

3. Methodology ..................................................................................................................... 20

3.1 Method of data collection ............................................................................................... 20

3.2 Experimental design ....................................................................................................... 20

3.3 Statistical test .................................................................................................................. 23

3.4 Sample size ..................................................................................................................... 24

3.5 Research ethics ............................................................................................................... 24

4. Analysis ................................................................................................................................ 25

4.1 Manipulation check ........................................................................................................ 25

4.2 Questionnaire respondents .............................................................................................. 26

4.3 Randomization check ..................................................................................................... 28

4.4 Measurement .................................................................................................................. 28

4.5 Factor analysis ................................................................................................................ 29

4.6 Assumptions ................................................................................................................... 30

5. Results .................................................................................................................................. 35

5.1 Main effects .................................................................................................................... 35

5.2 Covariates ....................................................................................................................... 37

6. Conclusion and Discussion .................................................................................................. 40

6.1 Theoretical implications ................................................................................................. 43

6.2 Managerial implications ................................................................................................. 44

6.3 Limitations and future research ...................................................................................... 46

References ................................................................................................................................ 49

Appendices ............................................................................................................................... 59

Appendix A: Questionnaire .................................................................................................. 59

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Appendix B: Original scales and translation ........................................................................ 84

Appendix C: Manipulation check ......................................................................................... 86

Appendix D: Factor Analysis ............................................................................................. 101

Appendix E: Manipulation check results ............................................................................ 103

Appendix F: ANCOVA assumptions ................................................................................. 105

Appendix G: ANCOVA ..................................................................................................... 109

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1. Introduction

In the Netherlands, the market for organic products is growing steadily. Throughout 2019, the

market share of organic products in supermarkets grew by 3% (Logatchena, 2020).

This growth of the organic market has gone hand in hand with the growth of environmental

consciousness, especially in developed countries (Naderi & van Steenburg, 2018; Chen &

Chai, 2010). As a result of this, consumers have grown more aware of making

environmentally responsible and conscious purchases, while also expecting firms and

institutions to behave responsibly concerning the environment (Fraj & Martinez, 2007). This

is a result of the perception that many consumers have that they do not have a meaningful

positive effect on the environment, resulting in consumers mainly looking at large

corporations to do their part (Salomon, Preston & Tannenbaum, 2017). A report has shown

that 83% of global online consumers say that it is important that companies implement

programs that improve the environment (Nielsen, 2011).

In organic farming and production, fewer pesticides and artificial fertilizers are used.

For these reasons, it is generally accepted that organic farming does less damage to the

environment than conventional farming (Van Doorn & Verhoef, 2011). A majority of

consumers in Western Europe also report concern for the environment as the main reason for

purchasing organic products (Yiridoe et al., 2005). This was in line with Seyfang (2006), who

found that protection of the environment is an important motivator for ethical consumerism,

which involves purchasing organic products out of ethical responsibility (Cho & Krasser,

2011). Bionext (2020) found that 41% of Dutch consumers perceive organic products to be

mainly environmentally friendly, ahead of other factors like healthiness.

Retailers have started recognizing and acknowledging this organic trend among

consumers. With supermarkets being the primary sales channel of organic products (Bionext,

2020), they have grown aware of the responsibility that consumers place in their hands

regarding pro-environmental behaviour.

As a consequence, companies have started using “green retailing”: including measures

to protect the environment within retail operations (Lai, Cheng & Tang, 2010). An example of

this is the fact that organizations have started communicating more about their pro-

environmental practices (Pancer, McShane & Noseworthy, 2017). Furthermore, retailers have

started introducing organic private label brands, which provide the retailer with an

opportunity to express environmental commitment (Mejri & Bhatli, 2014), as well as being

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able to offer organic products at more affordable prices (Konuk, 2018). An example of this is

AH Biologisch, which was introduced by Albert Heijn in 2015 (Albert Heijn, 2016).

Because private label brands are only sold at certain stores, they are highly connected to that

store. Therefore, private label brands are often seen as extensions of the store image and can

therefore contribute to store differentiation in the minds of consumers (Collins-Dodd &

Lindley, 2003). Different from private label brands, national brand products are not produced

by the retailer itself, but by an organization that sells its products to retailers, such as Coca-

Cola, Oreo, and Mars (Ailawadi & Harlam, 2004). As they are not connected to a single chain

of stores, national brand products are often widely sold. Due to their favorable level of brand

equity, consumers often perceive national brand products as higher quality, which past

research has shown to be largely a result of branding, instead of large differences in actual

quality (De Wulf et al., 2005).

As private label brands are more strongly connected to a specific store, past research

has shown that the image of a PLB can spill over to the overall image of the store that sells

the brand. This is especially the case with products that are related to corporate social

responsibility, of which organic products and environmental protection form a part. Wang &

Korschun (2015) found that this positive, eco-friendly image can carry over to the entire store.

However, it can generally be concluded that the amount of research that has been done

on the impact of a positive PLB image on store image has not been sufficient. So far, this

subject has also mostly been researched in a CSR context as a whole, instead of focusing on

the individual drivers of CSR, such as organic food products. Furthermore, according to

Schleenbecker & Hamm (2013), an insufficient amount of research has been done on

consumer’s expectations regarding organic product lines.

With the growth of environmental awareness and consciousness over past decades,

and consumers also expecting pro-environmental behaviour from companies, it is very

important for managers of supermarkets to know how they can influence the extent to which

consumers see their stores as eco-friendly. In this way, they can secure a competitive

advantage over competitors that do not correctly communicate their pro-environmental stance,

either through marketing or through including certain types of brands in their assortment.

Because PLBs can be seen as extensions of the store image, the effect of introducing organic

PLBs by supermarkets on the extent to which they are perceived to be environmentally

conscious is very relevant.

In this study, the effect of different brand types in an assortment, namely organic NBs

and organic PLBs, on the perceived eco-friendliness of a store will be compared, to each other

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and a baseline condition not containing organic products. In this way, it will be possible to

make conclusions about whether the introduction of organic PLBs or organic products in

general, actually affects the extent to which consumers perceive a supermarket as eco-

friendly. As the introduction of organic PLBs has been growing in popularity in recent years,

these conclusions will provide supermarket managers with relevant information.

Because private label brands are more strongly and directly associated with a specific

retailer than national brands, it is hypothesized that the positive effect on the perceived eco-

friendliness is stronger in the case of organic private label products than organic national

brand products. In this study, the effect of the presence of either organic NBs or organic PLBs

on the perceived eco-friendliness of the store will be compared, to be able to make

conclusions about whether the introduction of organic PLBs, which many stores have been

doing in recent years, actually has an impact on whether the said store is seen as eco-friendly.

This leads to the following research question: “To what extent do the types of organic brands

that are present in an assortment have an effect on the perceived eco-friendliness of a

supermarket?”

Furthermore, two food product categories will be compared, namely hedonic and

utilitarian products, to see whether the effect of the type of brand on perceived eco-

friendliness differs significantly between the two product categories. Also, some covariates

are added into the model, namely the extent to which consumers are involved with organic

products, as well as age and gender.

This research question will be answered through an experimental design, in which

participants will be exposed to fictional store shelves, either containing organic PLB products,

organic NB products, or no organic products altogether. Afterward, they will answer

questions regarding the extent to which they are involved with organic products and the extent

to which they perceive the store in the questionnaire to be environmentally friendly.

Regarding the research structure, chapter 2 begins with a literature review of the central

concepts of the study. In chapter 3, the methodology that will be used in the study is

discussed, as well as the design of the questionnaire, and the proposed statistical analysis of

the data. In chapter 4, the questionnaire results are analyzed. Chapter 5 contains the results of

the analysis, and chapter 6 discusses the conclusions and limitations of the study.

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2. Literature review

In this section, the main concepts of the study will be defined and operationalized.

Furthermore, the conceptual model of the study and the resulting hypotheses are constructed

and presented.

2.1 Organic products

Organic food can be defined as “natural food items which are free from artificial chemicals

such as fertilizers, herbicides, pesticides, antibiotics, and genetically modified organisms”

(Rana & Paul, 2017, pp.158). Consumers generally perceive organic products to be fresher,

tastier, healthier, and of higher nutritional quality than conventional products (Grunert, Bech-

Larsen & Bredahl, 2000; Wang, Wang & Huo, 2019). Magnusson et al. (2001) also found that

taste and health were the two most important purchase criteria that consumers had for buying

organic products. Nonetheless, Van Doorn & Verhoef (2015) found no significant positive

effect of health consciousness on organic purchase intention and showed that a focus on

health might even influence the purchase intention negatively. Another main motivation that

is generally found for buying organic food in past research is buying organic products out of

environmental grounds (Cicia, del Guidice & Ramunno, 2009; Grunert & Juhl, 1995).

Consumers perceive organic products to be more “natural”, and the word ‘organic’

generally serves as a heuristic cue for naturalness and greenness (Aarset et al., 2004).

Larceneux et al. (2012) also found that the organic label on a product, by which organic

products can often be recognized, has a significant positive effect on the belief that the

product is environmentally friendly. This also shows in the willingness to pay that European

consumers have for organic products, as stating that a product is organic and including its

positive impact on the environment increases the price that consumers are willing to pay for

that product (Vecchio, van Loo & Annunziata, 2016). These perceptions that consumers have

regarding the environmental properties are salient, as previous studies have not been able to

come to a definitive conclusion on whether organic agriculture is actually beneficial to the

environment (Lorenz & Lal, 2016). Nonetheless, the perceptions that consumers have are of

more relevance in the present study than the actual environmental impact.

Regarding the main point of purchase that consumers look to for purchasing organic

products, Weatherell, Tregear & Allison (2003) found that although consumers are willing to

engage with local food producers to purchase organic food, supermarkets are still the first

point of reference because they are more easily accessible. For this reason, organic products

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are very important for supermarkets in catering to the growing environmental awareness of

consumers.

Regarding the target group of organic products, past research shows that most

consumers only purchase organic products occasionally and that only a very small percentage

of consumers exclusively purchase organic products (Pearson & Henryks, 2008).

2.2 Perceived eco-friendliness

According to past research, food consumption is estimated to contribute between 20% and

30% of the total environmental impact in the Western world (Tukker & Jansen, 2006). With

growing environmental awareness in these same developed Western countries, consumers are

seeking to contribute positively to the environment, for instance through organic food choices,

which is generally seen as the most important attribute of environmental friendliness in food

(Tobler, Visschers & Siegrist, 2011).

To define the variable perceived eco-friendliness, it is necessary to define store image

first. Bloemer & De Ruyter (1998, pp.499) define it as follows: “the complex of a consumer’s

perceptions of a store on different (salient) attributes”, with the different attributes referring to

elements such as products, price, promotion etcetera. Consequently, the perceived eco-

friendliness of a supermarket forms a part of the store image, as it is a specific image that is

formed by a consumer or a group of consumers. It is defined as follows: “the extent to which

a store is perceived as environmentally friendly and is linked to environment commitment and

environment concerns in consumers’ mind” (Punyatoya, 2014). The extent to which a

supermarket is perceived as environmentally friendly creates a green image of the

supermarket in the mind of the consumer.

Over recent decades, consumers have grown increasingly aware of the importance of

taking action to preserve the environment and reduce the negative effects of global warming.

As a result, concern about the environment is evident around the world, and growing

(Kvaløy, Finseraas, & Listhaug, 2012). Nonetheless, consumers feel as though their

individual efforts do not have any impact on trying to curb climate change, leading to

demoralization and often refraining from pro-environmental actions altogether (Feijoo &

Moreira, 2020). As a result, consumers are progressively starting to look at big corporations,

as they feel that the big international organizations actually can play a role in slowing the

effects of climate change, and should take their responsibility in doing so (Salomon et al.,

2017).

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As a result, consumers actually do play a very significant role in more sustainable food

production, for example by steering the demand towards more sustainable food options

(Johnston, Fanzo & Cogill, 2014). In extreme situations, this could lead to consumers

effectively boycotting supermarket chains that do not behave according to their environmental

beliefs (Dono, Webb & Richardson, 2010). According to Ingenbleek & Reinders (2013), this

has directly lead to mainstream brands adopting these sustainability labels such as organic and

fair trade brands, possibly out of fear of consumers questioning their social behaviour, and

opting for other supermarkets in the future. This illustrates the relative power that consumers

can exert over organizations, by adapting their buying behaviour to only purchasing at

supermarkets that show they care about the environment and take pro-environmental actions.

Nonetheless, not much research has been done into what factors influence whether a

company is seen as environmentally friendly by consumers. With supermarkets being the

main retail outlet for food and groceries, it is important to gain more understanding into the

different factors that influence to what extent a supermarket is seen as eco-friendly. For

supermarket managers, it is especially relevant in current times to be aware of how to

influence these eco-friendly perceptions among consumers. As this is a relatively new

viewpoint in the field of environmental research, not much research has been done so far on

what factors influence the extent to which an organization is perceived to be eco-friendly.

However, in the case of products, researchers have found features that influence

whether consumers generally view them to be eco-friendly. In the past, it was often difficult

for consumers to assess whether a product was eco-friendly, as the environmental impact was

often not visible (Tanner & Jungbluth, 2003). Nowadays, with many labels relating to the

environment often present on packaging, including organic labels, consumers can deduce the

eco-friendliness of the product more easily (Tobler et al., 2011; Tanner & Kast, 2003), with

organic products being seen as more eco-friendly than conventional products. Past research

has furthermore shown a significant correlation between perceived healthiness and perceived

eco-friendliness: participants also deduce environmental perceptions from health aspects, and

vice versa (Lazzarini, Zimmermann & Visschers, 2016), meaning that participants often also

see healthier products are more eco-friendly. It was also found that the product category is an

important indicator for environmental friendliness, as participants saw plant- and milk-based

products as more environmentally friendly, which will be further discussed in section 2.5.

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2.3 Type of brand (Organic private label brands vs. organic national brands)

At supermarkets, products are sold under a multitude of different brands. A brand can be

defined as “a name, term, design, symbol or any other feature that identifies one seller's good

or service as distinct from those of other sellers” (American Marketing Association, 1960;

Bennett, 1988, pp.18).

In most supermarket assortments, a general divide can be made between private label

brands and national brands. Private label brands (PLBs) can be defined as follows: “brands

owned, controlled, and sold exclusively by retailers” (Sethuraman & Cole, 1999, pp. 340).

Under the PLB that is sold in a supermarket, a plethora of different product categories is often

sold. The main selling point of private label products has traditionally been their price

advantage and good value for money in comparison with national brands. As such, PLBs can

act as a cue to trigger a perception of value (Zeithaml, 1988). The main reason why retailers

have started introducing PLBs is to compete profitably in the price-sensitive segment (Hoch

& Banerjee, 1993).

The other type of brand that will be used in this study consists of national brand (NB)

products. The main difference between private label brands and national brands is the fact that

private label brands are manufactured by the retailer itself, while national brands are sold to

retailers by the companies that manufacture them. In the case of national brand products, this

means that both the manufacturer and the retailer add a profit margin to the price of the

product, resulting in a higher average price for national brand products (Ailawadi & Harlam,

2004).

Regarding conventional products, consumers are often suspicious of the quality of

PLBs as compared to NBs, because they are typically lower-priced, usually without

interesting packaging, and often have little advertising (Dick, Jain & Richardson, 1995).

Many NBs are perceived as being superior in reliability, prestige, and quality to PLBs

(Bellizzi, et al., 1981). To a lesser extent, they are perceived as superior in aspects like taste,

aroma, nutritional value, and freshness. De Wulf et al. (2005) found that this is mainly

because national brands enjoy a favorable level of brand equity, meaning it elicits strong and

favorable associations in the mind of the consumer (Keller, 1993). Nonetheless, PLBs are

generally perceived as providing better value for money than national brands, as national

brands are often seen as being too expensive in comparison to what they provide. (Nenycz-

Thiel & Romaniuk, 2009). In recent years, consumers have even started preferring PLBs over

NBs, indicating that objectively speaking, those products are often equally good or even better

than their national brand counterparts (Deloitte, 2015). Negative attitudes towards PLBs are

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generally present for consumers who do not use PLB products because Nenycz-Thiel &

Romaniuk (2009) found that for PLB users, trust and perceived quality for PLBs was just as

high as for NBs. In conclusion, perceptions of lower quality generally stem from consumers

who do not purchase and use PLB products.

Bauer, Heinrich & Schäfer (2013) found that the quality perception of private label

products in specific is most effectively influenced by an organic label, leading to the PLB

being viewed as of equal quality to local and national brands, while for conventional products,

PLBs are seen as being of lower quality. In this case, the organic label also showed a

significant effect on the perceived environmental friendliness of the products. Ngobo (2011)

also found that consumers are more likely to purchase organic PLBs than organic NBs.

Nonetheless, the consensus is still that generally, consumer preferences for national

brands are strong, and that a competitive national brand assortment is essential in establishing

profitability as an organization (De Wulf et al., 2005).

In the present study, this could relate to the difference between national brand

products, which are owned by a separate brand, and private label products, for which the

brand is the same as the retailer. In the case of the introduction of a new organic PLB, it is

both a new product that competes with existing brands and a new organic product that is sold

under the already existing brand name of the retailer as a PLB. Therefore, the supermarket can

to some extent be seen as both the retailer and the brand. This specific instance was not

researched in the article by Anagnastou, Ingenbleek & Van Trijp. (2015), but because a new

organic PLB can be seen as a new brand competing with the already existing assortment of

brands, it can be hypothesized that its introduction will lead to a positive spillover to the

retailer.

2.4 Spillover effect

The main question in this research is whether there is a spillover between the environmentally

friendly image of organic products to the retailer that offers these products.

The spillover effect can be defined as: “the extent to which information provided in

messages changes beliefs about attributes that are not mentioned in the messages.”

(Ahluwalia, Unnava & Burnkrant, 2001, pp. 458). In this case, the spillover effect would be

between the eco-friendly image of organic products that are introduced by the supermarket,

and the overall perceived eco-friendliness of the store, which can be seen as a dimension of

store image. Store image can namely be defined as: “the way a store is perceived by shoppers

and defined in the shoppers’ minds.” (Hartman & Spiro, 2005; pp. 1112).

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Unlike national brands, private label brands are strongly connected to the retailers that

sell them (Vahie & Paswan, 2006). Due to this strong connection, often in the case of negative

publicity or crises, the image of the private label can influence the image of other products

that are sold under that private label, or the image of the retailer itself (e.g. Gendel-Guterman

& Levy, 2017; Mackalski & Belisle, 2015). They found that in the case of very severe and

extreme negative publicity, the negative image of a PLB can spill over to the store image.

This can be seen as a spillover effect (Lutz, 1975). In this case, there would be a

spillover effect between the image of the brand and the image of the store. While instances of

positive spillovers have been found, not much research has been done on this phenomenon.

However, Wang & Korschun (2015) for instance found a spillover effect from a

company’s corporate social responsibility (CSR) activity at the product brand level to the

entire brand portfolio and the company itself in the case of food and drink products. In their

study, the researchers also indicated that an important gap still exists in the extant literature of

social responsibility on a product/brand level. With organic production being a component of

CSR (Pivato, Misani & Tencati, 2008), its positive social connotations can carry over to the

rest of the brand portfolio, as well as the retailer itself. This is in line with Ramesh et al.

(2019), who found that CSR activities, including selling organic products and environmental

protection, have a significant positive effect on the image of an organization. In the case of

the present study, the positive connotations that would spillover from the organic products in

the assortment to the store image would be the notion of eco-friendliness, as the presence of

organic products often carries an eco-friendly connotation. Past research has namely shown

that organic products can be seen as a cue for environmental friendliness and naturality.

(Aarset et al., 2004; Larceneux, Benoît-Moreau & Renaudin, 2012).

In this area, a very significant finding was also done by Anagnostou et al. (2015),

namely that when a completely new organic-fair trade brand is introduced to compete with

existing brands, its sustainability image spills over to the retailer. However, when a new

organic-fair trade product is introduced under the name of an already existing brand, the

positive image only spills over to the brand, and not the retailer. This result is especially

interesting because, in the case of PLBs, the retailer ís the brand. Therefore, it would be

interesting to see whether the notion of eco-friendliness would carry over to the retailer.

Bezençon & Blili (2010) found a similar result in the case of ethical or social products

such as organic products, namely that their distribution can go together with the reinforcement

of the retailer’s corporate image regarding ethical values. Mejri & Bhatli (2014) found that a

socially responsible PLB reinforces both the brand and the retailer in their socially responsible

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positioning. Furthermore, communicating the social value of the PLB significantly influences

the consumers’ loyalty to the retailer. As eco-friendliness is an example of an ethical value,

introducing organic products might have a similar effect.

Although past research has mainly focused on the ethical image of supermarkets and

stores in general, this research will specifically focus on the effect of the eco-friendly image

of organic products spilling over to the perceived eco-friendliness of the supermarket. As past

research has shown that the eco-friendly connotation of organic products can indeed carry

over to the retailer, especially in the case of a PLB (Vahie & Paswan, 2006), the following

hypotheses are used:

H1a: There is a significant effect of the type of brand on perceived eco-friendliness, with

organic PLBs leading to higher perceived eco-friendliness than organic NBs.

H1b: There is a significant effect of the type of brand on perceived eco-friendliness, with

organic NBs leading to higher perceived eco-friendliness than the situation without

organic products.

2.5 Product category (hedonic vs. utilitarian products)

In research into the food sector, two main product types are often distinguished: hedonic

products on one hand, and utilitarian products on the other. Hedonic products refer to

products that provide for experiential consumption, fun, pleasure, and excitement (Khan, Dhar

& Wertenbroch, 2004), like chocolate or ice cream. Hedonic products can therefore generally

be seen as “want-”, or vice products, that score high on affective preferences (Dhar &

Wertenbroch, 2000). In an organic context, this pleasure and excitement can also be driven by

the feeling of doing something right for the consumer’s health or for the environment (Petljak

et al., 2017).

While hedonic products are often focused on providing immediate benefits, they might

harm consumers in the long run, such as negative health consequences in the case of

chocolate. These negative consequences can lead to guilt in the mind of the consumer when

buying hedonic products (Giner-Sorolla, 1999). The other category, utilitarian products,

consists of products that mainly serve a practical purpose, based on the needs that consumers

have. Examples of utilitarian products would be products with low caloric content, or with

high nutritional value, like milk (Aigner, Wilken & Geisensdorf, 2019). Utilitarian products

can be viewed more as “should-” or virtue products, that mainly are based on reasoned

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preferences (Dhar & Wertenbroch, 2000). These utilitarian products are more related to

providing consumers with benefits in the long run, instead of pleasure at the moment of

consumption (Bazerman, Tenbrunsel & Wade-Benzoni, 1998). In the organic field, the

utilitarian value is often considered as the product’s instrumental functionality, for example,

low price, low caloric, or high nutritional value (Ghali-Zinoubi, 2020).

Although most products represent a combination of both hedonic and utilitarian

benefits, some product categories can be classified as primarily hedonic or utilitarian (Maehle

et al. 2015). An example of utilitarian cues in organic products is that they promise higher

quality and environmental protection than conventional products (Essoussi & Zahaf, 2008).

However, organic products also contain hedonic attributes, for example, the better taste that

organic products tend to have (McEachern & McClean, 2002; Hidalgo-Baz et al., 2017).

Previous research has found contradicting findings: Maehle et al. (2015) found that

consumers saw environmental friendliness as more important for utilitarian products than for

hedonic products. Mohammed (2020) also found that buying intentions of organic products

are mostly influenced by utilitarian values. Lee & Yun (2015) found that consumer’s

intentions to purchase organic foods are determined by both utilitarian attitudes and hedonic

attitudes. Ghali-Zinoubi (2020) found that consumers are willing to pay a higher price for

organic products, based on their utilitarian value, such as their superior quality or higher

nutritional value. Nonetheless, he concluded that buying organic products from an

environmental viewpoint was more related to hedonic value. Although there does not seem to

be a clear consensus regarding whether consumers mainly purchase organic products for

utilitarian value or hedonic value, most researchers state that consumers buy organic products

out of doing something right for the environment, which is generally seen as a utilitarian

value. For this reason, it is hypothesized that utilitarian products lead to a higher perceived

eco-friendliness than hedonic products:

H2: Utilitarian products lead to a higher perceived eco-friendliness than hedonic

products.

2.6 Organic involvement

Often, people seem to think that organic products are often purchased by small groups of

people who only purchase organic products. However, this does not seem the case. Although

there are consumers that are relatively highly involved with organic products, previous

research has shown that people who purchase organic products are generally in all

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demographic segments in the market and that they all purchase organic products only casually

(Pearson, Henryks & Jones, 2010).

Therefore, as the first covariate in this study, the extent to which consumers are

involved with organic products is added into the model, to see whether the small group of

people that are highly involved with organic products show different results to the general

public. Furthermore, organic involvement is included to reduce the effect of possible outliers

in this category. Because the literature shows that organic involvement is generally at a quite

equal level in society, results are more generalizable when controlling for organic

involvement. Furthermore, the organic involvement cannot be randomized, but it can be

measured. This is also a motivation to include a variable as a covariate (Hair et al., 2019)

First, the variable of organic involvement should be defined. Celsi & Olsson (1988,

p.211) define (felt) involvement as: “a consumer’s overall subjective feeling of personal

relevance.” Specifically in this study, the type of involvement that is present is “enduring

involvement”. This specification refers to an ongoing concern with a certain product type, as a

function of past experience with a product and the strength of values to which the product is

relevant. (Bloch & Richins, 1983). In the context of this study, the involvement with organic

products is defined as the extent to which consumers subjectively feel that organic products

are personally relevant to them.

As mentioned before, values that are related to purchasing organic products are for

example related to values such as health or the environment. Nonetheless, Collins, Steg &

Koning (2007) found that even though behaviour is related to values, this relationship is quite

weak. Barr (2006) also found that there is often a gap between consumers’ environmental

concerns and their choices of products related to these same environmental issues. For this

reason, it is more relevant to use the variable ‘involvement’, as its influence on shopping

behaviour has been widely researched, although not often in an organic context (Tarkiainen &

Sundqvist, 2009). Nonetheless, research has shown that involvement with organic products

positively impacts the purchase intention of organic products (Ghali-Zinoubi & Toukabri,

2019).

Because environmental values are an important predictor for positive attitudes towards

organic products, consumers who are highly involved with organic products will generally

also be more involved with the environment (e.g. Tarkiainen & Sundqvist, 2009; Teng & Lu,

2016; Smith & Paladino, 2010; Shafie & Rennie, 2012). Schifferstein & Oude Ophuis (1998)

found that for heavy users of organic products, both the health- and environmental attributes

were of similar importance, which was not the case for incidental buyers, for whom health

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attributes were more important. This means that consumers who are highly involved with

organic products will focus more on the environment-related aspects than consumers who do

not show much involvement with organic products. Consumers who are highly involved with

organic products are generally more willing to purchase organic products, pay a price

premium for their organic attributes, and make more sacrifices to obtain them (Rahman,

2018). Based on previous research, consumers who are more highly involved with organic

products will be more aware of the benefits of organic products for the environment. For this

reason, it can be expected that consumers that are more involved with organic products will

be more focused on the eco-friendliness of the product and will project it to the image of the

supermarket. This leads to the following hypothesis:

H3: There is a positive effect of organic involvement on perceived eco-friendliness.

2.7 Demographic variables

Finally, two demographic variables are added to the model to test their effects.

Age is included in the model, as research showed that the willingness to buy organic products

differs significantly for different age groups (Sivathanu, 2015; Kranjac, Vapa-Tankosi,

Knežević, 2017). The research showed that participants between the ages of 31 and 40

purchased the most organic products. Dettmann & Dimitri (2009) found that younger

participants were more likely to purchase organic products. Diamantopoulos et al. (2003) and

Jain & Kaur (2006) found similar results, showing that young participants have more

knowledge about issues regarding the environment, and actively search for environmentally

friendly products. For this reason, we believe that there is a significant effect of age on the

perceived eco-friendliness of the supermarket. This shows in the following hypothesis:

H4: There is a negative effect of age on perceived eco-friendliness.

Furthermore, the covariate gender will be included, as past research has also shown that there

is a significant difference between the two different genders in organic purchasing behaviour

(Sivathanu, 2015; Kranjac et al., 2015; Pearson et al., 2011), with female consumers

purchasing more organic products. Furthermore, Jain and Kaur (2006) found that females

outperform males in environmentally-friendly behaviour. Nonetheless, the majority of

conclusions of examples of previous research were based on hypotheses that are only partly

supported, lacking large explanative power. Therefore, it is still necessary and interesting to

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research the effect of gender on pro-environmental behaviour and perceptions of eco-

friendliness. Based on the previous results, it can be hypothesized that environmental aspects

are of higher importance for female consumers than male consumers. As they would focus

more on the environmental aspect of the organic products in the assortment, the spillover to

the overall store would be stronger. For this reason, it is expected that female participants will

generally report higher perceived eco-friendliness than male participants:

H5: There is an effect of gender on perceived eco-friendliness, with females reporting

higher perceived eco-friendliness than males.

2.8 Conceptual model

The goal of the present study is to analyze the extent to which the type of brand that is present

in an assortment affects the perceived eco-friendliness of the supermarket that offers these

products. It is expected that assortments containing organic PLBs will lead to higher

perceived eco-friendliness than assortments containing organic NBs (H1a). The assortments

with organic NBs will then lead to higher perceived eco-friendliness than the baseline

situation not containing organic products (H1b). Furthermore, it will be analyzed in this thesis

whether there is an effect of the product category on the perceived eco-friendliness,

differentiating between hedonic and utilitarian products. For this effect, it is expected that

utilitarian products will lead to a higher perceived eco-friendliness than hedonic products

(H2).

Also, three covariates are included in the model. The first covariate measures the

extent to which consumers are involved with organic products. For this variable, it is expected

that consumers that are more involved with organic products will report higher perceived eco-

friendliness (H3). The second covariate measures the age of participants. Here, it is expected

that younger participants will report higher perceived eco-friendliness than older participants

(H4). Finally, the gender of participants is analyzed, with the expectation that female

participants will report higher perceived eco-friendliness than male participants (H5).

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Figure 1: Conceptual model

H1

H2

H3-H5

Perceived eco-

friendliness of the

supermarket

Type of brand

(Without organic vs.

organic PLB vs.

organic NB)

Product Category

(Hedonic vs.

utilitarian products)

Covariates

- Organic

Involvement

- Age

- Gender

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3. Methodology

3.1 Method of data collection

As is illustrated in the conceptual model in Figure 1, the effect of the type of brands that are

present in a supermarket assortment and the product category that is present on the perceived

eco-friendliness is measured. This effect will be controlled for the effect of organic

involvement, age, and gender.

For this thesis, the quantitative research design of an online experiment was used.

Through this method, quantitative data was gathered regarding the perceived eco-friendliness

that participants reported for different experimental conditions. The research had a custom

design, to gain the results that were needed to be able to answer the research question.

Although the dependent variable was of ordinal measurement level, the results were analyzed

through the process of an analysis of covariance. The questionnaire followed an experimental

design, which is the appropriate method for identifying a causal connection between the

independent and dependent variables (Kirk, 2012).

The independent variables, the type of brand and product category, were manipulated

to test their effects on the dependent variable, the perceived eco-friendliness of the

supermarket. Furthermore, the covariates organic involvement, age, and gender were added,

to be able to control for their effects on the dependent variable. Finally, the demographic

variable educational level was added to the questionnaire, to see to what extent this variable

would be skewed or kurtotic, based on the use of snowball sampling.

3.2 Experimental design

In this section, the design of the experiment and the different stimuli will be discussed.

An experiment was used, in the form of an online questionnaire, in order to test the different

hypotheses. A 3 (Without organic products vs. containing an organic NB vs. containing an

organic PLB) x 2 (hedonic vs. utilitarian product category) design was used, meaning that

participants were divided over 6 different manipulations. A between-subjects design was

used, in which participants were randomly assigned to the different experimental groups. The

experimental design was based on the design by Butz (2020). Similar to the design by Butz

(2020), participants were exposed to one out of six possible store shelves.

Participants were given a short introduction to read before starting the questionnaire,

stating that filling in the questionnaire would only take about 5 minutes, and they could

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always come into contact to ask questions and could stop at any time. The goal of the research

was not disclosed, not to influence how participants would read and fill in the questionnaire.

In the first condition, participants were exposed to a supermarket shelf containing only

conventional products without organic products, consisting of the supermarket’s PLB and

three NBs, to make sure a substantial offering was provided. In the second condition, an

organic NB was added to the offering. In the third condition, instead of an organic NB, an

organic PLB was included in the offering. Furthermore, participants were randomly assigned

to one out of the two possible product categories, the utilitarian category yogurt, and the

hedonic category chocolate. The different shelves were manipulated in such a way that all

products had equal shelf space, and that the shelves looked like realistic supermarket store

shelves. Multiple versions of the same brand were added to the shelves, to give the impression

of realistic, full supermarket shelves.

Regarding the two product categories, the shelves contained an assortment of either

dark chocolate bars, as a hedonic product, or yogurt, as a utilitarian product (Huang & Lu,

2016). Regarding the assortment of Albert Heijn, these choices were justified, as the

supermarket offers both conventional and organic NBs, as well as conventional and organic

PLBs for both product categories (Albert Heijn, n.d.a.; n.d.b.). For yogurt, low-fat yogurt

containing 1.5% fat was used, known as “halfvol” in Dutch, which can be loosely translated

to “semi-skimmed”. This can be seen as the most general tier in between the variations

containing 0.5% and 3% fat, known as “magere” or thin yogurt and “volle” or full yogurt

(Albert Heijn, n.d.a.). Regarding the conventional and organic PLB, yogurt from the AH and

AH Bio brands was used. For the organic national brand, Arla organic yogurt was used. As

conventional national brands, the brands Campina, Melkan, and Melkunie were used. Melkan

and Melkunie are brands that are not sold at Albert Heijn. This was done because as a store,

Albert Heijn did not offer a larger variety of yogurt brands. However, the shelves were not

presented as being Albert Heijn shelves, they simply contain the Albert Heijn private label

brands. This was chosen because Albert Heijn is the most widely spread and well-known

supermarket in the Netherlands, with 34.9% of the total market share in supermarkets (Loon,

2020). For this reason, the Albert Heijn PLBs would be most recognizable as PLBs for Dutch

consumers, which was necessary for the study. This was also checked in the manipulation

check, which can be seen in Appendix C.

Even though the use of prices in the experimental condition would have added to the

realism of the experiment, prices were not added, for the reason that participants’ perception

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could have been influenced by the prices, instead of by the intended variables. Therefore,

prices did not play a role in the experiment, as it was not expected to affect the results.

In the case of the hedonic product chocolate, dark chocolate containing hazelnuts was

used, as this was the only variance of chocolate in the assortment for which all different types

of brands were offered. Again, the AH PLB and the organic PLB AH Bio were used. For the

organic national brand, Côte d’Or Bio was used. The conventional national brands that were

used in the study were the brands Verkade, Ritter Sport, and Côte d’Or. The manipulations

containing the supermarket shelves can be found in Appendix A.

In the questionnaire, the different variables were measured through 7-point Likert

scales, ‘1’ generally referring to a low score, and ‘7’ referring to the highest score. However,

some scales were reversed to prevent a response bias, in which participants would not be

focused on the questions anymore, and simply answer based on the expectation that 1 stands

for low, and 7 stands for high. The scales were gathered from previous research, to have

higher certainty that the scales are adequate, as they had been previously tested regarding

validity and reliability.

Perceived eco-friendliness was defined as: “The extent to which a store is perceived as

environmentally friendly and is linked to environment commitment and environment concerns

in consumers’ mind” (Punyatoya, 2014, pp. 280). A scale from Punyatoya (2014) was used,

containing 5 questions. Organic involvement, or the extent to which consumers subjectively

feel that organic products are personally relevant to them, was tested using a scale by

Zaichkowsky (1994). This scale was adapted to an organic context, as it is a scale that is used

to measure involvement in general, adaptable to more concrete subjects. The scale contained 8

questions. Furthermore, demographic variables were included in the questionnaire, including

the covariates age and gender. Finally, to test whether yogurt and dark chocolate containing

hazelnuts were actually representative for utilitarian and hedonic products respectively, scales

by Voss, Spangenberg & Grohmann (2003) were used. Regarding both the utilitarian and the

hedonic value of the products, 5 questions were used. In the end, these 5 scales were

combined into a hedonic and utilitarian score for both product categories.

The questions in the questionnaire were translated to Dutch, as only Dutch participants

were researched, who might not all have been fully fluent in English, which could have

affected the results. The translations from English to Dutch were checked by multiple people

and translated back to English, to make sure that the final questions in Dutch measured the

same concepts as the original questions. The original English scales and their Dutch

translations can be found in Appendix B.

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Participants were gathered through convenience sampling, as the specific

demographics were not of large importance to the study. Because the sample size

requirements were met, the sample can be viewed as a representative subset of the population.

The participants were exposed to one out of six possible manipulations. While still

being able to see the shelves, participants were asked to rate the extent to which they saw the

store as eco-friendly. Then, after going to the next page, they were asked to rate the utilitarian

and hedonic value of the product category they had been exposed to, as well as the extent to

which they were involved with organic products. Finally, they were asked to fill in some

demographic variables.

3.3 Statistical test

In this study, the relationship between a single dependent variable, two independent variables,

and three covariates was researched. The dependent variable, perceived eco-friendliness, was

measured using Likert scales. Likert scales are examples of scales of ordinal measurement

level. Normally, logistic ordinal regression would be an appropriate type of analysis for this

type of data. Nonetheless, due to a lack of experience with this method of analysis, the

decision was made to treat the ordinal outcome variable as a numeric interval variable and use

an analysis of covariance. According to past research, Likert scales with 5 or more categories

can often be treated as continuous without doing the dataset harm, which is called using an

“ordinal approximation of a continuous variable” (Johnson & Creech, 1983; Norman, 2010;

Sullivan & Artino, 2013; Zumbo & Zimmerman, 1993).

In using ANCOVA, this could lead to some different results, which will be addressed

in the limitations section. When using ANCOVA, some assumptions need to be met in order

to be able to conduct the tests. Firstly, the assumptions for regular analysis of variance should

be met, starting with the assumption that all observations should be independent. Secondly,

the independent variables should consist of two or more categorical groups. As a third

assumption, the dependent variable should be of interval or ratio level. Furthermore, the

dataset should contain no significant outliers. As a further assumption, the dependent variable

should be approximately normally distributed for each different category of the different

independent variables. Finally, regarding ANOVA, the last assumption that should be met is

the homogeneity of variances.

Subsequently, some ANCOVA-specific assumptions are expected to be met. Firstly,

for each level of the different independent variables, there should be a linear relationship

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between the dependent variable and the covariate. Secondly and finally, the factors or

independent variables and the covariate should be independent of one another.

3.4 Sample size

Making use of snowball sampling through social media, 158 participants were gathered. The

respondents were not aware of the manipulations that were used in the study, and they were

randomly assigned to one out of the six different conditions of the research. As can be seen in

Table 3 in section 4.2, the different groups do not contain sharply unequal sample sizes. As all

groups contain a reasonable number of participants of N>20, normality can be assumed,

meaning that the number of participants is adequate (Hair et al., 2019).

3.5 Research ethics

In this study, the general rules of conduct by Radboud University and the American

Psychological Association, as well as the Netherlands Code of Conduct for Academic Practice

(NVSU, 2014) are applied universally and without exception, to ensure that the research

process is carried out according to the generally accepted standards. In line with this code,

informed consent of all participants is essential, and participant responses were treated with

confidentiality and were only used for research purposes by the researcher. Participants were

informed about the fact that their answers and data would be used for scientific research, and

that individual response sets would not be publicized. If a participant chose not to finish

answering the questionnaire, their answers were not used, and the data of this participant was

deleted. Furthermore, participants were free to come into contact when there were aspects of

the questionnaire that are unclear or that need further specification. No participants reached

out with questions or aspects that were not clear in the questionnaire.

Academic sources were scrupulously referenced, and no texts and findings from others

were used without references or quotes. Furthermore, methodological procedures were used

and described in such a way that future researchers will be able to replicate the study and be

certain of the methodological quality of the research (VNSU, 2014). Finally, the researcher

was impartial and independent, to establish facts and generalizable conclusions, without

affiliation to certain viewpoints that are not supported by academic sources. Responsibility for

choices that are made in the study lies with the researcher.

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4. Analysis

In the following section, the data analysis is conducted. First, the results of the manipulation

check are discussed. Then, the distribution of participants over the different conditions is

presented, followed by a randomization check. Then, the reliability of the different variables

is checked. To check the factors once again, a factor analysis is also carried out. Finally, the

assumptions for ANCOVA are tested.

4.1 Manipulation check

In order to test the manipulations that were done for this study, a manipulation check was

carried out, which can be seen in Appendix C. A manipulation check is generally carried out

to test whether participants react to manipulations as expected by the researchers (Hoewe,

2017). Because the effect of the type of brand is essential in this study, it was important that

participants correctly identified the different brand types, and whether they were organic or

not. For this reason, participants were exposed to the different products included in the

experiment one by one, answering questions regarding whether they correctly identified the

products as organic or non-organic, and as a PLB or an NB. In most of the cases, the majority

of respondents correctly indicated whether the product was organic or not, and which type of

brand it was, as can be seen in Table 2, and more extensively in Table 18 in Appendix E.

Nonetheless, in the yogurt category, some products were thought to be organic by a

large part of respondents, while they were in reality not organic. This was especially the case

for Campina and the AH private label brand. Because there were not enough different brands

sold at Albert Heijn to be able to replace these products, they were kept in the study. This will

be addressed in the limitations section. Furthermore, also for these products, a large part did

still indicate correctly that the products were not organic. In the case of the chocolate

products, there were not as striking examples of participants erroneously perceiving products

to be organic. In Table 2, it can also be seen that for the utilitarian category yogurt,

participants had more problems in deciding correctly whether a product was organic or not.

When looking at whether participants correctly identified the type of brand as a PLB

or an NB, it seems in Table 2 that this task was significantly easier for participants than

indicating whether a product was organic or not, as on average, more than 90% correctly

indicated what type of brand was presented to them in the image. Finally, the manipulation

check was also used to test whether yogurt and dark chocolate with nuts were adequate and

representative examples of utilitarian and hedonic products respectively, using the scales by

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Voss et al. (2003). In past research, milk has often been used as a utilitarian product category,

while for hedonic products, often products like milk chocolate or ice cream have been used

(Dhar & Wertenbroch, 2000; Khan et al., 2004). In order to extend the body of research

regarding hedonic and utilitarian products, it was opted to choose slightly different products,

to test whether yogurt and dark chocolate with nuts would also be adequate for these product

categories.

As expected, as can be seen in Table 1, the chocolate category scored higher on

hedonic value, while the yogurt category scored higher regarding utilitarian value. For this

reason, these two product categories were also chosen to be used in the final questionnaire.

Nonetheless, to check once again whether the product categories were representative, the

checks regarding hedonic and utilitarian value were also included in the final questionnaire.

Table 1: Manipulation check for hedonic and utilitarian value

Product category Hedonic value M(SD) Utilitarian value M (SD)

Chocolate 3.40 (.73) 2.97 (.40)

Yogurt 3.10 (.39) 3.78 (.49)

Table 2: Manipulation check for whether a product is organic and the type of brand

Product category Organic or not - % correct PLB or NB - % correct

Hedonic (chocolate) 83.3% 97.2%

Utilitarian (yogurt) 72.2% 91.7%

4.2 Questionnaire respondents

The questionnaire was filled in by 158 respondents. Because of the option to make it

obligatory to answer the individual questions, no participants reported missing values. In the

case of the variable age, for which participants could fill in their age freely without

restrictions, there were also no significant outliers. The 6 different manipulations were

randomly divided among participants by Qualtrics, which provides the user with an option to

evenly divide participants over the different manipulations. As a result, the 158 participants

were more or less evenly divided over the conditions, as can be seen in Table 3.

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Table 3: Number of participants per manipulation

Yogurt Chocolate Total

Without organic products 23 (14.5%) 29 (18.4%) 52 (32.9 %)

With an organic NB 30 (18.9%) 27 (17.1%) 57 (36.1%)

With an organic PLB 29 (18.4%) 20 (12.7%) 49 (31%)

Total 82 (51.9%) 76 (48.1%) 158 participants

The age of participants ranged from 18 to 68, even though 50% of participants was 25 or

younger. The main reason for this skewed distribution is the fact that snowball sampling was

used, and therefore, the questionnaire was mainly distributed often among students. The

questionnaire was mainly shared among the personal network of the researcher, through social

media (e.g. Facebook, Whatsapp, etc.), and by asking participants to further share the

questionnaire among their networks. No form of incentive was used to gather more

participants.

The large representation by students can also be seen in the distribution of the

educational level of the participants, which was primarily included to test whether the sample

was representative or somewhat skewed or kurtotic, as the largest part of participants had

completed either higher professional education (HBO), namely 27.8%. Following this group,

24.1% had completed a university bachelor, and 21.5% had finished a university master.

Finally, 16.5% had completed lower professional education (MBO), while 9.5% only

completed secondary education, and 0.6% only completed primary education, which

corresponds with only one participant. These data are also skewed towards higher education,

again because of the use of snowball sampling. This will later be discussed in the limitations

section.

Regarding the gender of participants, 76 participants, or 48.1% were male, while 82

participants, or 51.9% consisted out of male participants. As this was almost evenly divided,

this seems representative of the population. No participants were deleted from the data file, as

there were no outliers reported, and everyone filled out the entire questionnaire. To ensure

that participants would not fall victim to response bias and fill in the questionnaire without

actively reading the separate scales, some scales were reversed to make sure that participants

would pay attention to individual scales. The scores of these scales were inverted again before

doing analyses.

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4.3 Randomization check

In order to check whether participants were assigned randomly to the 6 different

manipulations, chi square and univariate tests were carried out. The six different

manipulations did not differ significantly for the variables age (F (5, 152) = .595, p =.704),

gender (χ2 (5, N = 158) = 2.870, p = .720) and education level (χ2 (25, N = 158) = 31.084, p =

.186). Furthermore, the manipulations did not differ significantly concerning organic

involvement (F (5, 152) = .604, p = .697). Based on these results, it can be concluded that the

randomization of participants was successful.

4.4 Measurement

In order to be sure of the quality of the different variables and scales used in a study, it is

important to have internal consistency among the different items, which is called the

reliability of items. As a first measure to be sure of the reliability of items, the different scales

were largely gathered from previous research, in which the scales and items have already been

tested for reliability. Nonetheless, the scales were also tested in the current study, using

Cronbach’s alpha.

Normally, an alpha of 0.70 is generally accepted (Hair et al., 2019). The variable

perceived eco-friendliness consisted of 5 items (α = .862), which is good (Punyatoya, 2014).

The reliability could not be improved significantly by deleting items. The scale for the

variable organic involvement consisted of 8 items (α = .904), which is very good

(Zaichkowsky, 1994). The reliability of the scale could not be improved significantly by

deleting items.

Regarding the hedonic value of the products, which was not included as a variable in

the conceptual model, but used as a manipulation check for testing whether the product

categories were adequately chosen, the scale consisted of 5 items (α = .827). The reliability of

the scale could be improved significantly by deleting the item “for me, the product category

is: not thrilling – thrilling”. This leads to the scale consisting of 4 items, with α = .844, which

is good. Furthermore, the reliability could be improved by deleting the item “for me, the

product category is: dull – exciting. This leads to the scale consisting of 3 items, with α =

.867, which is good. The utilitarian value of the products consisted of 5 items (α = .861),

which is good. The scales measuring both the hedonic and utilitarian value for the product

categories were adapted from Voss et al. (2003). The reliability could not be improved

significantly by deleting items. The variables and measurement properties can also be seen in

Table 4.

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Table 4: Measurement properties of the dependent variables and covariates

Variable Number

of items

Reliability

(α)

Source

Perceived eco-

friendliness

5 .862 Punyatoya (2014)

Organic involvement 8 .904 Zaichkowsky (1994)

Hedonic value

(manipulation check)

3 (5) .844 Voss et al. (2003)

Utilitarian value

(manipulation check)

5 .861 Voss et al. (2003)

4.5 Factor analysis

To further test the number of constructs and structure of the measures, a confirmatory

factor analysis was carried out, as can be seen in Appendix D. Confirmatory factor analysis is

a statistical technique that is generally used to test whether the different measures of a

construct are accurately represented by the measured that a researcher has chosen to use in

research (Hair et al., 2019).

A confirmatory factor analysis using principal axis factor extraction was conducted to

determine and confirm the factor structure. In order to validate that factor analysis was a

suitable technique to use, Bartlett’s test of sphericity and a KMO test were conducted.

Bartlett’s test should be significant at α = .05, while the KMO test value should be ≥ .05.

Bartlett’s test (p < .001) and KMO value (.810) indicate that factor analysis is indeed an

appropriate technique to be used for this study. In order to check the number of factors that

are present in the dataset, the eigenvalues and explained variance were used. Normally, it

would be desirable for each factor to have an eigenvalue of at least one, and for the different

factors put together explaining at least 60% of the common variance. In the actual

questionnaire, 4 factors were intended. According to Table 16 in Appendix D, four factors

have an eigenvalue higher than one, and these four factors explain 66.2% of the common

variance in the dataset.

Then, the item’s communalities were checked. All communalities should be above .20,

and there should not be cross-loadings in the definitive factor solution (Hair et al., 2019). No

communalities below .20 were present, and there were no cross-loading variables. For this

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reason, it can again be concluded that no variables should be deleted from the dataset, and the

items are adequate.

In order to be able to carry out an ANCOVA, the different items measuring the

variables of interest were transformed into one average score for each variable. As a result,

mean scores were calculated for the variables perceived eco-friendliness and organic

involvement.

In the questionnaire, participants were asked to rate the product category they were

exposed to on both the hedonic and utilitarian qualities of the product categories. This was

included in the questionnaire to double-check whether yogurt was actually seen as a

representative utilitarian product category than chocolate and whether chocolate was seen as

more representative for a hedonic product category than yogurt. For both the hedonic value,

which consisted of 3 scales and the utilitarian value, which consisted of 5 scales, mean scores

were calculated that were compared. In the final questionnaire, regarding hedonic value, an

independent samples t-test showed a significant effect for product category t (144.242) = -

3.395, p = .001, with chocolate (M = 3.99, SD = .70) scoring higher than yogurt (M = 3.52,

SD = 1.01). In the case of utilitarian value, an independent samples t-test also showed a

significant effect for product category t (156) = 4.164, p < .001, with yogurt (M = 3.49, SD =

.83) scoring higher than chocolate (M = 2.95, SD = .79). These results can be found in Table

5, and Tables 19-22 in Appendix E. Seeing as the yogurt products were seen as significantly

more utilitarian, and the chocolate products were seen as significantly more hedonic, it can be

concluded that they stand for utilitarian and hedonic products in general respectively. For this

reason, these terms will be used interchangeably from this point on.

Table 5: Check for hedonic and utilitarian value in final questionnaire

Product category Hedonic value M(SD) Utilitarian value M (SD)

Chocolate 3.99 (.70) 2.95 (.79)

Yogurt 3.52 (1.01) 3.49 (.83)

4.6 Assumptions

In using inferential statistics, certain assumptions need to be met before being able to carry

out the research. When the assumptions are not met or violated, it changes the interpretation

of results and conclusions. These assumptions differ based on the statistical test that is chosen

(Hair et al, 2019).

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For a two-way ANCOVA test, first, the assumptions for ANOVA should be met.

As a first assumption, observations should be independent. This is the case, as all participants

filled in the questionnaire individually on the internet, being exposed randomly to one of the

six possible conditions of the study. A second assumption for an ANCOVA is that the

independent variables should consist of two or more categorical groups. This is also the case

in the present study, with the independent variable type of brand consisting of three groups,

and the independent variable product category consisting of two groups: the type of brand

consists of the situation without organic products, organic PLB products, and organic NB

products. The variable product category consists of the categories utilitarian and hedonic.

A third assumption is that the dependent variable is measured at an interval or ratio

level, which means that the dependent variable should be continuous. This is not the case in

the present study, as the dependent variable perceived eco-friendliness is measured through

multiple measurement items, in this case Likert scales. Likert scales are ordinal by definition

(Field, 2017), as they cannot be seen as containing numeric values. Although participants fill

in the Likert scales by giving scores, there is no numerical value, as a score of ‘4’ on a

particular scale cannot be interpreted as being twice as high as a score of ‘2’. Nonetheless, it

is common practice to still include ordinal dependent variables in ANCOVA or regression

analyses, as multi-item measurements are often used. For this reason, it is no longer a true

Likert scale, but a semi-continuous measurement, which can be treated as an interval variable,

which would make the variable adequate for ANCOVA. Other research also states that it is

acceptable to treat ordinal variables as of interval level (Williams, 2020). For this reason, it is

concluded that the assumption is met.

Furthermore, the dataset does not contain significant outliers. As all questions are

answered through 5- or 7-point Likert scales, limiting the possibilities of outliers, as the

possible answer properties are only the ones that fall inside of the Likert scales. The only

variable for which participants could answer without limitations was the variable age, for

which participants were asked to fill in their age, without limits regarding the numerical value

that participants could fill in. Even though it is skewed and kurtotic, the variable contains no

significant outliers.

As a further assumption, the dependent variable should be approximately normally

distributed for each category of the independent variables. From the Shapiro-Wilk test of

normality, it shows that the dependent variable is indeed normally distributed for the majority

of the different levels of the independent variables. This test should not be significant at a p-

value of .05. For the independent variable type of brand, the different scores are indeed all not

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significant, with p-values of .311, .092, and .194 respectively, as illustrated in Table 23. For

the variable product category, the product utilitarian category shows a p-value of .539, which

means it is not significant, as can be seen in Table 24. However, for the hedonic product

category, the p-value is .014, which is below the decided threshold of .05, which means the

dependent variable perceived eco-friendliness is not normally distributed for the hedonic

category. Based on the fact that for this group, the dependent variable is not normally

distributed, the assumption would normally have to be rejected. However, the issue of

normality is often only a problem when sample sizes are small (<20). When sample sizes are

larger than 30, the sampling distribution of the mean is always regarded to be normal,

regardless of the distribution of values in the population, which is known as the Central Limit

Theorem (Field, 2017). For this reason, although the assumption is not fully met, no actions

will be taken to make changes to the normality of the variable, as the hedonic product

category consists of 76 participants, which is significantly higher than the 30 that is required.

For this reason, the analysis will continue. For the covariate Gender, the different scores are

again not significant, with p-values of .150 and .285, as can be seen in Table 25.

The final assumption for ANOVA is the homogeneity of variances. Levene’s test is

used, with a non-significant effect meaning that the variances within groups are indeed equal,

and that there is no difference in variances. This is the case, with p = .162, which is higher

than the threshold of .05. Therefore, this assumption is also met, as can be seen in Table 26 in

Appendix F.

Furthermore, in the case of ANCOVA, two additional assumptions should be met on

top of the assumptions for ANOVA. Firstly, for each level of the independent variables, there

should be a linear relationship between the dependent variable and the covariate. This was

tested through a Pearson correlation analysis. As can be seen in Table 27 in Appendix F, the

correlation between the covariates organic involvement and age with the dependent variable

perceived eco-friendliness is significant for both covariates. Organic involvement and

perceived eco-friendliness were shown to be weakly negatively correlated, r = -.289, p <.001.

The other covariate, age, was shown to also be weakly negatively correlated with the

dependent variable perceived eco-friendliness, r = -.225, p = .004. For the final covariate,

gender, no significant correlation was found with the dependent variable perceived eco-

friendliness, r = .025, p = .751. For this reason, the assumption is not met for the variable

gender. Subsequently, the choice has been made to omit the variable gender from this point in

the study, as it does not seem relevant to include it, as it fails to meet the assumptions that are

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necessary for being included in the study. Therefore, it can be concluded that H5 is not

supported.

Because of the omission of this variable, the previous assumptions were tested again.

The only assumption that has shown a change is the homogeneity of variances. Levene’s test

is still non-significant, but it now shows a value of .157, which can be seen in Table 28 in

Appendix F.

As a second assumption for ANCOVA, the factors and the covariate should be

independent, with the factors in this study being the type of brand and the product category.

As can be seen in Tables 29 and 30 in Appendix F, this is indeed the case. For the variable

type of brand, this was tested through a one-way ANOVA, as the variable consists of three

levels. There was shown to be no significant effect of the type of brand on the organic

involvement, F(2, 155) = 1.019, p =.363. For the variable product category, this assumption

was tested through an independent samples t-test, as the variable consists of two groups:

utilitarian and hedonic products. The independent samples t-test also showed no significant

effect of the Product Category, t(156) = -.398, p = .698. As a result, the second assumption for

ANOVA is also met.

As a final assumption, the regression slopes should be homogenous. A test of

between-subjects effects was carried out, to test whether the assumption was met. For the

assumption to be met, the results should be non-significant, at a p-value of .05. In order to test

the assumption, all possible interaction effects between the different variables are tested. For

the interaction effect of the type of brand and organic involvement, the result was not

significant, F(2, 134) = .400, p = .671. For the interaction effect of product category and

organic involvement, the result was also not significant, F(1, 134) = .248, p =.620. For the

interaction effect between product category and age, the result was also not significant, F(1,

134) = 0, p = .984.

Regarding the interaction effects containing three variables, the interaction effect

between product category, age, and organic involvement was also not significant, F(1, 134) =

.007, p = .932. The interaction between the type of brand, age, and organic involvement was

also not significant, F(2, 134) = .218, p = .805. The interaction between the type of brand,

product category, and age was also not significant, F(2, 134) = .560, p = .560. The last of the

interactions containing three variables, namely the type of brand, product category, and

organic involvement was also not significant, F(2, 134) = .659, p = .519. Furthermore, for the

interaction effect between product category and age, the result was also not significant, F(2,

134) = 191, p = .826.

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Finally, the interaction effect between the type of brand, product category, organic

involvement, and age was also not significant, F(2, 134) = .847, p =.431. These results can

also be seen in Table 22 in Appendix F. Seeing that all interaction effects are not significant,

the null hypothesis that the regression slopes are homogenous should not be rejected, and it

can be concluded that the regression slopes are parallel and homogenous. For this reason, the

final assumption is also met. These results can be found in Table 31 in Appendix F.

In conclusion, all but two assumptions for ANCOVA were met. The two assumptions

that were strictly not met were the assumption that the dependent variable should be

continuous and the assumption that all variables should have a normal distribution, which was

not the case for the hedonic product category. Nonetheless, these violations should not lead to

large problems, based on theory, as was explained in the previous section. In the next section,

the results of the analysis of covariance will be presented.

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5. Results

In this study, a two-way ANCOVA was conducted to assess whether there was a statistically

significant difference in effects between a condition without organic products, a condition

containing an organic NB product, and a condition containing an organic PLB product on the

perceived eco-friendliness of a supermarket. Furthermore, it was assessed whether there is a

difference between hedonic and utilitarian products. The extent to which a consumer is

involved with organic products and the age of consumers were used as covariates, to control

for individual differences. The predetermined assumptions were tested and assumed to be

met. First, an ANOVA test was carried out without the covariates, to test the main effects.

5.1 Main effects

H1a: There is a significant effect of the type of brand on perceived eco-friendliness, with

organic PLBs leading to higher perceived eco-friendliness than organic NBs.

H1b: There is a significant effect of the type of brand on perceived eco-friendliness, with

organic NBs leading to higher perceived eco-friendliness than the situation without organic

products.

Before running all tests with the covariates, the main effects were tested without the inclusion

of the covariates organic involvement and age.

First, the main effect of the type of brand on the perceived eco-friendliness of the

supermarket was tested. The two-way analysis of covariance showed no significant effect of

the type of brand on perceived eco-friendliness after controlling for the extent to which

participants are involved with organic products and their age, F(2, 152) = 1.728, p = .181. In

conclusion, there were no significant differences between the conditions not containing

organic products, containing an organic NB product, and containing an organic PLB product.

For this reason, H1a has to be rejected, as there was no difference between the situation

containing the organic PLB and the situation containing the organic NB. H1b also had to be

rejected, as the situation containing an organic NB did not differ significantly from the

baseline situation without organic products regarding perceived eco-friendliness.

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H2: Utilitarian products lead to a higher perceived eco-friendliness than hedonic products.

When looking at the other independent variable, namely the product category, the two-

way analysis of covariance showed a significant effect of product category on perceived eco-

friendliness after controlling for the extent to which participants are involved with organic

products and their age, F(1, 152) = 5.589, p =.003. The effect was small (.055). This result

can be seen in Tables 6 and 8 in section 5.2. As can be seen in the tables, the utilitarian

product category showed significantly higher perceived eco-friendliness (M = 2.81, SD = .81)

than the hedonic product category (M = 2.42, SD = .77). Although the effects are significant,

H2 cannot be fully accepted yet, as the covariates will be added to the model before the

hypothesis is accepted or rejected.

Finally, the two-way analysis of covariance showed no significant effect of the

interaction effect between the type of brand and product category on perceived eco-

friendliness after controlling for the extent to which participants are involved with organic

products and their age, F(2, 152) = .640, p = .529.

Table 6: Main effects without controlling for covariates

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5.2 Covariates

Next, the covariates organic involvement and age were added into the model.

H3: There is a positive effect of organic involvement on perceived eco-friendliness.

H4: There is a negative effect of age on perceived eco-friendliness.

H5: There is an effect of gender on perceived eco-friendliness, with females reporting higher

perceived eco-friendliness than males.

Now, the covariates organic involvement were added into the model, to assess whether they

had a statistically significant effect and whether the significant main effect of product

category still stands when the covariates are added. First, it is tested whether the covariates

have a significant effect.

The two-way analysis of covariance showed a significant effect of the first covariate

organic involvement on the dependent variable perceived eco-friendliness, F(1, 150) = 9.117,

p < .01. The effect size was small (.057). The parameter estimates in Table 36 in Appendix G

show that the effect is negative (B = -.166). This shows that there is a negative relationship

between organic involvement and perceived eco-friendliness, meaning that as participants are

more involved with organic products, they rate the store as less eco-friendly. It was

hypothesized that the effect of organic involvement on perceived eco-friendliness would be

positive. For this reason, H3 has to be rejected.

Analyzing the second covariate, the covariate age was not significantly to the

perceived eco-friendliness, F(1, 150) = 3.324, p = .07. The result shows that the extent to

which participants reported the store as eco-friendly did not differ for age. For this reason, H4

is rejected. Nonetheless, as this covariate was added to the model for theoretical reasons, it is

decided that it will not be removed from the model.

Finally, because the covariate gender did not meet the different assumptions that were

set for ANCOVA, the variable was prematurely deleted, before conducting the analyses. For

this reason, it can be concluded that H5 has to be rejected, as it could not be tested.

Regarding the main effect of product category on perceived eco-friendliness, the result

stands when controlling for organic involvement and age F(1, 150) = 7.649, p = .006. The

effect size grew smaller by adding the covariates (.049). This result shows that the utilitarian

product category still shows higher perceived eco-friendliness than the hedonic product

category when controlling for organic involvement and age. For this reason, H2 can now be

fully accepted.

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Table 7: Between-subjects effects including covariates

Subsequently, the estimated marginal means are used to compare the situation without

the covariates yet included in the model, and the situation when controlled for the covariates.

The descriptive statistics show that when not controlling for the covariates, participants that

were exposed to the utilitarian shelves (M = 2.81, SD = .81) reported significantly higher

perceived eco-friendliness than participants that were exposed to the hedonic shelves (M =

2.42, SD = .77). This can also be seen in Table 8. When controlling for organic involvement

and age, the difference between the two product categories grows smaller, with the difference

between participants who had seen the utilitarian shelves (M = 2.78) and participants who had

seen the hedonic shelves (M = 2.45) growing smaller, as can also be seen in Table 32. The

difference is significant (p < .01). Nonetheless, as age was shown not to have a significant

effect, this difference is caused solely by the covariate organic involvement. In conclusion,

the covariate, which represents the extent to which participants are involved with organic

products, reduces the effect of product Category on perceived eco-friendliness. In table 10, a

summary can be found regarding the acceptance or rejection of the hypotheses.

Table 8: Perceived Eco-friendliness without controlling for covariates

M SD N

Utilitarian 2.81 .81 82

Hedonic 2,42 .77 76

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Table 9: Perceived Eco-friendliness when controlled for Organic Involvement and Age

M SE N

Utilitarian 2.78 .084 82

Hedonic 2,45 .088 76

Table 10: Acceptance/rejection of hypotheses

Hypothesis Hypothesis supported?

H1a Rejected

H1b Rejected

H2 Accepted

H3 Rejected

H4 Rejected

H5 Rejected

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6. Conclusion and Discussion

6.1 General discussion

To analyze the impact of organic private label products, the following research question was

used: “To what extent do the types of organic brands that are present in an assortment have

an effect on the perceived eco-friendliness of a supermarket?”

The main purpose of the study was to examine the effects that different types of

brands in a supermarket assortment have on the extent to which shoppers and consumers

perceive that supermarket to be environmentally friendly. The type of brand and product

category were selected as independent variables, as they were thought to affect the dependent

variable, the perceived eco-friendliness of the supermarket. As covariates, the organic

involvement was added into the model, together with the participants’ age and gender.

From previous studies, it was inferred that due to a spillover effect of socially

responsible products such as organic products, the image of the products could spill over to

the image of the supermarket (Wang & Korschun, 2020; Pivato et al., 2008; Mejri & Bhatli,

2014). Furthermore, it was hypothesized that this spillover effect would be stronger for

organic PLB products than for organic NB products, due to their stronger connection to a

specific store or chain of stores (Vahie & Paswan, 2006).

Nonetheless, this was not supported by the findings in the present study, as no

significant effect was found between the three types of brands. This means that there was no

difference between the situations that did not contain organic products and the situations that

did and that there was no significant difference between the situations containing organic NBs

and the situations containing organic PLBs. This is in line with Anagnostou et al. (2015), who

found that the introduction of a socially responsible organic product could influence the image

of other products under the same PLB, but not the image of the entire store. The image of

other products of the same brand was not considered in the present study.

A possible explanation could be that the different types of organic products did not

stand out enough from the rest of the products, or because only one product was changed or

added in each assortment, meaning the addition of the products did not play a large role in the

evaluation of the shelves. However, if the organic products were perceived and processed

either consciously or unconsciously by participants, it could still be that consumers simply do

not project their environmental perception of the shelves onto the entire supermarket. As

mentioned by Gershoff & Frels (2015), the perception of environmental benefits of a product

is often seen as a given, while many aspects influence how an environmental cue is processed,

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such as the centrality of the cue and colour. The results of the manipulation check also could

have played a role in the results of the final experiment, as the manipulation check showed

that for the hedonic category, 83.3% was able to identify whether a product was organic or

not, while for the utilitarian category, only 72.2% correctly identified whether the products

were organic. This shows that for a percentage of the participants, it could have simply been

too difficult to recognize whether the products were organic, meaning they would not

construct a socially responsible and eco-friendly image in their minds, leading to the fact that

there was no eco-friendly image to spill over to the image of the store. Rees, Tremna &

Manning (2019) also found that lack of knowledge plays a large role in the perception of

environmentally friendly cues, even when consumers are actively searching for the most eco-

friendly and sustainable option. Steenis et al. (2017) also found that consumers’ assessment of

eco-friendliness is highly influenced by mere graphical cues, that say nothing about the actual

environmental value of the product.

The other independent variable, product category, was shown to have a significant

effect on the perceived eco-friendliness of the supermarket. The results showed that

participants who were exposed to the utilitarian assortment saw the supermarket as more eco-

friendly than participants who were exposed to the hedonic assortment. This was in line with

expectations, as eco-friendliness was concluded to be more representative of a utilitarian

factor regarding organic products than a hedonic factor. Furthermore, the findings were in line

with Maehle et al. (2015), Essoussi & Zahaf (2008) & Mohammed (2020). However, it cannot

be fully concluded that the difference in results was actually caused by the difference between

hedonic & utilitarian products. For example, Lazzarini et al. (2016) has found that consumers

generally see products that are healthier as more eco-friendly as well. Although it was not

tested in the present study, it can be concluded that generally, yogurt is seen as healthier than

chocolate.

Moreau, Markman & Lehmann (2001) found that when relevant information is absent,

for example in this case information related to the eco-friendliness of a product, consumers

often use a single inference strategy. This means that because they are factually unable to

deduce whether the products and supermarket are eco-friendly, they will use their prior

knowledge and attitudes regarding the entire category. In this case, they would have relied on

their previous attitudes regarding yogurt and chocolate to decide their eco-friendliness and the

eco-friendliness of the entire supermarket, instead of basing their answers purely on the

stimuli they were exposed to. This might have influenced why participants who were exposed

to the utilitarian shelves perceived the supermarket to be more eco-friendly.

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Another factor that could have influenced the perceptions of participants is the

differences in packaging between the two product categories. In the example of the utilitarian

products, as can be seen in Appendix A and C, the packaging contained more “natural”

imagery, for example, images of cows and plants. Furthermore, many of the yogurt packages

contained the colour green, which is generally seen as the colour that most represents nature,

with the term “green” often being used interchangeably with “eco-friendly” (Pancer et al.,

2017). Also, some labels can be seen on the packaging of the yogurt products, representing

the quality of the products, as well as animal well-being, and the use of natural ingredients.

The combination of the aforementioned packaging aspects could have played a large role in

influencing the perceptions that participants had. Because they refer to the natural aspects of

the production process, it is only logical that these aspects are perceived as environmental

cues and have an effect on the perceived eco-friendliness.

Even though some labels referring to natural ingredients are present on the chocolate

packages, they are much less prevalent. Furthermore, the chocolate packaging makes much

less use of images that allude to nature, and the colour green is not as present. For this reason,

it seems that the different labels on the yogurt packaging play a role in determining whether

the supermarket that sells the products can be seen as environmentally friendly.

The covariate organic involvement was included to reduce its effect on the dependent

variable perceived eco-friendliness. Nonetheless, it is very interesting to see that there was a

direct negative effect of organic Involvement on perceived eco-friendliness, meaning that

participants who are more involved with organic products generally perceived supermarkets

to be less environmentally friendly than participants who are less involved with organic

products. As previous research found that consumers who are highly involved with organic

products are in general also highly involved with the environment (Tarkiainen & Sundqvist,

2009; Smith & Paladino, 2010; Shafie & Rennie, 2012), it was hypothesized that these highly

involved organic consumers would be more aware of the positive environmental attributes of

organic products, and would also attribute this positive image to the store.

Nevertheless, the exact opposite was the case, as higher organic involvement would

lead to consumers reporting a lower amount of perceived eco-friendliness. A possible

explanation for this effect could be that consumers who are more involved with organic

products also have more knowledge regarding organic products and their subsequent effect on

the environment. For this reason, it could be the case that consumers that are highly involved

with organic products also have large knowledge regarding the environment, and are more

knowledgeable about the fact that thus far, it has not been unanimously concluded that

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organic production is beneficial for the environment (Lorenz & Lal, 2016). Furthermore, they

might be less susceptive to the different environmental cues that are present on the packaging

of products, as they would be more critical. On the other hand, consumers who are not as

involved with organic products might not know what on what cues to decide whether a

product is eco-friendly, and be more easily influenced by cues such as colour and eco-labels,

as presented by Pancer et al. (2017).

6.1 Theoretical implications

Following on the findings by Wang & Korschun (2015), the present study focused on

advancing knowledge on how social corporate actions in the form of selling organic products

would have an effect on the extent to which consumers would perceive the supermarket as

eco-friendly. In current literature, little was so far known about this spillover effect of the

positive connotations of corporate social actions, even less so in the specific case of having

organic products in the assortment of the supermarket. In the past, research has shown that

only negative publicity or crises would spill over to the image of the entire store (e.g. Gendel-

Guterman, 2017). In the case of a positive image of a product, like in this study the eco-

friendly image that organic products have, Anagnostou et al. (2015), found that the image

would rather spill over to the image of the other products that are sold under the same PLB

brand, than to the image of the entire store. The current study adds to their findings, showing

that the positive, environmentally-friendly connotations of organic products do not carry over

to the image of the store, which was shown to be the case for both PLB and NB products.

Although it was hypothesized that especially for PLB products, the eco-friendly image would

carry over, due to the strong connection of the brand to the retailer, no significant results were

found. This contradicts the finding of Pivato et al. (2008), who found that in their case, the

positive eco-friendly connotations did carry over to the entire image of the organization.

Secondly, the current study adds to literature regarding the different product categories

and values, and their relationship with organic products and eco-friendliness. As past research

had not been conclusive in deciding whether eco-friendliness should be more seen as a

utilitarian or a hedonic value. In this study, the results showed that participants who were

exposed to the supermarket shelves containing utilitarian products perceived the store as a

whole as being more eco-friendly than the participants who were exposed to the hedonic

shelves. From this result, it is not directly possible to conclude whether eco-friendliness is

more of a utilitarian or a hedonic component, but the findings of the study does provide the

academic world with new possibilities to further investigate whether the effect that was found

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in the present holds for other examples of hedonic and utilitarian products, or whether the

effect would only be found for these two product types, yogurt and chocolate.

Finally, the current study adds to the existing research by investigating the highly

interesting effect of organic involvement on the extent to which a store is perceived to be

environmentally friendly. Unlike what is often thought, organic products are not mainly

purchased by a small group of highly involved organic consumers, but mainly by a large

group of consumers who occasionally purchase organic products (Pearson et al., 2010).

As previous research had found that consumers who are highly involved with organic

products will generally also be more involved with environment-related values, it was

hypothesized that for consumers who were highly involved with organic products, the

spillover of environmentally-friendly connotations to the image of the entire store would be

stronger. However, the findings show that as consumers are more involved with organic

products, they will generally perceive a store to be less environmentally friendly than

consumers who are not as involved with organic products would. This provides the academic

world with this interesting new line of research, as it provides researchers with possibilities to

do research on the underlying factors that influence this relationship, for example whether

consumers that are more involved with organic products are more critical of environmental

heuristic cues, and need more factual information regarding the environmental value of

products to get the feeling that a store is actually behaving environmentally-friendly.

Although the findings of the present study are interesting, more research is needed into the

underlying factors that influence the findings, to provide the academic world with more

insights and possibilities for further research. Nonetheless, the findings do already lead to

some relevant contributions for managers.

6.2 Managerial implications

Nowadays, it is of high importance for companies to be able to emit a positive image

regarding their stance and activities towards the environment. As consumers feel they do not

have a large influence on the environment, they expect organizations and institutions to

reduce their negative effect on the environment and even act pro-environmentally (Fraj &

Martinez, 2007; Salomon et al., 2017; Nielsen, 2011). Consumers will place more importance

on this aspect when deciding where to buy their products, trying to steer the demand towards

organizations that act in accordance with their beliefs regarding the environment (Johnston et

al., 2014). This could lead to consumers choosing to boycott organizations and retailers that

are not in line with their views and beliefs regarding the environment (Dono et al., 2010).

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Especially with the possibility of consumers spreading these views, for example through

social media, managers of supermarkets need to stay ahead of this movement and start acting

pro-environmentally, or be able to influence the extent to which consumers perceive the

supermarket to be eco-friendly.

One of the goals of this research was to provide managers with valuable implications

on how to make use of organic PLBs to influence public perception. However, no effect was

found of organic PLBs on the perceived eco-friendliness of the supermarket, or organic

products in comparison with conventional products altogether. This shows that it would not

be wise for supermarket managers to focus on introducing organic PLBs and focusing many

marketing efforts on these products, as their presence in an assortment does not significantly

influence the environmentally friendly image of the supermarket. Nonetheless, they can still

be used for other goals, such as profit maximization, expanding the brand portfolio, offering a

larger choice of different products to consumers etcetera. Further research should be done to

find other factors on which supermarket managers can act to be seen as environmentally

friendly, to be able to follow the current pro-environmental trend.

The present study has also shown that consumers that are more involved with organic

products generally perceive a supermarket to be less eco-friendly than consumers that are not

as involved with organic products. For this reason, it would be advisable to focus more on

consumers who are less involved with organic products, which is the case for a large part of

consumers, as most consumers that buy organic products only buy organic products

occasionally, making them quite casual organic shoppers (Pearson & Henryks, 2008). As

environmental attributes are more important for consumers who are highly involved with

organic products (Schifferstein & Oude Ophuis, 1998), they may be less susceptible to pro-

environmental cues, and they may be more difficult to be convinced of the eco-friendly stance

of a supermarket.

For consumers who are not as involved with organic products, simple heuristic cues

such as the use of the colour green and natural imagery might be sufficient. For this reason, it

is important for supermarket managers to also investigate the effects that seemingly small

alterations of product packaging designs could have, as Steenis et al. (2017) have shown. This

could be an adequate manner in which to influence the large group of consumers who are not

highly involved with organic products, in order to imprint an eco-friendly image in their

minds.

As the results showed that there was a significant effect of the product category on

perceived eco-friendliness, it seems that certain product categories are more suitable for being

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46

used to influence the perception that consumers have regarding the environmental stance of

the supermarket. Further, more specific research would still be needed to investigate what

types of product categories would be more and less suitable for using organic and

environmental claims. In that way, supermarkets could essentially target specific product

groups to influence their environmental image, to be able to position themselves in such a

way that they are the first supermarket that comes to mind when consumers want to choose a

more pro-environmental supermarket for doing their groceries.

6.3 Limitations and future research

In this research, limitations were present that could be kept in mind for future research. First,

the position of the different organic and conventional products on the shelves in the

supermarket could be randomized, which was not done in the present study. As Gershoff &

Frels (2015) pointed out, there are many more actors that play a role in how environmental

cues are processed, such as the centrality of the product, or its colour. These factors were not

taken into account in the present study but might lead to valuable findings in the future. For

example, the present study could be replicated, while randomizing the position of the different

products on the supermarket shelves, including the product’s position as a covariate.

Furthermore, fictional products could be used, to be able to test different factors in

packaging that could play a role, such as the colour of the packaging, what environmental

cues are used, or even the brand name. Real-life products could also be adapted to test

differences in packaging and their effect on the attitudes that consumers have regarding the

products in an environmental context.

Also, to improve the realism of the study, real brands were used in the experiment.

Regarding the PLB products, it was therefore necessary to use the products of a specific

supermarket, in this case Albert Heijn. In order to reduce the complexity of the questionnaire

and the study, it was chosen not to use a second supermarket, as this would double the number

of groups and manipulations. In an ideal situation, it would be desirable to compare two or

even more supermarkets, as participants always have some level of prejudice against some

supermarkets, either consciously or unconsciously. If more different supermarkets could be

compared in a study, the results would be more generalizable. For this reason, in future

research it would be a good idea to include multiple supermarket chains, to reduce the effect

of personal opinions and attitudes consumers might have towards specific chains.

As a further direction for future research, new product categories could be researched.

In this study, after a manipulation check, yogurt and chocolate were perceived to be

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47

representative of utilitarian and hedonic products respectively, but more different products

should be tested in the future to expand the body of research, and to add more products to the

list of hedonic and utilitarian products. For hedonic and utilitarian products, most research

currently focuses on regular milk chocolate and milk respectively (Dhar & Wertbroch, 2000).

For this reason, in the present study dark chocolate with hazelnuts and yogurt were used. Even

though there was a significant direct effect of product category on perceived eco-friendliness,

more product categories should be compared in the future to be certain that this result still

stands and to see whether the yogurt and chocolate used in the present study are actually

representative of the entire utilitarian and hedonic categories.

Another limitation that could be improved in further research, is that the sample was

quite heavily skewed regarding the age of participants. This was the case because

convenience sampling was used, and the questionnaire was shared mainly among students. As

a result, 50% of the sample consisted of participants that were 25 years old or younger.

Therefore, it is not entirely possible to make generalizations about the entire population, even

though also many older participants took part in the questionnaire, and the sample was of

adequate size While there was no significant effect of age in the present study, past research

found that mainly the age group of consumers between the ages of 31 and 40 were highly

interested in organic products (Sivathanu, 2015; Kranjac, Vapa-Tankosi, Knežević, 2017),

while precisely this age group was the least present among participants. In future research, it

would therefore be interesting to look for a more evenly distributed sample regarding the age

of participants.

Furthermore, the research was only done among Dutch participants, which means that

only one general cultural background was researched. It would be interesting and highly

relevant to be able to compare the findings to other countries and cultures, for example to

other cultures, in which there is not as high as a focus on the environment. This could be the

case in developing countries, for example in Africa (Sulemana, James & Valdivia, 2016). For

this reason, future research could include participants from different cultures, to see whether

different dimensions, such as Hofstede’s cultural dimensions could be compared to see what

dimensions are significant predictors for differences between cultures (Hofstede, Hofstede &

Minkov, 2010).

Moreover, the design of the experiment could be changed, possibly leading to different

results. Because in the present study, each time only one organic PLB or NB product was

added to the selection that participants saw, it could be that the differences between the

different manipulations were small to such an extent that it had no impact on how participants

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perceived the shelves. Furthermore, some variables were not measured, that could play a

significant role, for example the extent to which participants already see a product as eco-

friendly, the attitude participants already had to the product categories etcetera.

Lastly, ANCOVA was used as the method of analysis, even though the dependent

variable was of an ordinal measurement level. Among researchers, there is no consensus

regarding this practice, as some deem it not statistically possible, while others deem it

adequate to use Likert scales as interval variables in this case. Possibly, ordinal logistic

regression would have led to different results. In the future, research could be done on how

this method would influence the results, and if it would alter results significantly, or lead to

improvements in interpretation and relevance.

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Vahie, A., & Paswan, A. (2006). Private label brand image: its relationship with store image

and national brand. International Journal of Retail & Distribution Management.

Van Doorn, J., & Verhoef, P. C. (2015). Drivers of and barriers to organic purchase

behavior. Journal of Retailing, 91(3), 436-450.

Van Doorn, J., & Verhoef, P. C. (2011). Willingness to pay for organic products: Differences

between virtue and vice foods. International Journal of Research in Marketing, 28(3),

167-180.

Vecchio, R., Van Loo, E. J., & Annunziata, A. (2016). Consumers' willingness to pay for

conventional, organic and functional yogurt: evidence from experimental

auctions. International Journal of Consumer Studies, 40(3), 368-378.

VectorStock (n.d.). Empty store shelves showcase supermarket vector image.

https://cdn4.vectorstock.com/i/1000x1000/12/53/empty-store-shelves-showcase

supermarket-vector-18071253.jpg

Voss, Kevin E., Eric R. Spangenberg, and Bianca Grohmann (2003), “Measuring the Hedonic

and Utilitarian Dimensions of Consumer Attitude,” JMR, 40 (August), 310-320.

VSNU. (2014). The Netherlands Code of Conduct for Academic Practice [PDF]. The Hague:

Association of Universities in the Netherlands.

Wang, W., & Korschun, D. (2015). Spillover of social responsibility associations in a brand

portfolio. Journal of Product & Brand Management.

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Wang, L., Wang, J., & Huo, X. (2019). Consumer’s willingness to pay a premium for organic

fruits in China: A double-hurdle analysis. International Journal of Environmental

Research and Public Health, 16(1), 126.

Weatherell, C.; Tregear, A.; Allison, J. In search of the concerned consumer: UK public

perceptions of food, farming and buying local. J. Rural Stud. 2003, 19, 233–244.

Williams, R. A. (2020). Ordinal independent variables. SAGE Publications Limited.

Zaichkowsky, J. L. (1994). The personal involvement inventory: Reduction, revision, and

application to advertising. Journal of Advertising, 23(4), 59-70.

Zeithaml, V.A. (1988), “Consumer perceptions of price, quality and value: a means-end

model and synthesis of evidence”, Journal of Marketing, Vol. 52, July, pp. 2-22.

Zumbo, B. D., & Zimmerman, D. W. (1993). Is the selection of statistical methods governed

by level of measurement?. Canadian Psychology/Psychologie canadienne, 34(4), 390.

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59

Appendices

Appendix A: Questionnaire

Q2 Beste meneer/mevrouw,

Hartelijk dank voor uw deelname aan dit onderzoek! Mijn naam is Guus van den Munckhof,

masterstudent Marketing aan de Radboud Universiteit in Nijmegen. Het doel van dit onderzoek en

deze master thesis is om erachter te komen welke aspecten een invloed hebben op de mate waarin een

supermarkt als milieuvriendelijk wordt gezien.

Het invullen van de enquête duurt ongeveer 5 minuten. Deelname is geheel vrijwillig en anoniem, en

u kunt op ieder gewenst moment stoppen met het invullen van de enquête. Uw gegevens worden

uitsluitend gebruikt voor dit onderzoek. U kunt te allen tijde uw deelname stoppen door de vragenlijst

niet verder in te vullen en deze browser af te sluiten. Uw persoonlijke informatie zal dan niet worden

opgeslagen.

Door naar de volgende pagina te gaan bevestigt u dat u 18 jaar of ouder bent, en dat uw gegevens

mogen worden gebruikt voor dit onderzoek.

Hartelijk dank voor uw deelname!

Q53 Op de volgende pagina ziet u een afbeelding van een schap in een supermarkt. Hierna wordt u

gevraagd om te beoordelen hoe milieuvriendelijk de desbetreffende winkel is. Hierbij is het belangrijk

te vermelden dat het niet gaat om uw kennis en mening over bestaande supermarkten, en dat u bij het

bepalen van uw antwoord puur afgaat op het schap dat u voor u ziet.

Page 60: Master thesis Green retailing: the spillover-effect of

60

Manipulation 1

Figure 2: Manipulation 1, not containing organic products, for the utilitarian product category

(VectorStock, n.d.; Albert Heijn, n.d.c.; n.d.d.; Deen Supermarkten, n.d.a.; n.d.b.)

Q12 Geef aan in welke mate u het eens bent met de volgende stellingen:

Helemaal

mee oneens

Gedeeltelijk

mee oneens Neutraal

Gedeeltelijk

mee eens

Helemaal

mee eens

Dit is een

milieuvriendelijke

winkel o o o o o Consumenten doen

aankopen bij deze

winkel vanwege de

milieuvriendelijkheid

van de winkel

o o o o o

De winkel is goed

ingeburgerd op het

gebied van

milieukwesties o o o o o

De winkel is de beste

maatstaf op het

gebied van

milieuverplichtingen o o o o o

De winkel is

succesvol op het

gebied van

milieuprestaties o o o o o

Page 61: Master thesis Green retailing: the spillover-effect of

61

Q22 Hierna volgen nog enkele vragen over de productcategorie die u zojuist heeft gezien. Bij deze

vragen is het belangrijk dat u de gehele productcategorie in gedachte neemt, los van dit onderzoek en

los van het aspect "milieuvriendelijkheid".

Q45 Voor mij is de productcategorie yoghurt:

1 2 3 4 5

Niet leuk o o o o o Leuk

Saai o o o o o Spannend

Niet heerlijk o o o o o Heerlijk

Opwindend o o o o o Niet

opwindend

Onaangenaam o o o o o Aangenaam

Q46

1 2 3 4 5

Niet

effectief o o o o o Effectief

Niet nuttig o o o o o Nuttig

Niet

functioneel o o o o o Functioneel

Nodig o o o o o Onnodig

Onpraktisch o o o o o Praktisch

Q47 Hierna volgen nog enkele vragen over biologische producten in het algemeen.

Q9 Biologische producten zijn voor mij...

Page 62: Master thesis Green retailing: the spillover-effect of

62

1 2 3 4 5 6 7

Onbelangrijk o o o o o o o Belangrijk

Irrelevant o o o o o o o Relevant

Betekenisloos o o o o o o o Betekenisvol

Waardeloos o o o o o o o Waardevol

Interessant o o o o o o o Saai

Niet spannend o o o o o o o Spannend

Onaantrekkelijk o o o o o o o Aantrekkelijk

Niet nodig o o o o o o o Nodig

Page 63: Master thesis Green retailing: the spillover-effect of

63

Q20 Wat is uw leeftijd?

________________________________________________________________

Q19 Wat is uw geslacht?

o Man

o Vrouw

o Anders

Q10 Wat is uw hoogst afgeronde opleiding?

o Basisonderwijs

o Voortgezet Onderwijs

o MBO

o HBO

o WO Bachelor

o WO Master

Q35 Hartelijk dank voor uw deelname aan dit onderzoek. Voor vragen kunt u mij per mail bereiken

via [email protected]

Page 64: Master thesis Green retailing: the spillover-effect of

64

Manipulation 2

Figure 3: Manipulation 2, containing an organic PLB, for the utilitarian product category

(VectorStock, n.d.; Albert Heijn, n.d.c.; n.d.d.; n.d.e.; Deen Supermarkten, n.d.a; n.d.b.)

Q48 Geef aan in welke mate u het eens bent met de volgende stellingen:

Helemaal

mee oneens

Gedeeltelijk

mee oneens Neutraal

Gedeeltelijk

mee eens

Helemaal

mee eens

Dit is een

milieuvriendelijke

winkel o o o o o Consumenten doen

aankopen bij deze

winkel vanwege de

milieuvriendelijkheid

van de winkel

o o o o o

De winkel is goed

ingeburgerd op het

gebied van

milieukwesties o o o o o

De winkel is de beste

maatstaf op het

gebied van

milieuverplichtingen o o o o o

De winkel is

succesvol op het

gebied van

milieuprestaties o o o o o

Page 65: Master thesis Green retailing: the spillover-effect of

65

Q27 Hierna volgen nog enkele vragen over de productcategorie die u zojuist heeft gezien. Bij deze

vragen is het belangrijk dat u de gehele productcategorie in gedachten neemt, los van dit onderzoek en

los van het aspect "milieuvriendelijkheid".

Q43 Voor mij is de productcategorie yoghurt:

1 2 3 4 5

Niet leuk o o o o o Leuk

Saai o o o o o Spannend

Niet heerlijk o o o o o Heerlijk

Opwindend o o o o o Niet

opwindend

Onaangenaam o o o o o Aangenaam

Q44

1 2 3 4 5

Niet

effectief o o o o o Effectief

Niet nuttig o o o o o Nuttig

Niet

functioneel o o o o o Functioneel

Nodig o o o o o Onnodig

Onpraktisch o o o o o Praktisch

Page 66: Master thesis Green retailing: the spillover-effect of

66

Q47 Hierna volgen nog enkele vragen over biologische producten in het algemeen.

Q9 Biologische producten zijn voor mij...

1 2 3 4 5 6 7

Onbelangrijk o o o o o o o Belangrijk

Irrelevant o o o o o o o Relevant

Betekenisloos o o o o o o o Betekenisvol

Waardeloos o o o o o o o Waardevol

Interessant o o o o o o o Saai

Niet spannend o o o o o o o Spannend

Onaantrekkelijk o o o o o o o Aantrekkelijk

Niet nodig o o o o o o o Nodig

Page 67: Master thesis Green retailing: the spillover-effect of

67

Q20 Wat is uw leeftijd?

________________________________________________________________

Q19 Wat is uw geslacht?

o Man

o Vrouw

o Anders

Q10 Wat is uw hoogst afgeronde opleiding?

o Basisonderwijs

o Voortgezet Onderwijs

o MBO

o HBO

o WO Bachelor

o WO Master

Q35 Hartelijk dank voor uw deelname aan dit onderzoek. Voor vragen kunt u mij per mail bereiken

via [email protected]

Page 68: Master thesis Green retailing: the spillover-effect of

68

Manipulation 3

Figure 4: Manipulation 3, containing an organic NB, for the utilitarian product category

(VectorStock, n.d.; Albert Heijn, n.d.c.; n.d.d.; n.d.f.; Deen Supermarkten, n.d.a; n.d.b.

Q49 Geef aan in welke mate u het eens bent met de volgende stellingen:

Helemaal

mee oneens

Gedeeltelijk

mee oneens Neutraal

Gedeeltelijk

mee eens

Helemaal

mee eens

Dit is een

milieuvriendelijke

winkel o o o o o Consumenten doen

aankopen bij deze

winkel vanwege de

milieuvriendelijkheid

van de winkel

o o o o o

De winkel is goed

ingeburgerd op het

gebied van

milieukwesties o o o o o

De winkel is de beste

maatstaf op het

gebied van

milieuverplichtingen o o o o o

De winkel is

succesvol op het

gebied van

milieuprestaties o o o o o

Page 69: Master thesis Green retailing: the spillover-effect of

69

Q29 Hierna volgen nog enkele vragen over de productcategorie die u zojuist heeft gezien. Bij deze

vragen is het belangrijk dat u de gehele productcategorie in gedachte neemt, los van dit onderzoek en

los van het aspect "milieuvriendelijkheid".

Q41 Voor mij is de productcategorie yoghurt:

1 2 3 4 5

Niet leuk o o o o o Leuk

Saai o o o o o Spannend

Niet heerlijk o o o o o Heerlijk

Opwindend o o o o o Niet

opwindend

Onaangenaam o o o o o Aangenaam

Q42

1 2 3 4 5

Niet

effectief o o o o o Effectief

Niet nuttig o o o o o Nuttig

Niet

functioneel o o o o o Functioneel

Nodig o o o o o Onnodig

Onpraktisch o o o o o Praktisch

Q47 Hierna volgen nog enkele vragen over biologische producten in het algemeen.

Q9 Biologische producten zijn voor mij...

Page 70: Master thesis Green retailing: the spillover-effect of

70

1 2 3 4 5 6 7

Onbelangrijk o o o o o o o Belangrijk

Irrelevant o o o o o o o Relevant

Betekenisloos o o o o o o o Betekenisvol

Waardeloos o o o o o o o Waardevol

Interessant o o o o o o o Saai

Niet spannend o o o o o o o Spannend

Onaantrekkelijk o o o o o o o Aantrekkelijk

Niet nodig o o o o o o o Nodig

Page 71: Master thesis Green retailing: the spillover-effect of

71

Q20 Wat is uw leeftijd?

________________________________________________________________

Q19 Wat is uw geslacht?

o Man

o Vrouw

o Anders

Q10 Wat is uw hoogst afgeronde opleiding?

o Basisonderwijs

o Voortgezet Onderwijs

o MBO

o HBO

o WO Bachelor

o WO Master

Q35 Hartelijk dank voor uw deelname aan dit onderzoek. Voor vragen kunt u mij per mail bereiken

via [email protected]

Page 72: Master thesis Green retailing: the spillover-effect of

72

Manipulation 4

Figure 3: Manipulation 4, not containing organic products, for the hedonic product category

(VectorStock, n.d.; Albert Heijn, n.d.g.; n.d.h.; n.d.i.; n.d.j.)

Q50 Geef aan in welke mate u het eens bent met de volgende stellingen:

Helemaal

mee oneens

Gedeeltelijk

mee oneens Neutraal

Gedeeltelijk

mee eens

Helemaal

mee eens

Dit is een

milieuvriendelijke

winkel o o o o o Consumenten doen

aankopen bij deze

winkel vanwege de

milieuvriendelijkheid

van de winkel

o o o o o

De winkel is goed

ingeburgerd op het

gebied van

milieukwesties o o o o o

De winkel is de beste

maatstaf op het

gebied van

milieuverplichtingen o o o o o

De winkel is

succesvol op het

gebied van

milieuprestaties o o o o o

Page 73: Master thesis Green retailing: the spillover-effect of

73

Q30 Hierna volgen nog enkele vragen over de productcategorie die u zojuist heeft gezien. Bij deze

vragen is het belangrijk dat u de gehele productcategorie in gedachte neemt, los van dit onderzoek en

los van het aspect "milieuvriendelijkheid".

Q39 Voor mij is de productcategorie chocolade:

1 2 3 4 5

Niet leuk o o o o o Leuk

Saai o o o o o Spannend

Niet heerlijk o o o o o Heerlijk

Opwindend o o o o o Niet

opwindend

Onaangenaam o o o o o Aangenaam

Q40

1 2 3 4 5

Niet

effectief o o o o o Effectief

Niet nuttig o o o o o Nuttig

Niet

functioneel o o o o o Functioneel

Onnodig o o o o o Nodig

Praktisch o o o o o Onpraktisch

Page 74: Master thesis Green retailing: the spillover-effect of

74

Q47 Hierna volgen nog enkele vragen over biologische producten in het algemeen.

Q9 Biologische producten zijn voor mij...

1 2 3 4 5 6 7

Onbelangrijk o o o o o o o Belangrijk

Irrelevant o o o o o o o Relevant

Betekenisloos o o o o o o o Betekenisvol

Waardeloos o o o o o o o Waardevol

Interessant o o o o o o o Saai

Niet spannend o o o o o o o Spannend

Onaantrekkelijk o o o o o o o Aantrekkelijk

Niet nodig o o o o o o o Nodig

Page 75: Master thesis Green retailing: the spillover-effect of

75

Q20 Wat is uw leeftijd?

________________________________________________________________

Q19 Wat is uw geslacht?

o Man

o Vrouw

o Anders

Q10 Wat is uw hoogst afgeronde opleiding?

o Basisonderwijs

o Voortgezet Onderwijs

o MBO

o HBO

o WO Bachelor

o WO Master

Q35 Hartelijk dank voor uw deelname aan dit onderzoek. Voor vragen kunt u mij per mail bereiken

via [email protected]

Page 76: Master thesis Green retailing: the spillover-effect of

76

Manipulation 5

Figure 6: Manipulation 5, containing an organic NB, for the hedonic product category

(VectorStock, n.d.; Albert Heijn, n.d.g.; n.d.h.; n.d.i.; n.d.j.; n.d.k.)

Q51 Geef aan in welke mate u het eens bent met de volgende stellingen:

Helemaal

mee oneens

Gedeeltelijk

mee oneens Neutraal

Gedeeltelijk

mee eens

Helemaal

mee eens

Dit is een

milieuvriendelijke

winkel o o o o o Consumenten doen

aankopen bij deze

winkel vanwege de

milieuvriendelijkheid

van de winkel

o o o o o

De winkel is goed

ingeburgerd op het

gebied van

milieukwesties o o o o o

De winkel is de beste

maatstaf op het

gebied van

milieuverplichtingen o o o o o

De winkel is

succesvol op het

gebied van

milieuprestaties o o o o o

Page 77: Master thesis Green retailing: the spillover-effect of

77

Q31 Hierna volgen nog enkele vragen over de productcategorie die u zojuist heeft gezien. Bij deze

vragen is het belangrijk dat u de gehele productcategorie in gedachte neemt, los van dit onderzoek en

los van het aspect "milieuvriendelijkheid".

Q37 Voor mij is de productcategorie chocolade:

1 2 3 4 5

Niet leuk o o o o o Leuk

Saai o o o o o Spannend

Niet heerlijk o o o o o Heerlijk

Opwindend o o o o o Niet

opwindend

Onaangenaam o o o o o Aangenaam

Q38

1 2 3 4 5

Niet

effectief o o o o o Effectief

Niet nuttig o o o o o Nuttig

Niet

functioneel o o o o o Functioneel

Onnodig o o o o o Nodig

Praktisch o o o o o Onpraktisch

Q47 Hierna volgen nog enkele vragen over biologische producten in het algemeen.

Q9 Biologische producten zijn voor mij...

Page 78: Master thesis Green retailing: the spillover-effect of

78

1 2 3 4 5 6 7

Onbelangrijk o o o o o o o Belangrijk

Irrelevant o o o o o o o Relevant

Betekenisloos o o o o o o o Betekenisvol

Waardeloos o o o o o o o Waardevol

Interessant o o o o o o o Saai

Niet spannend o o o o o o o Spannend

Onaantrekkelijk o o o o o o o Aantrekkelijk

Niet nodig o o o o o o o Nodig

Page 79: Master thesis Green retailing: the spillover-effect of

79

Q20 Wat is uw leeftijd?

________________________________________________________________

Q19 Wat is uw geslacht?

o Man

o Vrouw

o Anders

Q10 Wat is uw hoogst afgeronde opleiding?

o Basisonderwijs

o Voortgezet Onderwijs

o MBO

o HBO

o WO Bachelor

o WO Master

Q35 Hartelijk dank voor uw deelname aan dit onderzoek. Voor vragen kunt u mij per mail bereiken

via [email protected]

Page 80: Master thesis Green retailing: the spillover-effect of

80

Manipulation 6

Figure 7: Manipulation 6, containing an organic PLB, for the hedonic product category

(VectorStock, n.d.; Albert Heijn, n.d.g.; n.d.h.; n.d.i.; n.d.j.; n.d.l.)

Q52 Geef aan in welke mate u het eens bent met de volgende stellingen:

Helemaal

mee oneens

Gedeeltelijk

mee oneens Neutraal

Gedeeltelijk

mee eens

Helemaal

mee eens

Dit is een

milieuvriendelijke

winkel o o o o o Consumenten doen

aankopen bij deze

winkel vanwege de

milieuvriendelijkheid

van de winkel

o o o o o

De winkel is goed

ingeburgerd op het

gebied van

milieukwesties o o o o o

De winkel is de beste

maatstaf op het

gebied van

milieuverplichtingen o o o o o

De winkel is

succesvol op het

gebied van

milieuprestaties o o o o o

Page 81: Master thesis Green retailing: the spillover-effect of

81

Q32 Hierna volgen nog enkele vragen over de productcategorie die u zojuist heeft gezien. Bij deze

vragen is het belangrijk dat u de gehele productcategorie in gedachte neemt, los van dit onderzoek en

los van het aspect "milieuvriendelijkheid".

Q33 Voor mij is de productcategorie chocolade:

1 2 3 4 5

Niet leuk o o o o o Leuk

Saai o o o o o Spannend

Niet heerlijk o o o o o Heerlijk

Opwindend o o o o o Niet

opwindend

Onaangenaam o o o o o Aangenaam

Q34

1 2 3 4 5

Niet

effectief o o o o o Effectief

Niet nuttig o o o o o Nuttig

Niet

functioneel o o o o o Functioneel

Onnodig o o o o o Nodig

Praktisch o o o o o Onpraktisch

Q47 Hierna volgen nog enkele vragen over biologische producten in het algemeen.

Q9 Biologische producten zijn voor mij...

Page 82: Master thesis Green retailing: the spillover-effect of

82

1 2 3 4 5 6 7

Onbelangrijk o o o o o o o Belangrijk

Irrelevant o o o o o o o Relevant

Betekenisloos o o o o o o o Betekenisvol

Waardeloos o o o o o o o Waardevol

Interessant o o o o o o o Saai

Niet spannend o o o o o o o Spannend

Onaantrekkelijk o o o o o o o Aantrekkelijk

Niet nodig o o o o o o o Nodig

Page 83: Master thesis Green retailing: the spillover-effect of

83

Q20 Wat is uw leeftijd?

________________________________________________________________

Q19 Wat is uw geslacht?

o Man

o Vrouw

o Anders

Q10 Wat is uw hoogst afgeronde opleiding?

o Basisonderwijs

o Voortgezet Onderwijs

o MBO

o HBO

o WO Bachelor

o WO Master

Q35 Hartelijk dank voor uw deelname aan dit onderzoek. Voor vragen kunt u mij per mail bereiken

via [email protected]

Page 84: Master thesis Green retailing: the spillover-effect of

84

Appendix B: Original scales and translation

Table 11: original scales, translation and adaption for the variable perceived eco-friendliness

Perceived eco-friendliness (Punyatoya,

2014)

Translation and adaptation

To me, this is an environment-friendly

brand.

Dit is een milieuvriendelijke winkel.

I do think that consumers buy this brand

because of its environment-friendliness.

Consumenten doen aankopen bij deze

winkel vanwege de

milieuvriendelijkheid van de winkel.

I do think that the brand is well

established about environmental

concerns.

De winkel is goed ingeburgerd op het

gebied van milieukwesties.

I feel that the brand is the best benchmark

of environmental commitments.

De winkel is de beste maatstaf op het

gebied van milieuverplichtingen.

I feel that the brand is successful about

environmental performance.

De winkel is succesvol op het gebied

van milieuprestaties.

Table 12: original scales, translation and adaption for the variable organic involvement

Organic involvement (Zaichkowsky,

1994)

Translation and adaptation

To me, organic products are… Biologische producten zijn voor mij…

Unimportant / important Onbelangrijk/ belangrijk

Irrelevant / relevant Irrelevant/ relevant

Means nothing to me / means a lot to me Betekenisloos/ betekenisvol

Worthless / valuable Waardeloos/ waardevol

Boring/ interesting Saai/ interessant

Unexciting/ exciting Niet spannend/ spannend

Unappealing/ appealing Onaantrekkelijk/ aantrekkelijk

Not needed/ needed Niet nodig/ nodig

Page 85: Master thesis Green retailing: the spillover-effect of

85

Table 13: original scales, translation and adaption for the hedonic value of the product

categories

Hedonic value (Voss et al., 2003) Translation and adaptation

To me, the product category of yogurt/

chocolate is…

Voor mij is de productcategorie

yoghurt/ chocolade…

Not fun/ fun Niet leuk/ leuk

Dull/ exciting Saai/ spannend

Not delightful/ delightful Niet heerlijk/ heerlijk

Not thrilling/ thrilling Niet opwindend/ opwindend

Unenjoyable/ enjoyable Onaangenaam/ aangenaam

Table 14: original scales, translation and adaption for the utilitarian value of the product

categories

Utilitarian value (Voss et al., 2003) Translation and adaptation

To me, the product category of yogurt/

chocolate is…

Voor mij is de productcategorie

yoghurt/ chocolade…

Not effective/ effective Niet effectief/ effectief

Not helpful/ helpful Niet nuttig/ nuttig

Not functional/ functional Niet functioneel/ functioneel

Not necessary/ necessary Onnodig/ nodig

Not practical/ practical Onpraktisch/ praktisch

Page 86: Master thesis Green retailing: the spillover-effect of

86

Appendix C: Manipulation check

Q1 Bedankt voor uw deelname. In deze enquête wordt getest of consumenten verschillende types

producten correct herkennen, en hoe zij ze beoordelen. Voordat de enquête begint, is het belangrijk dat

u de volgende definities leest.

Biologische voedingsproducten: Bij het produceren van biologische voedingsproducten wordt zo

veel mogelijk rekening gehouden met milieu- en dierenwelzijn. Zo worden geen chemische

bestrijdingsmiddelen gebruikt, wordt er geen gebruik gemaakt van genetische modificatie, en krijgt

vee betere leefomstandigheden dan normaal gebruikelijk is.

Huismerk: Een winkelmerk dat de naam van de desbetreffende winkelketen draagt. Het kan gezien

worden als het “eigen merk” van deze winkel, waaronder het verschillende types producten verkoopt.

A-merk: een merk dat door een bepaalde producent wordt geproduceerd, en (inter)nationaal wordt

verkocht in verschillende winkelketens, onder één merknaam. In tegenstelling tot een huismerk wordt

een A-merk door de producent verkocht aan retailers. A-merken hebben over het algemeen een grote

naamsbekendheid en een goede reputatie.

Hierna krijgt u 12 verschillende producten te zien uit twee verschillende productcategorieën. U wordt

gevraagd aan te geven wat voor type merk u herkent: huismerk of A-merk, en biologisch of niet-

biologisch. Verder krijgt u nog een aantal vragen over de productcategorie.

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87

Q11

Figure 8: Non-organic yogurt from the NB Campina

(Albert Heijn, n.d.c.)

Q8 Dit merk is een...

o Huismerk

o A-merk

o Weet niet

Q9 Dit product is...

o Biologisch

o Niet-biologisch

o Weet niet

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88

Q14

Figure 9: Non-organic chocolate from the NB Ritter Sport

(Albert Heijn, n.d.g.)

Q12 Dit merk is een...

o Huismerk

o A-merk

o Weet niet

Q13 Dit product is...

o Biologisch

o Niet-biologisch

o Weet niet

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89

Q15

Figure 10: Organic yogurt from the NB Arla

(Albert Heijn, n.d.f.)

Q16 Dit merk is een...

o Huismerk

o A-merk

o Weet niet

Q17 Dit product is...

o Biologisch

o Niet-biologisch

o Weet niet

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90

Q18

Figure 11: Non-organic chocolate from the NB Côte d’Or

(Albert Heijn, n.d.h.)

Q19 Dit merk is een...

o Huismerk

o A-merk

o Weet niet

Q20 Dit product is...

o Biologisch

o Niet-biologisch

o Weet niet

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91

Q22

Figure 12: Non-organic yogurt from the AH PLB

(Albert Heijn, n.d.d.)

Q23 Dit merk is een...

o Huismerk

o A-merk

o Weet niet

Q24 Dit product is...

o Biologisch

o Niet-biologisch

o Weet niet

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92

Q25

Figure 13: Non-organic chocolate from the NB Verkade

(Albert Heijn, n.d.j.)

Q26 Dit merk is een...

o Huismerk

o A-merk

o Weet niet

Q27 Dit product is...

o Biologisch

o Niet-biologisch

o Weet niet

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93

Q28

Figure 14: Organic yogurt from the AH Bio PLB

(Albert Heijn, n.d.e.)

Q29 Dit merk is een...

o Huismerk

o A-merk

o Weet niet

Q30 Dit product is...

o Biologisch

o Niet-biologisch

o Weet niet

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94

Q31

Figure 15: Organic chocolate from the AH Bio PLB

(Albert Heijn, n.d.l.)

Q32 Dit merk is een...

o Huismerk

o A-Merk

o Weet niet

Q33 Dit product is...

o Biologisch

o Niet-biologisch

o Weet niet

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95

Q34

Figure 16: Non-organic yogurt from the NB Melkunie

(Deen Supermarkten, n.d.b.)

Q35 Dit merk is een...

o Huismerk

o A-merk

o Weet niet

Q36 Dit product is...

o Biologisch

o Niet-biologisch

o Weet niet

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96

Q37

Figure 17: Organic chocolate from the NB Côte d’Or

(Albert Heijn, n.d.k.)

Q38 Dit merk is een...

o Huismerk

o A-merk

o Weet niet

Q39 Dit product is...

o Biologisch

o Niet-biologisch

o Weet niet

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97

Q41

Figure 18: Non-organic yogurt from the NB Melkan

(Deen Supermarkten, n.d.a.)

Q42 Dit merk is een...

o Huismerk

o A-merk

o Weet niet

Q43 Dit product is...

o Biologisch

o Niet-biologisch

o Weet niet

Page 98: Master thesis Green retailing: the spillover-effect of

98

Q40

Figure 19: Non-organic chocolate from the AH PLB

(Albert Heijn, n.d.i.)

Q44 Dit merk is een...

o Huismerk

o A-merk

o Weet niet

Q45 Dit product is...

o Biologisch

o Niet-biologisch

o Weet niet

Q46 Tot slot volgen nog een paar vragen over de productcategorieën, yoghurt en chocolade. Het is de

bedoeling dat u aangeeft hoe u de twee productcategorieën beoordeelt.

Page 99: Master thesis Green retailing: the spillover-effect of

99

Q47 Voor mij is de productcategorie chocolade:

1 2 3 4 5

Niet leuk o o o o o Leuk

Saai o o o o o Spannend

Heerlijk o o o o o Niet heerlijk

Niet

opwindend o o o o o Opwindend

Onaangenaam o o o o o Aangenaam

Q48 Voor mij is de productcategorie chocolade:

1 2 3 4 5

Effectief o o o o o Niet

effectief

Nuttig o o o o o Niet nuttig

Niet

functioneel o o o o o Functioneel

Nodig o o o o o Onnodig

Praktisch o o o o o Onpraktisch

Page 100: Master thesis Green retailing: the spillover-effect of

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Q49 Voor mij is de productcategorie yoghurt:

1 2 3 4 5

Effectief o o o o o Niet

effectief

Niet nuttig o o o o o Nuttig

Niet

functioneel o o o o o Functioneel

Onnodig o o o o o Nodig

Onpraktisch o o o o o Praktisch

Q50 Voor mij is de productcategorie yoghurt:

1 2 3 4 5

Niet leuk o o o o o Leuk

Saai o o o o o Spannend

Niet heerlijk o o o o o Heerlijk

Opwindend o o o o o Niet

opwindend

Onaangenaam o o o o o Aangenaam

Q51 Hartelijk dank voor uw deelname!

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Appendix D: Factor Analysis

Table 15: KMO and Bartlett’s Test

Kaiser-Meyer-Olkin Measure of Sampling

Adequacy.

,810

Bartlett's Test of

Sphericity

Approx. Chi-Square 1886,039

df 210

Sig. ,000

Table 16: Total variance explained by factors

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Table 17: Pattern matrix

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Appendix E: Manipulation check results

Table 18: Manipulation check results

Product Is the brand organic or

not?

%

Correct

Is this a PLB or an

NB?

%

Correct

Campina: non-

organic NB

(Yogurt)

Correct: 7 (Non-organic)

Incorrect: 4 (Organic)

Don’t know: 1

58.3% Correct: 12 (NB) 100%

Ritter Sport: non-

organic NB

(Chocolate)

Correct: 10 (Non-organic)

Don’t know: 2

83.3% Correct: 11 (NB)

Don’t know: 1

91.7%

Arla: Organic NB

(Yogurt)

Correct: 12 (Organic)

100% Correct: 10 (NB)

Don’t know: 2

83.3%

Côte d’Or: Non-

organic NB

(Chocolate)

Correct: 8 (Non-organic)

Incorrect: 2 (Organic)

Don’t know: 2

66.7% Correct: 12 (NB) 100%

AH: Non-organic

PLB (Yogurt)

Correct: 5 (Non-organic)

Incorrect: 4 (Organic)

Don’t know: 3

41.7% Correct: 12 (PLB) 100%

Verkade: Non-

organic NB

(Chocolate)

Correct: 9 (Non-organic)

Don’t know: 3

75% Correct: 12 (NB) 100%

AH Bio: Organic

PLB (Yogurt)

Correct: 12 (Organic) 100% Correct: 12 (PLB) 100%

AH Bio: Organic

PLB (Chocolate)

Correct: 11 (Organic)

Incorrect: 1 (Non-organic)

91.7% Correct: 12 (PLB) 100%

MelkUnie: Non-

organic NB

(Yogurt)

Correct: 8 (Non-organic)

Incorrect: 1 (Organic)

Don’t know: 3

66.7% Correct: 10 (NB)

Incorrect: 1 (PLB)

Don’t know: 1

83.3%

Côte d’Or:

Organic NB

(Chocolate)

Correct: 11 (Organic)

Incorrect: 1 (Non-organic)

91.7% Correct: 12 (NB) 100%

Melkan: Non-

organic NB

(Yogurt)

Correct: 8 (Non-organic)

Incorrect: 2 (Organic)

Don’t know: 2

66.7% Correct: 10 (NB)

Incorrect: 2 (PLB)

83.3%

AH: Non-organic

PLB (chocolate)

Correct: 11 (Non-organic)

Don’t know: 1

91.7% Correct: 11 (PLB)

Incorrect: 1 (NB)

91.7%

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Table 19: Hedonic score of product categories in final questionnaire

ProductCategory N Mean

Std.

Deviation

Std. Error

Mean

HedonicScore Yogurt 82 3,5244 1,01299 ,11187

Chocolate 76 3,9912 ,69703 ,07995

Table 20: Independent samples t-test of hedonic value of product categories

Table 21: Utilitarian score of product categories in final questionnaire

Group Statistics

ProductCategory N Mean

Std.

Deviation

Std. Error

Mean

UtilitarianScore Yogurt 82 3,4902 ,82800 ,09144

Chocolate 76 2,9526 ,79187 ,09083

Table 22: Independent samples t-test of utilitarian value of product categories

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Appendix F: ANCOVA assumptions

Table 23: Assumption of normality for the variable type of brand

Table 24: Assumption of normality for the variable product category

Table 25: Assumption of normality for the variable gender

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Table 26: Assumption of equality of variances

Table 27: Assumption of linearity

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Table 28: Assumption of homogeneity of variances, second iteration

Table 29: Assumption of independence of factors and covariate for the factor type of brand

Table 30: Assumption of independence of factors and covariate for the factor product

category

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Table 31: Assumption of homogeneity of regression slopes

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Appendix G: ANCOVA

Table 32: Estimates for both product categories

Table 33: Pairwise comparisons for both product categories

Table 34: Estimates for the three types of brands

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Table 35: Pairwise comparisons for the three types of brands

Table 36: Parameter estimates of the ANCOVA results