journal of macromarketing … · 2011. 10. 14. · 172 journal of macromarketing 30(2) 172...

16
http://jmk.sagepub.com/ Journal of Macromarketing http://jmk.sagepub.com/content/30/2/171 The online version of this article can be found at: DOI: 10.1177/0276146710361926 2010 30: 171 Journal of Macromarketing John Thøgersen Country Differences in Sustainable Consumption: The Case of Organic Food Published by: http://www.sagepublications.com On behalf of: Macromarketing Society can be found at: Journal of Macromarketing Additional services and information for http://jmk.sagepub.com/cgi/alerts Email Alerts: http://jmk.sagepub.com/subscriptions Subscriptions: http://www.sagepub.com/journalsReprints.nav Reprints: http://www.sagepub.com/journalsPermissions.nav Permissions: http://jmk.sagepub.com/content/30/2/171.refs.html Citations: at Avans Hogeschool on September 16, 2011 jmk.sagepub.com Downloaded from

Upload: others

Post on 20-Oct-2020

1 views

Category:

Documents


0 download

TRANSCRIPT

  • http://jmk.sagepub.com/Journal of Macromarketing

    http://jmk.sagepub.com/content/30/2/171The online version of this article can be found at:

    DOI: 10.1177/0276146710361926

    2010 30: 171Journal of MacromarketingJohn Thøgersen

    Country Differences in Sustainable Consumption: The Case of Organic Food

    Published by:

    http://www.sagepublications.com

    On behalf of:

    Macromarketing Society

    can be found at:Journal of MacromarketingAdditional services and information for

    http://jmk.sagepub.com/cgi/alertsEmail Alerts:

    http://jmk.sagepub.com/subscriptionsSubscriptions:

    http://www.sagepub.com/journalsReprints.navReprints:

    http://www.sagepub.com/journalsPermissions.navPermissions:

    http://jmk.sagepub.com/content/30/2/171.refs.htmlCitations:

    at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/http://jmk.sagepub.com/content/30/2/171http://www.sagepublications.comhttp://www.macromarketing.orghttp://jmk.sagepub.com/cgi/alertshttp://jmk.sagepub.com/subscriptionshttp://www.sagepub.com/journalsReprints.navhttp://www.sagepub.com/journalsPermissions.navhttp://jmk.sagepub.com/content/30/2/171.refs.htmlhttp://jmk.sagepub.com/

  • Country Differences in SustainableConsumption: The Case of Organic Food

    John Thøgersen1

    AbstractIn a sustainability perspective, consumption research has an unfortunate individualizing bias, which means that macro andstructural causes of unsustainable consumption tend to be ignored. Hence, a comprehensive model of determinants of thesustainability of consumption is developed and applied on a specific case: organic food consumption. The analyzed data are pub-lished research on why consumer purchase of organic food products differs between countries. As expected, organic food’s shareof total food consumption depends heavily on political regulation, including legal definitions and standards, financial support tofarmers, and a national labeling system. Other important structural factors are soil conditions, an effective and efficient distribu-tion system, and the size of the premium price demanded for organic food products. Macro factors such as the food culture andthe culture’s level of postmaterialism and environmental concern play an additional role. The evidence suggests that, together,macro and structural factors such as these are more, and probably considerably more, important for the sustainability of foodconsumption than are individual-level attitudinal variables.

    Keywordssustainable consumption, organic food consumption, country differences, Europe

    There is a growing consensus in society that, ‘‘altering

    consumption patterns’’ is ‘‘one of humanity’s greatest chal-

    lenges in the quest for environmentally sound and sustainable

    development’’ (Agenda 21, the action document from the Rio

    Summit in 1992, see Sitarz 1994). ‘‘Sustainable’’ here refers

    to a level and pattern of consumption, which meets the needs

    of the present without compromising the ability of future

    generations to meet their own needs (World Commission on

    Environment Development 1987). Some of the most serious

    environmental challenges currently facing humanity are related

    to our unsustainable consumption patterns and lifestyles

    (Durning 1992; European Environment Agency 2005; Sitarz

    1994; Stern 1992; United Nations 2002). The problem is not

    limited to marginal areas of consumption (e.g., the consump-

    tion of luxuries), but extends to the way industrial and emer-

    ging societies provide basic necessities, such as food, shelter,

    and transportation to its citizens (Durning 1992; European

    Environment Agency 2005).

    Despite the broad international consensus about the need for

    action, progress toward sustainable consumption is disappoint-

    ingly slow. For instance, in a report issued by United Nations

    Secretary-General Kofi Annan in preparation for the 2002

    Johannesburg Summit, it was concluded that ‘‘Progress toward

    the goals established at Rio has been slower than anticipated

    and in some respects conditions are worse than they were

    10 years ago.’’ Apparently, consumer-citizens, the business

    community, and their elected governments in industrial and

    emerging countries strive less hard at achieving sustainable

    lifestyles than is desired by the global community and than is

    in their collective long-term interest.

    When discussing the problem of unsustainable consump-

    tion, there is a perhaps natural tendency to focus on individual

    consumers’ decision making and behavior. However, it has

    been convincingly argued that the attitudes, preferences, and

    choices of individual consumers are less important for the

    sustainability of private consumption than are the macro and

    structural conditions that frame and constrain individual

    choices (e.g., Etzioni 2009; Kilbourne, McDonagh, and

    Prothero 1997; Thøgersen 2005b). Still, perhaps, because the

    activities and motivations of individual consumers are more

    obtrusive than the effects of macro and structural factors, both

    research and policy in the area of sustainable consumption have

    an unfortunate individualistic and individualizing bias (e.g.,

    Alfredsson 2004; Schaefer and Crane 2005).

    To capture the importance of macro and sociostructural fac-

    tors for sustainable consumption, the research focus needs to be

    broad enough to capture variation in relevant macro and/or

    1 Aarhus School of Business, University of Aarhus, Denmark

    Corresponding Author:

    John Thøgersen, Aarhus School of Business, University of Aarhus, Department

    of Marketing and Statistics, Haslegaardsvej 10, DK-8210 Aarhus, Denmark.

    Email: [email protected]

    Journal of Macromarketing30(2) 171-185ª The Author(s) 2010Reprints and permission:sagepub.com/journalsPermissions.navDOI: 10.1177/0276146710361926http://jmk.sagepub.com

    171 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • sociostructural factors. In practice, this usually means a cross-

    national focus (although large and heterogeneous nation states

    may sometimes contain sufficient heterogeneity within

    national borders). When attempting to explain differences and

    similarities between countries, macro- and structural- rather

    than individual-level factors become salient. In single-

    country studies, these factors tend to be ignored because they

    constitute the shared context and therefore cannot account for

    variation in (individual-level) behavior.

    In this article, a comparative, cross-national perspective is

    used as a means to focus attention to macro and sociostructural

    factors influencing the sustainability of the consumption

    pattern. By shifting the focus from individual-level factors to

    important macro and structural factors, a better foundation for

    effective sustainable consumption strategies can be created.

    The objective of the article is to demonstrate the crucial

    importance of macro and structural factors for (international)

    variations in the sustainability of private consumption. For this

    purpose, a comprehensive conceptual model for organizing and

    integrating important micro and macro determinants of the

    environmental sustainability of private consumption is (1)

    developed and (2) applied on an environmentally important

    area of consumption: private food consumption.

    Food Consumption

    Food consumption is obviously an important and unavoidable

    part of everyday consumption. In addition, it is one of the areas

    of private consumption that are most important for environ-

    mental sustainability (European Environment Agency 2005).

    It has been estimated that approximately one third of house-

    holds’ total environmental impact is related to food and drink

    consumption (Danish Environmental Protection Agency 2002).

    Food consumption is a broad and diverse field and the envi-

    ronmental sustainability of private food consumption depends

    on several variables, such as the amount of beef in the diet, the

    production system (e.g., organic vs. conventional), and how

    and how far the food products are transported. Extant research

    suggests that currently the most effective ways that affluent

    consumers can increase the sustainability of their food con-

    sumption are to (1) reduce the amount of meat, especially beef,

    in their diet, (2) buy organic instead of conventionally

    produced food products, and (3) avoid food products trans-

    ported by airplane (e.g., Carlsson-Kanyama and Gonzalez

    2009; Dabbert, Haring, Zanoli 2004).1 Due to space limita-

    tions, this article focuses on only one of these important ways

    to increase the sustainability of food consumption: choosing

    organic instead of conventional food. To illustrate the

    importance of macro and structural factors for the environmen-

    tal sustainability of private consumption, research on the

    causes of international variations in organic food consumption

    is reviewed.

    From its beginning, organic farming has rejected the

    chemical-based farming techniques of mainstream agriculture

    (Niggli 2007). This placed it in opposition to the dominant

    paradigm of agricultural policy in industrialized countries

    (Michelsen 2001a), which ‘‘emphasized technological progress

    as a means of improving farm incomes and securing food

    supplies’’ (Padel and Lampkin 2007, 95). The change in attitudes

    toward organic farming at the political level, first in Europe and

    later in North America and Japan, came in response to growing

    consumer interest in organic products combined with serious

    problems caused by the dominant technological paradigm, such

    as overproduction, environmental pollution, food scares, and the

    depopulation of rural areas (e.g., Lockeretz 2007a; Padel and

    Lampkin 2007). Hence, organic farming challenges consumers

    to consider not only the private utility of the food they buy but

    also whether it is produced in an acceptable way.

    Certified organic food products are produced with consider-

    ation for the environment and for animal welfare, controlled

    and certified by independent control organizations and usually

    labeled with an organic label to assist consumers in the super-

    market.2 Certified organic food products have experienced a

    remarkable increase in market shares in most industrialized

    countries in the last three decades (Aschemann et al. 2007;

    Richter et al. 2007). However, organic food has been much

    more successful in some than in other countries (see figure 1).

    Why is that?

    To answer why much more organic food is consumed in

    some than in other countries, cross-national research on the

    purchase of organic food products is compiled and reviewed.

    Because there are few comparative studies on organic food

    consumption involving countries outside Europe, the

    geographical coverage of the analyzed evidence is, by and

    large, limited to Europe. This reduces the complexity of the dis-

    cussion but also the variation in macro and structural factors.

    Hence, it is likely that the currently available evidence tends

    to underestimate (rather than overestimate) the impact of

    macro and structural factors on organic food consumption.

    In the following, the author will first give a brief status

    regarding organic food consumption (primarily) in Europe.

    Next, the author will present a comprehensive conceptual

    model to organize the factors and influences, which can explain

    global differences in consumption patterns and specifically in

    Figure 1. Market shares of organic food as percentage of the totalfood market in selected European countries in 2006. Source: Padelet al. (2008).

    172 Journal of Macromarketing 30(2)

    172 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • organic food consumption. This model is then used to structure

    the review of research on international differences in organic

    food consumption. Finally, the discussion of the evidence is

    summarized and possible avenues for future research are

    suggested.

    Organic Food Consumption in Europe

    Overall, the organic trend is weaker in the east and south of

    Europe (with the partial exception of Italy) than in the north-

    west. However, organic food consumption cannot be reduced

    to a northwest phenomenon. According to the best available

    international statistics, the per capita consumption of organic

    food in Italy is higher than in many countries in the northwest

    (Dabbert, Haring, Zanoli 2004; Padel et al. 2008), and the mar-

    ket shares of organic food as percentage of the total food mar-

    ket differ substantively between countries in the northwest as

    well (see figure 1).3

    There is a large and growing literature on the demand for

    organic (e.g., Fotopoulos and Krystallis 2002; Harper and

    Makatouni 2002; Hughner et al. 2007; Thøgersen 2009; Ver-

    meir and Verbeke 2006) and other types of ethical food prod-

    ucts (e.g., de Ferran and Grunert 2007; De Pelsmacker,

    Driesen, Rayp 2005; Doran 2009; Steinrücken and Jaenichen

    2007). However, there has been little research aiming to sys-

    tematically figure out why the tendency to buy organic (or

    other types of ethical) food products is stronger in some than

    in other countries (Daugbjerg and Halpin 2008). As previously

    mentioned, the individualizing bias in this research area is

    unfortunate, because it is likely to lead to underestimating the

    importance of macro and structural factors and, hence, to erro-

    neous inferences about the causes of unsustainable consump-

    tion patterns (individual choices vs. structural characteristics

    of the context) and about the most effective ways of intervening

    to promote more sustainable consumption (appealing to indi-

    vidual responsibility vs. structural changes). The problem is

    illustrated by a survey study of consumer acceptance of organic

    food in eight European countries (Thøgersen 2009). The study

    found little difference in what motivates consumers to buy

    organic food between countries, but the relationship between

    consumers’ intention to buy and actual (self-reported) buying

    of organic food was significantly weaker in the Mediterranean

    countries than in the northern European countries in the sam-

    ple. It is generally realized in social psychological research that

    the relationship between behavioral intentions and behavior

    depends on consumers having the requested abilities and

    resources and on the absence of unforeseen events blocking the

    act (Ajzen and Fishbein 1980; Fishbein and Ajzen 1975), but

    since abilities and opportunities, to a large extent, are situation

    specific (Belk 1975), they are often not or only vaguely speci-

    fied in individual-level research (such as Thøgersen 2009).

    The relatively few multicountry studies or reports that pro-

    pose possible pieces to the puzzle, to be reviewed in more detail

    in the following, are summarized in table 1. These main sources

    were supplemented by other available sources, including a cou-

    ple of excellent overview books on the historical development

    in organic farming worldwide, including the development in

    political regulation and the development of the organic market,

    written by groups of researchers with many years of experience

    in this field (Dabbert, Haring, Zanoli 2004; Lockeretz 2007b).

    For the comparative statistics, all of these sources rely on a

    mixture of national statistics, sales data, data from experts in

    the various countries, and survey data (Willer 2008a). As men-

    tioned in footnote 3, all of these data sources are fallible, so

    caution is warranted when interpreting the results.

    Among the possible reasons for the differences in the

    organic market, or in the consumption of organic food, between

    countries, these sources point at national differences in political

    regulation as well as differences at the level of the civil society

    or market forces. Of the latter, some emphasize differences at

    the supply-side (e.g., soil conditions, organic farmers organiza-

    tions, and distribution channels) while others focus more on

    demand-side factors (e.g., consumer disposable incomes, pre-

    ferences, and values). Furthermore, some point at general char-

    acteristics of the country (e.g., climate, culture, and level of

    economic development) as possible causes of differences in the

    size of the organic markets while others discuss sector-specific

    characteristics (e.g., the structure and organization of and con-

    flicts within the agricultural sector) or events (e.g., specific

    food scandals or scares).

    Hence a number of possible explanations for the differences

    in organic food consumption between countries have been sug-

    gested in the literature. Still, the overall picture is rather frag-

    mented (Daugbjerg and Halpin 2008). As concluded in an

    early study, ‘‘in each country, individual factors were found

    that appeared to have some impact on national growth’’

    (Michelsen 2001a, 16). Along the same lines, a more recent

    review of the literature on organic farming concluded that, ‘‘for

    the time being . . . the factors determining the regional distri-bution . . . are not yet fully understood’’ (Dabbert, Haring,Zanoli 2004, 16). This is equally true when turning to the

    demand side and trying to explain why the tendency to buy

    organic food products is stronger in some than in other

    countries.

    A Comprehensive Conceptual Model forSustainable Food Consumption

    A comprehensive understanding of the causes of unsustainable

    consumption, with regard to food and in general, requires a sys-

    tematic and cross-disciplinary approach to mapping potential

    causes. At the most abstract level, variations in consumption

    patterns can be attributed to political and market factors (Arndt

    1981). As discussed in the following, political intervention in

    the form of creating a legal basis for organic food production

    and marketing and various forms of direct and indirect subsi-

    dies as well as independent control, certification, and labeling

    schemes have played a key role in the creation and develop-

    ment of a market for organic food products. However, the

    available evidence strongly suggests that variation in govern-

    ment regulation is not the only reason why the consumption

    Thøgersen 173

    173 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • Table 1. Research on Differences and Similarities in Organic Food Consumption Across Countries

    References Countries Covered Method and Findings

    Sønderskov (2009) Twenty European countries A consumption index based on data from Willer and Yussefi(2005) and Hamm and Gronefeld (2004) is regressed on gener-alized social trust, generalized institutional trust (both based onthe first round of the European Social Survey [ESS], 2003), post-material values (the share of the respondents labeled ‘‘postma-terialist’’ by four-item Materialist/Postmaterialist battery ofInglehart et al. [2004], from European and World Values Survey2006), an estimate of the average price premium for organic food(from Hamm and Gronefeld 2004) and various descriptors of thedemographic composition from World Bank and Eurostatsources. Variables were national averages or shares. The level of‘‘postmaterialism’’ was the only significant predictor of organicfood consumption

    Daugbjerg and Sønderskov(2009)

    Denmark, Sweden, UK and USA Comparative policy analysis plus surveys with representativesamples of consumers from the four countries. Regressing self-reported organic consumption on country of residence, postma-terialism, perceptions regarding organic food and agriculture anddemographic variables. Some of the differences in aggregatedemand between Denmark and the other three countries cannotbe explained by the included control variables and are attributedto differences in policy. Besides policy, country differences can beexplained by differences in postmaterialism (higher in Denmarkand Sweden) and trust in organic labels (higher in Denmark)

    Willer (2008) and previouseditionsa

    Differ between editions, but in principle allorganic food producing and consumingcountries of the world

    Current statistics and market info collected by the ResearchInstitute of Organic Agriculture, the International Federation ofOrganic Agriculture Movements and the Foundation Ecology &Agriculture from national and international statistical bureaus,market research companies and experts. A basic source con-cerning developments and cross-national differences in organicfarming and the organic market

    Dimitri and Oberholtzer(2007)

    United States and European Union (EU) Market statistics and politics for the two areas are comparedsupplemented by a review of other material. It is assessed thatconsumers have become the driving market force in both regions.European consumers have faced more serious food scares thanhave American consumers. The stronger opposition againstgenetically modified organisms (GMOs) among European consu-mers has also favored organic food in Europe relative to America.The more proactive policy in Europe has led to organic having ahigher share of the food market and of agricultural land but due tostronger demand the market is currently growing faster in theUnited States. This suggests that the divergent policy directionsdo not matter in terms of meeting consumer demand, althoughthey may matter for other reasons

    Padel and Midmore (2005) Eighteen European countries The Delphi method, using experts of the organic food market ineighteen countries, is used to explore factors influencing thedevelopment of the organic market, future market prospects, andthe role of governments in future market development. It is foundthat short supply chains and focus on regional organic shops maybe an indication of an earlier stage of market development, likelyto be followed by integration into mainstream outlets andinvolvement of multiple retailers. It is concluded that the mutualbut mismatched interdependence of demand and supply acts as aconstraint to the overall development

    (continued)

    174 Journal of Macromarketing 30(2)

    at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • of organic food differs between countries (Padel, Lampkin, and

    Foster 1999). Various market factors also play a role.

    It is common to divide market factors into supply-side and

    demand-side factors. Both supply-side and demand-side factors

    influence consumer choices, including the consumption of

    organic food, but in different ways. In consumer research, a

    popular distinction is between factors determining consumers’

    motivation, ability, and opportunity to buy (in this case)

    organic food, as operationalized in the motivation–ability–

    opportunity model (e.g., Hoyer and MacInnis 2006; Ölander

    and Thøgersen 1995). These two distinctions are viewed as

    complementary in the current framework.

    Supply-side factors include a wide range of primary produc-

    tion, industry, and distribution-related characteristics, which

    might theoretically influence the consumption of organic food

    products in different ways, but which in practice primarily

    exert their influence through the availability and relative prices

    of the products (e.g., Magnusson et al. 2001; Zanoli and

    Naspetti 2002), that is, through influencing consumer opportu-

    nities for buying organic food. Demand-side factors include

    consumer beliefs, attitudes, and values (e.g., Magnusson

    et al. 2001; Thøgersen 2009), that is, factors influencing con-

    sumer motivation to buy organic food, as well as factors influ-

    encing their ability to do so, such as income, task-relevant

    knowledge, and habits (e.g., Thøgersen 2005a; Thøgersen and

    Ölander 2006).

    The proposed model for explaining variations in organic

    food consumption in a cross-national perspective is illustrated

    Table 1 (continued)

    References Countries Covered Method and Findings

    Hamm and Gronefeld (2004) Nineteen European countries Detailed data on organic production and consumption collectedby means of a questionnaire sent to a number of market experts ineach of the nineteen countries. Responses were cross-checkedand validated and supplemented by means of data from theInternet and other sources. Data were collected twice, in 2000and 2001 with the same questionnaire. Among the main resultsregarding cross-country differences were that (1) countries with ahigh organic share of total food sales also had a high percentage oforganic food sold through general food shops, such as multipleretailers, (2) in countries where general food shops were veryactive in the marketing of organic food, consumer price premiumswere usually lower, (3) most countries with high organic marketshares had a common national label and consumer recognition ofthis label was usually high, (4) to obtain an efficiently functioningmarket, both the supply side and the demand side must bedeveloped equally

    Michelsen et al. (1999) Eighteen European countries Data collected by national experts by contacting the most signif-icant marketing agents in each country. The information coversthe situation in 1997. The report is about market impacts ofpolicies and the contribution of organic food and feed markets tothe general policy objectives of the Common Agricultural Policy(CAP). The analysis focuses on market supply rather than onconsumer demand. It shows that adaptation of supply to demandrepresents a larger problem for the development of organic foodmarkets than does the development of sufficient demand

    Padel, Lampkin, and Foster(1999)

    Fifteen EU countries National experts in each country filled out standardized ques-tionnaires, supplemented with various published and unpublisheddata sources, and consultations with key individuals in specificfields. The influence of policy support on the development of theorganic sector is explored. Policies include the agri-environmentprogram (EU Regulation 2078/92), the EU regulation 2092/91defining organic crop production in statutory terms and policiesto support market and regional development and the informationprovision of organic farming. Policy makers have been interestedin organic farming for its environmental and health benefits andthe potential to contribute to the goals of regional developmentprograms. The evaluation suggests that the variation in supportpolicies alone cannot explain the different rates of conversion toorganic farming in the EU

    a ‘‘The world of organic agriculture’’ is a yearly publication since 2000, which uses national statistics and surveys with key persons to gather as precise a picture ofthe status of organic food production and consumption worldwide as possible. Hence, it mainly contains descriptive data and the judgments of differences andsimilarities are mainly presented as brief statements of facts rather than analyses.

    Thøgersen 175

    175 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • in figure 2. Within the broader framework outlined above, the

    model includes a specification of the political and market

    factors that are most important in the case of organic food con-

    sumption, with the latter divided into supply-side/opportunity

    and demand-side/motivation and ability factors and the former

    into political regulation and government-sponsored market

    development activities. The specific factors mentioned under

    each of these headlines are derived from the reviewed

    literature.

    In the following, this conceptual framework is used to

    structure the review of extant research on country differences

    in organic food consumption. The comprehensive framework

    makes it possible to effectively synthesize the evidence and

    to identify important knowledge gaps that call for further

    research.

    Political

    Regulation and Subsidies

    As is true for other factors, discussed below, there is a lack of

    systematic comparative research investigating the relationship

    between national policies and the development of the organic

    sector and market (Daugbjerg and Halpin 2008). However, the

    scattered evidence—supported by a few systematic empirical

    studies cited below—strongly suggests that differences in polit-

    ical regulation are among the factors explaining the differences

    in the success of organic farming between countries. Specifi-

    cally, in a thorough comparative analysis of European national

    politics in this area, it was concluded that ‘‘the leading

    countries in the development of organic farming (in terms of

    the percentage of organic to total land area) have most certainly

    experienced strong policy support for organic farming. In most

    cases, this has included special support for the markets for

    organic foodstuffs’’ (Dabbert, Haring, Zanoli 2004, 13).

    Switzerland and some countries in the European Union (EU)

    began subsidizing organic farmers, especially during the transi-

    tion period, in the late 1980s, and since 1994 all EU member

    states have been obliged to support the conversion to organic

    farming financially (Padel and Lampkin 2007). Although the

    national policies within the EU have been gradually harmo-

    nized over time, there is, and especially has been, quite a bit

    of variation between countries in the implementation of this

    policy. Some countries have been much more ambitious than

    others and implemented a variety of policies aimed at support-

    ing the growth of the organic food sector, both from the supply

    Figure 2. Determinants of organic food consumption.

    176 Journal of Macromarketing 30(2)

    176 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • and the demand sides (Daugbjerg and Sønderskov 2009;

    Dimitri and Oberholtzer 2007; Hamm and Gronefeld 2004;

    Padel and Lampkin 2007).

    Denmark, one of the top three organic countries in Europe,

    is often mentioned in this connection. The Danish law on

    organic farming from 1987 has been called ‘‘groundbreaking’’

    (Aschemann et al. 2007, 132). It was the first national law to

    define organic farming and support it financially (Padel,

    Lampkin, and Foster 1999). Later, when facing oversupply in

    some organic product groups, Denmark was also the first

    country to adjust its policy to focus more on demand strength-

    ening, instead of just using production subsidies to support the

    organic sector, with its national action plans of 1995 and 1999

    (Aschemann et al. 2007; Dabbert, Haring, Zanoli 2004). A sys-

    tematic, comparative study confirmed that the relatively ambi-

    tious Danish policy, with its emphasis on both supply- and

    demand-side instruments, is a significant contributing reason

    why organic food consumption is substantially higher in

    Denmark than in most other countries (Daugbjerg and

    Sønderskov 2009). Demand-side instruments will be discussed

    in more detail in the next section.

    Germany, the largest organic market in Europe in absolute

    terms (Padel et al. 2008), was the second to introduce a scheme

    to support conversion to organic farming financially, in 1989,

    in the context of the EU’s so-called extensification scheme

    (EC Reg. 4115/88; Padel, Lampkin, and Foster 1999).

    Germany was the first country to support the conversion to

    organic farming within this scheme.

    EC Regulation 2078/92 provided an even bigger boost to the

    development of organic farming than EC Regulation 4115/88

    (Aschemann et al. 2007). This regulation was intended as an

    agri-environmental program, and although it is in principle a

    common framework across the EU, its measures were

    implemented differently and with different degree of focus

    on environmental versus other objectives in different member

    countries. This is probably a contributing reason why the

    organic sector took different paths of development in the

    various countries (Aschemann et al. 2007).

    Especially, the EU’s agricultural policy was implemented

    with a different focus in northern Europe and in the Mediterra-

    nean countries. Although it led to the promotion of organic

    agriculture in northern Europe, it led to supporting traditional

    small-scale production of regional specialties in the Mediterra-

    nean countries (Kurzer and Cooper 2007). The latter was based

    on the EU Commission’s support of the promotion and protec-

    tion of regional specialties by introducing, in 1992, a system

    known as Protected Designation of Origin (PDO), Protected

    Geographical Indication (PGI), and Traditional Specialty

    Guaranteed (TSG). The purpose of these designations is to

    protect traditional products’ reputations from competition by

    cheaper imitations that assume the same name as the original.

    In the domestic market, the protection of traditional

    products tends to favor local relative to imported products,

    which benefits the environment due to the reduced transport.

    However, the protection and promotion of regional specialties

    is as much an export-oriented strategy, which leads to increased

    international trade within product categories and therefore to

    an increase in the transportation of products overall. Hence,

    it is dubious that this strategy promotes environmental

    sustainability.

    France, Italy, Greece, Spain, and Portugal have been granted

    the largest number of designations for geographically protected

    food products (Kurzer and Cooper 2007). In northern Europe,

    however, there are relatively few traditional, regional specialty

    foods produced. Hence, a contributing reason why Mediterra-

    nean countries have focused less on promoting organic farming

    than northern European countries seems to be that the national

    governments and most likely the countries’ farmers have per-

    ceived revitalizing and protecting traditional food specialties

    as a more attractive business strategy.

    Based on the cited studies, it is not possible to quantify the

    importance of differences in national political emphasis and

    regulation for the variation in organic food production and con-

    sumption between countries, but the evidence strongly suggests

    that variations in national political emphasis and regulation are

    the important contributing factors. It would be difficult to

    explain the substantial growth in (especially) the European

    organic sector since the 1980s without reference to its growing

    recognition by policy makers (Dabbert, Haring, Zanoli 2004;

    Dimitri and Oberholtzer 2007; Padel and Lampkin 2007).

    However, there is a lot of between-country variation in the

    development of organic farming and the organic market, which

    cannot be explained by variation in support policies alone

    (Aschemann et al. 2007; Dabbert, Haring, Zanoli 2004; Padel,

    Lampkin, and Foster 1999). As discussed in the following, in

    addition to political regulation, various market factors have

    contributed to the different development of the organic

    markets, in Europe and elsewhere.

    Demand-Side Instruments: Control, Certification, andLabeling

    Market development activities regarding the organic food mar-

    ket can be, and have been, carried out with or without political

    support. However, like other infant industries, emerging

    organic food sectors lack resources, reputation, and credibility,

    which the political system can provide. Hence, in practice,

    political support for market development activities for the

    national organic food market has made a lot of difference

    (Daugbjerg and Sønderskov 2009; Hamm and Gronefeld

    2004; Padel and Lampkin 2007).

    Next to the legal definition of organic farming, the most

    important market development activities are the establishment

    of credible control, certification, and labeling systems for

    organic food products (Michelsen 2001a). In different coun-

    tries, such systems have been organized by producer organiza-

    tions (e.g., the Soil Association in the UK), nongovernmental

    organizations (e.g., the Swedish KRAV labeling system), or

    governmental organizations (e.g., the Danish state-controlled

    organic label, the Ø label). A clearly defined production system

    guaranteed by control and certification systems is a prerequisite

    for the segmentation of the market into organic products and

    Thøgersen 177

    177 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • conventional products and thereby for the establishment of a

    market for organic food products (Aschemann et al. 2007;

    Dabbert, Haring, Zanoli 2004). The control and certification

    is communicated to consumers by means of a label or logo,

    which is essential for consumers to be able to recognize a

    product as organic, at least in a supermarket (Hamm and

    Gronefeld 2004). The credibility of the certifying body, both

    in terms of commitment and ability, is essential for consumer

    trust in the organic label and in organic food products (Eden

    1994; Howard and Allen 2006; Thøgersen 2002). In general,

    consumers seem to have more confidence in labels that are

    government backed than in labels that are not (Roosen, Lusk,

    and Fox 2003).

    A common EU organic logo exists, but until now it has had

    no practical relevance. Consumers have used national labeling

    schemes as guidance when buying organic food products. In

    addition, whereas there is only one organic label in some coun-

    tries, in others there is a range of logos, labels, and brands. Ger-

    many now has one national public organic logo (Bio-Siegel),

    but up until 2000 each of the nine producer associations used

    its own logo (Dabbert, Haring, Zanoli 2004). The evidence sug-

    gests that when there are several certifying bodies and labels in

    a country, it creates consumer confusion and undermines con-

    sumer confidence (Aschemann et al. 2007; Hamm and Grone-

    feld 2004).

    It seems likely that differences between countries with

    respect to the control, certification, and labeling systems is a

    contributing factor explaining differences in the development

    of the organic market (Hamm and Gronefeld 2004). Denmark

    seems to have benefitted most from a well-known and

    established organic label. A national, state-controlled organic

    certification and labeling scheme, introduced in the 1987, was

    part of the ‘‘package’’ that made the Danish organic market one

    of the most successful in the world (Aschemann et al. 2007;

    Daugbjerg and Sønderskov 2009; Hamm and Gronefeld

    2004). However, a national organic label alone is not sufficient

    to boost the organic market. For example, France lags behind

    most other western European countries in terms of organic mar-

    ket share (see figure 1), although it introduced its national label

    for organic food products, Agriculture Biologique, as early as

    in 1984 (Padel and Lampkin 2007).

    What happens if a national standard and label is introduced

    in an organic market that has already reached a certain level of

    maturity, in spite of the lack of these features? Here, the evi-

    dence is also mixed. Whereas the implementation of the

    National Organic Program and the United States Department

    of Agriculture (USDA) label in the United States in 2002 gave

    the organic sector a boost, Germany’s introduction of the

    national logo in 2001 did not seem to benefit the sector partic-

    ularly, at least in the short run (Aschemann et al. 2007).4 Of

    course, each case is unique, which means that the effects of a

    specific intervention, such as a national organic label, may be

    hidden by the (possibly larger) impact of other events, such

    as the economic recession in the first years of the millennium

    or the Nitrofen scandal in Germany in 2002, where a banned

    herbicide was found in organic feed.

    Hence, in spite of the indisputable importance of a credible

    control, certification, and labeling system for building con-

    sumer confidence and ability to choose organic food products

    in the supermarket, national differences in these systems can

    only explain a limited amount of the cross-national variation

    in the consumption of organic food. In particular, the positive

    impact of a credible control, certification, and labeling system

    depends on organic products being both desired by consumers

    and available and affordable. Thus, it also depends on random

    events as well as on policies to support conversion and contin-

    ued production and on a range of market factors to be discussed

    in the following (cf., Dabbert, Haring, Zanoli 2004; Michelsen

    et al. 1999; Padel and Midmore 2005).

    Market Factors

    Supply-Side Factors (Opportunity)

    It appears from the previous sections that differences between

    countries in the development of the organic food market can to

    a high extent, but not completely, be attributed to variations in

    political regulation and politically supported market develop-

    ment activities. A key mediating factor is farmers’ decisions

    to convert to organic agriculture. The economic position of

    organic farmers relative to nonorganic farmers, and thereby the

    incentive to convert (Michelsen 2001a), is obviously influ-

    enced by both political regulation and market factors (Dimitri

    and Oberholtzer 2007). Farmers are more inclined to look for

    supportive arrangements, such as support for organic farming,

    in periods of general agricultural recession than in periods of

    prosperity (Michelsen 2001a), which illustrates the importance

    of the incentive to convert for the development of national

    organic markets.

    Supply-side factors, such as the quality of soils and climate,

    have played an important role for the speed of conversion to

    organic production in different countries (e.g., Dabbert,

    Haring, Zanoli 2004). For example, in countries such as

    Germany, Austria, and Switzerland, organic farming is espe-

    cially prevalent in disadvantaged rural areas where extensive

    agriculture predominates. In disadvantaged regions, grasslands

    tend to be more important than arable land, and less fertilizer is

    used on agricultural lands in general. Extensive forms of ani-

    mal production tend to play a major role in these regions, both

    in organic and in conventional farming. Among other things,

    this means that the changes a farm has to undergo to convert

    to organic farming are relatively small. According to Dabbert,

    Haring, Zanoli (2004, 13):

    ‘‘Even if no additional price premium for organic produce is

    received and no policy-related payments are made for organic

    farming, the loss a farmer undergoes when converting to

    organic agriculture is fairly small. If, in such a situation, price

    premiums can be achieved or agri-environmental payments are

    made for being organic, organic farming tends to be more

    profitable than conventional farming.’’

    178 Journal of Macromarketing 30(2)

    178 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • Although there is clearly no one-to-one relationship between

    the share of agricultural land being managed organically and

    organic food’s share of the total food market, a large domestic

    production provide a ‘‘push’’ to organic consumption in a coun-

    try (Hamm and Gronefeld 2004). For example, at the change of

    the millennium, Italy’s organically cultivated agricultural land

    area was by far the largest in Europe in absolute terms and

    among the largest in terms of share of total agricultural land,

    but the per capita consumption of organic food products was

    much more modest (Hamm and Gronefeld 2004). This apparent

    discrepancy was the result of a combination of extensive

    organic agriculture (especially large areas used for sheep pro-

    duction) in some Italian regions and the fact that Italy exports

    a large share of its organic products (Dabbert, Haring, Zanoli

    2004). However, the early conversion of large areas of farm-

    land to organic production had a positive influence on the avail-

    ability and affordability of organic food products on the Italian

    market (Hamm and Gronefeld 2004). It seems likely that this is

    a contributing reason why Italy’s organic food consumption per

    capita is now substantively larger than in other Mediterranean

    countries (Padel et al. 2008).

    Another, important supply-side factor is the development of

    effective distribution channels (Hamm and Gronefeld 2004).

    Initially, organic food products were mostly sold directly by

    farmers to consumers, at the farm, through producer–consumer

    associations, or at farmers markets. Later, specialty (health

    food) stores played an increasing role in many countries, but

    now most organic food products in Europe are sold through

    conventional supermarkets, including discount stores (Asche-

    mann et al. 2007; Richter 2008). Conventional retail chains

    have been especially dominating in the most successful organic

    markets, Switzerland, Austria, and Denmark (Dabbert, Haring,

    Zanoli 2004; Michelsen et al. 1999; Richter 2008), which is

    probably a contributing reason for organic food’s relatively

    high market share in these countries (Hamm and Gronefeld

    2004). It is a general observation that after conventional super-

    markets start offering organic products, sales increase substan-

    tively (Aschemann et al. 2007). The major reason for this is

    higher availability for consumers, but as noted by Aschemann

    et al. (2007), a big company’s involvement in organic food is

    also normally accompanied by advertising and public relations

    campaigns, which are likely to increase the public’s interest in

    organic food in general.

    In parallel with conventional retailers increasing their

    assortments, and sale, of organic food products, the specialized

    organic retailing sector has gone through a restructuring and

    concentration process in many countries. For example, the Ita-

    lian organic supermarket chain Natura Si had 60 outlets in 2006

    (Richter 2008). A related trend has been for smaller regional

    organic wholesalers to merge into consolidated national whole-

    salers (Richter 2008). Among other things, the large organic

    wholesalers initiate joint marketing programs for the specialist

    retailers such as the German and Swiss (ECHT BIO.) program

    and the Italian ‘‘b’io’’ program (Richter 2008).5 In contrast to

    what one might expect, the sale of organic food products

    through conventional supermarket chains has not hurt the sale

    through specialized shops and direct sales by farmers, on the

    contrary (Aschemann et al. 2007). A likely reason, suggested

    by Aschemann et al. (2007), is that most conventional super-

    market chains have a rather narrow assortment of organic food

    products, so when their advertising and public relations cam-

    paigns increase interest in organic food, new consumers go to

    specialist retailers for their wider assortment, including

    regional organic food specialties.

    The effectiveness of the distribution channels also has

    important implications for total costs and therefore consumer

    prices (Aschemann et al. 2007; Hamm and Gronefeld 2004).

    In countries where most of the organic food products are sold

    through conventional supermarkets, lower price premiums

    tend to be charged for organic food products (Hamm and

    Gronefeld 2004; Michelsen et al. 1999). Although it has been

    suggested that ‘‘the significance of price premiums is declin-

    ing’’ (Aschemann et al. 2007, 137), extant research strongly

    suggests that high product prices are still one of the most

    important barriers to growth in the demand for organic food

    products (Dimitri and Oberholtzer 2007; Hughner et al. 2007;

    Padel and Midmore 2005).

    Due to the expansion of the organic market and the

    consolidation of its distribution channels, prices of organic

    food products have become more competitive in Europe

    (Aschemann et al. 2007). However, price premiums tend to

    be higher in countries with a low turnover of organic food prod-

    ucts compared with conventional products (Dabbert, Haring,

    Zanoli 2004). Hence, the relationship between organic con-

    sumption and prices is a two-way street: In markets with a low

    organic turnover, premium prices are high due to high costs,

    which impedes the expansion of the organic market. When the

    sale of organic food goes up, economies of scale in production

    and distribution allow more competitive prices and lowering of

    the price barrier. Hence, as in most other consumption areas,

    growth in organic food consumption is self-reinforcing.

    Demand-Side FactorsAbility. In the early days, the organic sector was mostly

    supply driven. Farmers introduced organic food products for

    various reasons. However, it has been suggested that more

    recently consumers have become the driving market force

    (Dimitri and Oberholtzer 2007).

    It is common to refer to average disposable incomes when

    commenting on differences between countries with respect to

    purchasing organic food products (Sahota, Willer, and Yussefi

    2007). Because consumers usually pay a premium price for this

    kind of product, it seems likely that consumers in richer

    countries will be more willing to do so. Reflecting this, the

    consumer market for organic products is mostly in the indus-

    trialized countries, whereas Oceania and Latin America

    account for a major part of the production area (Aschemann

    et al. 2007; Willer 2008b). However, a recent study of twenty

    European countries found that the variation in organic con-

    sumption across countries in Europe is not currently related

    to average national income (Sønderskov 2009).

    Thøgersen 179

    179 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • Others have linked the slowdown in the growth rate of the

    organic markets in some countries in the first years of the

    new millennium to the economic recession in this period

    (Aschemann et al. 2007). This assessment is supported by the

    repetition of this pattern during the recession at the end of the

    decade (Clarke 2009). It seems that the demand for organic

    food products is more sensitive to the general economic climate

    of the country than food in general. In this respect, organic food

    products share a characteristic of luxury goods, which are in

    general more sensitive to economic upturns and downturns

    than everyday necessities (Campbell and Li 2003).

    The income effect naturally depends on the price premiums

    charged for organic food products. As mentioned in the former

    section, organic food prices have become more competitive in

    Europe during the last two decades. Together with the rela-

    tively narrow variation in national incomes in Western Europe,

    the decrease in the premium prices charged for organic food

    could explain why variations in organic food consumption

    between European countries no longer seem related to average

    national incomes. Therefore, it is unlikely that the lack of an

    income effect on organic food consumption can be generalized

    outside Western Europe or the group of affluent, industrialized

    countries.

    Motivation. Another factor, possibly contributing to thevariation in organic food consumption between countries is

    motivational. Buying these kinds of products may be more con-

    sistent with the cultural values and norms of some than of other

    countries (Usunier and Lee 2009). National cultures differ in

    many ways that might have implications for the weight given

    to environmental and ethical concerns in food choice. General

    traits of the national culture may play a role, such as cultural

    value emphasis and religion (Schwartz 2009). However, it

    seems likely that cultural traits that are related to this specific

    area, such as environmentalism and food culture, are even more

    important (Askegaard and Madsen 1998; Thøgersen In

    press-d).

    Askegaard and Madsen (1998) found that food cultures to a

    high extent follow language and (therefore also) national bor-

    ders. For example, they identified unique food cultures in each

    of the Mediterranean countries (rather than a common Mediter-

    ranean food culture) as well as in each of the Nordic countries

    (rather than a common Nordic food culture). Hence, variations

    in national food cultures could account for some of the diver-

    sity in consumers’ preferences for organic food products across

    countries, in Europe and globally.

    Differences in national food cultures are, for example,

    reflected in the previously mentioned considerably larger num-

    ber of designations for geographically protected food products

    being granted in the Mediterranean countries than in northern

    European countries. It has been suggested that citizens in

    Mediterranean countries share an emotional attachment to

    small-scale traditional farming, regional produce, and regional

    gastronomic traditions (Torjusen et al. 2004) and that their

    designated geographically protected food products are ‘‘con-

    sidered part of the national patrimony or identity’’ (Kurzer and

    Cooper 2007, 1038). Research has also found that many

    consumers do not distinguish between local and organic food

    products (Roininen, Arvola, and Lähteenmäki 2006). A high

    involvement with traditional, local, or regional food products,

    especially if combined with a widespread belief that traditional

    domestic food production is virtually the same as organic, may

    create a mental ‘‘barrier to entry’’ for organic food. This seems

    to be the case in, but is not necessarily limited to, some

    Mediterranean countries.

    As regard, other specific value differences, it has been noted

    that animal welfare plays an important role in northern

    European countries whereas it is almost an unknown value to

    Italian or Greek consumers (Zanoli and Naspetti 2001). In addi-

    tion, reviews of consumer studies show that environmental

    concerns are central for many consumers with regard to organic

    food (Hughner et al. 2007; Torjusen et al. 2004). Pan-European

    opinion polls suggest that environmental concern—reflected in

    how much attention is paid to protecting the environment rela-

    tive to other issues—is higher in northern Europe than, for

    example, in Mediterranean countries (see figure 3), and envi-

    ronmental concern also seems to play a more important role

    in motivating consumer action in the north than in the south

    (European Commission 2008). In line with these data, it has

    been suggested that ‘‘interest in organic farming (in northern

    Europe, JT) grew out of strong popular environmental con-

    sciousness’’ (Kurzer and Cooper 2007, 1039). This assessment

    is backed by a recent comparative study of 20 European coun-

    tries, which found that cross-national variation in organic food

    Figure 3. Environmental concern measured as attention towardprotecting the environment in selected northern European andMediterranean countries, 2003–2008. Note: The graphs show thepercentage of large random samples of the population picking‘‘protecting the environment’’ as one of the two most importantissues (among fifteen issues) facing their country at the moment.Source: Eurobarometer 59 to Eurobarometer 70, The EuropeanCommission.

    180 Journal of Macromarketing 30(2)

    180 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • consumption is significantly related to the population’s

    postmaterialistic value orientation (Sønderskov 2009).

    Attitudes in the general population do not necessarily only

    influence the development of the organic food sectors via the

    market. In a thorough comparative analysis of the development

    of European policy in this area, it was suggested that ‘‘growing

    public interest in environmental matters led to greater sympa-

    thy for organic farming, which translated into a desire to give

    it political support for environmental reasons’’ (Dabbert,

    Haring, Zanoli 2004, 5). Others have speculated that attitudes

    in the general population influence farmers and that some have

    converted to organic production in an attempt to avoid the

    general criticism of agriculture’s environmental problems

    (Michelsen 2001a).

    However, differences in environmental concern obviously

    cannot explain the huge differences in organic food’s market

    shares between the Nordic countries (see figure 1) nor the fact

    that the organic food consumption per capita is considerably

    higher in Italy than in, for example, Finland (Padel et al.

    2008). Hence, differences in cultural values and concerns can

    only account for a limited share of the cross-country variation

    in organic food consumption.

    Discussion

    The sustainability of final consumption depends on individual

    consumer choices, but individual choices are severely

    constrained by a range of macro and structural factors. In this

    article, the importance of macro and structural factors for sus-

    tainable consumption is demonstrated in an environmentally

    important field: food consumption. Macro factors have been

    identified that contribute to explaining the level of sustainabil-

    ity of food consumption, specifically organic food consump-

    tion, based on a review of extant research on differences

    between, especially, European countries.

    With the existing evidence, a precise quantification of the

    relative importance of macro and structural factors is not

    possible. However, the quality of the reviewed research is suf-

    ficiently high to document without any reasonable doubt that

    macro and structural factors, both determined by policy and

    market actors, play a key role for the level of organic (and

    therefore also sustainable) consumption in a country.

    As reported in the reviewed literature, some countries have

    supported organic agriculture, and the development of an

    organic market, earlier, more persistently, and with a broader

    range of means than others. This has led to a range of impedi-

    ments to consumer organic choices being removed or substan-

    tially reduced, especially those related to availability, price,

    and consumer uncertainty. Generally, northern European coun-

    tries have supported organic food production and consumption

    more than the Mediterranean countries, and Denmark stands

    out in this respect. Denmark is one of the few countries where

    the government from the outset has intervened both at the sup-

    ply side and the demand side (‘‘push’’ and ‘‘pull’’, cf. Padel

    et al. 2002) to facilitate the development of an organic food

    sector, and this is one of the reasons why Denmark is one of the

    three countries in the world with the highest organic food

    market share (Daugbjerg and Sønderskov 2009).

    It has been suggested that the relatively weak political sup-

    port for organic food in Mediterranean countries is at least

    partly due to a stronger focus on regional and local specialties.

    More research is needed to document the veracity of this claim.

    However, it is obvious that, from a business strategy point of

    view, protected trade names based on systems of local and

    regional origin has many of the same merits as organic produc-

    tion, and they may even command a higher premium price. In

    addition, there is evidence suggesting that many consumers do

    not distinguish between local and organic food production.

    Future research should investigate the proposition made in this

    article that such beliefs, especially when combined with strong

    consumer attachment to local and regional products, create

    barriers to entry for new organic food products.

    Both the organic strategy in northern Europe and the

    regional and local specialties strategy in Mediterranean coun-

    tries have benefited from popular support. In Mediterranean

    countries, regional and local specialties are considered part of

    the national patrimony or identity (Kurzer and Cooper 2007).

    In northern Europe, organic food production has fit consumers’

    environmental concern (which has been focused in the direc-

    tion of agriculture and food production by various high-

    profile food scandals). The difference in agricultural focus

    between the north and south of Europe might partly be attrib-

    uted to these popular sentiments. Most likely, there are other

    contributing factors, however, including different opportunities

    (i.e., the fact that the southern European countries have a much

    larger richness of renowned local and regional specialties than

    northern European countries).

    The available evidence suggests that differences in political

    regulation are important, but not the only factors that have con-

    tributed to the variation in the consumption of organic food

    across European countries, however. It seems likely that a

    whole range of market factors, both on the supply and the

    demand side, have also played a role. For example, everything

    else being equal, the conversion of land to organic production

    has gone faster under conditions that favor extensive agricul-

    ture, most likely because the costs of converting are smaller

    under these conditions. This seems to have been a contributing

    factor for the relative success of organic farming in countries

    such as Austria and Switzerland, and perhaps also in countries

    such as Sweden, Italy, and Germany.

    Another supply condition that seems to have played an even

    bigger role for the development of the organic market in differ-

    ent countries is the maturity of the distribution channels (sale

    through conventional supermarkets vs. more extensive chan-

    nels such as farm sale, farmers’ markets, and health food

    stores). It differs substantively between countries how early

    and to which extent conventional retail chains have taken in

    and promoted organic food products. The available evidence

    suggests that when they have done so, this has boosted the

    consumption of organic food, both because of increased

    accessibility and lower prices and because of the increased pro-

    motion of organic food. Hence, it would be useful with more

    Thøgersen 181

    181 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • systematic research to clarify why countries differ in this

    respect and what hampers the evolution of efficient distribution

    channels for organic food products in some countries.

    The, related, size of the premiums charged for organic food

    products is another important supply condition. According to

    most consumer surveys, high price is one of the most important

    reasons for not buying organic food (Hughner et al. 2007),

    which suggests that differences between countries in this

    respect have contributed to the differences in aggregate

    demand. A study in Germany found that the prices of organic

    food products are equivalent to the 25 percent top conventional

    food brands in many product categories (Hamm Aschemann,

    and Riefer 2007). This means that the price premium for

    organic food products is not a problem as long as they only

    compete in the premium market. However, such a positioning

    also sets quite narrow limits to the reachable market share for

    organic food products and for organic food production’s contri-

    bution to a more sustainable consumption pattern. There is a

    need for more and more comparative research on the position-

    ing of organic food products and its implications for their price

    sensitivity.

    Another factor that seems to account for some of the differ-

    ences in organic demand between countries is the different

    ways control, certification, and labeling systems are organized.

    As mentioned above, the optimal way of organizing and

    implementing these systems is still not unequivocally settled.

    Hence, there is a need for detailed, comparative analyses of the

    approaches taken in different countries and their implications.

    How do particularly successful and unsuccessful national

    programs compare to one another and to approaches in other

    countries? Which other variables discussed in the current arti-

    cle (e.g., policy, culture, distribution system, and premium

    price) play a role in the development or acceptance of organic

    labels for food products? Which policy recommendations can

    be derived from a thorough comparative analysis of successful

    and unsuccessful certification, control, and labeling programs?

    There is strong evidence that also demand-side factors have

    contributed to the differences in organic food consumption

    between European countries. Especially, the development of

    the organic food market seems to have benefited from environ-

    mental concern and a postmaterialistic value orientation, both

    of which differ between European countries. Food scandals,

    which have created mistrust in conventional agriculture and

    food production, have also benefited the organic food market,

    especially in northern Europe (Aschemann et al. 2007; Hugh-

    ner et al. 2007). Furthermore, these demand-side factors may

    not only have benefited organic food production directly

    through the market, but perhaps also indirectly through paving

    the way for political support and putting pressure on farmers to

    convert to organic production. Hence, this article also illus-

    trates the practical relevance of research attempting to explain

    differences in environmental concern and values between

    countries (e.g., Inglehart 1995; Schultz et al. 2005). Because

    organic food production obviously challenges the technologi-

    cal dimension of the dominant social paradigm (DSP), the

    study also links into and informs research on differences and

    changes in the DSP (e.g., Dunlap and Van Liere 1978; Dunlap

    et al. 2000; Kilbourne et al. 2001; Kilbourne, Beckmann, and

    Thelen 2002).

    The factors covered in this review go some way toward

    explaining the main difference between the north and the south

    of Europe (primarily interacting differences in environmental

    concern, in the importance attributed to regional and local spe-

    cialties, in distribution channels, and in national policies) and

    some of the exceptional cases. In addition to relatively high

    environmental concern, the three countries with the highest

    organic market shares in Europe, and in the World, Switzer-

    land, Austria, and Denmark, all benefited from large retailers

    making organic food available and affordable to broad seg-

    ments of consumers early in the development of the organic

    market. In addition, the development of the organic sector in

    some countries has benefited from soil conditions that made

    organic agriculture relatively more profitable. Visionary polit-

    ical support was also a major contributing factor, including the

    implementation of a successful state-controlled organic label-

    ing system. That Italy is a positive outlier in the Mediterranean

    region seems to be partly attributable to early, large-scale

    conversion to organic agriculture due to a mixture of favorable

    soil conditions and a large organic export. It may also be part of

    the explanation that most of the organic food is sold in the big

    cities in northern Italy, which is more similar to northern

    Europe both in terms of incomes and values than southern Italy

    (Richter et al. 2007). A better understanding of the Italian case

    may be the key to identifying effective strategies for increasing

    the organic market in other Mediterranean countries. More

    research is needed in this area.

    However, there are other important holes in our understand-

    ing of the differences between countries in organic food

    consumption. Notably, the reviewed literature revealed no

    explanation for negative outliers in northern Europe, including

    Norway and Finland. Future research should investigate what

    has suppressed the demand for organic food in countries such

    as these.

    As mentioned several times, and as illustrated in the model

    in figure 2, the various factors influencing the development of

    the organic sector, and the demand for organic food, are not

    mutually exclusive or independent, but interact in a complex

    pattern. The consumer sentiments that created demand for

    organic food in some countries also influenced the political

    system and paved the way for political support to organic pro-

    ducers and production. Furthermore, the political system is

    obviously influenced by the economic interests of farmers,

    which means that the political regulation tends to become more

    favorable when organic agriculture has reached a size that

    makes it a political factor in the country. There are some early

    studies of the interaction between the political system, farmers’

    associations, and environmental and consumer interests (e.g.,

    Michelsen 2001a, 2001b), but this is an area where more

    research is needed (Daugbjerg and Halpin 2008).

    There is also a need for more research on the importance of

    national food cultures for the development of the organic sec-

    tor. The emphasis on traditional, local, and regional specialties

    182 Journal of Macromarketing 30(2)

    182 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • seems to have been a barrier for organic food in some Mediter-

    ranean countries. However, this barrier seems to have been

    overcome in Italy. Why is that? Is it because organic farming

    for export has become significant enough to be a political factor

    to Italian farmers to a greater extent than farmers in other Med-

    iterranean countries combining the organic and the designation

    of origin strategy. Or, perhaps is it because consumer-citizens

    in northern Italy are influenced by the same postmaterialist

    value tendencies found in countries in northern Europe? Future

    research should investigate this.

    In addition, it is a weakness of the approach used in this

    article that it does not allow a quantification of the relative

    importance of individual-level versus macro and structural

    factors. There are a few attempts in this direction in the

    reviewed research, but more systematic research is needed

    here. Furthermore, organic food is only one aspect of a sustain-

    able food consumption, and not even the most important

    (which is the amount of meat, and especially beef, in the diet),

    and food is only one among several areas that are important for

    the sustainability of private consumption (notably private

    transportation, home energy consumption). The environmental

    benefits of buying organic food may be partly or fully negated,

    for example, if the products are transported by airplane or if

    consumers buy more meat and/or dairy products because it is

    organic (the rebound effect, cf. Hertwich 2005). Hence, to

    strengthen the case of the importance of macro and structural

    factors for sustainable consumption, there is a need for

    extending this research to other consumption areas and to the

    interaction between consumption areas.

    Notes

    1. For a consumer-directed campaign promoting these changes in pri-

    vate food consumption, see www.sierraclub.org/truecostoffood/.

    2. See www.ifoam.org. Although it is not supported by scientific evi-

    dence, many consumers seem to believe that organic food products

    are also healthier and taste better than their conventional counter-

    parts. A number of empirical studies conclude that these beliefs are

    the main reasons why consumers buy organic food (cf., Renée

    Shaw Hughner et al. 2007 ‘‘Who are organic food consumers? A

    compilation and review of why people purchase organic food.’’

    Journal of Consumer Behaviour, 6). However, the basis for this

    conclusion has been questioned on methodological grounds and a

    recent study strongly suggests that the mentioned health and taste

    beliefs are products rather than antecedents of buying organic food

    (John Thøgersen In press-a, ‘‘Green shopping: For selfish reasons

    or the common good?’’ American Behavioral Scientist).

    3. The per capita consumption of organic food depends on food

    prices, which vary between countries. When expressed in a com-

    mon currency, it also depends on the exchange rate. Market shares

    are independent of the general price level and exchange rates, but

    they are not available from all countries. In addition, the market

    share of organic food depends on the price of organic relative to

    conventional food products and, not least, on how ‘‘the food sec-

    tor’’ is defined (e.g., just food or food and drinks), which may vary

    between countries. For these reasons, and because all of the

    measures are fallible, even the best available comparative statistics

    should be interpreted with caution.

    4. The researchers making these assessment have revised their assess-

    ment of the German national logo and believe that now seven to

    eight years after its introduction, it plays a major role for consumer

    awareness and trust and consequently for the current development of

    the German organic market (professor Ulrich Hamm and Dr. Jessica

    Aschemann-Witzel, personal communication).

    5. ‘‘[ECHT BIO.]’’ and ‘‘‘b’io’’’ are trademarks.

    Acknowledgments

    The author is grateful to Jessica Aschemann-Witzel, William

    Kilbourne, and three anonymous reviewers for helpful comments on

    an earlier version.

    Declaration of Conflicting Interests

    The author declared no potential conflicts of interest with respect to

    the authorship and/or publication of this article.

    Funding

    The author received no financial support for the research and/or

    authorship of this article.

    References

    Ajzen, I., and M. Fishbein. 1980. Understanding attitudes and

    predicting social behavior. Englewood Cliffs: Prentice-Hall.

    Alfredsson, E. C. 2004. ‘‘Green’’ consumption—No solution for

    climate change. Energy 29:513-24.

    Arndt, J. 1981. The political economy of marketing systems: Reviving

    the institutional approach. Journal of Macromarketing 1:36-47.

    Aschemann, J., U. Hamm, S. Naspetti, and R. Zanoli. 2007. The

    organic market. In Organic farming: An international history,

    ed. W. Lockeretz, 123-51. Wallingford, England: CABI.

    Askegaard, S., and T. K. Madsen. 1998. The local and the global:

    Patterns of homogeneity and heterogeneity in European food cul-

    tures. International Business Review 7:549-68.

    Belk, R. W. 1975. Situational variables and consumer behavior.

    Journal of Consumer Research 2:157-64.

    Campbell, S., and C. Li. 2003. Per capita consumption, luxury

    consumption and the presidential puzzle: A partial resolution.

    Providence, RI: Brown University, Department of Economics.

    Carlsson-Kanyama, A., and A. D. Gonzalez. 2009. Potential contribu-

    tions of food consumption patterns to climate change. American

    Journal of Clinical Nutrition 89:1704S-09-04S-09.

    Clarke, R. 2009. Organic gravy train runs out of steam? New Nutrition

    Business 14:22-6.

    Dabbert, S., A. M. Haring, and R. Zanoli. 2004. Organic farming:

    Policies and prospects. London: Zed Books.

    Danish Environmental Protection Agency. 2002. Danske husholdnin-

    gers miljøbelastning. Copenhagen, Denmark: Danish Environmen-

    tal Protection Agency.

    Daugbjerg, C., and D. Halpin. 2008. Sharpening up research on organ-

    ics: Why we need to integrate sectoral policy research into main-

    stream policy analysis. Policy Studies 29:393-93.

    Daugbjerg, C., and K. M. Sønderskov. 2009. Environmental policy

    performance revisited: Organic food policies and sustainable

    Thøgersen 183

    183 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • consumption in Denmark, Sweden, the United Kingdom and the

    United States. Aarhus, Denmark: Department of Political Science,

    Aarhus University.

    de Ferran, F., and K. G. Grunert. 2007. French fair trade coffee buyers’

    purchasing motives: An exploratory study using means-end chains

    analysis. Food Quality and Preference 18:218-29.

    De Pelsmacker, P., L. Driesen, and G. Rayp. 2005. Do consumers care

    about ethics? Willingness to pay for fair-trade coffee. Journal of

    Consumer Affairs 39:363-85.

    Dimitri, C., and L. Oberholtzer. 2007. Market-led versus government-

    facilitated growth. Development of the US and EU organic agricul-

    tural sectors. In Organic Agriculture in the US, ed. A. J. Wellson,

    97-127. New York: Nova Science Publishers.

    Doran, C. 2009. The role of personal values in fair trade consumption.

    Journal of Business Ethics 84:549-63.

    Dunlap, R. E., and K. D. Van Liere. 1978. The ‘‘new environmental

    paradigm’’: A proposed measuring instrument and preliminary

    results. Journal of Environmental Education 9:10-9.

    Dunlap, R. E., K. D. Van Liere, A. G. Mertig, and R. E. Jones. 2000.

    New trends in measuring environmental attitudes: Measuring

    endorsement of the new ecological paradigm: A revised NEP scale.

    Journal of Social Issues 56:425-42.

    Durning, A. T. 1992. How much is enough? The consumer society and

    the future of the earth. London: Earthscan Publications Ltd.

    Eden, S. 1994. Business, trust and environmental information:

    Perceptions from consumers and retailers. Business Strategy and

    the Environment 3:1-7.

    Etzioni, A. 2009. Spent. America after consumerism. The New

    Republic, June.

    European Commission. 2008. Attitudes of European citizens towards

    the environment, Special Eurobarometer 295/ EB 68.2. Brussels,

    Belgium: European Commission.

    European Environment Agency. 2005. Household consumption and the

    environment. Copenhagen, Denmark: European Environment Agency.

    Fishbein, M., and I. Ajzen. 1975. Belief, attitude, intention, and

    behavior. Reading, MA: Addison-Wesley.

    Fotopoulos, C., and A. Krystallis. 2002. Purshasing motives and pro-

    file of the Greek organic consumer: A countrywide survey. British

    Food Journal 104:730-65.

    Hamm, U., J. Aschemann, and A. Riefer. 2007. Sind die hohen Preise

    für Öko-Lebensmittel wirklich das zentrale Problem für den

    Absatz? Zeitschrift für Agrarpolitik und Landwirtschaft 85:252-71.

    Hamm, U., and F. Gronefeld. 2004. The European market for organic

    food: Revised and updated analysis. Aberystwyth, Wales: School

    of Management and Business.

    Harper, G. C., and A. Makatouni. 2002. Consumer perception of

    organic food production and farm animal welfare. British Food

    Journal 104:287-99.

    Hertwich, E. G. 2005. Consumption and the rebound effect: An

    industrial ecology perspective. Journal of Industrial Ecology

    9:85-98.

    Howard, P. H., and P. Allen. 2006. Beyond organic: Consumer interest

    in new labelling schemes in the Central Coast of California. Inter-

    national Journal of Consumer Studies 30:439-51.

    Hoyer, W. D., and D. J. MacInnis. 2006. Consumer behavior. 4th ed.

    Boston: Houghton Mifflin.

    Hughner, R. S., P. McDonagh, A. Prothero, C. Shultz, and J. Stanton.

    2007. Who are organic food consumers? A compilation and review

    of why people purchase organic food. Journal of Consumer Beha-

    viour 6:94-110.

    Inglehart, R. 1995. Public support for environmental protection:

    Objective problems and subjective values in 43 societies. PS:

    Political Science and Politics 28:57-72.

    Kilbourne, W. E., S. C. Beckmann, A. Lewis, and Y. V. Dam. 2001. A

    multinational examination of the role of the dominant social para-

    digm in environmental attitudes of university students. Environ-

    ment & Behavior 33:209-28.

    Kilbourne, W. E., S. C. Beckmann, and E. Thelen. 2002. The role of

    the dominant social paradigm in environmental attitudes: A multi-

    national examination. Journal of Business Research 55:193-204.

    Kilbourne, W., P. McDonagh, and A. Prothero. 1997. Sustainable

    consumption and the quality of life: A macromarketing challenge

    to the dominant social paradigm. Journal of Macromarketing

    17:4-24.

    Kurzer, P., and A. Cooper. 2007. What’s for dinner?: European farm-

    ing and food traditions confront American biotechnology. Com-

    parative Political Studies 40:1035-58.

    Lockeretz, W. 2007a. What explains the rise of organic farming?

    In Organic farming: An international history, ed.

    W. Lockeretz, 1-8. Wallingford: CABI.

    ———. ed. 2007b. Organic farming: An international history. Wall-

    ingford: CABI.

    Magnusson, M. K., A. Arvola, U. K. Hursti, L. Åberg, and

    P. O. Sjöden. 2001. Attitudes towards organic foods among Swed-

    ish consumers. British Food Journal 103:209-26.

    Michelsen, J. 2001a. Recent development and political acceptance of

    organic farming in Europe. Sociologia Ruralis 41:3-20.

    ———. 2001b. The diffusion and institutionalization of organic farm-

    ing. Organic farming in a regulatory perspective. The Danish case.

    Sociologia Ruralis 41:62-84.

    Michelsen, J., U. Hamm, E. Wynen, and E. Roth. 1999. The European

    market for organic products: growth and development. In Organic

    farming in Europe: Economics and policy, ed., S. Dabbert, N.

    Lampkin, J. Michelsen, H. Nieberg, and R. Zanoli. Stuttgart-

    Hohenheim: Universität Hohenheim.

    Niggli, U. 2007. The evolution of organic practice. In Organic farm-

    ing: An international history, ed. W. Lockeretz, 73-92. Walling-

    ford: CABI.

    Ölander, F., and J. Thøgersen. 1995. Understanding of consumer beha-

    viour as a prerequisite for environmental protection. Journal of

    Consumer Policy 18:317-57.

    Padel, S., A. Jasinska, M. Rippin, and D. Schaack. 2008. The Eur-

    opean market for organic food in 2006. In The world of organic

    agriculture—Statistics and emerging trends 2008, eds.,

    H. Willer, M. Yussefi-Menzler, and N. Sorensen, 131-39. London:

    Earthscan.

    Padel, S., and N. H. Lampkin. 2007. The development of governmen-

    tal support for organic farming in Europe. In Organic farming: An

    international history, ed. W. Lockeretz, 93-122. Wallingford:

    CABI.

    Padel, S., N. H. Lampkin, S. Dabbert, and C. Foster. 2002. Organic

    farming policy in the European Union. In Economics of pesticides,

    184 Journal of Macromarketing 30(2)

    184 at Avans Hogeschool on September 16, 2011jmk.sagepub.comDownloaded from

    http://jmk.sagepub.com/

  • sustainable food production and organic food markets, eds.,

    D. C. Hall and L. J. Moffitt, 169-94. Oxford: Elsevier Science.

    Padel, S., N. Lampkin, and C. Foster. 1999. Influence of policy

    support on the development of organic farming in the European

    Union. International Planning Studies 4:303-15.

    Padel, S., and P. Midmore. 2005. The development of the European

    market for organic products: Insights from a Delphi study. British

    Food Journal 107:626-47.

    Richter, T. 2008. Trends in the organic retailing sector in Europe

    2007. In The world of organic agriculture—Statistics and

    emerging trends 2008, eds., H. Willer, M. Yussefi-Menzler, and

    N. Sorensen, 140-47. London: Earthscan.

    Richter, T., S. Padel, H. Willer, and M. Yussefi. 2007. The

    European market for organic food. In The world of organic

    agriculture—Statistics and emerging trends 2007. 143-54. Bonn,

    Germany: International Federation of Organic Agriculture Move-

    ments IFOAM and Frick, Switzerland: Research Institute of

    Organic Agriculture FiBL.

    Roininen, K., A. Arvola, and L. Lähteenmäki. 2006. Exploring

    consumers’ perceptions of local food with two different qualitative

    techniques: Laddering and word association. Food Quality and

    Preference 17:20-30.

    Roosen, J., J. L. Lusk, and J. A. Fox. 2003. Consumer demand for and

    attitudes toward alternative beef labeling strategies in France,

    Germany, and the UK. Agribusiness 19:77-90.

    Sahota, A., H. Willer, and M. Yussefi. 2007. Overview of the global

    market for organic food and drink. In The world of organic agricul-

    ture—Statistics and emerging trends 2007. 52-55. Bonn, Germany:

    International Federation of Organic Agriculture Moveme