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The dilemma of healthy eating and environmental sustainability: the case of fish

Published online by Cambridge University Press:  24 May 2011

Angie Clonan*
Affiliation:
Division of Nutritional Sciences, School of Biosciences, University of Nottingham, Loughborough LE12 5RD, UK
Michelle Holdsworth
Affiliation:
UMR NUTRIPASS, Institute of Research for Development, UM1, UM2, Supagro, Montpellier, France
Judy A Swift
Affiliation:
Division of Nutritional Sciences, School of Biosciences, University of Nottingham, Loughborough LE12 5RD, UK
Didier Leibovici
Affiliation:
Centre for Geospatial Science, University of Nottingham, Nottingham, UK
Paul Wilson
Affiliation:
Division of Nutritional Sciences, School of Biosciences, University of Nottingham, Loughborough LE12 5RD, UK Division of Agricultural and Environmental Sciences, School of Biosciences, University of Nottingham, Loughborough, UK
*
*Corresponding author: Email angieclonandilley@gmail.com
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Abstract

Objective

Despite widespread concern over exploitation of the European Union's fish stocks, dietary guidelines in the UK continue to recommend two portions of fish per week. The present study sought to investigate whether health and/or sustainability are motivating factors when purchasing and consuming fish and whether there are sociodemographic trends.

Design

A structured, self-completion postal questionnaire exploring consumers’ attitudes towards purchasing fish, their dietary intake, stated purchasing behaviour and sociodemographic information.

Setting

Nottinghamshire, UK.

Subjects

Adults from 842 households randomly selected from the electoral register.

Results

Over half of the participants (57·0 %) were aware of the health benefits of fish consumption and reported health as a primary motivator for purchasing fish; however, only 26·8 % actively sought to purchase fish from a sustainable source (e.g. Marine Stewardship Council (MSC) certified fish). Only 30·6 % of participants met current dietary recommendations for fish intake. Older respondents (>60 years of age) were more likely to report purchasing fish for health reasons and to buy MSC fish. Participants were significantly less likely to report MSC purchases if they agreed with the statement ‘I am confused about which type of fish I should be eating to protect fish stocks’ (P < 0·001).

Conclusions

The number of consumers purchasing fish for health reasons was more than those seeking sustainably sourced fish; yet, they still failed to meet the recommended intake set by the Food Standards Agency. Dietary advice to the public to increase consumption of fish conflicts with the prevailing pressure on fish stocks. Clear advice should be communicated enabling consumers to meet nutritional needs while protecting fish stocks.

Type
Research paper
Copyright
Copyright © The Authors 2011

UK dietary guidelines continue to recommend the consumption of at least two portions of fish per week, one of which should be oily(1), as regular fish consumption is associated with decreased risk of several health problems including CVD(2) and cancer(Reference Terry, Rohan and Wolk3). The beneficial effect of fish consumption, especially that of oily fish, is derived from omega-3 (n-3) fatty acids – in particular from the bioactive properties of EPA and DHA, both long-chain PUFA (LCPUFA) present only in the n-3 fats from marine sources. Although man can endogenously convert EPA and DHA from alternative sources of n-3 fatty acids, such as seeds, nuts and tofu(4), it is not a particularly efficient process(Reference Penny, Harris and Appel5). Fish, therefore, remains the predominant and most readily available source of n-3 fatty acids. Fish also has the advantage of being low in saturated fat, yet high in protein and Se, making it a healthy alternative to meat(Reference Brunner, Jones and Friel6). A recent review by the World Cancer Research Fund(7) advocates reducing the intake of red meat in the diet and partly replacing it with poultry or ‘all types of fish’; heeding such advice could place further demands on fish stocks.

If the UK population is to achieve the Food Standards Agency's (FSA) recommendation for fish intake of two 140 g portions per week(8), current consumption will need to be increased from the average of 1·2 portions per week reported in the most recent National Diet and Nutrition survey data(9). This would increase the demand on fish stocks in the European Union (EU) and around the world, which are already under pressure(10); some estimates suggest that fish stocks of over three-quarters of the world(11) and EU(Reference Thurstan, Brocklington and Roberts12) are currently either fully exploited or over-exploited. For consumers, balancing health motivation with concerns over sustainability can present a dilemma, particularly as very little guidance is available.

The second report of the Council of Food Policy Advisors (specifically entrusted with the task of making policy recommendations for sustainable production and consumption of food) highlights fish consumption as a core issue and recommends shifting targets for consumption towards produce that has come from only sustainably managed stocks, eliminating the consumption of threatened species(13). Although the problem has been highlighted, it has not yet been communicated effectively to the public. Although the FSA has acknowledged the need to raise consumers’ awareness of the type of fish consumed(14), and indeed recently updated its consumer guidelines for fish consumption to incorporate some information on sustainability and help consumers choose appropriate types of fish(15), the primary message for consumers to increase fish consumption remains unchanged. Moreover, its recommendations still include several types of fish that the UK Marine Conservation Society (MCS) believes are the most vulnerable to over-fishing and/or are fished using methods that damage the environment(16). In an effort to aid consumers, the Marine Stewardship Council (MSC), the world's leading certification and eco-labelling programme for sustainable seafood, uses its eco-label to communicate whether a fish or fish product is from a sustainable source(17). In addition, the MCS provides a ‘pocket guide’ to consumers(16) listing fish from sustainable sources and those to be avoided. Sustain(18), the alliance for better food and farming, reports only five types of fish that can be recommended to the consumer wishing to purchase for health and sustainability reasons. Communicating the complex information to consumers about choosing fish from sustainable sources is, however, challenging (Table 1).

Table 1 Guidelines for consumers on sustainability of tuna fish (adapted from guidelines provided by the Marine Conservation Society(16))

MSC, Marine Stewardship Council.

†No sustainable source identified.

It is clear that consumption of fish and fish products has a considerable impact on human nutrition, on the marine environment and on the long-term viability of fish stocks, but very little guidance is available to consumers when making purchasing decisions. Therefore, the present study sought to determine whether health and/or sustainability were motivating factors in terms of purchasing and consuming fish. In addition, the study aimed to examine the extent to which consumers were concerned about where the fish they purchased came from and whether they regularly purchased fish certified as sustainable by the MSC. Finally, the study aimed to investigate sociodemographic trends in the purchase of MSC fish, as well as attitudes towards fish purchase and consumption.

Methods

Design and sample

Nottinghamshire is situated in the East Midlands region, and this was selected as a useful study site as it offers a representative sample of the UK in terms of climate and geography(Reference Pettinger19). In addition, data from the most recent Family Food Survey show that the population of East Midlands consumes an average of 1·15 portions of fish per week, which is close to the national average(20). Self-administered questionnaires were mailed to 2500 Nottinghamshire residents, accompanied by an invitation letter, an information sheet and a freepost return envelope. Potential participants were randomly selected from five electoral registers encompassing both urban and rural areas (Nottingham City, Broxtowe, Rushcliffe, Gedling and Erewash). All non-responders were followed up with reminders after two weeks. All responses were anonymous and no incentive was provided.

Measures

Attitudes

Attitudinal items were created from thematic categories that were derived from qualitative interviews conducted by the authors with eleven Nottinghamshire adults (A Clonan, JA Swift, M Holdsworth et al., unpublished results). The interview schedule used in the qualitative interviews was structured around the consumer guidelines for sustainable food provided by Sustain(21), as it provides the best possible working definition for consumers that is currently available in the UK. Items were designed using the guiding principles outlined by Oppenheim(Reference Oppenheim22); for example, some items were worded positively and some negatively to avoid acquiescence response bias. The questionnaire was piloted using a sample consisting of forty-two women and thirty-eight men, recruited using opportunistic sampling. Frequency analysis was conducted on the pilot data and several statements were either removed or replaced because of their poor discriminative properties. The final attitudinal section consisted of seventy-two items covering a variety of sustainability-related issues that consumers are confronted with at the time of purchase (e.g. animal welfare, local food and organic food). Readers are invited to contact the corresponding author for a full copy of the questionnaire used. Six of these items related to fish purchase and consumption (Table 2). A 5-point Likert scale was used to assess attitudinal statements, with the scale ranging from ‘strongly agree’ to ‘strongly disagree’; participants were also able to state that the item was ‘not applicable’ to account for non-fish eaters and to reduce false reporting. To simplify analysis, responses to the attitudinal variables were categorized into ‘agree’ (combined responses for ‘strongly agree’ and ‘agree’), ‘neither agree nor disagree’ and ‘disagree’ (combined responses for ‘strongly disagree’ and ‘disagree’). The six items about fish purchase and consumption produced a Cronbach's α coefficient of 0·60, indicating that the construct was internally consistent and therefore reliable(Reference Bowling23). In addition, the six items produced a good spread of responses (Table 2) establishing their face validity(Reference Oppenheim22). The scale was also assessed for readability using the Flesch–Kincaid Reading Grade Level(Reference Kincaid, Fishburne and Rogers24) and achieved a score of 3·8, indicating that it was suitable reading material for 10–11-year-olds and therefore acceptable for use in a general UK population.

Table 2 Participants’ attitudes towards fish purchase/consumption

Purchasing behaviour

Participants were asked to indicate how frequently they purchased a range of categories of ‘sustainable food’. For fish, participants were asked to choose whether they purchased MSC-approved fish using a 4-point frequency scale ‘always’, ‘often’, ‘sometimes’ or ‘never’. Participants were also asked to indicate whether in the past 12 months they had purchased MSC fish ‘more often’, ‘less often’ or whether there was ‘no change’, when compared with the previous year.

FFQ

A semi-quantitative FFQ was developed on the basis of the five food groups defined in the UK's Eatwell plate(25). Participants were asked to choose how frequently they consumed fish on a scale from ‘never’ to ‘twice a day or more’. Standard food portion sizes were included on the basis of national food portion sizes, which for fish was ‘1 average fillet’, together with an image depicting one portion size. Daily intakes were calculated using this information.

Sociodemographic characteristics

Socio-economic and sociodemographic data were collected at both individual (gender, age, educational level and profession) and household levels (urban/rural, household income). Age groups were created by dividing participants into four groups on the basis of a life-stage approach: 18–30, 31–45, 46–60 and 61–91 years. Using multiple correspondence analyses (MCA), a socio-economic score was created that ranked participants using four demographic variables: educational level, occupation, household income and individual food expenditure (calculated by household food expenditure/number of people in the household). MCA is a multivariate statistical technique used to reduce the number of variables in a data set to a smaller number of dimensions and has been previously validated and used in the nutritional field(Reference Holdsworth, Gartner and Landais26Reference Leibovici28). The socio-economic score produced a Cronbach's α coefficient of 0·7, indicating reliability(Reference Bowling23). Participants were then ranked and divided into three groups – higher, medium and lower socio-economic status – each tertile representing one-third of the sample.

Data analysis

Data were entered into the Statistical Package for the Social Sciences statistical software package version 16·0 (SPSS Inc., Chicago, IL, USA) using EpiData software version 3·1 (EpiData Association, Odense, Denmark)(Reference Lauritsen, Bruus and Myatt29). An intra-rater reliability check was conducted on a random 10 % sample of questionnaires, which revealed an error rate of <1 %(Reference Meeuwisse, Hagel and Fick30). Categorical data were analysed using the χ 2 test, followed by the adjusted χ 2 test to ensure that observed differences were not due to confounding variables of gender, age group or socio-economic group. Significance was taken as P < 0·05.

Ethical considerations

The present study received approval from the Nottingham University Ethics Committee. Participants were considered to have given their consent to participate in the study if they completed and returned the questionnaire.

Results

Response rate

Of the 2500 individuals invited to participate in the present study, 842 usable responses were received and, following adjustment for people who had moved or died, a response rate of 35·6 % was achieved. Within the sample of 842 usable responses, participants ranged in age from 18 to 91 years, the majority of whom were in the two oldest age groups (31·8 % aged 46–60 years; 33·6 % aged ≥61 years; Table 3). Just under two-thirds of the sample were women (n 497, 59·9 %; Table 3).

Table 3 Sociodemographic characteristics of participants

Dietary intake

Participants consumed an average of 1·4 portions of fish per week. Overall, 31·7 % of participants consumed two or more portions of fish per week, but over two-thirds (68·3 %) did not meet the recommendation of two portions per week; in addition, 6·2 % reported ‘never’ consuming fish. Women were significantly (χ 2 (1) = 4·28; P < 0·05) more likely than men to meet this recommendation, as were participants in the oldest age group (χ 2 (3) = 10·58; P < 0·05; Table 4). These effects persisted when adjusted for age, gender and socio-economic group (Table 4). In addition, participants ranked in the highest socio-economic group were more likely to meet the required intake (χ 2 (2) = 5·75; P < 0·05), although this effect was diminished when the data were adjusted for gender and age (Table 4).

Table 4 Relationship between fish consumption and sociodemographic profile

*P < 0·05.

†Adjusted for gender, age and socio-economic group.

Attitudes to fish

More than half of the participants (57·0 %; Table 2) agreed that they purchased fish ‘mainly for the health benefits’ and a similar proportion disagreed with the statement ‘I am confused about which type of fish I should eat for health reasons’ (57·3 %; Table 2). Those participants agreeing that they bought fish ‘mainly for the health benefits’ were significantly more likely to meet the dietary recommendations for fish consumption (χ 2 (2) = 17·55; P < 0·001), as were those disagreeing that they were ‘confused about which type of fish I should eat for health reasons’ (χ 2 (2) = 15·17; P < 0·001). Just over a quarter of participants (29·0 %; Table 2) disagreed that they ‘don't usually check where the fish has come from’, whereas a similar proportion reported that they ‘always check that the fish I'm buying has come from a sustainable source’ (26·8 %; Table 2). In addition, more than a quarter of the participants were ‘confused about which type of fish I should be eating to protect fish stocks’ (28·5 %; Table 2) and over one-third (38·4 %; Table 2) agreed that they were ‘not sure whether to buy farmed fish’.

Participants from the oldest age group (61–91 years) were more likely to agree that they ‘buy fish mainly for the health benefits’ (χ 2 (6) = 40·53; P < 0·001) and also more likely to ‘check that the fish I'm buying has come from a sustainable source’ (χ 2 (6) = 17·89; P < 0·01), compared with the youngest age group (Table 5). No significant age effects were observed for the other attitudinal items. Women were also more likely to agree that they were ‘not sure whether to buy farmed fish’ (χ 2 (2) = 17·65; P < 0·001). No significant effects were observed between gender and socio-economic group for the other attitudinal items.

Table 5 Relationship between attitude towards fish and sociodemographic profile

*P < 0·05, **P < 0·01, ***P < 0·001.

†Adjusted for gender, age group and socio-economic group.

Purchasing data

Less than 10 % of participants reported purchasing MSC-labelled fish ‘always’ or ‘often’, whereas the majority (75 %) of participants declared ‘never’ purchasing MSC-labelled fish. No significant relationship between purchasing of MSC-labelled fish and gender, age or socio-economic group was observed.

Participants were significantly more likely to buy MSC-labelled fish regularly if they agreed with the statement ‘I always check that the fish I'm buying comes from a sustainable source’ (χ 2 (4) = 26·31; P < 0·001). Similarly, participants were significantly more likely to buy MSC-labelled fish regularly if they disagreed with the statement ‘I don't usually check where the fish has come from’ (i.e. implicitly suggesting that they do check) (χ 2 (4) = 18·45; P < 0·001). In addition, those participants were significantly less likely to buy MSC-labelled fish if they agreed with the statements ‘I am confused about which type of fish I should be eating to protect fish stocks’ (χ 2 (4) = 21·34; P < 0·001) and ‘I am not sure whether to buy farmed fish’ (χ 2 (4) = 23·12; P < 0·001).

Discussion

Just over half of the participants in the present study reported that they buy fish mainly for health reasons, indicating that health is important for some, particularly older, consumers – a finding that concurs with previous research(Reference Olsen31Reference Verbeke and Vackier34). As a consequence, just under half of the participants disagreed that they bought fish mainly for health reasons and approximately one-fifth (18·5 %) reported being confused about which type of fish to eat for health reasons. Interestingly, those participants who were meeting the recommended consumption were significantly more likely to be the ones who also agreed that they ‘buy fish mainly for health’ and were not confused about health issues. Therefore, although some participants have heeded the public health nutrition message, a considerable proportion of participants have not necessarily followed up on the health benefits associated with fish consumption. This strongly suggests that further health promotion in this area is required, an assertion that is further justified by the positive relationship between achieving the dietary recommendations of fish and beliefs about the health benefits of fish consumption found by the present study. Having said this, it has been estimated that if all consumers were to increase intake in order to meet the FSA's recommendation for fish intake of two 140 g portions per week, then supply in the UK would also have to be increased by 40 %(35). Increasing supply is, however, problematic as the marine ecosystem is already being exploited to such an extent that it is projected that worldwide fish stocks will be depleted by 2050(Reference Worm, Barbier and Beaumont36).

Although the public health nutrition message seems to have been taken on board by some UK consumers, there appears to be less awareness regarding sustainability issues when purchasing fish. Just over a quarter of the participants responded in a way that indicated that they usually check where their fish has come from, whereas a similar proportion indicated that they were not confused about which type of fish they should be eating to protect fish stocks (i.e. strongly disagree or disagree with negatively worded statements). Farmed fish represented a further source of confusion for a considerable number of participants, and this also requires clarification to enable consumers to make an informed choice. Low awareness levels are problematic as they are shown here to be associated with negative purchasing behaviour, and the reported purchasing of MSC fish in the present study was minimal.

Strengths and limitations

Much consideration was given to the construction of the questionnaire, particularly with regard to the issues of reliability and validity that were addressed during the development stage and that improved following piloting. Strategies were used to optimize the response rate(Reference Edwards, Roberts and Clarke37), which, following adjustment, was 35·6 %, with the female/oldest age group over-represented and the male/youngest age group under-represented, which is comparable to similar research conducted(Reference Pettinger, Holdsworth and Gerber38) and is favourable when considering the length of the questionnaire (twelve pages). Of the 2500 questionnaires sent out, a total of 842 were returned completed; as the sample was randomly selected the sociodemographic characteristics of non-responders remained unknown, which may have influenced the resulting data(Reference Kotaniemi, Hassi and Kataja39). Further limitations include space available in the questionnaire, particularly in the food-frequency section where the ideal would have discriminated between different types of fish consumed; however, as the questionnaire was self-completed, conciseness was paramount. Therefore, data on fish intake refer to total fish consumed and do not discriminate between canned and fresh fish. In addition, the FFQ has not been tested against any other measure for validity as its main purpose was to rank individuals’ intakes relative to each other within the sample, rather than be a measure of absolute intake. As the questionnaire was self-completed, other potential biases included the inability to verify whether participants had understood questions correctly and missing data from non-response. To counter these potential sources of bias, the questionnaire was piloted during its development to ensure that ambiguous questions were removed. Its subsequent simplicity was verified by its readability level that indicated that it was suitable reading material for 10–11-year-olds and therefore acceptable for use in a general UK population. Respondents with missing data were automatically excluded from the analysis for the overall scale; thus, this potential bias was accounted for.

Cronbach's α measuring internal consistency of the fish attitudinal scale was lower than what one would expect from a homogeneous scale that encompassed only one concept. However, this scale included attitudes towards health and sustainability of fish and hence α measured the coherence of these two combined concepts. Consequently, although the items were related and showed good internal consistency(Reference Streiner and Norman40), the resulting α might be expected to be lower than that of a scale testing only one homogeneous concept. Cronbach's α is also proportional to the number of items on a scale; hence, a scale of six items with an α of 0·6 is still acceptable.

Conclusions

The basis of the evidence that underpins current FSA recommendations for fish consumption (based on the Scientific Advisory Committee on Nutrition and the Committee on Toxicity report(2)) has recently been called into question(41). Further research is needed to assess whether two 140 g portions of fish (of which one should be oily) provides significant beneficial effects for all population groups(41). In the meantime, although the FSA may address the need for clearer information on the proposed ‘integrated food advice and information for consumers’, which will work alongside other UK Government departments after its launch in early 2011(13), at present there are more UK consumers stating that they buy fish for personal health reasons than there are stating that they buy after considering environmentally sustainable choices. It may be theoretically possible to do both(41), but scant guidelines are currently available to guide consumers. Data shown in the present study have demonstrated that there is not only a lack of awareness but also confusion, which is important as these factors were shown to be associated with low purchase of MSC-certified fish.

Implications for practice

One possible solution for the consumer's dilemma is ‘choice editing’, whereby retailers sell only sustainably sourced fish(42). At present, this option has been fully implemented by only one UK retailer(43) as others who initially pledged to sell only MSC-certified fish relinquished this goal after realizing that supply could not match demand(44). Action also needs to be taken at a food policy level to tackle the environmental impact of the food supply(Reference Caraher and Coveney45) so that the onus does not fall on the consumer to deal with such a pressing issue alone. The Sustainable Development Commission made some recommendations to the government in its recent report ‘Setting the Table’, which included promotion of sustainable fish by a celebrity chef, expansion of the MSC accreditation scheme and development of herbivore aquaculture(46). The report also suggested changing dietary guidelines to recommend eating less fish, and pointed out that public health problems resulting from a lack of fish will be worse in the long term if stocks deplete as estimates have predicted(46). All these suggestions require further consideration as it is likely that policy makers will have to implement a combination of measures to start addressing this issue.

Health promotion could be used to provide clearer messages to the public to support wider policy changes. Recommendation of only those species of fish certified as sustainable needs to be made in a plain and simple manner, and promotion of other sustainable sources of LCPUFA, such as algae(41), should be considered. The latter may mean revising current recommendations for fish intake, which have been described as unethical by some(Reference Bere and Brug47). Public health nutritionists and dietitians need to play a key role in communicating in simple terms to the general public how nutritional needs can be met while protecting fish stocks. As recently stated by Sulda et al.(Reference Sulda, Coveney and Bentley48) ‘…nutritionists have a responsibility to promote a food supply that is not only nutritious, but also sustainable’ (p. 305).

Acknowledgements

The present study was funded by the University of Nottingham. The authors have no conflict of interest to declare. A.C., M.H, J.A.S. and P.W. designed the project; A.C. analysed and interpreted the data with statistical input from D.L., M.H. and J.A.S.; A.C. drafted the article and M.H, J.A.S., D.L. and P.W. reviewed it critically for important intellectual content. All authors approved the final version to be published. The authors thank all participants for taking time to complete the questionnaire.

References

1. Food Standards Agency (2004) Oily fish advice: your questions answered. http://food.gov.uk.multimedia/faq/oilyfishfaq/ (accessed September 2009).Google Scholar
2. Scientific Advisory Committee on Nutrition, Committee on Toxicity (2004). Advice on Fish Consumption: Benefits and Risks. London: The Stationery Office.Google Scholar
3. Terry, PD, Rohan, TE & Wolk, A (2003) Intakes of fish and marine fatty acids and the risks of cancers of the breast and prostate and of other hormone related cancers: a review of the epidemiological evidence. Am J Clin Nutr 77, 532543.Google Scholar
4. The Vegetarian Society (2009) Information sheet – omega 3. http://www.vegsoc.org/info/omega3.html (accessed October 2009).Google Scholar
5. Penny, MEK, Harris, WS & Appel, LJ (2002) Fish consumption, fish oil, omega-3 fatty acids, and cardiovascular disease. Circulation 106, 27472757.Google Scholar
6. Brunner, EJ, Jones, PJS, Friel, S et al. (2009) Fish, human health and marine ecosystem health: policies in collision. Int J Epidemiol 38, 93100.CrossRefGoogle ScholarPubMed
7. World Cancer Research Fund/American Institute for Cancer Research (2007) Food, Nutrition, Physical Activity and the Prevention of Cancer: A Global Perspective. Washington, DC: AICR.Google Scholar
8. Food Standards Agency (2010) Fish and shellfish. http://www.eatwell.gov.uk/healthydiet/nutritionessentials/fishandshellfish/ (accessed October 2009).Google Scholar
9. Food Standards Agency (2010) National Diet Nutrition Survey: headline results from year 1. http://www.food.gov.uk/science/dietarysurveys/ndnsdocuments/ndns0809year1 (accessed June 2010).Google Scholar
10. Department for the Environment, Food and Rural Affairs (2009) Fish stocks: Common Fisheries Policy (CFP) Reform. http://www.defra.gov.uk/foodfarm/fisheries/policy/cfp/cfp-reform.html (accessed October 2009).Google Scholar
11. Food and Agriculture Organization of the United Nations (2006) The State of World Fisheries and Aquaculture. Rome: United Nations.Google Scholar
12. Thurstan, RH, Brocklington, S & Roberts, CM (2010) The effects of 118 years of industrial fishing on UK bottom trawl fisheries. Nat Commun 1, 15.CrossRefGoogle ScholarPubMed
13. Department for the Environment, Food and Rural Affairs (2010) Food: a recipe for a healthy, sustainable and successful future. Second Report of the Council of Food Policy Advisors. http://www.defra.gov.uk/foodfarm/food/policy/council/pdf/cfpa-rpt-100315.pdf (accessed November 2009).Google Scholar
14. Food Standards Agency (2009) Review of agency's advice on fish consumption. http://www.food.gov.uk/consultations/consulteng/2009/advicefishconsumption (accessed June 2009).Google Scholar
15. Food Standards Agency (2009) Agency's fish advice takes account of sustainability. http://www.food.gov.uk/news/newsarchive/2009/sep/fish (accessed October 2009).Google Scholar
16. Marine Conservation Society (2008) Fish Online: fish to avoid. http://www.fishonline.org/advice/avoid/ (accessed September 2009).Google Scholar
17. Marine Stewardship Council (2009) What we do. http://www.msc.org/about-us/what-we-do (accessed September 2009).Google Scholar
18. Sustain (2005) Like shooting fish in a barrel. http://www.sustainweb.org/foodfacts/like_shooting_fish_in_a_barrel/ (accessed October 2009).Google Scholar
19. Pettinger, C (2004) A comparison of the influences on food choice in Southern France and Central England. PhD Thesis, University of Nottingham.Google Scholar
20. Department for the Environment, Food and Rural Affairs (2008) Family Food. London: The Stationery Office.Google Scholar
21. Sustain (2009) Consumer guide to sustainable food. http://www.sustainweb.org/sustainablefood/ (accessed September 2009).Google Scholar
22. Oppenheim, AN (2005) Questionnaire Design, Interviewing and Attitude Measurement. London: Continuum.Google Scholar
23. Bowling, A (2002) Research Methods in Health: Investigating Health and Health Services, 2nd ed. Buckingham: Open University Press.Google Scholar
24. Kincaid, JP, Fishburne, RP, Rogers, RL et al. (1975) Derivation of New Readability Formulas (Automated Readability Index, Fog Count and Flesch Reading Ease Formula) for Navy Enlisted Personnel. Memphis, TN: Naval Air Station.CrossRefGoogle Scholar
25. Food Standards Agency (2008) The Eatwell plate. http://www.food.gov.uk/multimedia/pdfs/publication/eatwellplate0210.pdf (accessed September 2009).Google Scholar
26. Holdsworth, M, Gartner, A, Landais, E et al. (2004) Perceptions of healthy and desirable body size in urban Senegalese women. Int J Obes (Lond) 28, 15611568.CrossRefGoogle ScholarPubMed
27. Vyas, S & Kumaranayake, L (2006) Constructing socio-economic status indices: how to use principal components analysis. Health Policy Plan 21, 459468.CrossRefGoogle ScholarPubMed
28. Leibovici, DG (2010) Spatio-temporal multiway decomposition using principal tensor analysis on k-modes: the R package PTAk. J Statist Softw 34, 134.CrossRefGoogle Scholar
29. Lauritsen, JM, Bruus, L & Myatt, M (2000) EpiData: A Tool for Validated Data Entry and Documentation of Data. Denmark: Brixton Health.Google Scholar
30. Meeuwisse, WH, Hagel, BE & Fick, GH (1999) The impact of single versus dual data entry on accuracy of relational database information. J Inform Primary Care June issue, 28.Google Scholar
31. Olsen, SO (2001) Consumer involvement in seafood as family meals in Norway: an application of the expectancy–value approach. Appetite 36, 173186.CrossRefGoogle ScholarPubMed
32. Gempesaw, CM, Bacon, JR, Wessells, CR et al. (1995) Consumer perceptions of acquaculture products. Am J Agric Econ 77, 13061312.CrossRefGoogle Scholar
33. Olsen, SO (2003) Understanding the relationship between age and seafood consumption: the mediating role of attitude, health involvement and convenience. Food Qual Prefer 14, 199209.CrossRefGoogle Scholar
34. Verbeke, W & Vackier, I (2005) Individual determinants of fish consumption: application of the theory of planned behaviour. Appetite 44, 6782.CrossRefGoogle ScholarPubMed
35. The Royal Commission on Environmental Pollution (2004) Turning the tide: addressing the impact of fisheries on the marine environment. http://www.rcep.org.uk/reports/25-marine/documents/Turningthetide.pdf (accessed February 2011).Google Scholar
36. Worm, B, Barbier, EB, Beaumont, N et al. (2006) Impacts of biodiversity loss on ocean ecosystem services. Science 314, 787790.CrossRefGoogle ScholarPubMed
37. Edwards, P, Roberts, I, Clarke, M et al. (2002) Increasing response rates to postal questionnaires: systematic review. BMJ 324, 1183.CrossRefGoogle ScholarPubMed
38. Pettinger, CH, Holdsworth, M & Gerber, M (2006) Meal patterns and cooking practices in Southern France and Central England. Public Health Nutr 9, 10201026.Google Scholar
39. Kotaniemi, JT, Hassi, J, Kataja, M et al. (2001) Does non-responder bias have a significant effect on the results in a postal questionnaire study? Eur J Epidemiol 17, 809817.CrossRefGoogle Scholar
40. Streiner, DL & Norman, GR (2008) Health Measurement Scales: A Practical Guide to their Development and Use. Oxford: Oxford University Press.Google Scholar
41. National Heart Forum (2009) Fish: dietary advice and dwindling marine stocks – How do we manage the policy conflicts? Members Meeting 11 September 2009. http://nhfshare.heartforum.org.uk/RMAssets/NHFMeetingnotes/2009/Fish,%20sustainability%20&%20CHD%20prevention%20-%20Summary%20note_Sep%2009.pdf (accessed February 2011).Google Scholar
42. Sustainable Development Commission (2009) Sustainable Development Commission's response to the Review of Food Standard Agency's advice on fish consumption. http://www.sd-commission.org.uk/publications/downloads/SDCResponse_FSAReviewFishConsumption_Final.pdf (accessed October 2009).Google Scholar
43. Marks and Spencers (2009) Plan A: sustainable raw materials; fish. http://plana.marksandspencer.com/we-are-doing/sustainable-raw-materials/progress (accessed October 2009).Google Scholar
44. Natural England (2009) Sea fisheries: steps to sustainability. http://www.naturalengland.org.uk/Images/SeaFisheriesReport_tcm6-13325.pdf (accessed October 2009).Google Scholar
45. Caraher, M & Coveney, J (2004) Public health nutrition and food policy. Public Health Nutr 7, 591598.CrossRefGoogle ScholarPubMed
46. Sustainable Development Commission (2009) Setting the table: advice to government on priority elements of sustainable diets. http://www.sd-commission.org.uk/publications/downloads/Setting_the_Table.pdf (accessed July 2010).Google Scholar
47. Bere, E & Brug, J (2008) Towards health-promoting and environmentally friendly regional diets – a Nordic example. Public Health Nutr 12, 9196.CrossRefGoogle Scholar
48. Sulda, H, Coveney, J & Bentley, M (2009) An investigation of the ways in which public health nutrition policy and practices can address climate change. Public Health Nutr 13, 304313.CrossRefGoogle ScholarPubMed
Figure 0

Table 1 Guidelines for consumers on sustainability of tuna fish (adapted from guidelines provided by the Marine Conservation Society(16))

Figure 1

Table 2 Participants’ attitudes towards fish purchase/consumption

Figure 2

Table 3 Sociodemographic characteristics of participants

Figure 3

Table 4 Relationship between fish consumption and sociodemographic profile

Figure 4

Table 5 Relationship between attitude towards fish and sociodemographic profile