FNR Food & Nutrition Research 1654-6628 1654-661X Co-Action Publishing 19805 10.3402/fnr.v57i0.19805 Original Article Dietary intake and main sources of plant lignans in five European countries Tetens Inge 1 * Turrini Aida 2 Tapanainen Heli 3 Christensen Tue 1 Lampe Johanna W. 4 Fagt Sisse 1 Håkansson Niclas 5 Lundquist Annamari 3 Hallund Jesper 1 Valsta Liisa M. 3 6 The Phytohealth WP1 working group Division of Nutrition, National Food Institute, Technical University of Denmark, Søborg, DK, Denmark National Institute for Research on Food and Nutrition, Rome, IT, Italy National Institute for Health and Welfare, Helsinki, FI, Finland Fred Hutchinson Cancer Research Centre, Cancer Prevention Program, Seattle, WA, USA Institute of Environmental Medicine, Karolinska Institute, Stockholm, SE, Sweden European Food Safety Authority, Parma, IT, Italy Inge Tetens, Division of Nutrition, National Food Institute, Technical University of Denmark, Mørkhøj Bygade 19, DK-2860 Søborg, Denmark. Tel: +45 3588 7400. Email: intet@food.dtu.dk 11 06 2013 2013 57 10.3402/fnr.v57i0.19805 02 10 2012 08 04 2013 23 04 2013 © 2013 Inge Tetens et al. 2013

This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Background

Dietary intakes of plant lignans have been hypothesized to be inversely associated with the risk of developing cardiovascular disease and cancer. Earlier studies were based on a Finnish lignan database (Fineli®) with two lignan precursors, secoisolariciresinol (SECO) and matairesinol (MAT). More recently, a Dutch database, including SECO and MAT and the newly recognized lignan precursors lariciresinol (LARI) and pinoresinol (PINO), was compiled. The objective was to re-estimate and re-evaluate plant lignan intakes and to identify the main sources of plant lignans in five European countries using the Finnish and Dutch lignan databases, respectively.

Methods

Forty-two food groups known to contribute to the total lignan intake were selected and attributed a value for SECO and MAT from the Finnish lignan database (Fineli®) or for SECO, MAT, LARI, and PINO from the Dutch database. Total intake of lignans was estimated from food consumption data for adult men and women (19–79 years) from Denmark, Finland, Italy, Sweden, United Kingdom, and the contribution of aggregated food groups calculated using the Dutch lignin database.

Results

Mean dietary lignan intakes estimated using the Dutch database ranged from 1 to 2 mg/day, which was approximately four-fold higher than the intakes estimated from the Fineli® database. When LARI and PINO were included in the estimation of the total lignan intakes, cereals, grain products, vegetables, fruit and berries were the most important dietary sources of lignans.

Conclusion

Total lignin intake was approximately four-fold higher in the Dutch lignin database, which includes the lignin precursors LARI and PINO, compared to estimates based on the Finnish database based only on SECO and MAT. The main sources of lignans according to the Dutch database in the five countries studied were cereals and grain products, vegetables, fruit, berries, and beverages.

lignan intake secoisolariciresinol matairesinol lariciresinol pinoresinol

Plant lignans are plant-derived diphenolic compounds that belong to the group of phytoestrogens that are structurally similar to 17-estradiol. After ingestion, plant lignans are metabolized to the enterolignans enterodiol (END) and enterolactone (ENL) by colonic bacteria before they are absorbed (1, 2). END and ENL are detected in plasma within 8–10 h after intake of plant lignans (3), and their half-lives in plasma are approximately 5 and 13 h, respectively (4, 5). However, a substantial inter-individual variation has been detected in plasma concentrations and urinary excretion of enterolignans, partly due to the complex interaction between colonic environment and external and internal factors (6) which moreover, seems to be more dependent on the dietary lignan source than the absolute lignan intake (7). Reliable methods of exposure measurement are crucial for understanding the possible health benefits of plant lignans and the first step in this process is to establish comprehensive dietary databases to estimate plant lignan exposure in population-based studies (6).

Observational studies have examined the association between habitual intake of plant lignans – estimated from the intake of selected food items and their content of two major precursors of enterolignans secoisolariciresinol (SECO) and matairesinol (MAT) – and risk of developing lifestyle-related diseases, such as cardiovascular disease (8, 9), breast cancer (10), and prostate cancer (11). The metabolite responsible is ENL showing an inverse association with postmenopausal breast cancer risk (12) and mortality risk due to coronary heart disease, cardiovascular disease (13), and breast cancer (14) at high ENL serum levels. Furthermore, animal experiments on rats (15) and studies in vitro showed a breast cancer protective effect of END and ENL that is discussed to be imputable to their higher biological activity (16). Dietary lignan intake was also found to decrease the risk of adenocarcinoma of the esophagus and gastroesophageal junction on a case-control study (17).

As progress has been made in this area, a food database of Dutch plant foods was published (18) with data on the content of SECO and MAT, as well as two more recently identified precursors of mammalian lignans, lariciresinol (LARI) and pinoresinol (PINO) (19). Estimated dietary intakes of lignans in the Dutch diet based on the new food database of Dutch plant foods (20) suggest that plant lignan intakes are much higher than first reported (2124) and that LARI and PINO contribute approximately 75% to the estimated intake of plant lignans in the Dutch diet with the primary food group sources of lignans being beverages, vegetables, nuts and seeds, bread and fruits (20). A few oilseeds, such as flaxseed and sesame seeds have a high content of plant lignans (18), but the intake of such foods is only used by a small proportion of the population and commonly, the amounts consumed are low (20).

In addition to the improved understanding of the importance of total lignan intakes, it has become clear that the contribution of selected food groups to the total plant lignan intake may be different than originally expected due to the contribution from LARI and PINO. Therefore, it is necessary to re-estimate and re-evaluate the total intake of plant lignans and contribution from different food groups to the total intakes in other European countries.

The main objective of this study is to estimate the total intake of plant lignans and identify the main food sources of plant lignans in different European countries by using a Finnish lignan database (Fineli®) which includes two enterolignan precursors MAT and SECO and a Dutch lignan database which includes four enterolignan precursors SECO, MAT, LARI, and PINO.

Methods

The lignan intakes were calculated from 42 food groups that included plant foods and beverages known to be sources of lignans among European men and women. Each of the 42 food groups were given a lignan value for the content of the mammalian lignan precursors MAT, SECO, PINO, and LARI based on the lignan database of Dutch plant foods (18) or on only MAT and SECO based on the Fineli® database from Finland (24) as described in Appendix A. Both databases provide the Linnean binomial nomenclature for plants. The new lignan values for food groups were either weighted values or arithmetic means based on the food content of plant lignans available from commonly consumed food items best representing that food group. For example, in the case of Fineli®-based values, the lignan content of whole grain rye flour contributed most to the food group ‘rye’, whereas the value for cabbages was the arithmetic mean of all available lignan values for different types of cabbages. In the case of food group values based on the Dutch database, the food group values were based on a single analyzed food item (e.g. value of strawberry for the group ‘berries’) or arithmetic means drawn from the analyzed values available in the database (e.g. mean of tofu and soy milk for the group ‘soy products’).

Food consumption data for men and women were available for Denmark, Finland, Italy, Sweden, and the United Kingdom. The data included individual data from national dietary surveys (DK, FI, IT, UK) and from cohort studies in Sweden. An overview of the studies is presented in Table 1. All analyses were performed by using SPSS statistical software package (version 12, Chicago). The non-parametric Kruskal-Wallis ranked test was used to test the differences in the distribution of the total lignan intakes between Denmark, Finland, and Italy. Lignan intakes and source estimates were calculated by Microsoft Office Excel (2003).

Description of the food consumption data

Country Year Dietary data level N, age Methodology used Reference
Denmark 2000–2002 National dietary survey, data at individua. level F: 1,307; M: 1,156 25–64 years 7-day pre-coded food record (25)
Finland 2002 National dietary survey (FINDIET), data at individual level F: 1,095; M: 912 25–64 years 48-h dietary recall (26)
Italy 1994–1996 National dietary survey, data at individual level F: 682; M: 586 25–64 years 7-day mixed survey technique (27)
Sweden 1987–1990 Cohort studies (Swedish Mammography Cohort (SMC) & Cohort of Swedish Men (COSM), data at group level F: 37,854; M: 45,906 45–79 years 96-item food frequency questionnaire (FFQ) (28)
United Kingdom 2000–2001 National dietary survey, data at individual level F: 958; M: 76619–64 years 7-day dietary record (29)

F = females; M = males.

Results

The mean lignan intake estimated using the Dutch lignan database with the four lignan precursors SECO, MAT, LARI, and PINO was lowest among Finnish women (1,036 µg/day) and highest among Swedish men (1,947 µg/day) (Table 2). It is noticeable that the SECO and MAT figures are systematically smaller when calculated using the Dutch data set compared with the Finnish database. SECO contributed between 11 and 22% to the lignan intake, MAT between 1 and 3%, LARI between 41 and 45% and PINO between 32 and 44%. The total lignan intake was approximately four times higher when the estimates were calculated using the Dutch lignan database compared to the results based on the Finnish lignan database (Fineli® database). According to the latter estimates, the mean lignan intake was lowest among Italian women (272 µg/day) and highest among Danish women (439 µg/day) and SECO contributed between 81 and 94% to the lignan intake and MAT between 6 and 19%.

Lignan intakes (g/day) from five European countries calculated using the Dutch and the Finnish (Fineli®) lignan database (mean values)

Dutch lignan database Finnish (Fineli®) lignan database


Country Estimated lignan intake (g/day) Estimated lignan intake (g/day)
SECO MAT LARI PINO Total SECO MAT Total
Denmark
 All (n = 2,463) 314 41 630 473 1,459 375 57 432
 Female (n = 1,307 ) 314 43 641 486 1,484 380 59 439
 Male (n=1,156) 315 38 618 459 1,430 370 54 424
Finland
 All (n=2,007) 188 23 469 401 1,081 245 40 285
 Female (n=1,095) 176 21 455 384 1,036 245 34 279
 Male (n=912) 202 26 486 422 1136 246 48 293
Italy
 All (n=1,268) 143 11 500 467 1,120 290 19 309
 Female (n=682) 125 9 477 452 1,062 257 16 272
 Male (n=586) 165 14 527 484 1,188 329 23 351
Sweden
 All (n=83,760) 224 37 735 777 1,773 318 60 377
 Female (n=37,854) 203 28 657 675 1,563 300 39 339
 Male (n=45,906) 242 45 799 861 1,947 332 77 409
United Kingdom
 All (n=1,724) 205 19 535 480 1,239 267 17 285
 Female (n=891) 197 19 507 450 1,173 265 17 282
 Male (n=833) 214 19 570 518 1,321 270 18 288

The frequency distribution of the estimated total lignan intake among Danish, Finnish, and Italian adults using the Dutch and Finnish (Fineli®) lignan databases is shown in Fig. 1. The mean lignan intake between countries estimated using the Dutch lignan database of plant foods ranged from 404 µg/day among Finnish adults to 569 µg/day among Italian adults and was slightly skewed toward higher values. The mean lignan intake estimated using the Finnish (Fineli®) lignan database within one country ranged from 91 to 2,335 µg/day among Italian adults and was strongly skewed toward higher values. Significant differences were found between the three countries in the total lignan intakes estimated using both the Dutch database (P<0.001) and the Finnish (Fineli®) lignan databases (P<0.001) (data not shown).

Distribution of estimated lignan intake (µg/day) among adults in Denmark (A), Finland (B), and Italy (C) calculated using the Dutch and the Finnish (Fineli®) lignan database.

The main food groups and food items contributing to the lignan intake estimated using the Dutch lignan database are shown in Table 3. Only food groups and food items, that contributed more than 5% to total lignan intake, have been included in the table. The most important food groups were ‘cereals and grain products’, ‘vegetables’, and ‘fruit and berries’. Cereals and grain products contributed 15–43% of total lignan intake, vegetables16–30%, and fruit and berries 15–46%.

Contribution of aggregated food groups and individual foods to the total lignan intake by gender in five European countries calculated using the Dutch lignan database1(%)

Denmark Finland Italy Sweden United Kingdom





Food groups Men (%) Women (%) Men (%) Women (%) Men (%) Women (%) Men (%) Women (%) Men (%) Women (%)
Cereals and grain products 30 27 36 27 17 17 43 26 17 15
Rye 17 21 24 17 0 0 0 0 0 0
Wheat 7 4 7 6 11 9 24 12 8 6
Other grains 2 2 1 1 1 2 5 4 8 8
Crisp breads 0 0 2 2 3 5 14 10 0 0
Vegetables 19 20 16 20 26 28 18 30 23 25
Cabbages 5 5 4 6 5 5 11 19 16 17
Fruit vegetables 5 6 6 7 15 16 2 3 3 3
Onion-family vegetables 5 5 3 3 2 2 2 2 0 0
Fruit and berries 18 25 22 31 42 46 15 23 15 20
Citrus fruit 1 2 4 6 4 4 2 3 1 1
Malaceous and prunus fruit 1 2 5 8 36 38 7 10 6 7
Other fruit 14 19 4 5 1 1 2 4 5 7
Berries 1 1 5 8 1 2 4 5 2 4
Beverages 21 21 17 17 4 5 19 18 30 32
Coffee 15 12 12 10 3 3 9 9 11 10
Tea 5 9 5 8 1 2 10 9 19 22
Alcohol beverages 11 5 5 2 9 4 5 2 10 4
Beers 6 1 4 1 1 0 4 1 8 1
Wine 5 4 1 1 8 3 1 1 2 3

Only food groups and food items, which contributed to more than 5% of the total lignan intake at least in one of the countries, are included.

The Dutch food database includes the lignan precursors; secoisolariciresinol (SECO), matairesinol (MAT), lariciresinol (LARI), and pinoresinol (PINO).

Appendix A. Content of lignan and lignan precursors (SECO, MAT, LARI, PINO) in foods and notes on which the lignan values were chosen

Finnish (Fineli®) database Dutch database


Total lignanug/100g SECOug/100g MATug/100g Notes Total lignanug/100g LARIug/100g PINOug/100g SECOug/100g MATug/100g Notes
Cereal and grain products
Rye 95 40 55 Weighted mean (whole grain rye flour) 458 175 246 23 20 Ryebread x 1.43
Wheat 25 20 5 Weighted mean (wheat flour) 99 60 29 12 0 Wheatbread x 1.43
Oats and barley 18 13 5 Mean (rolled oats) 107 60 29 13 5 Estimate based on FINMAT&SECO and the proportions of new precursors
Rice 27.4 26.4 1 Mean of foods in the group of rice/rice containing foods 23.5 17.5 3.5 1.5 1 Mean of white rice and whole grain rice
Pasta and macaroni 14.5 11.6 2.9 Mean of all pastas 16 7 5 4 0 Cooked pasta
Other grains 16 15 1 Weighted mean (millet, corn, buckwheat) 485 157 313 15 0 Mean of 3 müslies
Crispbreads (as eaten) 52.4 27.4 25 Mean of foods in the food group, MAT-value weighted by rye crisp bread 412 156 221 21 18 Rye flour x 0.9
Biscuits (as eaten) 7.2 6.8 0.4 Mean of all foods in the group 18 9 4 5 0 White flour (taking into account the moisture)
Potatoes
Potato 3.2 2.0 1.2 Weighted mean (potato) 16 10 0 4 2 Potatoes (seco and matai estimates based on Fineli and proportions of new precursors)
Potato products 3.2 2.0 1.2 Weighted mean (french fries) 16 10 0 4 2 Potatoes
Vegetables
Root vegetables and tubers 17.5 16.6 0.9 Mean of root vegetables and tubers (excluding dried carrots) 88 31.5 9.5 47 0 Mean of carrot and red beet
Leafy vegetables 30.5 30 0.5 Weighted mean (lettuce) 57 35 12.5 9.5 0 Mean of spinach, chicory, endive, lettuce, Iceberg lettuce
Cabbages 30.5 30.3 0.2 Mean of the group 600 255 335 8 2 Weighted mean (most common cabbages)
Fruit vegetables 5.5 5.49 0.01 Weighted mean (tomato and cucumber) 132 103 19 10 0 Mean of sweet pepper, zucchini, cucumber and tomato
Onion-family vegetables 23.8 20 3.8 Mean, Seco-value weighted by onion 287 153 100 34 0 Mean of garlic, leek and onion
Canned vegetables 20 20.0 0.02 Mean of processed vegetables (excluding pickled pumpkin) 104 58.3 40.0 5.3 0 Mean of corn and pea
Edible fungi 6.0 2.4 3.7 Mean of the food group 0 0 0 0 0 Mushroom
Pulses and nuts
Pulses 4.5 4.4 0.1 Weighted mean (pea) 93 67 14 12 0 Estimate according to beans
Nuts and seeds 300 299 0.9 Weighted mean (almond, nuts) 287 8.2 25.3 253 0.5 Mean (nuts)
Soy products 30.5 30 0.5 Estimate according to major soy containing foods (soy flour, soy beans) 88.9 33.8 45.5 9.6 0 Mean of tofu and soy milk
Fruits
Citrus fruit 14.6 14.6 0.02 Mean of all citrus fruit 112 71 33 6 1.5 Mean of grape fruit, mandarine and orange
Malaceous and prunus species fruits 70.3 70 0.3 Mean of all malaceous and prunus species fruits 251 78 157 15.5 0 Mean of apricot, peach, pear, nectarine, prunes and apple
Other fruits 91.8 87.3 4.4 Mean of all other fruit 192 76.5 50 56 9.5 Mean of raisins, cherries, kiwi, olives, melons, grapes, pineapple and banana
Canned fruits 55.6 51.2 4.4 Mean of canned fruit 20 3 5 7 5 Canned pineapple
Berries 188 186 2.3 Mean of all berries 334 117 212 5 0 Strawberry
Juices 17 15 2 Weighted mean (orange juice) 18.1 5.4 4.1 6.7 1.9 Mean of grape, tomato, orange and grape fruit juices
Juice drinks 10.3 10 0.3 Weighted mean (berry juices) 35.5 3 1.5 30 1 Estimated according to Fineli berry juices and Milder et al. Berry values
Fats
Oils 0.7 0.6 0.1 Mean of oils 124 2.5 122 0 0 Mean of olive, soy and sunflower oils
Margarine and fat spread 0.01 0.01 0 Mean of margarines 39 7 0 32 0 Margarine
Beverages
Coffee 10 10 0 Estimate according to Milder et al. and Mazur et al. 25 11.1 0.95 12.7 0.35 Mean of three analyzed coffees
Tea 6 5 1 Calculated according to Mazur et al. 58.4 24.8 23.2 9.00 1.6 Mean of three black and one green teas
Soft drinks 1.3 1.3 0 0 0 0 0 0 Cola drink
Alcoholic beverages
Beers 1 1 0 Estimate according to Milder et al. 25.5 7.6 17.4 0.5 0 Mean of three lager bears
Wines 62.4 56.9 5.5 Mean of all foods in the group 55.7 10.4 6.8 33.3 5.3 Mean of three red and three white wines
Sugar and confectionery
Sugar and syrups 0 0 0 0 0 0 0 0
Other sugar products 5.3 5 0.3 Estimate according to nutspread and licoridgesauce 0 0 0 0 0
Non-chocolate confectionery 19.9 19.0 0.8 Mean (excluding halva) 0 0 0 0 0
Chocolate 10.1 10 0.1 Weighted mean (milk chocolate and mean chocolate) 43 20 23 0 0 Dark chocolate
Spices
Dried herbs 297 295 1.5 Mean of all in the food group 0 0 0 0 0
Dried spices 0 0 0 0 0 0 0 0
Condiments 27.9 27.7 0.3 Mean of all in the food group 0 0 0 0 0
Manufactured foods
Snacks 7.6 6.2 1.4 Mean of all in the food group 0 0 0 0 0
Chocolate powder 32.9 32.9 0 From the Fineli database 60 26 26 8 0 Cocoa powder

Beverages were an additional major source of lignans in all countries. The importance of selected food items varied across countries. Rye was the most important contributor to the lignan intake in the Scandinavian countries Denmark and Finland, whereas wheat and other grains were more important in Sweden, Italy, and United Kingdom. Cabbages were important contributors to lignan intake in Sweden and United Kingdom, whereas the group ‘fruit vegetables’ (e.g. sweet pepper, tomatoes) contributed most to the lignan intake from vegetables in Italy. Malaceous and prunus species fruits (e.g. apricot, peach, pear, and nectarines) were the most important contributors to lignan intake in Italy but were less important contributors in other counties. Tea was the most important contributor to lignan intake in the United Kingdom and in combination with coffee, was a major source to lignan intake in all countries. Among men in Denmark, Italy, and United Kingdom, alcoholic beverages, especially beer and wine contribute to about 10% of the total lignan intake (Table 3).

Discussion

The estimated mean lignan intake was approximately fourfold higher when calculations were based on the Dutch lignan database of plant foods including four lignan precursors compared with the calculations using the Finnish lignan database (Fineli®) that includes two lignan precursors SECO and MAT. The additional contribution to the mean lignan intake from the two additional precursors LARI and PINO was 41–45% and 32–44%, respectively. These results are in accordance with data from other investigators concluding LARI and PINO to present >70% of the total lignan intake (30). Dietary lignan intake further was more strongly associated with plasma enterolignan concentrations when taking all four mammalian lignans into account (31).

Estimations of lignan intake based on the Dutch lignan database showed that the major sources of lignans in Europe are from the food groups: ‘cereals and grain products’, ‘vegetables’, ‘fruit and berries’, and ‘beverages’.

In this study, we introduced a relatively simple approach to estimate total lignan intake when food intake data are available. In our approach, average lignan values were applied to food groups that are common in food databases. We used food groups that are known to contribute considerably to the total lignan intake and aggregated them into 42 food groups. The total amount of lignan intake was calculated based on the aggregated amounts of food consumed and the average weighted lignan content of that food group.

In this study, the estimated total lignan intakes based on the Dutch lignan database including four lignan precursors were of similar range as an earlier estimate of the lignan intake of 979 µg/day among Dutch men and women aged 19–97 years (20) and very recent estimates among Finnish men (7) and Italian men and women (32). Compared to the total lignan intakes among Dutch men and women, the total lignan intakes were higher in Denmark and Sweden and within similar range in Finland, Italy, and United Kingdom. The high lignan intakes in Denmark and Sweden were mainly due to a higher consumption of rye and wheat products, respectively. In all Scandinavian countries, cereals and grain products are important contributors to lignan intake whereas fruits and berries are main contributors in Italy and beverages (tea, coffee, and beer) are main contributors in the United Kingdom.

The inclusion of the precursors LARI and PINO in the estimated total lignan intake has shown that more food groups contribute to the total lignan intakes than earlier expected. Vegetables, fruit, and berries are important contributors to the total lignan intakes because they have a relatively high content of LARI and PINO (18). When using four lignan precursors, LARI, and PINO were the main contributors to the lignan intake in all five countries. This has been confirmed also in more recent studies (7, 32).

In earlier studies, where the lignan intakes was estimated based on MAT and SECO, the major contributor to the lignan intakes was grain products, whereas tea, coffee, nuts, seeds, and selected fruits and vegetables only contributed to a smaller proportion of the intake (21, 22) (33). The systematically lower values for the SECO + MAT intake values estimated using the Dutch database compared with the values estimated from the Finnish database can be explained mainly by the different analytical methods (18, 24).

Some issues need to be discussed in order to fully appreciate the results. First, the 42 food groups were selected because they are important contributors to lignan intake based on former knowledge (24). For each of the 42 food groups, a lignan value was chosen to represent the lignan content of all foods from that food group. The decisions on which these plant lignan values were chosen are provided in Appendix A. The lignan values were calculated from a mean of all foods from a particular food group or from a weighted average. An average was weighted according to the importance of foods consumed from a particular food group and taken into account that certain single foods such as sesame seeds and flaxseeds have a high lignan content. It should be noted that the approach used in this study results in a relatively narrow range of lignan intake. Furthermore, both food databases used in this study have been developed from analyses of locally representative foods in the Netherlands and Finland, respectively. Possible differences in the lignan content of country-specific foods due to differences in types of foods available, preparation of foods, available brands are not taken into account in this study. Finally, the fact that the food consumption data were collected using three different dietary assessment methods, i.e. 7-day food records in Denmark, Italy, and the United Kingdom, a 48-h dietary recall in Finland, and a food frequency questionnaire (FFQ) in Sweden, the results are not directly comparable. This may have led to a larger variation and differences in the estimated lignan intakes across countries. However, the results also reflect different dietary patterns and different food intakes.

In conclusion, we have shown that the total lignan intake was approximately fourfold higher after inclusion of the two new mammalian lignan precursors, LARI and PINO, when compared to estimates based on only SECO and MAT. Furthermore, we have shown that LARI and PINO contributed the majority of the lignan intakes in all five countries. When LARI and PINO were included in the estimation of the total lignan intakes, the major sources of lignans were cereals and grain products, vegetables, fruit, berries, and beverages.

Conflict of interest and funding

The authors have not received any funding or benefits from industry or elsewhere to conduct this study.

Acknowledgements

This article is written on behalf of the Phytohealth consortium WP1. Special thanks go to Taina Öhman, Corinna Koebnik, Eva Crammatiki, Alicia Wolk, Yannis Manios, Clarissa Bingham, and Aedin Cassidy for their collaboration to this work. This work was carried out with financial support from the Commission of the European Communities, PHYTOHEALTH QLRT-2001-09453. It does not necessarily reflect its views and in no way anticipates the Commission's future policy in this area.

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