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Omega-3 fatty acids and incident type 2 diabetes: a systematic review and meta-analysis

Published online by Cambridge University Press:  17 May 2012

Jason H. Y. Wu*
Affiliation:
Department of Epidemiology, Harvard School of Public Health, Boston, 665 Huntington Ave, Kresge Building-913, BostonMA 02115, USA School of Medicine and Pharmacology, University of Western Australia, Perth, Australia
Renata Micha
Affiliation:
Department of Epidemiology, Harvard School of Public Health, Boston, 665 Huntington Ave, Kresge Building-913, BostonMA 02115, USA
Fumiaki Imamura
Affiliation:
Department of Epidemiology, Harvard School of Public Health, Boston, 665 Huntington Ave, Kresge Building-913, BostonMA 02115, USA
An Pan
Affiliation:
Department of Nutrition, Harvard School of Public Health, Boston, MA, USA
Mary L. Biggs
Affiliation:
Department of Biostatistics, University of Washington, Seattle, USA
Owais Ajaz
Affiliation:
Divisions of Aging, Department of Medicine, Brigham and Women's Hospital and Harvard Medical School, MA, USA Massachusetts Veterans Epidemiology and Research Information Center, Boston Veterans Affairs Healthcare System, Boston, MA, USA
Luc Djousse
Affiliation:
Divisions of Aging, Department of Medicine, Brigham and Women's Hospital and Harvard Medical School, MA, USA Massachusetts Veterans Epidemiology and Research Information Center, Boston Veterans Affairs Healthcare System, Boston, MA, USA
Frank B. Hu
Affiliation:
Department of Epidemiology, Harvard School of Public Health, Boston, 665 Huntington Ave, Kresge Building-913, BostonMA 02115, USA Department of Nutrition, Harvard School of Public Health, Boston, MA, USA Channing Laboratory, Department of Medicine, Brigham and Women's Hospital and Harvard Medical School, Boston, MA, USA
Dariush Mozaffarian
Affiliation:
Department of Epidemiology, Harvard School of Public Health, Boston, 665 Huntington Ave, Kresge Building-913, BostonMA 02115, USA Department of Nutrition, Harvard School of Public Health, Boston, MA, USA Channing Laboratory, Department of Medicine, Brigham and Women's Hospital and Harvard Medical School, Boston, MA, USA Division of Cardiovascular Medicine, Department of Medicine, Brigham and Women's Hospital and Harvard Medical School, Boston, MA, USA
*
*Corresponding author: J. H. Y. Wu, fax +617 566 7805, email jasonwu@hsph.harvard.edu
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Abstract

The relationship between omega-3 polyunsaturated fatty acids (n-3 PUFA) from seafood sources (eicosapentaenoic acid, EPA; docosahexaenoic acid, DHA) or plant sources (alpha-linolenic acid, ALA) and risk of type 2 diabetes mellitus (DM) remains unclear. We systematically searched multiple literature databases through June 2011 to identify prospective studies examining relations of dietary n-3 PUFA, dietary fish and/or seafood, and circulating n-3 PUFA biomarkers with incidence of DM. Data were independently extracted in duplicate by 2 investigators, including multivariate-adjusted relative risk (RR) estimates and corresponding 95 % CI. Generalized least-squares trend estimation was used to assess dose–response relationships, with pooled summary estimates calculated by both fixed-effect and random-effect models. From 288 identified abstracts, 16 studies met inclusion criteria, including 18 separate cohorts comprising 540 184 individuals and 25 670 cases of incident DM. Consumption of fish and/or seafood was not significantly associated with DM (n = 13 studies; RR per 100 g/d = 1·12, 95 % CI = 0·94, 1·34); nor were consumption of EPA+DHA (n = 16 cohorts; RR per 250 mg/d = 1·04, 95 % CI = 0·97, 1·10) nor circulating levels of EPA+DHA biomarkers (n = 5 cohorts; RR per 3 % of total fatty acids = 0·94, 95 % CI = 0·75, 1·17). Both dietary ALA (n = 7 studies; RR per 0·5 g/d = 0·93, 95 % CI = 0·83, 1·04) and circulating ALA biomarker levels (n = 6 studies; RR per 0·1 % of total fatty acid = 0·90, 95 % CI = 0·80, 1·00, P = 0·06) were associated with non-significant trend towards lower risk of DM. Substantial heterogeneity (I2~80 %) was observed among studies of fish/seafood or EPA+DHA and DM; moderate heterogeneity ( < 55 %) was seen for dietary and biomarker ALA and DM. In unadjusted meta-regressions, study location (Asia vs. North America/Europe), mean BMI, and duration of follow-up each modified the association between fish/seafood and EPA+DHA consumption and DM risk (P-interaction ≤ 0·02 each). We had limited statistical power to determine the independent effect of these sources of heterogeneity due to their high collinearity. The overall pooled findings do not support either major harms or benefits of fish/seafood or EPA+DHA on development of DM, and suggest that ALA may be associated with modestly lower risk. Reasons for potential heterogeneity of effects, which could include true biologic heterogeneity, publication bias, or chance, deserve further investigation.

Type
Full Papers
Copyright
Copyright © The Authors 2012

Introduction

Type 2 diabetes mellitus (DM) accounts for 90–95 % of all diabetes cases and has reached epidemic proportions globally, including in both developed and developing countries(Reference Steyn, Mann and Bennett1). As a major risk factor for coronary heart disease, stroke, blindness, kidney failure, and peripheral arterial disease, DM poses tremendous public health burdens. Epidemiological and clinical trial evidence demonstrate that lifestyle including diet plays a major role in the development of DM(Reference Schulze and Hu2). Further understanding of the role of specific foods and nutrients in the pathogenesis of DM is of paramount importance.

Omega-3 polyunsaturated fatty acids (n-3 PUFA) include eicosapentaenoic acid (EPA, 20 : 5n-3) and docosahexaenoic acid (DHA, 22 : 6n-3) from seafood, and alpha-linolenic acid (ALA, 18 : 3n-3) from plant sources. Based on animal experimental studies, n-3 PUFA improve several metabolic abnormalities underlying the development of DM. Such effects include insulin-sensitizing effects via increased production and secretion of adipocytokines such as adiponectin and leptin(Reference Banga, Unal and Tripathi3Reference Perez-Matute, Perez-Echarri and Martinez6); and potential prevention of insulin resistance via anti-inflammatory effects mediated directly(Reference Oh, Talukdar and Bae7) or through conversion to specialized pro-resolution mediators such as resolvins and protectins(Reference Gonzalez-Periz, Horrillo and Ferre8, Reference Serhan, Chiang and Van Dyke9). Through modulation of transcription factors (e.g. sterol regulatory element binding protein-1c), n-3 PUFA could also enhance fatty acid oxidation and reduce de novo lipogenesis, effects which could reduce hepatic fat accumulation and preserve hepatic insulin sensitivity(Reference Tanaka, Zhang and Sugiyama10Reference Jump13).

Despite metabolic benefits in animal experiments, the impact of n-3 PUFA consumption on risk of DM in humans remain uncertain. In meta-analyses of controlled supplementation trials, n-3 PUFA supplementation does not produce major changes in biomarkers of glucose-insulin homeostasis in subjects with DM(Reference Friedberg, Janssen and Heine14Reference Montori, Farmer and Wollan16); similar trials in healthy subjects have reported conflicting findings(Reference Fedor and Kelley17). In addition to these short-term trials, which generally tested high supplemental doses of n-3 PUFA, several long-term prospective studies have assessed how habitual dietary consumption of n-3 PUFA or seafood, or circulating biomarkers of consumption, relate to incidence of DM, but with mixed findings. Therefore, whether n-3 PUFA influence risk of incident DM and, if so, the direction and magnitude of effect remain unknown. To address these important scientific and public health questions, we carried out a systematic review and meta-analysis of prospective studies that assessed the relation of dietary n-3 PUFA, fish and/or seafood consumption, and biomarker levels of n-3 PUFA with the incidence of DM.

Methods

Search strategy and eligibility criteria

We followed the Meta-analysis of Observational Studies in Epidemiology guidelines for the design, implementation, analysis and reporting of this study(Reference Stroup, Berlin and Morton18). We searched for all prospective cohort studies, including nested prospective studies, that assessed the association of dietary n-3 PUFA intake (ALA, EPA+DHA, or EPA and DHA individually), dietary fish and/or seafood intake, and biomarkers of n-3 PUFA (ALA, EPA+DHA, or EPA and DHA individually) with incidence of DM. Searches were performed electronically through MEDLINE, EMBASE, Latin American and Caribbean Health Sciences Literature (LILACS), related articles, hand-searching of references, and direct author contact. Key words included (among others) omega-3, alpha-linolenic acid, eicosapentaenoic acid, docosahexaenoic acid, fish oils, fishes, diabetes mellitus, cohort studies, prospective studies, and nested case control; the full search terms are available on request. Searches included the earliest available online indexing year through to June 30, 2011, with no language restrictions.

Studies were eligible for inclusion if they were prospective cohort studies that provided a multivariate-adjusted effect estimate (odds ratio, relative risk [RR], or hazard ratio) and information about its variance for any of the exposures of interest and incident DM. Exclusion criteria included studies of pregnant women or children ( < 19 y), studies of type 1 diabetes, retrospective case-control studies, cross-sectional and ecological studies, literature reviews, commentaries, editorials, letters, case reports, studies which investigated only shellfish or selected subtypes of fish intake (e.g., fried fish), and studies which provided only crude risk estimates. If multiple manuscripts were published from the same cohort, we included the most up-to-date analyses that had accrued the highest number of DM cases.

Selection of articles

The titles and abstracts of all identified articles were screened by one investigator (J. W.) for eligibility. Two investigators (J. W., R. M.) assessed independently and in duplicate the full texts of the remaining articles to reach a final decision on inclusion or exclusion, with differences resolved by consensus. Of 288 initially identified articles, 262 were excluded based on title and abstract (Fig. 1). Of 26 full text articles, 10 were excluded because they were duplicate publications from the same cohort (n = 3)(Reference Salmeron, Hu and Manson19Reference Song, Manson and Buring21), assessed consumption of restaurant fried fish intake but not overall fish intake (n = 1)(Reference Krishnan, Coogan and Boggs22), lacked RR estimates for fish or n-3 PUFA exposures (n = 4)(Reference Feskens, Virtanen and Rasanen23Reference Harding, Day and Khaw26), or did not separately report results for DM vs. impaired glucose tolerance (n = 2)(Reference Feskens, Bowles and Kromhout27, Reference Laaksonen, Lakka and Lakka28). After final exclusions, 16 studies were identified for inclusion in the meta-analysis(Reference Brostow, Odegaard and Koh29Reference Wang, Folsom and Zheng44).

Fig. 1 Search, screening, and selection process of prospective cohort studies of dietary n-3 PUFA, fish/seafood, and circulating n-3 PUFA biomarkers and risk of type 2 diabetes.

Data extraction

For each included study, data were extracted independently and in duplicate by two investigators (J. W., R. M.) using a standardized electronic form, including information on study design, study location (North America, Europe, or Asia/Australia), whether the analysis was pre-specified or post hoc, subject inclusion and exclusion criteria, sample size, subject age, body mass index (BMI), co-morbidities, gender, race, duration of follow-up (mean, median or max number of years), number of events, methods for dietary assessment and diagnosis of DM, laboratory procedure for fatty acid biomarkers (e.g. plasma phospholipid measurements), covariates adjusted for, and multivariable-adjusted risk estimates including data needed to calculate its variance (e.g., CI, SE, or P-value). For studies reporting risk across categories of exposure, we further recorded for each study the exposure-category-specific data on person-years of follow up, number of subjects, number of DM cases, median value of exposures, and risk estimate including its variance. For studies reporting on both fish and total seafood intake, we extracted both estimates. When more than one multivariable model was assessed, we extracted risk estimates having the greatest adjustment for potential confounders that did not also include potential intermediates (blood glucose, triglyceride, or inflammatory biomarkers). Whereas no single accepted criteria for grading quality of cohort exists, such grading can be useful for exploring quality and heterogeneity. We assessed quality using previously reported methods by considering 5 criteria: appropriateness and reporting of inclusion and exclusion criteria, methods for assessment of exposure, methods for assessment of outcome, adjustment for confounding, and evidence of bias(Reference Micha, Wallace and Mozaffarian45).

Among the 16 studies included in the meta-analysis, we contacted and received responses from authors of 11 studies for relevant missing information, such as baseline characteristics (age, BMI, exposure distributions) or exposure category data (number of participants, person-years of follow-up, number of cases, median level of exposure, or risk estimates and 95 % CI).

Statistical analysis

Because nearly all studies reported risk across exposure categories, risk estimates were meta-analyzed using the 2-step generalized least-squares trend (GLST) model(Reference Greenland and Longnecker46, Reference Orsini, Bellocco and Greenland47). This method utilizes all information from all exposure categories to estimate the log-linear dose-response slope within each study, which are then pooled to derive an overall risk estimate. For studies already reporting risk estimates for linear differences in exposure (e.g., per sd change in biomarker levels(Reference Krachler, Norberg and Eriksson34)) rather than in categories, data were added to the GLST model at the second stage. Because DM events were relatively rare in all studies, we considered odds ratios and hazard ratios to approximate RR. Necessary data for the first step of GLST included, for each exposure category in each study, the multivariable-adjusted risk estimate and its corresponding standard errors, person-years of follow-up (for prospective cohort studies) or number of subjects (for nested case-cohort studies), median level of exposure, and number of cases in each exposure category. When category-specific median intakes were not reported, they were imputed based on the midpoint of intake in the range in each category(Reference Vang, Singh and Lee42), or, for estimating category-specific EPA+DHA intake from fish or seafood intakes(Reference Nanri, Mizoue and Noda37, Reference Patel, Sharp and Luben39, Reference Vang, Singh and Lee42), by using a conversion factor calculated from nationally representative dietary surveys as part of our work in the Global Burden of Diseases study(Reference Micha, Kalantarian and Wirojratana48). The I 2 statistic was used to assess heterogeneity(Reference Higgins, Thompson and Deeks49). Fixed effect models were used to pool results with low I 2 ( < 35 %), whereas random effect models were used to pool studies with moderate or higher I 2 ( ≥ 35 %). We conducted secondary meta-analyses without GLST, by pooling the risk estimates comparing the highest to the lowest category in each study.

Potential heterogeneity was explored by meta-regression to examine whether risk estimates were significantly different according to several prespecified factors, each modeled individually and then, if significant in univariate models, together with other significant factors to determine independence. Potential sources of heterogeneity included age ( < or ≥  median of all cohorts; continous), study location (Asia or North America/Europe), sex (percent male or female), BMI ( < or ≥  median of all cohorts; continous), duration of follow-up (( or ≥  median of all cohorts; continuous), study quality score (low, 0–3 or high, 4–5), and whether the reported analysis was pre-specified or post hoc. Publication bias was assessed by visual inspection of funnel plots as well as with Begg's test(Reference Begg and Mazumdar50). All analyses were performed using STATA 10·0 (StataCorp, College Station, Tex), with 2-sided alpha=0·05.

Results

Study populations

The 16 studies covered 4 continents, including 9 studies in the US, 5 in Europe, 3 in Asia, and 1 in Australia (Table 1). In sum, 25 670 cases of incident DM were identified among 540 184 participants. The average participant was middle-aged, although ranges of ages within each cohort were relatively broad. The average follow-up duration in each study varied from 4·0 to 16·7 y among the 15 studies that reported this value. The majority of studies (14 of 16) were judged to be of high quality (quality score 4 or 5). Among dietary exposures, 13 cohorts provided risk estimates for fish and/or seafood, 12 cohorts for EPA+DHA with 4 additional cohorts having data allowing imputation of EPA+DHA, and 7 cohorts for ALA. Among biomarker exposures, 5 cohorts provided risk estimates for EPA alone, DHA alone, and EPA+DHA, and 6 cohorts for ALA. The ranges of dietary and biomarker exposure distributions for each study were broad (Supplementary Tables 1–2). All studies provided multivariable-adjusted risk estimates without adjustment for the potential intermediates of blood glucose, triglycerides, or inflammatory biomarkers.

Table 1 Characteristics of the identified 16 studies including 18 prospective cohorts that evaluated dietary n-3 PUFA, fish/seafood consumption, or biomarker n-3 PUFA levels and incidence of type 2 diabetes*

EPIC, European Prospective Investigation into Cancer and Nutrition; JPHC, Japan Public Health Center-based Prospective Study; Fish, refers to finfish; Seafood, refers to finfish and shellfish combined.

* All exposure-type 2 diabetes risk assessments were pre-specified primary analyses, except dietary fish/n-3 PUFA intake in Djousse et al (Reference Djousse, Biggs and Lemaitre30), which were secondary analyses.

Dietary exposures were all assessed using food frequency questionnaires; fatty acid biomarkers were measured in plasma phospholipids(Reference Djousse, Biggs and Lemaitre30, Reference Hodge, English and O'Dea32, Reference Patel, Sharp and Jansen38, Reference Wang, Folsom and Zheng44), plasma cholesterol esters(Reference Wang, Folsom and Zheng44); red blood cell membranes(Reference Krachler, Norberg and Eriksson34); red blood cell phospholipids(Reference Kroger, Zietemann and Enzenbach35, Reference Patel, Sharp and Jansen38), by gas or gas-liquid chromatography.

Degree of covariate adjustment indicated by (+): sociodemographics; (++): sociodemographics and other risk factors; (+++): sociodemographics and other risk factors and dietary variables.

§ Quality of each study was assessed by 5 separate criteria on an integer scale (0 or 1, with 1 being better). These included: appropriateness and reporting of inclusion and exclusion criteria, assessment of exposure (1 point if habitual n-3 PUFA/fish/seafood consumption was assessed with a validated diet assessment method, i.e. a validated FFQ or repeated short term measures; for biomarkers, a published laboratory assay), assessment of outcome (1 point if diagnosis of DM was confirmed according to accepted criteria and not based on self report), control of confounding (1 point if adjusted for socio-demographic plus either other risk factors or dietary variables for dietary studies; 1 point if adjusted for socio-demographic plus other risk factors for biomarker studies) and evidence of bias (1 point if no evidence of bias). Scores were summed and studies with scores from 0 to 3 and 4 to 5 were considered lower and higher quality, respectively.

Dependent on the study, additional data requested included baseline characteristics (age, BMI, exposure distributions) and exposure category-specific data (number of participants, person-years of follow-up, number of cases, median level of exposure, risk estimates and 95% CI).

Nested selection of cases and controls within the original cohort. The total number of participants recruited in the original cohorts were: Melbourne Collaborative Cohort Study, n 41 528(Reference Hodge, English and O'Dea32); Vasterbotton intervention program(Reference Krachler, Norberg and Eriksson34), n 33 336; EPIC-Norfolk, n 25 639(Reference Patel, Sharp and Jansen38).

** Dietary EPA+DHA in these studies were imputed from fish/seafood intake by using a conversion factor calculated from nationally representative dietary surveys as part of our work in the Global Burden of Diseases study(Reference Micha, Kalantarian and Wirojratana48).

Fish/seafood consumption

Across 13 cohorts, consumption of fish and/or seafood was not significantly associated with incidence of DM (per 100 g/d, RR = 1·12, 95 % CI = 0·94, 1·34, P = 0·21, Fig. 2). Substantial between-study heterogeneity was evident (I 2 = 82·9 %). In stratified analyses and unadjusted meta-regressions, study location (Asia vs. North America/Europe), mean BMI, and duration of follow-up each significantly modified the association of fish/seafood intake and risk of DM. Lower risk was seen in studies from Asia, in studies with lower mean BMI ( < 24·5 kg/m2), and in studies with shorter durations of follow-up ( < 10 y); and higher risk in studies from North America/Europe, with higher mean BMI ( ≥ 24·5 kg/m2), and with longer durations of follow-up ( ≥ 10 y) (P-Interaction ≤ 0·007 each). For example, fish/seafood was associated with lower DM risk in Asia cohorts (RR per 100 g/d = 0·89, 95 % CI = 0·81, 0·98), and higher risk in North America/Europe cohorts (RR per 100 g/d = 1·38, 95 % CI = 1·13, 1·70) (Fig. 3).

Fig. 2 Relative risk of type 2 diabetes associated with fish and/or seafood consumption in 13 prospective cohorts including 481 489 participants and 20 830 cases of incident diabetes. Within-study relative risks and 95 % CI's were quantified using generalized least squares trend estimation, and study-specific results were pooled using random effect meta-analysis. For 3 cohorts reporting effect estimates for both fish and seafood intake, (Reference Brostow, Odegaard and Koh29, Reference Villegas, Xiang and Elasy43) effects estimates for fish were used in the primary analysis; findings using seafood did not appreciably alter results (not shown).

Fig. 3 Relative risk of type 2 diabetes associated with fish and/or seafood consumption in prospective cohort studies stratified according to study location in North America/Europe (top panel) vs. Asia (bottom panel). Within-study relative risks and 95 % CI's were quantified using generalized least squares trend estimation, and study-specific results were pooled using random effect meta-analysis. Effect modification by study location was significant (P-Interaction = 0·007).

Because study location, mean BMI, and duration of follow-up were highly collinear across studies – the cohorts from Asia were generally the same as those with lower mean BMI and shorter durations of follow-up (Fig. 3) – none of these three factors remained statistically predictive of heterogeneity in multivariable meta-regression including all three factors (P ≥ 0·18 each). Even among studies restricted to North America/Europe, substantial unexplained heterogeneity remained (I 2 = 70·1 %); no heterogeneity was evident across studies in Asia (I 2 = 0 %).

When we repeated meta-analysis of risk estimates comparing the top to the bottom exposure category in each study, similar results were seen, with no overall pooled association between fish/seafood consumption and incidence of diabetes (RR = 1·07, 95 % CI = 0·94, 1·22, P = 0·29, I 2 = 77·7 %). When evaluated separately, study location, mean BMI, and duration of follow-up each again significantly modified the association between fish/seafood intake and risk of DM (P-interaction < 0·05 each), with similar collinearity as above. Overall findings were also similar when restricted to the 8 risk estimates for fish consumption alone or the 8 risk estimates for seafood consumption alone (data not shown).

Dietary EPA and DHA

Across 16 cohorts, estimated EPA+DHA consumption was not associated with DM risk (per 250 mg/d, RR = 1·04, 95 % CI = 0·97-1·10, P = 0·27, Fig. 4). Substantial heterogeneity was evident (I 2 = 82 %). Because these studies of estimated EPA+DHA consumption were largely overlapping with the studies of fish consumption described above, in unadjusted meta-regressions this heterogeneity again appeared partly related to varying study location, mean BMI, and durations of follow-up (P-interaction ≤ 0·02 each), with similar collinearity among these factors as described previously. For example, in studies in Asia, EPA+DHA consumption was associated with lower incidence of DM (per 250 mg/d, RR = 0·95, 95 % CI = 0·91, 0·99), with minimal heterogeneity across studies (I 2 = 14·7 %); whereas in studies in North America/Europe, EPA+DHA consumption was associated with higher incidence of DM (per 250 mg/d, RR = 1·12, 95 % CI = 1·05, 1·20), with substantial remaining heterogeneity (I 2 = 67·5 %) (Supplementary Fig. 1).

Fig. 4 Relative risk of type 2 diabetes associated with estimated dietary EPA+DHA in 16 prospective cohorts including 440 873 participants and 21 512 cases of incident diabetes. Within-study relative risks and 95 % CI's were quantified using generalized least squares trend estimation, and study-specific results were pooled using random effect meta-analysis. Exclusion of 4 studies for which the EPA+DHA intake was imputed from dietary fish/seafood(Reference Nanri, Mizoue and Noda37, Reference Patel, Sharp and Luben39, Reference Vang, Singh and Lee42), did not appreciably alter the results (per 250 mg/day, RR = 1·06, 95 % CI = 0·99, 1·14, P = 0·08).

Meta-analysis of risk estimates comparing the top vs. bottom exposure category in each study gave similar results, with no overall pooled association between EPA+DHA consumption and incidence of diabetes (RR = 1·04, 95 % CI = 0·94, 1·16, P = 0·46, I 2 = 79·0 %). Among the 5 cohorts reporting risk estimates for estimated dietary EPA or DHA separately, neither EPA (per 125 mg/d, RR = 1·07, 95 % CI = 0·85, 1·34, P = 0·58) nor DHA (per 125 mg/d, RR = 1·04, 95 % CI = 0·90, 1·21, P = 0·59) were significantly associated with incidence of DM, although substantial heterogeneity was present for both estimates (I 2 = 77·4 % and 80·2 %, respectively).

Circulating EPA+DHA

Among 5 cohorts that evaluated circulating EPA+DHA biomarkers, no association was seen between EPA+DHA concentrations and incidence of DM: per 3 % of total fatty acids, RR = 0·94, 95 % CI = 0·75, 1·17, P = 0·56 (Fig. 5). Moderate heterogeneity was evident (I 2 = 40·4 %). Meta-regression did not identify any statistically significant sources of heterogeneity, although statistical power was limited due to only 5 studies. Four cohorts were from North America/Europe, and one from Australia; none were from Asia. Excluding the Australian cohort, EPA+DHA concentrations were not associated with higher incidence of DM: per 3 % of total fatty acids, RR = 0·88, 95 % CI = 0·72, 1·08). Meta-analysis of risk estimates for the top vs. bottom exposure category in each study gave similar results (RR = 0·94, 95 % CI = 0·82, 1·09, I 2 = 47 %). When circulating EPA and DHA were evaluated separately, neither EPA (per 1 % of total fatty acids, RR = 0·96, 95 % CI = 0·86, 1·07, P = 0·48, I 2 = 0 %) nor DHA (per 1 % of total fatty acids, RR = 1·00, 95 % CI = 0·91, 1·10, P = 0·97, I 2 = 0 %) were significantly associated with incidence of DM.

Fig. 5 Relative risk of type 2 diabetes associated with EPA+DHA biomarker concentrations (as % of total fatty acids) in 5 prospective cohorts including 10 382 individuals and 1581 incident diabetes cases. Within-study relative risks and 95 % CI's were quantified using generalized least squares trend estimation, and study-specific results were pooled using random effect meta-analysis. Pooling results using the alternative biomarker measurements (red blood cell phospholipids) in Patel et al (Reference Patel, Sharp and Jansen38), did not appreciably alter the results (per 3 % of total fatty acids, RR = 0·96, 95 % CI = 0·76–1·21). The study by Wang et al (Reference Wang, Folsom and Zheng44), was not included due to insufficient information to allow extraction of effect estimates. However, EPA and DHA were not associated with risk of diabetes (Reference Wang, Folsom and Zheng44), and inclusion of this study is unlikely to appreciably alter the observed results.

Dietary ALA

Across 7 cohort studies, estimated ALA consumption was associated with a non-significant trend toward lower incidence of DM (per 0·5 g/day, RR = 0·93, 95 % CI = 0·83, 1·04, P = 0·20, Fig. 6). Heterogeneity was present (I 2 = 54·3 %), but no statistically significant sources of heterogeneity were identified by meta-regression, although power was limited. Similar results were obtained in meta-analysis of risk estimates comparing the top to the bottom exposure category in each study (RR = 0·92, 95 % CI = 0·80, 1·05, P = 0·21, I 2 = 40·3 %).

Fig. 6 Relative risk of type 2 diabetes associated with dietary ALA in 7 prospective cohorts including 131 940 individuals and 7365 incident DM cases. Within-study relative risks and 95 % CI's were quantified using generalized least squares trend estimation, and study-specific results were pooled using random effect meta-analysis.

Circulating ALA

In 6 cohorts that assessed circulating ALA biomarkers, higher ALA levels were associated with a non-significant trend towards lower risk of DM (per 0·1 % of total fatty acids, RR = 0·90, 95 % CI = 0·80, 1·00, P = 0·06, Fig. 7). Between-study heterogeneity was not evident (I 2 = 17·9 %). Results were similar in meta-analysis of risk estimates in the top vs. bottom exposure category in each study (RR = 0·87, 95 % CI = 0·74, 1·01, P = 0·07, I 2 = 18·9 %).

Fig. 7 Relative risk of type 2 diabetes associated with ALA biomarker (as % of total fatty acids) in 6 prospective cohorts including 13 291 individuals and 1833 incident diabetes cases. Within-study relative risks and 95 % CI's were quantified using generalized least squares trend estimation, and study-specific results were pooled using random effect meta-analysis. Pooling results using the alternative lipid compartment of biomarker measurements from Wang et al. (Reference Wang, Folsom and Zheng44) and Patel et al. (Reference Patel, Sharp and Jansen38) did not appreciably alter the results (per 0·1 % of total fatty acids, RR = 0·93, 95 % CI = 0·85–1·02, P = 0·11).

Publication bias

For dietary fish/seafood intake, visual inspection of the funnel plot found that individual study RR estimates were reasonably symmetrical about the pooled effect estimate, suggesting no evidence of publication bias (Supplementary Fig. 2, top panel). This was supported by a null Begg's test for publication bias (P = 0·45). For dietary EPA+DHA intake, the funnel plot showed slightly more data points among the smaller studies to the left of the pooled estimate of RR, indicating possible publication bias in favor of a protective association (Supplementary Fig. 2, bottom panel). Begg's test (P = 0·59) suggested no significant evidence of publication bias. There was also little evidence for publication bias for all other exposure-outcome relationships based on either visual inspection of funnel plots or Begg's test (data not shown).

Discussion

The overall findings from this systematic review and meta-analysis suggest that dietary EPA+DHA and fish/seafood consumption do not have either major harmful or beneficial associations with the development of DM. However, we identified substantial heterogeneity in findings across studies. Our findings also suggest that plant-derived ALA could be protective, though this result was of borderline statistical significance.

Fish/seafood intake, n-3 PUFA, and DM risk

We found little evidence that fish or seafood, dietary EPA+DHA, or circulating EPA+DHA biomarkers were associated with risk of DM overall. These studies typically comprised moderately overweight but otherwise generally healthy participants at baseline. Prior short-term randomized controlled trials have found very little effect of n-3 PUFA supplementation on glucose metabolism or indices of insulin resistance in healthy subjects(Reference Itoh, Suganami and Satoh5, Reference Griffin, Sanders and Davies51Reference Egert, Fobker and Andersen53). Therefore, our overall findings are consistent with these prior metabolic trials and suggest that, at typical dietary levels of consumption in generally healthy subjects, fish, seafood, or dietary EPA+DHA may have minimal effects on development of DM.

Our results also demonstrate large heterogeneity between study results. Such heterogeneity could be due to chance, or related to variations in population characteristics, geographical locations, or study methodology. Studies included in the meta-analyses generally had high quality score ( ≥ 4) and were pre-specified analyses, and these factors were not significant sources of heterogeneity. Conversely, EPA+DHA and fish/seafood consumption were associated with lower risk of DM in studies conducted in Asia, and higher risk of DM among studies conducted in North America/Europe. Mean cohort BMI and duration of follow-up were also potential sources of heterogeneity, but these study characteristics tracked with study location and their independent effects could not be confirmed.

Reasons for heterogeneity of effects by region could include true biologic diversity, publication bias, or chance. For example, average types of fish consumed or fish preparation methods may be different in Asia vs. North America/Europe, with potentially greater fatty fish and raw/steamed fish in the former, vs. white fish or deep fried fish in the latter, that could influence risk of DM. Pathophysiologic pathways for DM risk could also differ, and be differently influenced by n-3 fatty acids, in Asian vs. Caucasian populations; for example, Asians suffer DM at much lower BMI, with reasons not yet fully understood(Reference Chiu, Austin and Manuel54, Reference Wildman, Gu and Reynolds55). Given potential benefits of fish or EPA+DHA consumption on total mortality, (Reference Mozaffarian and Wu56) greater survivorship could also be a partial explanation for higher risk of DM in longer-term studies, but this seems less likely to us and should be evaluated by assessment of competing mortality in future studies. All of these subgroup findings may also be due to chance and also should be interpreted cautiously as all analyses of heterogeneity were based on average study-level, rather than individual-level, characteristics. Additional studies in diverse cultures and geographical regions, as well as studies assessing potential interaction with BMI or individual-level duration of follow-up, should explore these issues. Notably, studies that used objective biomarkers of EPA+DHA found no evidence for higher diabetes risk, including cohorts from North America/Europe. This suggests that the observed higher risk in stratified analyses including only North America/Europe studies that utilized self-reported estimates of fish or EPA+DHA consumption could be partly related to the dietary assessment method, rather than to biologic effects of EPA+DHA per se.

ALA and DM risk

Compared with seafood sources, we identified fewer prospective studies of ALA and incident DM. We found that both estimated dietary consumption and circulating biomarkers of ALA were associated with a modest, nonstatistically significant trend towards lower risk of DM. These pooled estimates demonstrated relatively low heterogeneity between-studies, suggesting more consistent findings among studies. In several animal models, dietary ALA or flaxseed oil (a rich source of ALA) improved insulin sensitivity and glycemic responses(Reference Ghafoorunissa, Ibrahim and Natarajan57Reference Kelley, Vemuri and Adkins59). Similarly, some(Reference Wendland, Farmer and Glasziou60, Reference Bloedon, Balikai and Chittams61), but not other(Reference Egert, Fobker and Andersen53), short-term randomized clinical trials found that ALA or flaxseed oil moderately improved fasting plasma glucose and markers of insulin resistance in humans. Our current results add to these limited but potentially important data that ALA may provide moderate protection against the development of DM. Because plant sources of n-3 PUFA are potentially more widely available on a global basis, our findings highlight the need for further clinical and observational investigation of these effects.

Strength and limitations

Our analysis had several strengths. Multiple databases were systematically searched to ensure identification of all relevant published studies, and we also obtained clarification and/or additional data from several authors to minimize misclassification and potential for publication bias. The prospective cohort design of the included studies reduces the possibility of recall and selection bias. The large number of total incident DM cases provided statistical power to detect clinically meaningful associations. We pooled all available information from each study using GLST, which accounts for both categories of exposure and dose-response, rather than simply pooling often incomparable single extreme categories. We evaluated both dietary estimates and objective biomarkers of n-3 PUFA, and consistent findings for each increased confidence in validity of our findings. Studies were identified from wide geographical locations (North America, Europe, Asia, Australia) with varied population characteristics (age, BMI, sex, exposure distributions), increasing generalizability.

Potential limitations should be considered. Although most studies adjusted for major sociodemographic, lifestyle, clinical, and other dietary risk factors, the possibility of residual confounding by unmeasured or imprecisely measured factors remains a possibility, particularly as both seafood and ALA consumption are often associated with healthier lifestyles. Conversely, measurement error in exposures could have attenuated true effects towards the null, causing underestimation of associations. The consistency of findings for both dietary and biomarker exposures is reassuring, as self-reported dietary estimates and n-3 PUFA biomarkers are subject to differing types of error and sources of confounding. Most studies evaluated total fish and/or seafood consumption, and we were unable to evaluate specific fish species or preparation methods which might influence effects on DM. As in all meta-analyses, publication bias is possible. However, visual inspection of funnel plots did not suggest publication bias was a substantial problem; our direct contact with authors and experts minimized the possibility of missing unpublished studies; and the overall null pooled findings are typically less subject to influence from publication bias than significant positive or inverse relations.

Conclusions

Based on all available evidence from prospective studies, neither EPA+DHA nor fish/seafood intake have significant associations with risk of DM overall, while plant-derived ALA is associated with nonsignificant trends toward lower risk.

Acknowledgements

The study was supported by the NHLBI, NIH, with additional support from the Office of Dietary Supplements (R01 HL085710) and by a Research Fellowship from the National Heart Foundation of Australia. We thank the following authors for providing clarification on their published articles and/or additional unpublished data: Aaron Folsom, Katie Meyer, Lu Wang, Allison Hodge, Benno Krachler, Nita Forouhi, Pinal Patel, Geertuida van Woudenbergh, Andrew Odegaard, Janine Kröger, Akiko Nanri, and Raquel Villegas. We would also like to thank the NHLBI, NIH and National Heart Foundation of Australia for funding support. Conflict of Interest Statement: Dr. Mozaffarian reports research grants from GlaxoSmithKline, Sigma Tau, Pronova (significant), ad hoc travel reimbursement and/or honoraria from International Life Sciences Institute, Unilever, Bunge, SPRIM, Nutrition Impact (modest); ad hoc consulting fees from Foodminds, McKinsey Health Systems Institute (modest); and royalties from UpToDate (modest). The other authors report no conflicts of interest. Author Contributions: Jason Wu: study concept and design; data extraction and statistical analysis; interpretation of data; drafting of the manuscript; critical revision of the manuscript for important intellectual content; approval of final manuscript for submission. Renata Micha: data extraction; interpretation of data; critical revision of the manuscript for important intellectual content; approval of final manuscript for submission. Fumiaki Imamura: statistical advice; interpretation of data; critical revision of the manuscript for important intellectual content; approval of final manuscript for submission. An Pan: interpretation of data; critical revision of the manuscript for important intellectual content; approval of final manuscript for submission. Mary Biggs: interpretation of data; critical revision of the manuscript for important intellectual content; approval of final manuscript for submission. Owais Ajaz: interpretation of data; critical revision of the manuscript for important intellectual content; approval of final manuscript for submission. Luc Djousse: interpretation of data; critical revision of the manuscript for important intellectual content; approval of final manuscript for submission. Frank Hu: interpretation of data; critical revision of the manuscript for important intellectual content; approval of final manuscript for submission. Dariush Mozaffarian: study concept and design; statistical advice; obtained funding; drafting the manuscript; interpretation of data; critical revision of the manuscript for important intellectual content; approval of final manuscript for submission. Supported by the NHLBI, NIH, with additional support from the Office of Dietary Supplements (R01 HL085710) and by a Research Fellowship from the National Heart Foundation of Australia. The supporting agencies had no role in the design or conduct of the study, the collection, management, analysis, or interpretation of the data, or the preparation, review, and approval of the manuscript.

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Figure 0

Fig. 1 Search, screening, and selection process of prospective cohort studies of dietary n-3 PUFA, fish/seafood, and circulating n-3 PUFA biomarkers and risk of type 2 diabetes.

Figure 1

Table 1 Characteristics of the identified 16 studies including 18 prospective cohorts that evaluated dietary n-3 PUFA, fish/seafood consumption, or biomarker n-3 PUFA levels and incidence of type 2 diabetes*

Figure 2

Fig. 2 Relative risk of type 2 diabetes associated with fish and/or seafood consumption in 13 prospective cohorts including 481 489 participants and 20 830 cases of incident diabetes. Within-study relative risks and 95 % CI's were quantified using generalized least squares trend estimation, and study-specific results were pooled using random effect meta-analysis. For 3 cohorts reporting effect estimates for both fish and seafood intake, (29,43) effects estimates for fish were used in the primary analysis; findings using seafood did not appreciably alter results (not shown).

Figure 3

Fig. 3 Relative risk of type 2 diabetes associated with fish and/or seafood consumption in prospective cohort studies stratified according to study location in North America/Europe (top panel) vs. Asia (bottom panel). Within-study relative risks and 95 % CI's were quantified using generalized least squares trend estimation, and study-specific results were pooled using random effect meta-analysis. Effect modification by study location was significant (P-Interaction = 0·007).

Figure 4

Fig. 4 Relative risk of type 2 diabetes associated with estimated dietary EPA+DHA in 16 prospective cohorts including 440 873 participants and 21 512 cases of incident diabetes. Within-study relative risks and 95 % CI's were quantified using generalized least squares trend estimation, and study-specific results were pooled using random effect meta-analysis. Exclusion of 4 studies for which the EPA+DHA intake was imputed from dietary fish/seafood(37,39,42), did not appreciably alter the results (per 250 mg/day, RR = 1·06, 95 % CI = 0·99, 1·14, P = 0·08).

Figure 5

Fig. 5 Relative risk of type 2 diabetes associated with EPA+DHA biomarker concentrations (as % of total fatty acids) in 5 prospective cohorts including 10 382 individuals and 1581 incident diabetes cases. Within-study relative risks and 95 % CI's were quantified using generalized least squares trend estimation, and study-specific results were pooled using random effect meta-analysis. Pooling results using the alternative biomarker measurements (red blood cell phospholipids) in Patel et al(38), did not appreciably alter the results (per 3 % of total fatty acids, RR = 0·96, 95 % CI = 0·76–1·21). The study by Wang et al(44), was not included due to insufficient information to allow extraction of effect estimates. However, EPA and DHA were not associated with risk of diabetes (44), and inclusion of this study is unlikely to appreciably alter the observed results.

Figure 6

Fig. 6 Relative risk of type 2 diabetes associated with dietary ALA in 7 prospective cohorts including 131 940 individuals and 7365 incident DM cases. Within-study relative risks and 95 % CI's were quantified using generalized least squares trend estimation, and study-specific results were pooled using random effect meta-analysis.

Figure 7

Fig. 7 Relative risk of type 2 diabetes associated with ALA biomarker (as % of total fatty acids) in 6 prospective cohorts including 13 291 individuals and 1833 incident diabetes cases. Within-study relative risks and 95 % CI's were quantified using generalized least squares trend estimation, and study-specific results were pooled using random effect meta-analysis. Pooling results using the alternative lipid compartment of biomarker measurements from Wang et al.(44) and Patel et al.(38) did not appreciably alter the results (per 0·1 % of total fatty acids, RR = 0·93, 95 % CI = 0·85–1·02, P = 0·11).

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