Ultra-Processed Food Availability and Noncommunicable Diseases: A Systematic Review
Abstract
:1. Introduction
2. Materials and Methods
2.1. Data Sources and Search Strategy
2.2. Eligibility Criteria
2.3. Data Extraction
2.4. Quality Assessment
3. Results
4. Discussion
Limitations and Strengths
5. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Author (Publ. Year) | Country | Study Design | Data Source (Study Year) | Exposure Variables | Outcome Variables | Statistical Analysis Method | Main Results |
---|---|---|---|---|---|---|---|
de Freitas et al. (2019) [30] | Brazil (Belo Horizonte) | Ecological Cross-sectional | Sample representative of the municipality: 2810 participants in 18 Health Academy Program (HAP) units selected by stratified cluster sampling according to 9 administrative regions of the city (2013) | Availability of fruits and vegetables and UPF on consumer food environment—all retail stores and open-air food markets located within 1600 m of each HAP unit | Prevalence of overweight | Multivariable multilevel logistic regression | No significant association between UPF availability and overweight. A smaller variety of vegetables was associated with overweight |
Ferreti and Mariani (2019) [31] | 150 countries worldwide | Ecological | Data on per capita sugar-sweetened beverage (SSB): Euromonitor ** 2012 edition. Age-standardized mean BMI: Global Burden of Metabolic Risk Factors of Chronic Diseases Collaborating Group (2014–2015) | Percentage of the consumer’s income (measured by the gross national income per capita) required to buy 100 L of SSB | Prevalence of overweight and obesity | Multivariate regression | Positive association between increase in SSB affordability (10%) and overweight (0.4 more adults per 100) and obesity (0.38 more cases per 100 adults). |
Vale et al. (2019) [32] | Brazil | Ecological | Household Budget Survey (POF) and National Household Sample Survey (PNAD): Brazil’s 27 states (national representative sample). POF: each household is assigned a sampling weight from which the estimates of prevalence of excess weight are obtained. (2008–2009) | Proportion of unprocessed or minimally and ultra-processed foods (according to the NOVA classification.) on annual per capita household food purchases in kg | Prevalence of the excess weight | Spatial analysis: correlation | A moderate correlation between purchase of ultra-processed foods and prevalence of excess weight (p = 0.01). |
Vandevijvere et al. (2019) [33] | 80 countries | Ecological | Data on total volume sales of foods and drinks per capita: Euromonitor ** (80 countries) Food subgroups: NOVA classification. BMI data: NCD-RisC group (all countries). (2002–2016) | Total volume sales of ultra-processed drinks (UPD) and ultra-processed foods (UPF) per capita summed by country and year. | Mean BMI * | Mixed models for repeated measures: spatial power covariance structure | Positive association between total increase of UPF and UPD sales and increase of mean BMI for both men and women. |
Monteiro et al. (2018) [34] | 19 European countries | Ecological | UPF household availability data from Data Food Networking (DAFNE): European data depository of national household budget surveys; and the Living Costs and Food Survey (for UK data) National representative samples. (1991–2008) | National average daily per capita availability of NOVA food groups expressed as percentage of total purchased dietary energy. | Prevalence of obesity | Linear regression | Significant positive association between national household availability of UPF and prevalence of obesity in adults. Each 1% increase of UPF household availability = 0.25% increase in obesity prevalence (r = 0.63; 95% CI = 0.05, 0.45; p < 0.02) |
Goryakin et al. (2017) [35] | 78 countries | Ecological (cross-national time series) | Data on soft drink sales: Euromonitor ** 2014 edition. Data on age-standardized country-level BMI levels, overweight, obesity and diabetes prevalence: NCD-RisC group. (1999–2014) | Per capita sales of carbonated soft drinks derived by dividing the off trade volume of these drinks by the population of each country. | Mean BMI *, overweight, obesity and diabetes prevalence. | Longitudinal panel analyses; Multivariate regression models of fixed effects | Trends of increase soft drink sales per capita have been accompanied by an increase in mean BMI and in average overweight and obesity prevalence. Soft drink sales were unrelated to diabetes prevalence. |
Juul and Hemminssong (2015) [36] | Sweden | Ecological | Food availability data: Swedish Board of Agriculture (4000 randomly selected households—national representative sample). Overweight and obesity data: nationwide database of Statistics Sweden and the WHO Global Health Observatory Data Repository (+18 years). (1960–2010) | Per capita availability of unprocessed or minimally processed foods, processed culinary ingredients, processed and ultra-processed foods (NOVA system) | Mean BMI *, prevalence of overweight and obesity | Time-trend descriptive analysis | Trends of increase UPF availability have been accompanied by an increase in overweight and obesity prevalence. |
Canella et al. (2014) [37] | Brazil | Ecological | Complex clustered sampling procedure, first selecting census tracts and then selecting households within those tracts.National representative sample: 55,970 households. (2008–2009) | Purchase data of all foods and drinks for home consumption, expressed in daily kilocalories (kcal) per capita, classified into 3 groups: fresh or minimally processed foods, processed culinary ingredients, processed or ultra-processed food (UPF). | BMI * and Z-scores of BMI-for-age (≤19 y). Prevalence of excess weight and obesity | Linear regression | Positive and independent association between household availability of UPF (1st to 4th quartile) and BMI z-score (0.53–0.81), excess weight (35.6–41.7%) and obesity (9.9–13.6%). |
De Vogli et al. (2014) [38] | 25 countries *** | Ecological (cross-national time series) | Data on per capita fast food transactions: Euromonitor ** 2012 edition. Age-standardized mean BMI: Global Burden of Metabolic Risk Factors of Chronic Diseases Collaborating Group (1999–2008) | Industry records of annual sales of meals and refreshments delivered in local and transnational fast food outlets, including chain restaurants, independent eateries and convenience stores. | Mean BMI * | Longitudinal panel analyses; Multivariate regression models of fixed effects | Positive association between increase in annual fast food transactions (1-unit per capita) and increase in age-standardized mean BMI (0.033 kg/m2 95% CI: 0.013–0.052). Only the intake of soft drinks mediated the observed association (β: 0.030; 95% CI = 0.010–0.050). |
Basu et al. (2013) [39] | 75 countries | Ecological (cross-national time series) | Data on soft drink sales: Euromonitor ** 2011 edition. Age-standardized overweight prevalence data: World Health Organization’s Global Database on BMI (2011 edition). Diabetes data: International Diabetes Federation. (1997 to 2010) | Per capita annual sales of carbonated soft drinks in gallons, including both imported drinks and those manufactured domestically | Prevalence of overweight, obesity and diabetes | Multivariate linear regression | Strong and positive correlate with the prevalence of overweight (r = 0.62; p < 0.001) and obese adults (r = 0.55; p < 0.001). Increase in soft drink consumption (1%) was associated with an additional 4.8 overweight and 2.3 obese adults per 100 (95% CI = 3.1, 6.5; 1.1, 3.5), and 0.3 adults with diabetes/100 (95% CI = 0.1, 0.8) |
Asfaw (2011) [40] | Guatemala | Ecological | National representative sample: 7276 households (38 municipalities in 22 departments and eight regions) (2000) | Per capita value of meals consumed outside home and per capita total food expenditure with unprocessed, primary processed and highly processed food | BMI *, prevalence of overweight/obesity | Generalized method of moments regression | Positive association between increase of highly processed food expenditure (10%) and increase of body mass index—BMI (4.25%). |
Selection (Max. 5) | Comparability (Max. 2) | Outcome (Max. 3) | |||||||
---|---|---|---|---|---|---|---|---|---|
Representativeness of the Sample (Max. 1) | Sample Size (Max. 1) | Non-Respondents (Max. 1) | Ascertainment of Exposure (Max. 2) | Comparable Subjects in Different Outcome Groups. Confounding Factors Controlled. | Assessment of Outcome (Max. 2) | Statistical Test (Max. 1) | Score | Maximum Score | |
de Freitas P.P. et al. (2019) [30] | 1 | 1 | 0 | 2 | 2 | 2 | 1 | 9 | 10 |
Ferreti F. and Mariani M. (2019) [31] | 1 | 1 | NA | 1 | 2 | 0 | 1 | 6 | 9 |
Vale D. et al. (2019) [32] | 1 | 1 | 0 | 1 | 0 | 0 | 1 | 4 | 10 |
Vandevijvere S. et al. (2019) [33] | 1 | 1 | NA | 1 | 2 | 0 | 1 | 6 | 9 |
Monteiro C.A. et al. (2018) [34] | 1 | 1 | 0 | 1 | 2 | 0 | 1 | 6 | 10 |
Goryakin Y. et al. (2017) [35] | 1 | 1 | NA | 1 | 2 | 0 | 1 | 6 | 9 |
Juul F. and Hemminssong E. (2015) [36] | 1 | 1 | 0 | 1 | 1 | 0 | 0 | 4 | 10 |
Canella D.S. et al. (2014) [37] | 1 | 1 | 0 | 1 | 2 | 2 | 1 | 8 | 10 |
De Vogli R. et al. (2014) [38] | 1 | 1 | NA | 1 | 2 | 0 | 1 | 6 | 9 |
Basu S. et al. (2013) [39] | 1 | 1 | NA | 1 | 2 | 0 | 1 | 6 | 9 |
Asfaw A. (2011) [40] | 1 | 1 | 0 | 1 | 2 | 0 | 1 | 6 | 10 |
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de Araújo, T.P.; de Moraes, M.M.; Magalhães, V.; Afonso, C.; Santos, C.; Rodrigues, S.S.P. Ultra-Processed Food Availability and Noncommunicable Diseases: A Systematic Review. Int. J. Environ. Res. Public Health 2021, 18, 7382. https://doi.org/10.3390/ijerph18147382
de Araújo TP, de Moraes MM, Magalhães V, Afonso C, Santos C, Rodrigues SSP. Ultra-Processed Food Availability and Noncommunicable Diseases: A Systematic Review. International Journal of Environmental Research and Public Health. 2021; 18(14):7382. https://doi.org/10.3390/ijerph18147382
Chicago/Turabian Stylede Araújo, Taissa Pereira, Milena M. de Moraes, Vânia Magalhães, Cláudia Afonso, Cristina Santos, and Sara S. P. Rodrigues. 2021. "Ultra-Processed Food Availability and Noncommunicable Diseases: A Systematic Review" International Journal of Environmental Research and Public Health 18, no. 14: 7382. https://doi.org/10.3390/ijerph18147382