Estimation of chronic dietary intake of pesticide residues

Jacqueline Mary Gerage Marques Marina Vieira da Silva About the authors

ABSTRACT

OBJECTIVE

To estimate the maximum theoretical daily intake of pesticides potentially consumed, chronically, by the Brazilian population.

METHOD

By using data from the food consumption section of the 2008–2009 Household Budget Survey to characterize the population diet, a database was built to group the foods based on the NOVA classification. Considering the maximum residue limit values of each pesticide authorized in the country until 2016, the limits of all consumed foods were added and multiplied by the amount consumed, resulting in the maximum theoretical intake index, which was compared with the acceptable daily intake.

RESULTS

The results show that, of the 283 pesticides considered in the database, 71 (25%) compounds had estimates of zero intake, 144 compounds (50.8%) reached acceptable daily intake values and 68 compounds (24%) showed median intake that exceeded the acceptable daily value. The pesticide intake estimation according to the different regions of the country showed a variation in the amount of compounds that exceeded the acceptable daily intake (48 to 69 substances) due to the different consumption patterns. The categories of products that most exceeded the limits were the insecticides, herbicides and fungicides.

CONCLUSION

The application of this methodology is valid for the first step in risk assessment, but the resulting values may be different from the actual exposure since they do not include other factors, such as the combined use of pesticides or unauthorized products. The importance of developing research on specific national food consumption data in a systematic way is emphasized, which generates data and analyses that allow a detailed risk assessment.

Food Pollutants, Chemical; Agrochemicals, adverse effects; Agro Toxic Maximum Allowable Limit on Food; Pesticide Exposure; Food and Nutrition Security

INTRODUCTION

The relation between food supply and consumption by the population, considering both availability and access, is the basis for food and nutritional security. The subject involves different areas of knowledge, such as health, agriculture, economy, food and environment, reaching different meanings. The concept of food security is evolving, being also related to sustainability, which has had an increasing importance in a scenario of climate change, affecting prices and causing interruptions in the food supply chain. Nutrition and food sovereignty also contribute to the improvement of this concept11. Maluf RS. Segurança alimentar e nutricional. 2. ed. Petrópolis: Vozes; 2009.174 p..

The large-scale production of commodities in Brazil, driven by the increased global demand for food, increased by 135% the total consumption of pesticides from 2000 to 201466. Bombardi LM. Geografia do uso de agrotóxicos no Brasil e conexões com a União Europeia. São Paulo: Laboratório de Geografia Agrária, Faculdade de Filosofia, Letras e Ciências Humanas – FFLCH-USP; 2017. 296 p., thus enhancing the exposure to their residues. Pesticide residues can be either a substance or a mixture of substances remaining in food or in environment. Besides, they can also be the conversion, degradation, and reaction products, and metabolites and impurities with toxicological importance77. Brasil. Decreto n° 4.074, de 4 de janeiro de 2002. Regulamenta a Lei no 7.802, de 11 de julho de 1989, que dispõe sobre a pesquisa, a experimentação, a produção, a embalagem e rotulagem, o transporte, o armazenamento, a comercialização, a propaganda comercial, a utilização, a importação, a exportação, o destino final dos resíduos e embalagens, o registro, a classificação, o controle, a inspeção e a fiscalização de agrotóxicos, seus componentes e afins, e dá outras providências. Diário Oficial da União. 8 jan. 2002. Seção 1:4. Acute poisoning occurs due to exposure to large amounts of residues, and the chronic form due to a long-term exposure to small amounts. Not only fresh plant-based foods show toxicological potential, but also prepared, such as homemade recipes, and processed foods, found in any supermarket.

Few studies assess the risks of pesticides poisoning from food consumption, especially for the Brazilian population. This assessment is based on the identification of potentially hazardous substances, thus allowing risk characterization. Population consumption data and anthropometric data contribute to the development of this type of assessment.

Our study aimed at estimating the maximum theoretical daily intake (TMDI) of pesticides potentially consumed by the Brazilian population in food, based on consumption data obtained in the Household Budget Survey (HBS) conducted by the Brazilian Institute of Geography and Statistics (IBGE) between 2008–2009, emphasizing the substances that exceeded the intake limits, considering the products authorized for use in Brazil until 2016.

METHODS

The database used in the estimation was built using the microdata of the food consumption section of the HBS, which records the consumption of the individuals aged 10 years or older. Data on a sample of 13,569 households were available, of which 33,613 individuals whose anthropometric data were fully identified were considered eligible, since the proposed analyses required the information on each individual’s body weight.

In the food consumption section of this survey, food items are recorded according to their consumption form. In the construction of the database, the foods were grouped according to the respective agricultural crops, and then the data on residue limit found in the monographs of each pesticides were applied88. Pires MV. Desenvolvimento e emprego de um banco de dados para a condução de estudos de avaliação do risco da exposição crônica a resíduos de agrotóxicos na dieta [dissertação]. Londrina, PR: Universidade Estadual de Londrina; 2013.. Using the NOVA classification99. Monteiro CA, Levy RB, Claro RM, Castro IRR, Cannon G. A new classification of foods based on the extent and purpose of their processing. Cad Saude Publica. 2010;26(11):2039-49. https://doi.org/10.1590/S0102-311X2010001100005
https://doi.org/10.1590/S0102-311X201000...
,1010. Monteiro CA, Cannon G, Levy RB, Moubarac JC, Jaime P, Martins AP, et al. NOVA. The star shines bright. World Nutr. 2016;7(1-3):28-40. as a basis, the food was classified into three groups: fresh, processed, and prepared.

Fresh foods were considered those that do not receive any kind of preparation. Prepared foods involve several ingredients, which were identified in proportion, based on standard recipes and reference tables1111. Fisberg RM, Villar BS. Manual de receitas e medidas caseiras para cálculo de inquéritos alimentares: manual elaborado para auxiliar o processamento de dados de inquéritos alimentares. São Paulo: Signus; 2002. 67 p.. Regarding processed foods, the composition of food as a percentage of ingredients was researched, based on product labels, current laws of the National Health Surveillance Agency (Anvisa) and/or of Ministry of Agriculture, Livestock and Supply1515. Ministério da Saúde (BR), Secretaria de Atenção à Saúde, Departamento de Atenção Básica. Alimentos regionais brasileiros. 2. ed. Brasília, DF; 2015. 484 p., reference tables1111. Fisberg RM, Villar BS. Manual de receitas e medidas caseiras para cálculo de inquéritos alimentares: manual elaborado para auxiliar o processamento de dados de inquéritos alimentares. São Paulo: Signus; 2002. 67 p. and internet search.

Foods of animal origin were also included in the database, which were grouped into: beef, pork, chicken meat, poultry meat, sheep meat, goat meat, mammalian meat, cattle offal, poultry offal, eggs and milk. For these groups, we used the maximum residue limit (MRL) values obtained from the Codex Alimentarius2323. Food and Agriculture Organization of the United Nations; World Health Organization. Codex Alimentarius: pesticide residues in food and feed. Rome (IT); 2010 [cited 2019 Dec 15]. Available from: http://www.fao.org/fao-whocodexalimentarius/standards/pestres/pesticides
http://www.fao.org/fao-whocodexalimentar...
, considering only the compounds authorized for use in Brazil, since Anvisa has no guidelines covering this category of products on the subject.

Food and beverages from the light, diet and organic categories, and foods whose composition could not be found or lacked MRL value defined by Anvisa were excluded from the study. At the end, a total of 743 foods were selected to data analysis.

The MRL values recorded in the monographs of pesticides (n = 283) with authorized use in the country until 2016 were adopted. The MRL values were summed according to the record of food consumed obtained from the HBS and multiplied by the amount consumed, resulting in the TMDI, which indicates the degree of exposure, according to Equation 1.

Equation 1. TMDI estimationaa World Health Organization. Guidelines for predicting dietary intake of pesticide residues (revised): prepared by the Global Environment Monitoring System – Food Contamination Monitoring and Assessment Programme (GEMS/Food) in collaboration with the Codex Comitee on Pesticide Residues. Zurich, 1997, 40 p..

TMDI=(MRLi×Fi)

The results were compared with the values of acceptable daily intake (ADI), published in the pesticide monographs by Anvisa, according to Equation 2. When the national data were not existent, the values of international agencies such as the Environmental Protection Agency (EPA), Codex Alimentarius and the Australian government health department2323. Food and Agriculture Organization of the United Nations; World Health Organization. Codex Alimentarius: pesticide residues in food and feed. Rome (IT); 2010 [cited 2019 Dec 15]. Available from: http://www.fao.org/fao-whocodexalimentarius/standards/pestres/pesticides
http://www.fao.org/fao-whocodexalimentar...
were used. The lowest value was used when there was more than one record for the same compound.

Equation 2. TMDI comparison with ADI.

%ADI=TMDI×100ADI× body weight

RESULTS

Of the 283 pesticides studied, 71 compounds (25%) had an estimate of intake equal to zero. We also identified that other 144 compounds (50.8%) met the ADI values, and other 113 had a value recommended by Anvisa. Table 1 shows that the remaining 68 compounds (24%) had a median intake that exceeded the ADI value.

Table 1
Extrapolation intervals compared to acceptable daily intake (ADI).

Table 2 indicates the 10 compounds with the highest estimates of intake by the population, of which seven (acephate, methyl bromide, diazinon, fentin, fipronil, phosphine and terbufos) exceeded ten times the ADI value. The other three (diquat, diurom and propanil) exceeded nine to ten times the ADI value.

Table 2
Estimation of pesticides most consumed by the Brazilian population through diet.

The pesticide intake estimation according to the different regions of the country showed a variation in the amount of compounds that exceeded the ADI due to the difference in consumption patterns and diversity of foods conditioned by different variables, especially family income, habits, cultural identity of the population and food regional availability. Table 3 indicates the amount of compounds that exceeded ADI by region.

Table 3
Amount of compounds that exceeded acceptable daily intake according to the region.

In the North region, the same ten compounds with higher median intake obtained for the entire Brazilian population were observed. Methyl bromide compound remained as the most consumed, with different amounts of consumption of the other compounds. Propanil, a product with few records of poisoning and indicated for application in rice crop2626. Ministério da Saúde (BR), Agência Nacional de Vigilância Sanitária. Monografias de agrotóxicos: monografias autorizadas. Brasília, DF: ANVISA; 2020 [cited 2019 Nov 20]. Available from: https://www.gov.br/anvisa/pt-br/setorregulado/regularizacao/agrotoxicos/monografias/monografias-autorizadas-por-letra
https://www.gov.br/anvisa/pt-br/setorreg...
, was the second most consumed.

The dissulfoton compound exceeded the ADI limit only in the Northeast region. This is an organophosphate insecticide applied in coffee culture, the second food item with the highest number of references in the food record of the first day of the HBS 2008–2009, which has the highest per capita consumption in the country in this region, reaching 230.4 g/day2626. Ministério da Saúde (BR), Agência Nacional de Vigilância Sanitária. Monografias de agrotóxicos: monografias autorizadas. Brasília, DF: ANVISA; 2020 [cited 2019 Nov 20]. Available from: https://www.gov.br/anvisa/pt-br/setorregulado/regularizacao/agrotoxicos/monografias/monografias-autorizadas-por-letra
https://www.gov.br/anvisa/pt-br/setorreg...
.

For the Southeast, the ethion compound was identified among the ten compounds with the highest intake potential. This is a compound indicated for foliar application in pineapple, cotton, eggplant, coffee, citrus, apple, watermelon, melon, pear, pepper and tomato crops2626. Ministério da Saúde (BR), Agência Nacional de Vigilância Sanitária. Monografias de agrotóxicos: monografias autorizadas. Brasília, DF: ANVISA; 2020 [cited 2019 Nov 20]. Available from: https://www.gov.br/anvisa/pt-br/setorregulado/regularizacao/agrotoxicos/monografias/monografias-autorizadas-por-letra
https://www.gov.br/anvisa/pt-br/setorreg...
, which are foods commonly consumed in the states of the region.

In a specific analysis, we used only data related to the state of São Paulo, since its socioeconomic characteristics differ from other states and regions, being used information related to 2,250 individuals. Ethion and propamocarb compounds exceeded ADI limits in this state. Studies show that residues from both compounds were reduced by processing procedures, such as oil refining, washing and cooking2929. Abdel-Gawad H, Mahdy F, Hashad A, Elgemeie GH. Fate of 14C-ethion insecticide in the presence of deltamethrin and dimilin pesticides in cotton seeds and oils, removal of ethion residues in oils, and bioavailability of its bound residues to experimental animals. J Agric Food Chem. 2014;62(51):12287-93. https://doi.org/10.1021/jf504010h
https://doi.org/10.1021/jf504010h...
,3030. Bonnechère A, Hanot V, Bragard C, Bedoret T, Loco J. Effect of household and industrial processing on the levels of pesticide residues and degradation products in melons. Food Addit Contam Part A Chem Anal Control Expo Risk Assess. 2012;29(7):1058-66. https://doi.org/10.1080/19440049.2012.672339
https://doi.org/10.1080/19440049.2012.67...
. However, only food processing cannot guarantee they reach the ADI levels.

The South region stands out for presenting a smaller amount of compounds that exceeded the ADI limit. According to data from Vigitel3131. Ministério da Saúde (BR), Agência Nacional de Saúde Suplementar. Vigitel Brasil 2015. Saúde suplementar: vigilância de fatores de risco e proteção para doenças crônicas por inquérito telefônico. Brasília, DF; 2015. 165 p. Available from: http://www.ans.gov.br/images/stories/Materiais_para_pesquisa/Materiais_por_assunto/2015_vigitel.pdf
http://www.ans.gov.br/images/stories/Mat...
, the capitals of the states of the Southern region are among the ten cities considered the major consumers of fruits and vegetables in the country, being the best index identified in Florianópolis, state of Santa Catarina. Regarding the use of pesticides, the states with the highest consumption record are Paraná, with 11.6%, and Rio Grande do Sul, with an average consumption of 10.2% of the total applied in the country3232. Bombardi LM. Pequeno ensaio cartográfico sobre o uso de agrotóxicos no Brasil. São Paulo: Laboratório de Geografia Agrária da Universidade de São Paulo; 2016. 40 p.. On the other hand, this was the region that recorded the highest consumption of organic foods, according to the HBS.

Regarding the Midwest region, the profile of the compounds that exceeded ADI limits was similar to that of the state of São Paulo, especially for the ethion compound.

DISCUSSION

Chronic exposure to residues of organophosphate and carbamate pesticides, categories in which most pesticides exceeded ADI, can be related to a number of symptoms, such as neurotoxic effects, chromosomal alterations, liver and kidney damage, arrhythmias, allergies, asthma, Parkinson’s disease, different types of cancer and hearing loss3333. Gerage JM, Meira APG, Silva MV. Food and nutritional security: pesticide residues in food. Nutrire. 2017;42:3. https://doi.org/10.1186/s41110-016-0028-4
https://doi.org/10.1186/s41110-016-0028-...
. The products in these categories can also act as acetylcholinesterase inhibitors, which affects the transmission of nerve impulses to the brain.

Methyl bromide, which stood out as the product with the highest intake potential, is applied in wooden crates for post-harvest storage. This compound has a high MRL, but a low ADI, which justifies the high value of TMDI, calling attention to the potential for high intake. In general, herbicides, one of the most commercialized categories of pesticides in the world, have high ADI values when compared with fungicides and insecticides, and therefore the category did not stand out in the results.

This type of evaluation is valid as a first step in risk assessment, since MRL is not the best indicator for estimating average residue levels. Likewise, performing the sum of all doses of pesticides is not ideal for assessing the cumulative risk, and the cumulative and synergistic effects of substances that cause the same toxic effects on tissues, organs and physiological systems and are able to produce joint and cumulative toxicity should also be studied – even if they have different modes of action3434. European Food Safety Authority. Public consultation: cumulative risk assessment of pesticides. Parma (IT): EFSA; 2019 [cited 2019 Nov 19]. Available from: https://www.efsa.europa.eu/en/press/news/public-consultation-cumulative-risk-assessment-pesticides
https://www.efsa.europa.eu/en/press/news...
.

We emphasize that our estimates do not consider the volume of pesticides illegally acquired, which enter the country without permission, or even the use of counterfeit products, which are not as much efficient and safe as the products attested by the responsible agencies. Trade in illegal pesticides accounts for 24% of Brazilian agricultural pesticide market, according to data from the Federação das Indústrias do Estado de São Paulo (FIESP – Federation of Industries of the State of São Paulo)3838. Instituto do Desenvolvimento Econômico e Social de Fronteiras. O contrabando de defensivos agrícolas no Brasil. Foz do Iguaçu, PR: IDESF; 2019 [cited 2019 Nov 15]. Available from: https://sindiveg.org.br/wp-content/uploads/2019/06/O-Contrabando-de-Defensivos-Agricolas-no-Brasil_Idesf-2019.pdf
https://sindiveg.org.br/wp-content/uploa...
.

An efficient program for monitoring the waste and the system of application of pesticides conducted continuously is essential as a strategy for the management of food safety in the country. Our results may support measures such as field education for the application of good agricultural practices, health risk assessment due to exposure and reassessment of products and substances.

We also would like to stress the use of individual food consumption data in the database. The proportional use of samples of population groups is important for this type of estimation, including stratification by age group, gender and education level.

The study by Meira et al.3939. Meira APG, Silva MV. Resíduos de agrotóxicos potencialmente contidos na dieta habitual de escolares. Segur Aliment Nutr. 2019;26:e019021. https://doi.org/10.20396/san.v26i0.8654932
https://doi.org/10.20396/san.v26i0.86549...
gathers estimates of pesticide consumption, focusing on the group of schoolchildren from the public school system of a municipality of the state of São Paulo. The authors show that of the 272 compounds considered in the study, 58 exceeded the maximum intake value. Some of these compounds may act as endocrine disruptors, which may lead to development changes, a fundamental concern for the sample in question.

This evidences the need to encourage the development of specific national studies on processing factors for the levels of residues found. The studies available show that all types of processing contribute to reduce risk due to exposure4040. Lehmann E, Turrero N, Kolia M, Konaté Y, Alencastro LF. Dietary risk assessment of pesticides from vegetables and drinking water in gardening areas in Burkina Faso. Sci Total Environ. 2017;601-2:1208-16. https://doi.org/10.1016/j.scitotenv.2017.05.285
https://doi.org/10.1016/j.scitotenv.2017...
4747. Mekonen S, Ambelu A, Spanoghe P. Reduction of pesticide residues from teff (Eragrostis tef) flour spiked with selected pesticides using household food processing steps. Heliyon. 2019;5(5):e01740. https://doi.org/10.1016/j.heliyon.2019.e01740
https://doi.org/10.1016/j.heliyon.2019.e...

A survey conducted in a vegetarian community in Israel4848. Berman T, Göen T, Novack L, Beacher L, Grinshpan L, Segev D, et al. Urinary concentrations of organophosphate and carbamate pesticides in residents of a vegetarian community. Environ Int. 2016;96:34-40. https://doi.org/10.1016/j.envint.2016.08.027
https://doi.org/10.1016/j.envint.2016.08...
identified an increase in the concentration of organophosphate residues in urine samples, and residents that consumed a larger portion of organic foods showed lower results for pesticide residues. Thus, the consumption of organic products can offer some protection against exposure. Agroecology is a form of sustainable management of agricultural production, considering social, political, cultural, environmental and ethical issues – working condition in the field, compatibility of culture to the ecosystem and the level of industrialization of the whole process. It is a modality that avoids the use of pesticides and chemical fertilizers and stimulates the planting of organics, being driven by family farming. However, the results of the production at scale, the costs involved and the time allocated to planting and harvesting, and productivity, should be considered.

The perspectives for future use of pesticides should be evaluated, not only regarding the effects on crops, occurrence of pests and pesticide efficiency, but also their implications for the technological development of regulations and economic situation. Given the expectations around climate change, the increase in temperatures will act on the change in rainfall regimes, favoring the development of pests and pathogens. Consequently, an increase in dosage, frequency of application and types of pesticides is expected. Therefore, new compounds may emerge, and both application of combinations and toxicity of the assets may increase, thus increasing the dietary intake of residues4949. Maggioni DA, Signorini ML, Michlig N, Repetti MR, Sigrist ME, Beldomenico HR. Comprehensive estimate of the theoretical maximum daily intake of pesticide residues for chronic dietary risk assessment in Argentina. J Environ Sci Health B. 2017;52(4):256-66. https://doi.org/10.1080/03601234.2016.1272997
https://doi.org/10.1080/03601234.2016.12...
.

Few studies have investigated the ecotoxicological effects resulting from the application of pesticides in tropical regions, and studies applied in temperate regions are mostly used as references. The adaptation of existing tests for tropical regions is indicated4747. Mekonen S, Ambelu A, Spanoghe P. Reduction of pesticide residues from teff (Eragrostis tef) flour spiked with selected pesticides using household food processing steps. Heliyon. 2019;5(5):e01740. https://doi.org/10.1016/j.heliyon.2019.e01740
https://doi.org/10.1016/j.heliyon.2019.e...
.

CONCLUSION

The guarantee of residue-free foods integrates the human right to adequate food, reinforcing the need for rigorous monitoring of pesticide residues, considered important for a national food and nutrition safety program. According to the results, many pesticides applied in crops consumed in Brazil have an intake potential that may exceed the recommended indices. Thus, we suggest that the national health system evaluate the real potential of exposure to pesticide residues, also due to perspectives of global climate changes, which would imply changes in the use of these products.

Systematic generation of food consumption data is also necessary to assess chronic, acute and cumulative risks more realistically. There is no way to assess the effects of exposure through the consumption of food and water, we can only use models based on the precautionary principle; however, it is already known that a low-dose exposure already induces cell death and reduces cell viability.

REFERENCES

  • 1
    Maluf RS. Segurança alimentar e nutricional. 2. ed. Petrópolis: Vozes; 2009.174 p.
  • 2
    Torres EAFS, Machado FMS, editores. Alimentos em questão. São Paulo: Ponto Crítico; 2006. v. 2.
  • 3
    Brasil. Lei n°11.346, de 15 de setembro de 2006. Cria o Sistema Nacional de Segurança Alimentar e Nutricional – SISAN com vistas em assegurar o direito humano à alimentação adequada e dá outras providências. Diário Oficial da União, 8 set 2006. Seção 1:1
  • 4
    Maluf RS, Burlandy L, Santarelli M, Schottz V, Speranza JS. Nutrition-sensitive agriculture and the promotion of food and nutrition sovereignty and security in Brazil. Cienc Saude Coletiva. 2015;20(8);2303-12. https://doi.org/10.1590/1413-81232015208.14032014
    » https://doi.org/10.1590/1413-81232015208.14032014
  • 5
    United Nations. Intergovernmental Panel on Climate Change: final government distribution. Geneva; 2019. Chapter 5, Food Security.
  • 6
    Bombardi LM. Geografia do uso de agrotóxicos no Brasil e conexões com a União Europeia. São Paulo: Laboratório de Geografia Agrária, Faculdade de Filosofia, Letras e Ciências Humanas – FFLCH-USP; 2017. 296 p.
  • 7
    Brasil. Decreto n° 4.074, de 4 de janeiro de 2002. Regulamenta a Lei no 7.802, de 11 de julho de 1989, que dispõe sobre a pesquisa, a experimentação, a produção, a embalagem e rotulagem, o transporte, o armazenamento, a comercialização, a propaganda comercial, a utilização, a importação, a exportação, o destino final dos resíduos e embalagens, o registro, a classificação, o controle, a inspeção e a fiscalização de agrotóxicos, seus componentes e afins, e dá outras providências. Diário Oficial da União. 8 jan. 2002. Seção 1:4
  • 8
    Pires MV. Desenvolvimento e emprego de um banco de dados para a condução de estudos de avaliação do risco da exposição crônica a resíduos de agrotóxicos na dieta [dissertação]. Londrina, PR: Universidade Estadual de Londrina; 2013.
  • 9
    Monteiro CA, Levy RB, Claro RM, Castro IRR, Cannon G. A new classification of foods based on the extent and purpose of their processing. Cad Saude Publica. 2010;26(11):2039-49. https://doi.org/10.1590/S0102-311X2010001100005
    » https://doi.org/10.1590/S0102-311X2010001100005
  • 10
    Monteiro CA, Cannon G, Levy RB, Moubarac JC, Jaime P, Martins AP, et al. NOVA. The star shines bright. World Nutr. 2016;7(1-3):28-40.
  • 11
    Fisberg RM, Villar BS. Manual de receitas e medidas caseiras para cálculo de inquéritos alimentares: manual elaborado para auxiliar o processamento de dados de inquéritos alimentares. São Paulo: Signus; 2002. 67 p.
  • 12
    Pinheiro ABV, Lacerda EMA, Benzecry EH, Gomes MCS, Costa VM. Tabela para avaliação de consumo alimentar em medidas caseiras. 5. ed. São Paulo: Atheneu; 2005. 131p.
  • 13
    Instituto Brasileiro de Geografia e Estatística. Pesquisa de Orçamentos Familiares 2008-2009: tabelas de composição nutricional dos alimentos consumidos no Brasil. Rio de Janeiro: IBGE; 2011. 351 p.
  • 14
    Universidade Estadual de Campinas, Núcleo de Estudos e Pesquisa em Alimentação. Tabela brasileira de composição de alimentos. 4. ed. Campinas, SP: NEPA; 2011 [cited 2019 Oct 11]. 161 p. Available from: http://www.unicamp.br/nepa/taco/Tabela.php?ativo=Tabela
    » http://www.unicamp.br/nepa/taco/Tabela.php?ativo=Tabela
  • 15
    Ministério da Saúde (BR), Secretaria de Atenção à Saúde, Departamento de Atenção Básica. Alimentos regionais brasileiros. 2. ed. Brasília, DF; 2015. 484 p.
  • 16
    Ministério da Saúde (BR), Comissão Nacional de Normas e Padrões para Alimentos. Resolução - CNNPA n° 12, de 1978. A Comissão Nacional de Normas e Padrões para Alimentos, em conformidade com o artigo no 64, do Decreto-lei no 986, de 21 de outubro de 1969 e de acordo com o que foi estabelecido na 410a. Sessão Plenária, realizada em 30/03/78, resolve aprovar as seguintes NORMAS TÉCNICAS ESPECIAIS, do Estado de São Paulo, revistas pela CNNPA, relativas a alimentos (e bebidas), para efeito em todo território brasileiro. À medida que a CNNPA for fixando os padrões de identidade e qualidade para os alimentos (e bebidas) constantes desta Resolução, estas prevalecerão sobre as NORMAS TÉCNICAS ESPECIAIS ora adotadas. Diário Oficial da União. 24 jul. 1978. Seção 1, Parte 1:11528.
  • 17
    Brasil. Resolução de diretoria colegiada n° 272 de 22 de setembro de 2005. Aprova o “regulamento técnico para produtos de vegetais, produtos de frutas e cogumelos comestíveis”. Diário Oficial da União. 23 set 2005.
  • 18
    Ministério da Agricultura e do Abastecimento (BR), Secretaria de Defesa Agropecuária. Instrução Normativa n° 4, de 31 de março de 2000. Aprova os Regulamentos Técnicos de Identidade e Qualidade de Carne Mecanicamente Separada, de Mortadela, de Lingüiça e de Salsicha. Diário Oficial da União. 5 abr. 2000. Seção 1:6
  • 19
    Ministério da Agricultura e do Abastecimento (BR), Secretaria de Defesa Agropecuária. Instrução Normativa n° 20, de 31 de julho de 2000. Aprova os Regulamentos Técnicos de Identidade e Qualidade de Almôndega, de Apresuntado, de Fiambre, de Hamburguer, de Kibe, de Presunto Cozido e de Presunto. Diário Oficial da União. 3 ago. 2000. Anexos I, II, III, IV, V, VI, VI, VII.
  • 20
    Ministério da Agricultura e do Abastecimento (BR), Secretaria de Defesa Agropecuária. Instrução Normativa n° 6 de 15 de fevereiro de 2001. Aprova os Regulamentos Técnicos de Identidade e Qualidade de Paleta Cozida, Produtos Cárneos Salgados, Empanados, Presunto tipo Serrano e Prato Elaborado Pronto ou Semipronto Contendo Produtos de Origem Animal. Diário Oficial da União. 19 fev. 2001. Anexos I, II, III, IV, V.
  • 21
    Ministério da Saúde (BR), Agência Nacional de Vigilância Sanitária. Resolução RDC n° 267, de 25 de setembro de 2003. Dispõe sobre o Regulamento Técnico de Boas Práticas de Fabricação para Estabelecimentos Industrializadores de Gelados Comestíveis e a Lista de Verificação das Boas Práticas de Fabricação para Estabelecimentos Industrializadores de Gelados Comestíveis. Diário Oficial da União. 26 set 2003. Anexo I.
  • 22
    São Paulo (Estado), Secretaria de Agricultura e Abastecimento, Coordenadoria de Defesa Agropecuária. Instrução Normativa DAS n° 83, de 21 de novembro de 2003. Regulamentos Técnicos de Identidade e Qualidade de Carne Bovina em Conserva (Corned Beef) e Carne Moída de Bovino. Campinas, SP; 2003 [cited 2019 Nov 23]. Available from: https://www.defesa.agricultura.sp.gov.br/legislacoes/instrucao-normativa-sda-83-de-21-11-2003,666.html
    » https://www.defesa.agricultura.sp.gov.br/legislacoes/instrucao-normativa-sda-83-de-21-11-2003,666.html
  • 23
    Food and Agriculture Organization of the United Nations; World Health Organization. Codex Alimentarius: pesticide residues in food and feed. Rome (IT); 2010 [cited 2019 Dec 15]. Available from: http://www.fao.org/fao-whocodexalimentarius/standards/pestres/pesticides
    » http://www.fao.org/fao-whocodexalimentarius/standards/pestres/pesticides
  • 24
    United States Environmental Protection Agency. Integrated risk information system - IRIS. Washington, DF: EPA; 2019 [cited 2019 Dec 15]. Available from: https://www.epa.gov/iris
    » https://www.epa.gov/iris
  • 25
    Australian Government, Department of Health, Office of Chemical Safety. ADI List: acceptable daily intakes for agricultural and veterinary chemicals. Camberra (AU); 2015. 119 p.
  • 26
    Ministério da Saúde (BR), Agência Nacional de Vigilância Sanitária. Monografias de agrotóxicos: monografias autorizadas. Brasília, DF: ANVISA; 2020 [cited 2019 Nov 20]. Available from: https://www.gov.br/anvisa/pt-br/setorregulado/regularizacao/agrotoxicos/monografias/monografias-autorizadas-por-letra
    » https://www.gov.br/anvisa/pt-br/setorregulado/regularizacao/agrotoxicos/monografias/monografias-autorizadas-por-letra
  • 27
    Instituto Brasileiro de Geografia e Estatística. Pesquisa de Orçamentos Familiares 2008-2009: análise do consumo alimentar pessoal no Brasil. Rio de Janeiro: IBGE; 2011. 150 p.
  • 28
    Souza AM, Pereira RA, Yokoo EM, Levy RB, Sichieri R. Alimentos mais consumidos no Brasil: Inquérito Nacional de Alimentação 2008-2009. Rev Saude Publica. 2013;47 Supl 1:190s-5s. https://doi.org/10.1590/S0034-89102013000700005
    » https://doi.org/10.1590/S0034-89102013000700005
  • 29
    Abdel-Gawad H, Mahdy F, Hashad A, Elgemeie GH. Fate of 14C-ethion insecticide in the presence of deltamethrin and dimilin pesticides in cotton seeds and oils, removal of ethion residues in oils, and bioavailability of its bound residues to experimental animals. J Agric Food Chem. 2014;62(51):12287-93. https://doi.org/10.1021/jf504010h
    » https://doi.org/10.1021/jf504010h
  • 30
    Bonnechère A, Hanot V, Bragard C, Bedoret T, Loco J. Effect of household and industrial processing on the levels of pesticide residues and degradation products in melons. Food Addit Contam Part A Chem Anal Control Expo Risk Assess. 2012;29(7):1058-66. https://doi.org/10.1080/19440049.2012.672339
    » https://doi.org/10.1080/19440049.2012.672339
  • 31
    Ministério da Saúde (BR), Agência Nacional de Saúde Suplementar. Vigitel Brasil 2015. Saúde suplementar: vigilância de fatores de risco e proteção para doenças crônicas por inquérito telefônico. Brasília, DF; 2015. 165 p. Available from: http://www.ans.gov.br/images/stories/Materiais_para_pesquisa/Materiais_por_assunto/2015_vigitel.pdf
    » http://www.ans.gov.br/images/stories/Materiais_para_pesquisa/Materiais_por_assunto/2015_vigitel.pdf
  • 32
    Bombardi LM. Pequeno ensaio cartográfico sobre o uso de agrotóxicos no Brasil. São Paulo: Laboratório de Geografia Agrária da Universidade de São Paulo; 2016. 40 p.
  • 33
    Gerage JM, Meira APG, Silva MV. Food and nutritional security: pesticide residues in food. Nutrire. 2017;42:3. https://doi.org/10.1186/s41110-016-0028-4
    » https://doi.org/10.1186/s41110-016-0028-4
  • 34
    European Food Safety Authority. Public consultation: cumulative risk assessment of pesticides. Parma (IT): EFSA; 2019 [cited 2019 Nov 19]. Available from: https://www.efsa.europa.eu/en/press/news/public-consultation-cumulative-risk-assessment-pesticides
    » https://www.efsa.europa.eu/en/press/news/public-consultation-cumulative-risk-assessment-pesticides
  • 35
    European Food Safety Authority. Technical Annex A: Harmonised technical approach on the parameters governing retrospective cumulative exposure assessment. Parma (IT): EFSA; 2019 [cited 2019 Nov 27]. Available from: https://ec.europa.eu/food/plant/pesticides/max_residue_levels/cumulative_risk/technical-annex_en
    » https://ec.europa.eu/food/plant/pesticides/max_residue_levels/cumulative_risk/technical-annex_en
  • 36
    European Food Safety Authority. Outcome of the public consultation on the draft scientific report on the cumulative dietary risk characterisation of pesticides that have acute effects on the nervous system. EFSA Support Pub. 2020;17(4). https://doi.org/10.2903/sp.efsa.2020.EN-1835
    » https://doi.org/10.2903/sp.efsa.2020.EN-1835
  • 37
    European Food Safety Authority, Craig PS, Dujardin B, Hart A, Hernandez-Jerez AF, Bennekou SH, Kneuer C, Ossendorp B, et al. Cumulative dietary risk characterisation of pesticides that have chronic effects on the thyroid. EFSA J. 2020;18(4);6088. https://doi.org/102903/j.efsa.2020.6088
    » https://doi.org/102903/j.efsa.2020.6088
  • 38
    Instituto do Desenvolvimento Econômico e Social de Fronteiras. O contrabando de defensivos agrícolas no Brasil. Foz do Iguaçu, PR: IDESF; 2019 [cited 2019 Nov 15]. Available from: https://sindiveg.org.br/wp-content/uploads/2019/06/O-Contrabando-de-Defensivos-Agricolas-no-Brasil_Idesf-2019.pdf
    » https://sindiveg.org.br/wp-content/uploads/2019/06/O-Contrabando-de-Defensivos-Agricolas-no-Brasil_Idesf-2019.pdf
  • 39
    Meira APG, Silva MV. Resíduos de agrotóxicos potencialmente contidos na dieta habitual de escolares. Segur Aliment Nutr. 2019;26:e019021. https://doi.org/10.20396/san.v26i0.8654932
    » https://doi.org/10.20396/san.v26i0.8654932
  • 40
    Lehmann E, Turrero N, Kolia M, Konaté Y, Alencastro LF. Dietary risk assessment of pesticides from vegetables and drinking water in gardening areas in Burkina Faso. Sci Total Environ. 2017;601-2:1208-16. https://doi.org/10.1016/j.scitotenv.2017.05.285
    » https://doi.org/10.1016/j.scitotenv.2017.05.285
  • 41
    Mahugija JAM, Kayombo A, Peter R. Pesticide residues in raw and processed maize grains and flour from selected areas in Dar es Salaam and Ruvuma, Tanzania. Chemosphere. 2017;185:137-44. https://doi.org/10.1016/j.chemosphere.2017.07.014
    » https://doi.org/10.1016/j.chemosphere.2017.07.014
  • 42
    Oliva J, Cermeño S, Cámara MA, Martínez G, Barba A. Disappearance of six pesticides in fresh and processed zucchini, bioavailability and health risk assessment. Food Chem. 2017;229:172-7. https://doi.org/10.1016/j.foodchem.2017.02.076
    » https://doi.org/10.1016/j.foodchem.2017.02.076
  • 43
    López-Blanco R, Moreno-González D, Nortes-Méndez R, García-Reyes JF, Molina-Díaz A, Gilbert-López B. Experimental and theoretical determination of pesticide processing factors to model their behavior during virgin olive oil production. Food Chem. 2018;239:9-16. https://doi.org/10.1016/j.foodchem.2017.06.086
    » https://doi.org/10.1016/j.foodchem.2017.06.086
  • 44
    Alister C, Araya M, Becerra K, Volosky C, Saavedra J, Kogan M. Industrial prune processing and its effect on pesticide residue concentrations. Food Chem. 2018;268:264-70. https://doi.org/10.1016/j.foodchem.2018.06.090
    » https://doi.org/10.1016/j.foodchem.2018.06.090
  • 45
    Duan J, Cheng Z, Bi J, Xu Y. Residue behavior of organochlorine pesticides during the production process of yogurt and cheese. Food Chem. 2018;245:119-24. https://doi.org/10.1016/j.foodchem.2017.10.017
    » https://doi.org/10.1016/j.foodchem.2017.10.017
  • 46
    Jankowska M, Łozowicka B, Kaczy´nski P. Comprehensive toxicological study over 160 processing factors of pesticides in selected fruit and vegetables after water, mechanical and thermal processing treatments and their application to human health risk assessment. Sci Total Environ. 2019;652:1156-67. https://doi.org/10.1016/j.scitotenv.2018.10.324
    » https://doi.org/10.1016/j.scitotenv.2018.10.324
  • 47
    Mekonen S, Ambelu A, Spanoghe P. Reduction of pesticide residues from teff (Eragrostis tef) flour spiked with selected pesticides using household food processing steps. Heliyon. 2019;5(5):e01740. https://doi.org/10.1016/j.heliyon.2019.e01740
    » https://doi.org/10.1016/j.heliyon.2019.e01740
  • 48
    Berman T, Göen T, Novack L, Beacher L, Grinshpan L, Segev D, et al. Urinary concentrations of organophosphate and carbamate pesticides in residents of a vegetarian community. Environ Int. 2016;96:34-40. https://doi.org/10.1016/j.envint.2016.08.027
    » https://doi.org/10.1016/j.envint.2016.08.027
  • 49
    Maggioni DA, Signorini ML, Michlig N, Repetti MR, Sigrist ME, Beldomenico HR. Comprehensive estimate of the theoretical maximum daily intake of pesticide residues for chronic dietary risk assessment in Argentina. J Environ Sci Health B. 2017;52(4):256-66. https://doi.org/10.1080/03601234.2016.1272997
    » https://doi.org/10.1080/03601234.2016.1272997
  • 50
    Delcour I, Spanoghe P, Uyttendaele M. Literature review: Impact of climate change on pesticide use. Food Res Int. 2015;68:7-15. https://doi.org/10.1016/j.foodres.2014.09.030
    » https://doi.org/10.1016/j.foodres.2014.09.030
  • 51
    Daam MA, Chelinho S, Niemeyer JC, Owojori OJ, Silva PMCS, Sousa JP, et al. Environmental risk assessment of pesticides in tropical terrestrial ecosystems: test procedures, current status and future perspectives. Ecotoxicol Environ Saf. 2019;181:534-47. https://doi.org/10.1016/j.ecoenv.2019.06.038
    » https://doi.org/10.1016/j.ecoenv.2019.06.038
  • 52
    Carneiro FF, Augusto LGS, Rigotto RM, Friedrich K, Búrigo AC, organizadores. Dossiê ABRASCO: um alerta sobre os impactos dos agrotóxicos na saúde. São Paulo: Expressão Popular; 2015.

  • a
    World Health Organization. Guidelines for predicting dietary intake of pesticide residues (revised): prepared by the Global Environment Monitoring System – Food Contamination Monitoring and Assessment Programme (GEMS/Food) in collaboration with the Codex Comitee on Pesticide Residues. Zurich, 1997, 40 p.

  • Funding: DS/CAPES post-graduate scholarship granted by the Post-Graduate Program in Food Science and Technology.

Publication Dates

  • Publication in this collection
    23 June 2021
  • Date of issue
    2021

History

  • Received
    20 July 2020
  • Accepted
    6 Oct 2020
Faculdade de Saúde Pública da Universidade de São Paulo São Paulo - SP - Brazil
E-mail: revsp@org.usp.br