Abstract

This article aims to analyze levels of exhaled carbon monoxide, carboxyhemoglobinand cardiopulmonary variables in old people practicing exercise in external environments, and correlate them with climate and pollution factors. Temporal ecological study with118 active elderly people in the city of Cuiabá, in the state of Mato Grosso, Brazil. Data were obtained on use of medication, smoking, anthropometric measurements, spirometry, peak flow, oxygen saturation, heart rate, exhaled carbon monoxide, carboxyhemoglobin, climate, number of farm fires and pollution. Correlations were found between on the one hand environmental temperature, relative humidity of the air and number of farmers’ fires, and on the other hand levels of carbon monoxide exhaled and carboxyhemoglobin (p < 0.05).There was a correlation between heart rate and changes in environmental temperature, time of exposure to the sun and relative humidity (p < 0.05). In elderly people, environmental factors influence levels of exhaled carbon monoxide, carboxyhemoglobin and heart rate. There is thus a need for these to be monitored during exercise. The use of a carbon monoxide monitor to evaluate exposure to pollutants is suggested.

Exercise; Environmental pollution; Elderly people

Introduction

Environmental pollution and climate changes have been described as responsible for influencing the health of the population, and causing damage to the cardiovascular and respiratory systems¹1. Arbex MA, Santos UP, Martins LC, Saldiva PHN, Pereira LAA, Braga ALF. Poluição do ar e o sistema respiratório. J Bras Pneumol 2012; 38(5):643-655.^,22. Silva-Júnior JLR, Padilha TF, Jordana ER, Rabelo ECA, Ferreira ACG, Rabahi MF. Efeito da sazonalidade climática na ocorrência de sintomas respiratórios em uma cidade de clima tropical. J Bras Pneumol 2011; 37(6):759-767.. The attempt to understand the action of pollutants and the climate in human health has led to studies aiming to assess the risks to the population when submitted to short or long periods of exposure³3. Brunekreef B, Beelen R, Hoek G, Schouten L, Bausch-Goldbohm S, Fischer P, Armstrong B, Hughes E, Jerrett M, van den Brandt P. Effects of Long-Term Exposure to Traffic-Related Air Pollution on Respiratory and Cardiovascular Mortality in the Netherlands: The NLCS-AIR Study. Res Rep Health Eff Inst 2009; 139:5-71.^,44. Giles LV, Carlsten C2, Koehle MS. The effect of pre-exercise diesel exhaust exposure on cycling performance and cardio-respiratory variables Inhalation. Toxicology 2012; 24(12):783-789..

Sources that produce pollution include vehicles, industrial emissions and burning of biomass – the latter being more common in farming regions or regions of native surface biomass, such in the Brazilian Cerrado region¹1. Arbex MA, Santos UP, Martins LC, Saldiva PHN, Pereira LAA, Braga ALF. Poluição do ar e o sistema respiratório. J Bras Pneumol 2012; 38(5):643-655.^,55. Telles J, Rodriguez A, Fajardo A. Contaminacion por Monóxido de Carbono: um Problema de Salud Ambiental. Rev Salud Pública 2006; 8(1):108-117.. The most important pollutants include carbon monoxide (CO), sulfur dioxide (SO₂), nitrogen dioxide (NO₂) and particulate matter (PM_2,5), also known as particle pollution. These can damage the organism when a person remains is continuously exposed to them in environments with concentrations above the tolerance threshold⁶6. Barcellos C, Monteiro AMV, Corvalán C, Gurgel HCL, Sá Carvalho M, Artaxo P, Hacon S, Ragoni V. Mudanças climáticas e ambientais e as doenças infecciosas: cenários e incertezas para o Brasil. Epidemiol Servi Saúde 2009; 18(3):285-304.; and depending on the local climate situation, these primary pollutants can suffer chemical changes giving rise to the formation of secondary pollutants, principally ozone, further exacerbating the quality of the air being breathed⁶6. Barcellos C, Monteiro AMV, Corvalán C, Gurgel HCL, Sá Carvalho M, Artaxo P, Hacon S, Ragoni V. Mudanças climáticas e ambientais e as doenças infecciosas: cenários e incertezas para o Brasil. Epidemiol Servi Saúde 2009; 18(3):285-304.^,77. Aránguez E, Ordonez J M, Serrano J, Aragonês N, Fernández-Patier R, Gandarillas A. Contaminantes Atmosféricos Y su Vigilância. Rev Esp Salud Pública 1999; 73(2):123-132..

Climatic changes in themselves, in situations of high or low temperatures, associated with changes in the relative humidity of the air, have also been described as directly responsible for harming the respiratory and cardiovascular systems⁸8. Rosa AM, Ignotti E, Botelho C, Castro HA, Hacon SS. Respiratory disease and climatic seasonality in children under 15 years old in a town in the Brazilian Amazon. J Pediatr 2008; 84(6):543-549.

9. United States Environmental Protection Agency (EPA). [internet]. New York: Climate Impact on human Health. [acessado 2014 ago 21]. Disponível em: http://www.epa.gov/climatechange/impacts-adaptation/health.html
http://www.epa.gov/climatechange/impacts... ^-1010. Rogot E, Padgett SJ. Associations of coronary and stroke mortality with temperature and snowfall in selected areas of the United States, 1962-1996. Am J Epidemiol 1976; 103(6):565-575.. Thus, both environmental pollution and climate variations can jointly or in isolation influence human health, principally that of the populations that are more susceptible, such as the elderly and children²2. Silva-Júnior JLR, Padilha TF, Jordana ER, Rabelo ECA, Ferreira ACG, Rabahi MF. Efeito da sazonalidade climática na ocorrência de sintomas respiratórios em uma cidade de clima tropical. J Bras Pneumol 2011; 37(6):759-767.^,1111. Botelho C, Correia AL, Silva AM, Macedo AG, Silva CO. Environmental factors and hospitalization of under-five children with acute respiratory infection. Cad Saude Publica 2003; 19(6):1771-1780..

Mato Grosso is a Brazilian state responsible for a high level of issuance of environmental pollution, generated by intentional burning of vegetation, which is intensified in the dry period¹²12. Centro de Previsão do Tempo e Estudos Climáticos CPTEC [internet]. Cachoeira Paulista: Qualidade do Ar. [acessado 2013 set 1]. Disponível em: http://meioambiente.cptec.inpe.br
http://meioambiente.cptec.inpe.br... . The city of Cuiabá has a semi-humid tropical climate, with low wind speeds and high temperatures, and its own geomorphological characteristics that can make dispersion of pollutants less likely at times of atmospheric stability¹³13. Santos FMM, Musis CR, Nogueira JS, Pinto-Júnior OB, Santos MCJAN. Análise da variação higrotérmica ocasionada pela influência da ocupação do solo na cidade de Cuiabá-MT. Rev Elet em Gestão, Educação e Tecnologia Ambiental 2013; 9(9):1932-1945.^,1414. Oliveira AS, Nogueira MCJA, Sanches L, Musis CR. Microclima Urbano: Praças Públicas em Cuiabá/MT/Brasil. Caminhos de Geografia 2012; 13(43):311-325.. As a further cause of air pollution there is an old custom of burning domestic garbage; and in the last decade there has been an accentuated increase in the number of vehicles in use¹⁵15. Departamento Estadual de Trânsito-MT (Detran-MT). Frota de veículos em Mato Grosso: frota de veículos em circulação cadastrados por município, de acordo com o tipo no estado. Cuiabá, Detran; 2013. [acessado 2013 jul 20]. Disponível em: http://www.detran.mt.gov.br/estatisticas
http://www.detran.mt.gov.br/estatisticas... .

Since exercise is healthy, and with the trend to aging in the population, with a consequent increase in the number of elderly people, professionals have increasingly stimulated these individuals’ to adopt training regimes as a resource to improve their quality of life¹³13. Santos FMM, Musis CR, Nogueira JS, Pinto-Júnior OB, Santos MCJAN. Análise da variação higrotérmica ocasionada pela influência da ocupação do solo na cidade de Cuiabá-MT. Rev Elet em Gestão, Educação e Tecnologia Ambiental 2013; 9(9):1932-1945.^,1616. Deslandes A. The biological clock keeps ticking, but exercise may turn it back. Arq Neuropsiquiatr 2013; 71(2):113-118.^,1717. Benavent-Caballer V, Rosado-Calatayud P, Segura-Orti E, Amer-Cuenca JJ, Lisón JF. Effects of three different low-intensity exercise interventions on physical performance, muscle CSA and activities of daily living: A randomized controlled trial. Exp Gerontol 2014; 58:159-165.; but these individuals can become a group at risk by exposing themselves to adverse climate situations or to polluted environments. Having in mind the climate conditions of the city and the large numbers of fires in the dry period, this study aimed to ascertain the levels of exhaled carbon monoxide (COex) and carboxyhemoglobin (COHb), and cardiopulmonary changes in elderly people who practice exercise in external environments, and to assess the correlation with climatic variables, air pollution and fires.

Method

This was a temporal ecological observational study, involving 118healthy non-smoking residents of the city of Cuiabá, in the state of Mato Grosso, over the age of 60, of both genders, who practice exercise and participate in the “Healthy Longevity” (Longevidade Saudável) program of the Federal University of Mato Grosso (UFMT).This type of study considers a unit of time in a single location, with analysis by units of time – years, months or days¹⁸18. Castro HA, Gouveia N, Escamilla-Cejudo JA. Questões metodológicas para a investigação dos efeitos da poluição do ar na saúde. Rev. Bras. Epidemiol. 2003; 6(2):135-148..

For the choice of a month with dry climate, a prior analysis was made of records obtained by the Airforce Meteorological Command Network (REDEMET) over the period 2001 through 2012. Climatic data during the period of the study were supplied by reports from the Airforce Command, and the following averages established:

Average temperature of the day (TmdºC); average temperature of the period (TmpºC); average relative humidity of the day (URAmd%); average relative humidity of the period (URAmp%); average atmospheric pressure of the day (Pamd hPa); average atmospheric pressure of the period (Pamp hPa); average wind speed of the day (Velmd kt); and average wind speed of the period (Velmp kt). The period considered was late afternoon and early evening, the time of day when the subject took physical exercise.

Average data for agricultural fires per municipality per day (FQmd) and total of fires per day for the state (FQtot) were obtained from the National Space Research Institute (IMPE) and the Environmental Information System (SISAM) by online research referenced to the municipality of Cuiabá. Information on average daily environmental carbon monoxide (COmd ppb) and average particulate material_2,5per day (PMmd µg/m³) was also obtained.

To obtain the total number of fires (FQtot), the sum of fires produced by all the municipalities daily in the month in question (September) was used, considering the total of each day for the analysis, and for FQmd the sum of all the fires of the day divided by141 municipalities was used.

Individuals were included who did not present illnesses nor use medication, and did not have ventilation issues on the spirometry testing. Of the total of 153 subjects who practiced exercise, 35 were excluded (22.9%): of this total, 9 (5.8%) because they did not succeed in doing the spirometry test and/or had alterations in levels that indicated some breathing disturbance; 11 (7.2 %) were excluded because they reported an illness that justified non-participation; 12 (7.8%) due to their use of medication; and 3 (1.9%) because they refused to answer questions in the questionnaire.

After approval by the Ethics Committee of the Júlio Muller University Hospital (UFMT), under Opinion number 427.028, explanation on the objective of the survey and signature of the consent form, analysis of the lung function was made using a One-Flow spirometer (Clement Clark Ltda.),using the Brazilian Consensus of Spirometry¹⁹19. Pereira CAC. Consenso de Espirometria. J Pneumol 2002; 28(Supl. 3):S1-S82. as a parameter. Reading of peripheral oxygen saturation (SatO₂) and heart beat frequency (heart rate) was then carried out with a Nonin-Onyx II 9550 pulse oximeter, standardizing use of the index finger and reading time of one minute, to establish stable parameters. Peak expiratory flow (PEF) was evaluated using the Clement Clark Ltda. portable flow meter with volume variation of 60-900 L/min, keeping the patient seated, with three explosive measurements of total lung capacity (TLC).The value adopted was that of the curve with the highest value provided that the individual measurements did not have a difference higher than 20L between them¹⁹19. Pereira CAC. Consenso de Espirometria. J Pneumol 2002; 28(Supl. 3):S1-S82..Levels of COex and COHb were measured using a Micro-CO carbon monoxide monitor (Micro Medical S.A), using 6ppm as parameter for COex and 2.5% as parameter for COHb²⁰20. Santos UP, Gannan S, Abe JM, Esteves PB, Filho MF, Wakassa TB, Issa JS, Terra-Filho M, Stelmach R, Cukier A. Emprego da determinação de monóxido de carbono no ar exalado para a detecção do consumo de tabaco. J Pneumol 2001; 27(5):231-236.^,2121. Siqueira MEPB, Martins I, Costa AC, Andrade EL, Esteves MTC, Lima SA.Valores de referência para Carboxihemoglobina. Rev Saude Publica 1997; 31(6):618-263..

The data were collected in the period of afternoon to early evening at the same time of day, prior to exercise. A total of 584 measurements were made of each variable and the average data was obtained from the sum of all the individual daily analyses totaling 18 averages of measures carried out in the month, which represented the average levels of the population per day.

For statistical analysis the Minitab 6.0 and SPSS-PASW-18.0 software was used, with application of the Anderson-Darling test, the Student T-test, the Mann-Whitney and Kruskal-Wallis tests, and Pearson correlation when indicated. Multiple linear regression was carried out aiming to estimate the influence of the variables for climate and pollution on exhaled levels of COex and COHb, generating an equation based on the variables PM_2,5md, COmd, Tmp, URAmp, Pamp, Velmp andFQmd, for carbon monoxide (COex = 86.4-6,72PMmd-0.534COmd-1.31Tmp-0.172URAmp+0.067Pamp-102velmp+0.421FQmd)and for carboxyhemoglobin (COHb = 11.6-1.22PMmd-0.098COmd-0.236Tmp- 0.0292URAmp +0.0162Pamp-0.0206 velmp+0.0770 FQmd).

Moving averages were calculated, to smooth the oscillations of the temporal and pollutant variables. Temporal assessment was carried out, considering the month at two moments, approaching FQtot and COex for the purpose of understanding the performance of the variables.

Results

Of the subjects, 92 (79%) were female, with average age of 67.53 ± 5.07 years, weight 69.61 ± 10.42kg; average height 1.57 ± 0.08m and BMI 28.14 ± 4.10kg/m².All stated themselves to be non-smokers or former smokers, having ceased to smoke at least six months ago. The analysis of the data categorized by gender showed different averages for age and height (p = 0.00), and equal values of BMI among the subjects (p = 0.62), as shown in Table 1.

The overall average of COex was 2.69 ± 0.88ppm, and of COHb 0.43 ± 0.14, with exhaled levels showing no difference between males and females, nor between the fact of having or not having smoked (p > 0.05).

The overall average PEF found was 355.86 ± 17.15 L/min, with higher levels in the men (p = 0.00), with an average diminution of 16% for men and 4.5% for women, with no difference found between former smokers and non-smokers. Average SatO₂ was 96.45 ± 0.43% and average heart rate was 79.17 ± 3.06 bpm, the amounts being within the levels of normalcy, similar between the genders, and similar between ex-smokers and non-smokers (p > 0.05) (Table 1).

Analysis of the environment showed that in the reported month there were approximately 186 field fires for the city of Cuiabá, an average of 999.77 fires/day for the state, daily average environmental carbon monoxide (CO) emission levels of 46.6 ppb and a daily average of 11.53 µg of particulate material per m³ of air (Table 2).

A significant increase in temperatures in the late afternoon was found (p = 0.00) to be associated with a lower relative humidity of the air (p = 0.00), with values reaching levels lower than those recommended for health. Also, analysis of the data showed low wind speed, with a slight increase at twilight (p = 0.03), but still remaining lower than the levels appropriate for a good dispersion of pollutants. No difference was observed in atmospheric pressure between the average for the day and the average for the late afternoon-early evening period (p = 0.05), as observed in Table 2.

The Pearson correlation analysis confirmed a positive relationship between levels of COex and COHb exhaled by the subjects, and FQtot and FQmd, respectively (p < 0.05) (Table 3).

The multiple regression model applied showed itself to be appropriate for COex (R² = 90.3%; p = 0.02) and for COHb (R² = 88.5%; p = 0.03 ) and analysis of the data showed that Tmp (p = 0.04);(p = 0.04), URAmp (p = 0.03); (p = 0.04), FQmd (p = 0.04); (p = 0.04) respectively, explained more than 88% of the alterations in COex gases exhaled and the levels of COHb.

In relation to the climate variables, COex and COHb also showed a positive linear regression with four-day moving average for Tmxd, but negative correlation when evaluated against URAmd (p < 0.05), indicating a possible relationship between the alterations found in the levels of gases exhaled by the subjects, and COHb, when the environmental variables changed (Table 3).

In the period it was also found that there was a linear relationship between the average temperature of the period (p = 0.00), average temperature of the day (p = 0.02), time of exposure to the sun (p = 0.03), average relative humidity of the period (p = 0.01), and changes in heart rate response (Table 3).

In the temporal assessment, separating the month of September into two consecutive periods (1^st to 15^th day; and 16^thto 30^th day), there was an increase, in the course of the month, in the average levels of carbon monoxide exhaled–Coex[(2.31 ± 0.83 and 3.06 ± 0.78 (p = 0.04))], and in the total number of fires in the day –FQtot [(549.33 ± 502.46 and 1,450.20 ± 801.70 (p = 0.00))]. The higher averages were for the period from the 16^th to 30^th day, for both variables, as shown in Graphics 1 and 2.

Discussion

Carbon monoxide is the product of incomplete combustion of organic material. Due to its affinity with hemoglobin, when it links with hemoglobin it alters the blood’s capacity to transport oxygen, modifying the oxyhemoglobin curve²²22. Chasin AAM, Pedroso MFM, Silva ES. Fatores que interferem nos resultados das análises toxicológicas dos indicadores biológicos de monóxido de carbono. Rev Bras Toxicol 1994; 7(1/2):15-22., causing a toxic action when inhaled.

In the present study the average levels of carbon monoxide exhaled by the subjects, although they varied daily, remained within the acceptable range, with an average of 2.69ppm, reaching values for carboxyhemoglobin of 0.43%, no difference being found between the genders nor between smokers and non-smokers²³23. Lindell K, Weaver MD. Carbon Monoxide Poisoning. N Engl J Med 2009; 360:1217-1225..

The values for COex and COHb found in the study are very close to those described by Santos et al.²⁰20. Santos UP, Gannan S, Abe JM, Esteves PB, Filho MF, Wakassa TB, Issa JS, Terra-Filho M, Stelmach R, Cukier A. Emprego da determinação de monóxido de carbono no ar exalado para a detecção do consumo de tabaco. J Pneumol 2001; 27(5):231-236., who found an average of 2.5 ± 2.1ppm, and 0.43 ± 0.14% when evaluating individuals who were both non-smokers and former smokers. It is known that observation of the levels of COex and COHb in these individuals is important when planning external activities, since levels detected in the blood can be related to environmental exposure. Thus, prior identification of these gases by direct or indirect method constitutes a pair of biological indicators that can determine the risks of exposure²²22. Chasin AAM, Pedroso MFM, Silva ES. Fatores que interferem nos resultados das análises toxicológicas dos indicadores biológicos de monóxido de carbono. Rev Bras Toxicol 1994; 7(1/2):15-22..

The similarity between the values for exhaled CO found during the analyses in this study across the variables gender, age and smoking history has also been shown in other surveys, strengthening the conclusion that carbon monoxide levels do not change with individual characteristics²⁰20. Santos UP, Gannan S, Abe JM, Esteves PB, Filho MF, Wakassa TB, Issa JS, Terra-Filho M, Stelmach R, Cukier A. Emprego da determinação de monóxido de carbono no ar exalado para a detecção do consumo de tabaco. J Pneumol 2001; 27(5):231-236.^,2424. Shafig M, Khan S, Khawaia MR, Haque S, Khan JA. Socio-demographic correlates of exhaled breath carbon monoxide in Karachis`s adult population. J Pak Med Assoc 2008; 58(2):75-78..

Although COex levels of the subjects were found to be within the levels of normality²¹21. Siqueira MEPB, Martins I, Costa AC, Andrade EL, Esteves MTC, Lima SA.Valores de referência para Carboxihemoglobina. Rev Saude Publica 1997; 31(6):618-263., there was a variation in daily measurements with a significant increase toward the end of the month, coinciding with increases in numbers of fires, as shown by the temporal analysis for COex and fires.

Since there was no influence of the individual variables on gases exhaled, the alterations found in the subjects maybe associated with higher environmental emission of CO coming from the fires which increased in this period, associated with the concentrations of pollutants emitted by vehicles, exacerbated by the local climate conditions.

The fact that strengthens the possibility of influence of pollutants on the levels exhaled is that the group of subjects in this study comprised active individuals, with exclusion of those who used medication, who presented some type of acute illness or some treatment for chronic illness that might increase endogenous production that might in turn alter levels of COex²⁰20. Santos UP, Gannan S, Abe JM, Esteves PB, Filho MF, Wakassa TB, Issa JS, Terra-Filho M, Stelmach R, Cukier A. Emprego da determinação de monóxido de carbono no ar exalado para a detecção do consumo de tabaco. J Pneumol 2001; 27(5):231-236.^,2525. Johnson RA, Kozma F, Colombari E. Carbon monoxide: from toxin to endogenous modulator of cardiovascular functions. Braz J. Med. 1999; 32(1):1-14..

Further, the participants in the present study live in an urban center, being subject to greater action of pollutants, high temperatures and low relative humidity. In these locations, drier and hotter periods can alter the local atmosphere, creating situations of atmospheric stability that are an obstacle to dispersion of pollutants – which have a tendency to accumulate in lower regions – causing the population to be more exposed²⁶26. Instituto Nacional de Pesquisas Espaciais (INPE). Estudo de influência da poluição atmosférica e das condições meteorológicas na saúde em São José dos Campos. Relatório final de projeto de iniciação científica (PIBIC/CNPq/IMPE). Julho 2006. [acessado 2014 out 1]. Disponível em: http://mtc-m15.sid.inpe.br/.
http://mtc-m15.sid.inpe.br/... ^,2727. Jardim CH. Relações entre temperatura, umidade relativa do ar e pressão atmosférica em área urbana: comparação horária entre dois bairros no município de São Paulo-SP. Geografias 2011; 7(1):128-142..

Associated with this factor, the city of Cuiabá is located in a depression that favors concentration of pollution during fires, with winds tending to blow toward the urban region, increasing the possibility of concentration of pollution in the more central regions²⁶26. Instituto Nacional de Pesquisas Espaciais (INPE). Estudo de influência da poluição atmosférica e das condições meteorológicas na saúde em São José dos Campos. Relatório final de projeto de iniciação científica (PIBIC/CNPq/IMPE). Julho 2006. [acessado 2014 out 1]. Disponível em: http://mtc-m15.sid.inpe.br/.
http://mtc-m15.sid.inpe.br/... .

Winds also favor transport of environmental CO from distant fires, and this factor could increase the levels of CO in the air in populated regions by up to 70% ²⁸28. Aires CB, Kirchhoff VWJH. Transporte de monóxido de carbono gerado em queimadas para regiões onde não se queima. Rev Bras Geof 2001; 19(1):61-74..

Levels of CO in the organism can be increased by direct inhalation of the environmental gases or by oxidative stress due to exposure to various pollutants²⁵25. Johnson RA, Kozma F, Colombari E. Carbon monoxide: from toxin to endogenous modulator of cardiovascular functions. Braz J. Med. 1999; 32(1):1-14.^,2929. Dawson TM, Snyder SH. Gases as Biological Messengers: Nitric Oxide and Carbon Monoxide in the Brain. J Neurosci 1994; M(9):5147-5159.^,3030. Wu L, Wang R. Carbon monoxide: endogenous production, physiological functions, and pharmacological applications. Pharmacol Rev 2005; 57(4):585-630.; the alterations found in the subjects of this survey might be the result of either or both of these factors.

The figures for temperature, fires and relative humidity and those for exhalation of gases by the subjects suggests inter-dependence between the two.

It is difficult to separate the action of the climate and of pollution in the air breathed, since there is a relationship between the two and these factors finish up exercising an additive effect in the response of the respiratory and cardiovascular apparatus to aggressions³¹31. Goldberg MS, Burnett RT, Stieb DM, Brophy JM, Daskalopoulou SS, Valois MF, Brook JR. Associations between ambient air pollution and daily mortality among elderly persons in Montreal Quebec. Sci Total Environ 2013; 46(4):931-942.

32. Tamura k, Jinsart W, Yano E, Karita K, Boudoung D. Particulate air pollution and chronic respiratory symptoms among traffic policemen in Bangkok. Arch Environ Health 2003; 58(4):201-207.^-3333. Barraza-Villarreal A, Sunver J, HJernandez-Cadena L, Escamilla-Nunez MC, Sienra-Monge JJ, Ramirez-Aquilar M, Cortez-Lugo M, Holguin F, Diaz-Sánchez D, Olin AC, Romieu I. Air Pollution, Airway Inflammation, and Lung Function in a Cohort Study of Mexico City Schoolchildren. Environ. Health Perspect 2008; 116(6):832-838..

The association of climatic factors with heat and pollution by environmental CO has also been described as responsible for risk of acute episodes of infarct of the myocardium and cephalic vascular accident, principally in old people. Thus caution is recommended in physical exercise and exposure to the sun on days of high temperatures and high concentrations of CO in the air³⁴34. Rumel D, Riedel LF, Latorre MRDO, Duncan BB. Infarto do miocárdio e acidente vascular cerebral associados à alta temperatura e monóxido de carbono em área metropolitana do sudeste do Brasil. Rev Saude Publica 1993; 27(1):15-22..

This is in line with the findings of this study on the relationships between climate and levels of COex, and indicates the existence of a greater risk of practicing exercise by elderly people in the dry period in external environments, since in this period there is an increase in the occurrence of forest fires, associated with high temperatures. Also exercise increases lung ventilation, leading to greater inhalation of pollutants, with negative effects on transport of oxygen²³23. Lindell K, Weaver MD. Carbon Monoxide Poisoning. N Engl J Med 2009; 360:1217-1225.^,3535. Aydin S, Cingi C, San T, Ulusoy S, Orhan I. The effects of air pollutants on nasal functions of outdoor runner. Eur Arch Otorhinolaryngol 2014; 271(4):713-717.^,3636. Carlisle AJ, Sharp NCC. Exercise and Outdoor ambient air pollution. Br J Sports Med 2001; 35(4):214-222..

It should also be taken into consideration that the obtaining of the environmental data in this study relating to the emissions of pollutants was not made by monitoring on at ground level but from satellite data that estimate levels of pollutants well above the level of the ground, and it is possible that concentrations at ground level were underestimated.

As well as the association between climate and pollution, variations in environmental temperature have been described as an important cause of death from cardiovascular and respiratory disease in children and old people³⁷37. Wyndham CH, Felligham SA. Climate and Disease. S Afr Med J 1978; 53(26):1051-1062.. Cardiovascular mortality takes place when the body exceeds the thermoregulatory threshold generating changes in heart rate, viscosity of the blood, change in coagulability of the blood, reduction in cerebral perfusion and attenuation in vasomotor responses³⁸38. Gasparrini A, Guo Y, Hashizume M, Lavigne E, Zanobetti A, Schuwatz J, Tobias A, Tong S, Rocklöv J, Forsberg B, Leone M, De Sario M, Bell ML, Guo YL, Wu CF, Kan H, Yi SM, de Sousa Zanotti Stagliorio Coelho M, Saldiva PH, Honda Y, Kim H, Armstrong B. Mortality risk attributable to high and low ambient temperature: a multicountry study. Lancet 2015; 386(9991):369-375..

In the present study there was a positive relationship between heart rate and time of exposure to the sun and environmental temperature, and a negative one with relative humidity. The influence of climate in elderly individuals can cause an increased cardiac load, especially on days that are hotter with lower relative humidity, exposing the heart to greater work during exercise³⁹39. Chan EYY, Goggins WB, Yuea JSK, Bull PLB. Hospital admissions as a function of temperature, other weather phenomena and pollution levels in an urban setting in China. World Health Organ 2013; 91(8):576-584.^,4040. Camargo MG, Furlan MMDP. Resposta Fisiológica do Corpo às Temperaturas Elevadas: Exercício, Extremos de Temperatura e doenças térmicas. Rev Saúde e Pesquisa 2011; 4(2):278-288..

Elderly individuals have lower homeostatic responses to the control of body temperature, and this is a factor that can cause hyperthermia when exposed to high temperatures and a greater predisposition to dehydration when associated with low relative humidity⁴⁰40. Camargo MG, Furlan MMDP. Resposta Fisiológica do Corpo às Temperaturas Elevadas: Exercício, Extremos de Temperatura e doenças térmicas. Rev Saúde e Pesquisa 2011; 4(2):278-288.^,4141. Kenneyh WL, Craighead DH, Alexander LM. Heat Waves, Aging and Human Cardiovascular Health. Med Sci Sports Exerc 2014; 46(10):1891-1899.. Also, for efficient cooling of the body in hotter periods there is a need to increase the distribution of the flow of blood to cover a larger area of the surface of the body, causing a greater load on the heart which is often debilitated by the process of aging⁴⁰40. Camargo MG, Furlan MMDP. Resposta Fisiológica do Corpo às Temperaturas Elevadas: Exercício, Extremos de Temperatura e doenças térmicas. Rev Saúde e Pesquisa 2011; 4(2):278-288.^,4141. Kenneyh WL, Craighead DH, Alexander LM. Heat Waves, Aging and Human Cardiovascular Health. Med Sci Sports Exerc 2014; 46(10):1891-1899..

Thus, in spite of the physiological responses being efficient, situations of high environmental temperatures and low relative humidity associated with intense muscular work and lack of acclimatization of the organism can lead the elderly individual to heat stress, causing a range of factors from simpler alterations such as syncope and edemas to more serious conditions such as dehydration and hyperthermia⁴⁰40. Camargo MG, Furlan MMDP. Resposta Fisiológica do Corpo às Temperaturas Elevadas: Exercício, Extremos de Temperatura e doenças térmicas. Rev Saúde e Pesquisa 2011; 4(2):278-288.. Reinforcing the influence of the temperature in the cardiovascular response, a study carried out in Boston in 2000 through 2008 found a lower variability in heart rate in elderly people with high temperatures⁴²42. Ren C, O’Neill MS, Park SK, Sparrow D, Vokonas P, Schwartz J. Ambient Temperature, Air Pollution, and Heart Rate Variability in an Aging Population. Am J Epidemiol 2011; 173(9):1013-1021..

As well as influencing the cardiovascular responses, high environmental temperatures have also been cited as a factor responsible for an increased number of hospitalizations, increase of mortality and morbidity in elderly individuals for various pathologies⁴³43. Soares FV, Greve P, Sendín FA, Benze BG, Castro AP, Rebelatto JR. Relação entre alterações climáticas e fatores determinantes da mortalidade de idosos no município de São Carlos (SP) em um período de dez anos. Cien Saude Colet 2012; 17(1):135-146.

44. Gouveia N, Hajat S, Armstrong B. Socioeconomic differentials in the temperature mortality relationship in São Paulo, Brazil. Internat J Epidemiol 2003; 32(3):390-397.^-4545. Chen R, Wang C, Meng X, Chen H, Thach TQ, Wong CM, Kan H. Both low and high temperature may increase the risk of stroke mortality. Neurology 2013; 81(12):1064-1070.. Temperatures above 30ºC have been associated with increases in cases of ischemic cardiovascular diseases and respiratory diseases such as asthma and bronchitis⁴⁶46. Azevedo JMF. A influência das variáveis ambientais (meteorológicas e de qualidade do ar) na mortalidade respiratória e cardiovascular na área metropolitana do Porto [tese].São Paulo: de São Paulo; 2010..

As well as high temperatures, damage can be caused to the bronchial tubes in periods of dry climate by the great quantity of dust and materials suspended in the air such as pollens and other inhalable particles. Thus, greater exposure to suspended particles due to lower humidity may explain the findings of reduced PEF found in the elderly people in this study²2. Silva-Júnior JLR, Padilha TF, Jordana ER, Rabelo ECA, Ferreira ACG, Rabahi MF. Efeito da sazonalidade climática na ocorrência de sintomas respiratórios em uma cidade de clima tropical. J Bras Pneumol 2011; 37(6):759-767.^,88. Rosa AM, Ignotti E, Botelho C, Castro HA, Hacon SS. Respiratory disease and climatic seasonality in children under 15 years old in a town in the Brazilian Amazon. J Pediatr 2008; 84(6):543-549.^,4343. Soares FV, Greve P, Sendín FA, Benze BG, Castro AP, Rebelatto JR. Relação entre alterações climáticas e fatores determinantes da mortalidade de idosos no município de São Carlos (SP) em um período de dez anos. Cien Saude Colet 2012; 17(1):135-146.^,4747. Centro de Pesquisas Meteorológicas e Climáticas Aplicadas à Agricultura (CEPAGRI). [Internet]. Campinas: Umidade no ar- Saúde no inverno: Escala psicrométrica UNICAMP para indicação de níveis de umidade relativa do ar prejudiciais à saúde humana. [acessado 2014 out 10]. Disponível em: http://www.cepagri.unicamp.br/artigos-especiais/umidade-do-ar-saude-no-inverno.html.
http://www.cepagri.unicamp.br/artigos-es... .

Low humidity of the air can cause various health problems to the elderly population, such as nosebleeds, irritation in the eyes, drying of the skin, acute respiratory insufficiency, irritations of the respiratory system, drying of the mucous tissues, all of which can be exacerbated by pollutants⁴⁸48. World Health Organization (WHO). Environmental Health Criteria 213: Carbon Monoxide (second edition).Effects on Humans. [Internet]. [acessado 2014 set 5]. Disponível em: http://www.who.int/ipcs/publications/ehc/ehc_213/en/
http://www.who.int/ipcs/publications/ehc... .

Thus, based on the research studied and the results presented that the period of late afternoon / early evening was the time at which there were higher environmental temperatures and lower relative humidity, it is shown that the practice of exercise for these individuals should be avoided in this period, since the elderly person’s difficulty in thermoregulation, ease of dehydration and lower perspiration, associated with higher environmental temperature, can lead to various events including cephalic vascular accidents and respiratory diseases³⁴34. Rumel D, Riedel LF, Latorre MRDO, Duncan BB. Infarto do miocárdio e acidente vascular cerebral associados à alta temperatura e monóxido de carbono em área metropolitana do sudeste do Brasil. Rev Saude Publica 1993; 27(1):15-22.^,4949. Gouveia N, Freitas CU, Martins LC, Marcilio IO. Hospitalizações por causas respiratórias e cardiovasculares associadas à contaminação atmosférica no Município de São Paulo, Brasil. Cad Saude Publica 2006; 22(12):2669-2677..

The data of this study shows that alterations in FC, COex and COHb were related to environmental exposure, confirming that the elderly population is at risk of damage to health during the practice of exercise in the periods of fires and dry climate in the city of Cuiabá, MT. Thus, when exercising in external environments, elderly people should be monitored by professionals giving greater attention to climate conditions and pollution; the use of a portable monoxide monitor is suggested.

This study brings to light a process of potential illness in elderly individuals exercising in external environments in the city of Cuiabá, MT. Exposure to high temperatures and pollutants could be reduced by: more effective health supervision action; greater attention; and training of exercise professionals, minimizing risks to the health of the elderly population.

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