Research Article | Open Access
Valeria C. Morales-Ancajima, Vilma Tapia, Bryan N. Vu, Yang Liu, Dulce E. Alarcón-Yaquetto, Gustavo F. Gonzales, "Increased Outdoor PM2.5 Concentration Is Associated with Moderate/Severe Anemia in Children Aged 6–59 Months in Lima, Peru", Journal of Environmental and Public Health, vol. 2019, Article ID 6127845, 8 pages, 2019. https://doi.org/10.1155/2019/6127845
Increased Outdoor PM2.5 Concentration Is Associated with Moderate/Severe Anemia in Children Aged 6–59 Months in Lima, Peru
Anemia affects 1.62 billion people worldwide. Although iron deficiency is the main cause of anemia, several other factors may explain its high prevalence. In this study, we sought to analyze the association between outdoor particulate matter PM2.5 levels with anemia prevalence in children aged 6–59 months residing in Lima, Peru (n = 139,368), one of the cities with the worst air pollution in Latin America. The study period was from 2012 to 2016. Anemia was defined according to the World Health Organization (Hb < 11 g/dL). PM2.5 values were estimated by a mathematical model that combined data observed from monitors, with satellite and meteorological data. PM2.5 was analyzed by quintiles. Multiple linear and logistic regressions were used to estimate the associations between hemoglobin concentration (beta) and anemia (odds ratio) with PM2.5, after adjusting by covariates. Prevalence of anemia was 39.6% (95% confidence interval (CI): 39.3–39.9). Mild anemia was observed in 30.8% of children and moderate/severe in 8.84% of children. Anemic children compared with nonanemic children are mainly males, have low body weight, higher rate of stunting, and live in an environment with high PM2.5 concentration. A slight decrease in hemoglobin (4Q B: −0.03, 95% CI: −0.05 to −0.02; 5Q B: −0.04, 95% CI: −0.06 to −0.01) and an increase in the probability of moderate/severe anemia (4Q OR: 1.18, 95% CI: 1.10–1.27; 5Q OR: 1.18, 95% CI: 1.08–1.29) were observed with increased exposure to PM2.5. We conclude that outdoor PM2.5 levels were significantly associated with decreased hemoglobin values and an increase in prevalence of moderate/severe anemia in children under 5 years old.
Anemia affects 1.62 billion people worldwide  and is associated with numerous adverse health outcomes, including increased mortality and cognitive disorders. Developing countries account for 89% of all anemia-related disability .
According to the WHO, 50% of cases of anemia are due to iron deficiency, while 42% of the cases are of inflammatory origin (inflammatory anemia). Inflammatory anemia or anemia of inflammation (AI) in children aged 6–59 months is mainly related to infectious diseases particularly in less developed countries . However, infections are not the only cause for inflammation. Evidence suggests that chronic diseases such as chronic kidney disease, congestive heart failure, chronic pulmonary disease, and obesity may result in AI [4, 5].
Another potential cause of inflammatory anemia is exposure to air pollutants since fine particulate matter equal or less than 2.5 microns in diameter (PM2.5) and NO2 produce systemic inflammation  and directly affect bone marrow . From these, PM2.5 is one of the most toxic pollutants, and short-term exposure to PM2.5 causes a 2.8% increase in mortality rates with adverse effects in human health . In addition, long-term exposure to PM2.5 is associated with cardiovascular disease and chronic obstructive pulmonary disease  and may cause oxidative stress-dependent inflammation in the lungs [10, 11].
Inflammation-inducible cytokines increase serum levels of hepcidin, the main regulator of iron homeostasis, which in turn will block iron absorption in the duodenum and cause iron retention in reticuloendothelial cells resulting in iron-restricted erythropoiesis. In addition, shortened erythrocyte half-life suppressed erythropoietin response to anemia and inhibition of erythroid cell differentiation by inflammatory mediators, further contributing to AI . Oxidative stress has been considered as a cause of eryptosis or shortening of erythrocyte half-life .
An emerging body of evidence has associated exposure to air pollution with anemia in an older population, with C-reactive protein, an inflammatory marker acting as a mediator . In addition, exposure to long-term PM2.5 and NO2 was associated with decreased cognitive function . Most of these studies relating air pollution with inflammation and anemia have been performed in older people in whom it is possible to determine long-term exposure. According to different studies, all of these adverse outcomes seem to be related to moderate/severe anemia .
It is important to know if the effect of air pollution on hemoglobin (Hb) and anemia is also observed in other age groups and how associated it is to the severity of anemia. A study in 29 developing countries revealed that both moderate exposure and high exposure to biofuel smoke at the country level were associated with moderate/severe anemia in children (odds ratio (OR): 2.36; 95% confidence interval (95% CI): 1.28–4.36 vs OR: 2.80; 95% CI: 1.37–5.72) .
A strong association between biofuel use and risk of anemia and stunting in children suggests that exposure to biofuel smoke may contribute to chronic nutritional deficiencies in infants. 31% of moderate-to-severe anemia and 37% of severe stunting among children aged 6–35 months in India may be attributable to exposure to biofuel smoke .
Despite there are data regarding indoor air pollution and anemia, the effect of outdoor air pollution, especially PM2.5, on anemia in children is still unknown.
According the World Health Organization (WHO), Lima, Peru, is one of the Latin American cities with the highest mean annual PM2.5 values, a matter of severe public health concern . In fact, PM2.5 levels in Lima between 2001 and 2011 averaged 50 μg/m3. It was estimated that the excess of PM2.5 in Lima (above 10 μg/m3 of the reference level) during this period, resulted in approximately 2,300 premature adult deaths from cardiorespiratory disease annually .
Air quality guidelines given by the WHO state that the annual mean value of PM2.5 concentration should be 10 μg/m3 and 25 μg/m3 for a 24-hour mean . This threshold is not met by many countries including Peru, where the Ministry of Environment (MINAM) recommends a threshold of 25 μg/m3 for an annual mean and 50 μg/m3 for a 24-hour mean . These different guidelines, besides creating confusion, might have effects when trying to assess the impact of air pollution on health.
For the aforementioned reasons, the present study was designed to determine the relationship between Hb and anemia with PM2.5 concentration in children aged 6–59 months residing in Lima, Peru. The study also aims to determine the association between anemia levels and high PM2.5 values using the thresholds provided by the WHO and MINAM.
2. Materials and Methods
2.1. Study Area
The metropolitan city of Lima is the capital of Peru with more than 10 million inhabitants. It is located in the central coast of the country (150 m.a.s.l.), next to the Pacific Ocean. Lima is divided into 43 districts, which cover 2,672.28 km2 of the land; those include the actual city (825.88 km2) and the city outskirts (1,846.40 km2). For this study, districts of Lima have been divided into 5 zones: North Lima, Center Lima, South Lima, East Lima, and West Lima (which include the constitutional region of Callao). Center Lima is considered more economically developed than the rest of the zones, but the entire city is highly urbanized. The population density of Lima by district can be seen in Supplementary Figure 1(a).
2.2. Study Population
The study analyzed the Nutritional Status Information System (SIEN in Spanish), a database provided by the National Center of Feeding and Nutrition (CENAN in Spanish), an institution belonging to the National Institutes of Health in Peru. Data analyzed in the current study included 139,368 infants and children aged 6 to 59 months with permanent residence on the districts that comprise the metropolitan city of Lima. Distribution of the sample by district can be seen in Supplementary Figure 1(b). 4,208 registries lacked hemoglobin (Hb) data or had implausible Hb values < 3 g/dL (n = 28) or >30 g/dL (n = 64). These data were excluded from analysis. Data were collected yearly from 2012 to 2016.
Hemoglobin (Hb) was measured in each health center by trained personnel using the Hemocue method and is expressed in grams per deciliter (g/dL). Anemia in children aged 6 to 59 months was defined as Hb < 11 g/dL according to the WHO guidelines . Anemia was categorized according to severity as mild (10–10.9 g/dL), moderate (<10–7 g/dL), and severe (<7 g/dL) .
Daily PM2.5 exposure levels from 2010 to 2016 were estimated using a random forest (RF) model . The RF model integrates satellite remote sensing aerosol optical depth (AOD) data with meteorological variables from chemical transport and forecast models and land use variables to predict existing ground measurements from the SENAMHI (10 stations) and Johns Hopkins (6 aggregated stations) networks. MAIAC (Multiangle Implementation of Atmospheric Correction) retrieved AOD was cross-validated with ground AOD from Arica (https://aeronet.gsfc.nasa.gov/cgi-bin/type_one_station_opera_v2_new?site=Arica&nachal=2&level=1&place_code=10), the nearest AERONET site located in Chile for 2010 to 2015, and gap-filled through a random forest model (cross validation (CV) R2 = 0.82) .
Meteorological variables from WRF-Chem (Weather Research and Forecast model coupled with Chemistry) and ECMWF (European Centre for Medium-Range Weather Forecasts) were collected at 5 km2 and 1 km  spatial resolution, respectively, and interpolated to 1 km2 resolution through inverse-distance weighting. Land use variables such as percent urbanization, elevation, population density, and distance to road were also calculated for use in the model. The RF model to predict daily PM2.5 levels achieved an R2 (and CV R2) of 0.70 (RMSE = 5.95 μg/m3, CV RMSE = 5.97 μg/m3) .
Finally, we assigned the average of the last month prior to the measurement of hemoglobin to each child. PM2.5 data was estimated from each participant’s district of residence.
Other variables were age (expressed in months) and stunting (defined as height for age Z-score (HAZ) < −2.0). Lima area includes the 43 districts grouped as north (8 districts), center (15 districts), south (12 districts), east (8 districts), and west (1 district, Callao) (Supplementary Figure 2). The poverty index as defined by the Peruvian Institute of Statistics and Informatics (INEI) . In brief, their prediction model uses the logarithm of the per capita income along with data of the National Household Survey that includes variables such as educational characteristics, economically active population, availability of electric lighting, type of water supply, hygienic services, material of the walls and floors of the house, possession of electronic equipment, and telecommunication services. This index was used as a continuous variable. The variables year and month correspond to the date of the measurement of hemoglobin. Season was defined as cold and hot months.
This study was approved by the IRB at the Universidad Peruana Cayetano Heredia (SIDISI 103700).
2.4. Statistical Analysis
Software STATA 14.0 (StataCorp, Texas, USA) was used for statistical analysis and QGis 2.18.16 Las Palmas (http://www.qgis.org) was used for map construction. Data are presented as mean values ± standard deviations for continuous variables and as percentages for categorical variables. For statistical analysis, anemia was further categorized as mild and moderate/severe since cases of severe anemia were scarce. PM2.5 concentration does not have normal distribution; therefore, nonparametric tests were used to compare PM2.5 and anemia in the different zones of Lima. For categorical variables such as anemia and stunting, the chi-square test was used to compare them between the five zones of Lima. Differences between normally distributed variables among the five zones of Lima were assessed with ANOVA test. Those variables that were not normally distributed were assessed with nonparametric Wilcoxon test.
Multiple linear regression and logistic regression models were used to associate hemoglobin concentration or prevalence of anemia with PM2.5 concentration. In addition, severity of anemia was evaluated by logistic regression with two models, one for mild anemia and the other for moderate/severe anemia. Both crude and adjusted models were run. Adjustment was made with age, gender, stunting, year, month, Lima zone, poverty, and season. First, we analyzed PM2.5 as a continuous variable, then PM2.5 values were categorized in quintiles: 1Q: 17.39 μg/m3 (13.62–18.22); 2Q: 19.18 μg/m3 (18.23–20.25); 3Q: 21.89 μg/m3 (20.26–24.89); 4Q: 26.87 μg/m3 (24.97–28.83); and 5Q: 32.69 μg/m3 (28.85–51.0). We additionally generated a new variable with values recommended by the WHO (25 μg/m3) and MINAM (50 μg/m3) as cut-off of permissible PM2.5 values in order to compare the risk between both thresholds.
To assess if a certain age group is more vulnerable to the exposure, we further stratified by age from 6 to 11, 12 to 35, and 36 to 59 months. This categorized variable has been included in all statistical models. A value <0.05 was considered as significant.
3. Results and Discussion
Characteristics of the study population are shown in Table 1. From the total population (n = 139,368 children), 55,216 (39.6%) children had anemia (Hb < 11 g/dL). Anemic children compared to nonanemic children are mainly young children, male, with low body weight, higher rate of stunting, and live in an environment with high PM2.5 concentration. Mild anemia was observed in 30% of the population, while severe/moderate anemia was observed in 8.8% of the population.
Values are frequencies and percentage (%) or mean ± SD. Comparison is between no anemia vs. mild and moderate/severe anemia. Chi-square test: , no anemia vs mild and moderate/severe anemia. ANOVA: , no anemia vs mild and moderate/severe anemia. Chi-square test: , no anemia vs moderate/severe anemia. Wilcoxon: , no anemia vs mild and moderate/severe anemia. ANOVA: , no anemia vs mild anemia.
In Table 2, data related to the five zones of Lima are shown. Here, the 43 districts are included. The east sector of Lima has the lowest hemoglobin concentration (11.09 ± 1.05 g/dL, mean ± SD), the highest prevalence of anemia (41.3%), and the highest concentration of PM2.5 (31.6 μg/m3 ± 5.6). The highest concentration of Hb was observed in the West zone, and it was associated with the lowest prevalence of anemia, lower prevalence of stunting, and lower PM2.5 values.
Anemia: hemoglobin (Hb) < 11 g/dL. North Lima compared to others zones. ANOVA: Hb: North vs the rest. Age: North vs the others. Wilcoxon test: North vs the others. Chi-square test: stunting North vs Central. Anemia North vs Central, South, and West.
Figure 1(a) shows the different concentrations of PM2.5 in the districts of metropolitan Lima from 2012 to 2016. The lighter blue tone corresponds to lower concentration of PM2.5 (13.6–18.23), and the darkest tone corresponds to the highest concentration of PM2.5 (28.85–50.83). Figure 1(b) shows the prevalence of anemia by district during the same period. The lighter tone of red corresponds to the lower anemia prevalence (16.9–25.2%), and the darkest color corresponds to the highest (49.8–58.1%). Anemia prevalence above 25% is observed in almost all districts.
The linear regression analysis between quintiles of PM2.5 concentration and hemoglobin showed a decline in Hb concentration with increasing PM2.5. Interestingly, exposure to values of the quintile 4 (24.97–28.84 μg/m3) resulted in a significant decrease in hemoglobin levels (Table 3). Hemoglobin increases with age; is higher in female than male children, higher in cold seasons, and lower in children with stunting and in those with high poverty index; and increases over time from 2014 onwards.
Linear regression model adjusted by age, gender, stunting, season, poverty, months, year, and Lima zone. Bold values denote statistical significance.
When magnitude of anemia was assessed, the effect of exposure to high concentrations of PM2.5 was seen in moderate/severe anemia. After adjusting for several variables, the OR for moderate/severe anemia was significantly higher in quintiles 2, 3, 4, and 5, while the OR for mild anemia was not different among PM2.5 quintiles (Table 4). Quintile 2 includes values of PM2.5 below the threshold recommended by the WHO (PM2.5 = 25 μg/m3).
Models are adjusted by gender, stunting, season, poverty, months, year, and Lima zone. Bold values denote statistical significance.
We analyzed the thresholds used by the WHO and MINAM as cut-off point to define PM2.5 permissible values and their association with anemia. When using the threshold recommended by the WHO (PM2.5 = 25 μg/m3), a reduction of hemoglobin is observed even at lower than permitted values (beta: −0.01; 95% CI: −0.030 to −0.01). With the threshold recommended by the MINAM (PM2.5 = 50 μg/m3), a greater decline of hemoglobin concentration was observed (beta: −0.39; 95% CI: −0.595 to −0.1965).
Mild anemia and severe/moderate anemia have been evaluated at the different air quality cut-off points. When using the threshold recommended by the WHO, PM2.5 was associated with moderate/severe anemia (OR: 1.08; 95% CI: 1.02–1.14). However, when using MINAM reference values, PM2.5 over the threshold were associated with both moderate/severe anemia (OR: 2.83; 95% CI: 1.39–5.75) and mild anemia (OR: 2.76; 95% CI: 1.72–4.41).
After adjusting for confounding variables, such as age, gender, stunting, season, poverty, month, year, and Lima zone, PM2.5 was negatively associated with hemoglobin levels at 6–35 months of age (coefficient of regression ± standard error: 0.0015 ± 0.0007; 95% CI: −0.029 to −0.0001; ). This was not observed in the group of 36–59 months ().
This study assessed outdoor PM2.5 exposure and its association with anemia prevalence in children aged 6 to 59 months residents in Lima, Peru, one of the cities with the worst air pollution in Latin America. The anemia rates shown in these studies are high and are in line with official statistics for metropolitan Lima . Anemia is one of Peru’s major public health problems. Our findings show that exposure to increasing concentrations of PM2.5 is associated with a decrease in hemoglobin levels. This, in turn, increases the prevalence of anemia. For instance, when people are exposed to concentrations between 25 μg/m3 (WHO reference value) and 50 μg/m3 (MINAM reference value), a decrease in hemoglobin is observed. Moreover, the higher the concentration of PM2.5 to which a child is exposed, the greater the reduction in hemoglobin concentration.
Peru has its own guideline thresholds for PM2.5 that differs from the ones recommended by the WHO. The prevalence of anemia increases at 50 μg/m3 PM2.5 . Also, an increase in anemia prevalence is observed at concentrations between the referential air quality values of PM2.5 (25–50 μg/m3), meaning that particulate matter at higher concentrations is an important health problem for populations exposed to this pollutant.
Furthermore, our results report an association with moderate/severe anemia, even with PM2.5 values below the threshold recommended by the WHO. Most of the children with anemia have mild anemia . The group of mild anemic may be worsened in the presence of air pollution (PM2.5) moving anemia from mild to moderate/severe. Our hypothesis is based on the fact that threshold of PM2.5 recommended by the WHO and MINAM was associated to moderate/severe anemia.
As evidenced by the results in this study, children exposed to high concentrations of PM2.5 hold a greater risk of a decrease in hemoglobin values and an increase in anemia prevalence. With MINAM’s referential daily value of 50 μg/m3, children are at an even higher risk for moderate/severe anemia. Data from the present study reveal that even values below the threshold recommended by the WHO are associated with anemia in children. Guidelines to define permissible values of daily PM2.5 concentration should be revised. In Lima, the main sources of outdoor air pollution are automotive fleet and industrial activities . A recent study showed that a change of policy regarding traffic regulation of one of Lima’s main avenues, significantly decreased PM2.5 values , meaning that similar changes may have an impact improving air quality.
In Peru, children begin preschool after turning 3 years old. Before this age, they mainly stay at their homes, so assessing the exposure with the district of residence gives a good estimate of how permanently exposed these children are to pollutants. Furthermore, children tend to attend preschool institutions close to their homes at the same district, so estimating exposure based on the district of residence is also applicable for the older age group.
The plausibility of our findings is that air pollutants generate an inflammatory process in the human body [26, 27]. PM2.5 has been shown to increase systemic inflammation  and produce chronic inflammation . These systemic processes potentially contribute to the association with low hemoglobin levels and an increase in prevalence of anemia as observed in the present study. Poursafa et. al. showed that increased levels of PM10 were associated with a reduction of hemoglobin concentration and red blood cell counts but increased white blood cell counts suggesting a direct association with inflammation and an inverse relationship with hemoglobin levels . Furthermore, Honda et al. (2017) showed that an increased exposure to PM2.5 was associated with a decrease of 0.81 g/dL of hemoglobin in an elderly population . Other volatile pollutants have also been linked to a decrease in Hb and other hematological markers with an increase in proinflammatory cytokines .
Particulate matter, as any other pollutant, generates an inflammatory response in the human body [32–35]. These effects are almost immediate since it has been shown that after a 1- to 3-day exposure to PM2.5, C-reactive protein levels, an inflammatory marker, increase . Therefore, children under 5 years represent a good model to assess the effects of PM2.5 exposure and anemia.
Hepcidin, the hepatic peptide hormone in charge of controlling iron homeostasis, and ferroportin, a transmembrane receptor which exports iron into blood plasma, control the main routes of iron transport and availability and determine total body iron content . Inflammation generated by PM2.5 increases serum hepcidin levels, degrading ferroportin as a host defense mechanism . This mechanism is induced by proinflammatory cytokines that enhance hepcidin levels. This results in an increased internalization and degradation of ferroportin followed by cellular iron retention, ultimately leading to insufficient iron bioavailability. This iron deficiency can lead to an inflammatory anemia . Another explanation for the link between outdoor air pollution and anemia is hemolysis or the destruction of red blood cells. This event can be triggered by the mineral particles adsorbed after airborne pollution exposure . Both the cascading effect produced by PM2.5 on hepcidin and the hemolysis need further research.
This study has certain limitations. First, our database was obtained from the Information System of Nutritional Status (SIEN in Spanish) of the National Institutes of Health in Peru. The rates of anemia prevalence only correspond to the population which was attended at public health care centers. People attended in private health care system, which accounts for 10% of the population, and those attended by the Social Health Insurance (EsSalud in Spanish), nearly 39% , are not included.
This limitation may explain why some of the more residential or high-income districts have a high percentage of anemia prevalence since it does not include the populations with a high or high-average socioeconomic level that are attended at private health care centers. PM2.5 data have been linked to each participant’s district of residence; it could not be linked to each participant’s exact address. Another major limitation is that inflammatory markers have not been assessed in this study. C-reactive protein (CRP) and hepcidin levels should be measured in future studies to properly explain the mechanism by which exposure to increased PM2.5 increases anemia prevalence.
Even though the study is not prospective, it appears as children with mild anemia (control group) may worsen and become moderate to severe anemic when exposed to increased PM2.5 concentrations, particularly over 50 μg/m3. This, however, needs to be proven in further research, as well as the higher susceptibility of younger children since PM2.5 is more strongly related to anemia in the younger age group.
Anemia is currently the major public health problem Peru is facing; this paper sheds light on other reasons that might explain the high anemia prevalence in the country. Exposure to higher than allowed (25 μg/m3) concentrations of PM2.5 is associated with an increased prevalence of anemia in children aged less than five years particularly moderate/severe anemia, constituting a new risk factor to be taken into account when designing policies aiming to eradicate anemia worldwide. Since the risk of decreased hemoglobin levels is seen even at lower values than those suggested by the WHO and local regulatory agencies (MINAM), we call for a revision of current guidelines. The mechanisms by which PM2.5 exposure might decrease hemoglobin concentrations need to be studied further but might be related to the activation of inflammatory processes.
Data from this study are available upon request.
Conflicts of Interest
The authors have no conflicts of interest to disclose.
This study was funded by the National Institutes of Health (Fogarty Program) (grant U01TW010107), 1/2 Regional GEOHealth Hub, centered in Peru.
Supplementary Figure 1: (a) population density of Lima by district; (b) distribution of the study population by district. Supplementary Figure 2: (a) average PM2.5 values by Lima zone; (b) anemia prevalence (%) by Lima zone. (Supplementary Materials)
- WHO, The Global Prevalence of Anaemia in 2011, WHO, Geneva, Switzerland, 2015.
- N. J. Kassebaum, “The global burden of anemia,” Hematology/Oncology Clinics of North America, vol. 30, no. 2, pp. 247–308, 2016.
- J. Wirth, T. Rajabov, N. Petry et al., “Micronutrient deficiencies, over- and undernutrition, and their contribution to anemia in Azerbaijani preschool children and non-pregnant women of reproductive age,” Nutrients, vol. 10, no. 10, p. 1483, 2018.
- G. Weiss, T. Ganz, and L. T. Goodnough, “Anemia of inflammation,” Blood, vol. 133, no. 1, pp. 40–50, 2019.
- A. Flynn, S. Begum, S. White et al., “Relationships between maternal obesity and maternal and neonatal iron status,” Nutrients, vol. 10, no. 8, p. 1000, 2018.
- J. E. Mirowsky, R. E. Peltier, M. Lippmann et al., “Repeated measures of inflammation, blood pressure, and heart rate variability associated with traffic exposures in healthy adults,” Environmental Health, vol. 14, no. 1, p. 66, 2015.
- S. F. V. Eeden and J. C. Hogg, “Systemic inflammatory response induced by particulate matter air pollution: the importance of bone-marrow stimulation,” Journal of Toxicology and Environmental Health, Part A, vol. 65, no. 20, pp. 1597–1613, 2002.
- I. Kloog, B. Ridgway, P. Koutrakis, B. A. Coull, and J. D. Schwartz, “Long- and short-term exposure to PM2.5 and mortality,” Epidemiology, vol. 24, no. 4, pp. 555–561, 2013.
- J. Po, N. Shahidi, J. M. FitzGerald, and C. Carlsten, “Respiratory disease associated with solid biomass fuel exposure in rural women and children: systematic review and meta-analysis,” in Indoor and Outdoor Air Pollution Exposures and Epidemiology, American Thoracic Society, New York, NY, USA, 2009.
- B. Yang, J. Guo, and C. Xiao, “Effect of PM2.5 environmental pollution on rat lung,” Environmental Science and Pollution Research, vol. 25, no. 36, pp. 36136–36146, 2018.
- T. Honda, V. C. Pun, J. Manjourides, and H. Suh, “Anemia prevalence and hemoglobin levels are associated with long-term exposure to air pollution in an older population,” Environment International, vol. 101, pp. 125–132, 2017.
- R. Bissinger, A. A. M. Bhuyan, S. M. Qadri, and F. Lang, “Oxidative stress, eryptosis and anemia: a pivotal mechanistic nexus in systemic diseases,” The FEBS Journal, vol. 286, no. 5, pp. 826–854, 2019.
- R. J. Sram, M. Veleminsky, M. Veleminsky, and J. Stejskalová, “The impact of air pollution to central nervous system in children and adults,” Neuro Endocrinology Letters, vol. 38, no. 6, pp. 389–396, 2017.
- V. Mishra and R. D. Retherford, “Does biofuel smoke contribute to anaemia and stunting in early childhood?” International Journal of Epidemiology, vol. 36, no. 1, pp. 117–129, 2007.
- WHO, Ambient (Outdoor) Air Pollution in Cities Database 2014, WHO, Geneva, Switzerland, 2016.
- G. F. Gonzales and K. Steenland, “Environmental health in Peru: outdoor and indoor air contamination,” Revista Panamericana de Salud Públicaa, vol. 36, no. 2, p. 141, 2014.
- WHO, WHO Air Quality Guidelines for Particulate Matter, Ozone, Nitrogen Dioxide and Sulfur Dioxide, WHO, Geneva, Switzerland, 2006.
- B. Vu, O. Sánchez, J. Bi et al., “Developing an advanced PM2.5 exposure model in Lima, Peru,” Remote Sensing, vol. 11, no. 6, p. 641, 2019.
- MINAM, 7 Normas Legales Miércoles 7 de Junio de 2017, MINAM, Magdalena del Mar, Peru, 2017.
- Instituto Nacional de Estadística e Informática (INEI), Mapa de Pobreza Provincial y Distrital. El Enfoque de La Pobreza Monetaria, Instituto Nacional de Estadística e Informática, Lima, Peru, 2009.
- WHO, Haemoglobin Concentrations for the Diagnosis of Anaemia and Assessment of Severity, WHO, Geneva, Switzerland, 2011.
- J. Bi, J. H. Belle, Y. Wang, A. I. Lyapustin, A. Wildani, and Y. Liu, “Impacts of snow and cloud covers on satellite-derived PM2.5 levels,” Remote Sensing of Environment, vol. 221, pp. 665–674, 2019.
- Instituto Nacional de Estadística e Informática (INEI), Encuesta Demográfica y de Salud Familiar 2018, Instituto Nacional de Estadística e Informática, Lima, Peru, 2019.
- J. Silva, J. Rojas, M. Norabuena, C. Molina, R. A. Toro, and M. A. Leiva-Guzmán, “Particulate matter levels in a South American megacity: the metropolitan area of Lima-Callao, Peru,” Environmental Monitoring and Assessment, vol. 189, no. 12, p. 635, 2017.
- V. Tapia, L. Carbajal, V. Vásquez et al., “Reordenamiento vehicular y contaminación ambiental por material particulado (2,5 y 10), dióxido de azufre y dióxido de nitrógeno en Lima Metropolitana, Perú,” Revista Peruana de Medicina Experimental y Salud Pública, vol. 35, no. 2, pp. 190–197, 2018.
- J. L. Quay, W. Reed, J. Samet, and R. B. Devlin, “Air pollution particles induce IL-6 gene expression in human airway epithelial cells via NF-κ B activation,” American Journal of Respiratory Cell and Molecular Biology, vol. 19, no. 1, pp. 98–106, 1998.
- J. Hella, C. I. Cercamondi, F. Mhimbira et al., “Anemia in tuberculosis cases and household controls from Tanzania: contribution of disease, coinfections, and the role of hepcidin,” PLoS One, vol. 13, no. 4, Article ID e0195985, 2018.
- S. Rajagopalan, S. G. Al-Kindi, and R. D. Brook, “Air pollution and cardiovascular disease,” Journal of the American College of Cardiology, vol. 72, no. 17, pp. 2054–2070, 2018.
- M. He, T. Ichinose, S. Yoshida et al., “PM2.5-induced lung inflammation in mice: differences of inflammatory response in macrophages and type II alveolar cells,” Journal of Applied Toxicology, vol. 37, no. 10, pp. 1203–1218, 2017.
- P. Poursafa, R. Kelishadi, A. Amini et al., “Association of air pollution and hematologic parameters in children and adolescents,” Journal de Pediatria, vol. 87, no. 4, pp. 350–356, 2011.
- M. T. Samadi, M. Shakerkhatibi, J. Poorolajal, A. Rahmani, H. Rafieemehr, and M. Hesam, “Association of long term exposure to outdoor volatile organic compounds (BTXS) with pro-inflammatory biomarkers and hematologic parameters in urban adults: a cross-sectional study in Tabriz, Iran,” Ecotoxicology and Environmental Safety, vol. 180, pp. 152–159, 2019.
- M. Radan, M. Dianat, M. Badavi, S. A. Mard, V. Bayati, and G. Goudarzi, “In vivo and in vitro evidence for the involvement of Nrf2-antioxidant response element signaling pathway in the inflammation and oxidative stress induced by particulate matter (PM10): the effective role of gallic acid,” Free Radical Research, vol. 53, no. 2, pp. 210–225, 2019.
- P.-C. Lee, E. O. Talbott, J. M. Roberts, J. M. Catov, R. K. Sharma, and B. Ritz, “Particulate air pollution exposure and C-reactive protein during early pregnancy,” Epidemiology, vol. 22, no. 4, pp. 524–531, 2011.
- N. Zhao, J. Qiu, Y. Zhang et al., “Ambient air pollutant PM10 and risk of preterm birth in Lanzhou, China,” Environment International, vol. 76, pp. 71–77, 2015.
- J. Liao, Y. Li, X. Wang et al., “Prenatal exposure to fine particulate matter, maternal hemoglobin concentration, and fetal growth during early pregnancy: associations and mediation effects analysis,” Environmental Research, vol. 173, pp. 366–372, 2019.
- S.-Y. Chen, C.-C. Chan, and T.-C. Su, “Particulate and gaseous pollutants on inflammation, thrombosis, and autonomic imbalance in subjects at risk for cardiovascular disease,” Environmental Pollution, vol. 223, pp. 403–408, 2017.
- J. Ćulafić, J. Kolarović, L. Pezo et al., “Serum concentration of hepcidin as an indicator of iron reserves in children,” Journal of Medical Biochemistry, vol. 37, no. 4, pp. 456–464, 2018.
- A. L. Langer and Y. Z. Ginzburg, “Role of hepcidin-ferroportin axis in the pathophysiology, diagnosis, and treatment of anemia of chronic inflammation,” Hemodialysis International, vol. 21, pp. S37–S46, 2017.
- M. D. Cappellini, J. Comin-Colet, A. de Francisco et al., “Iron deficiency across chronic inflammatory conditions: international expert opinion on definition, diagnosis, and management,” American Journal of Hematology, vol. 92, no. 10, pp. 1068–1078, 2017.
- A. Mesdaghinia, Z. Pourpak, K. Naddafi et al., “An in vitro method to evaluate hemolysis of human red blood cells (RBCs) treated by airborne particulate matter (PM10),” MethodsX, vol. 6, pp. 156–161, 2019.
- ESSALUD, Encuesta Nacional Socieconómica de Acceso a La Salud de Los Asegurados de EsSalud: Diseño, Metodología, Resultados Generales, ESSALUD, Lima, Peru, 2015.
Copyright © 2019 Valeria C. Morales-Ancajima et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.