Effects of emissions from sugar cane burning on the trachea and lungs of Wistar rats (2024)

Language: English | Portuguese

ABSTRACT

Keywords: Saccharum, Smoke, Inflammation, Respiratory system

RESUMO

Descritores: Saccharum, Fumaça, Inflamação, Sistema respiratório

INTRODUCTION

Sugar cane, Saccharum officinarum, is widely cultivated in Brazil for the production of ethanol and sugar, being essential to the country’s economy.^1,2 Harvesting of sugar cane, when performed manually, is preceded by burning of sugar cane fields to remove dry leaves, facilitate cutting, and reduce the risk of bites and stings by venomous animals.^3-7

Sugar cane combustion releases a large quantity of particulate matter (PM), in addition to gases, such as ozone, carbon monoxide, nitric oxide, sulfur oxide, formaldehyde, benzopyrene, and polycyclic aromatic hydrocarbons,^6-8 all of which contribute to air pollution and adversely affect human health.^2,9,10

The PM and toxic compounds generated by sugar cane burning are harmful to the respiratory tract, because as they are inhaled and deposited in the lower airways, they are phagocytosed by alveolar macrophages, which release cytotoxic cytokines, thus inducing inflammation.^4,8 The stress caused by smoke can trigger a series of cellular reactions that aim to restore stability; however, when this stress is chronic, it causes irreversible cellular damage.¹¹ Coarse PM from smoke damages the upper airways, which are directly exposed to the external environment, whereas fine PM from smoke accumulates in the bronchi and bronchioles, leading to permanent damage and fibrosis.^12,13 Alveolar structures are susceptible to responses of an inflammatory nature and can cause pathological reactions with obstructive and restrictive consequences,^11,12,14-16 generally associated with the process of tissue remodeling.¹⁴

Although the risks from exposure to smoke, such as tobacco smoke or emissions from fossil fuel burning, are known, there have been few studies on this topic. Therefore, the objective of the present investigation was to use an experimental model to evaluate the effects of exposure to emissions from sugar cane burning on inflammatory mechanisms in tissues of the trachea and lung parenchyma after different periods of exposure.

METHODS

This was an experimental open randomized study. In the study, 28 male Wistar rats weighing 250-300 g were housed in cages with sawdust bedding, maintained on a 12/12-h light/dark cycle at 25-28°C, and provided free access to standard rodent chow and filtered water. The animals were divided into four groups: a control group (CG) of 4 animals underwent standard laboratory conditions for 24 h; and three experimental groups of 8 animals each were exposed to emissions from sugar cane straw burning for consecutive periods of 1, 7, and 21 days (EG1, EG7, and EG21, respectively). For the purposes of the study, a combustion chamber with a portable air extraction device was built where 200 g of sugar cane straw were burnt, generating a continuous stream of smoke that was piped into the cages of the experimental animals for 2 h daily at the same time of day (Figure 1).

The animals were euthanized by i.p. administration of 5% ketamine/xylazine diluted with 2 mL of physiological saline. After this procedure, the trachea was exposed and cannulated, a laparotomy was performed to separate the organs, and the abdominal aorta and inferior vena cava were sectioned. The trachea was then occluded by suture to maintain the lungs at functional residual capacity. A trans-sternal thoracotomy was performed through the diaphragm to remove the trachea and lungs. The collected organs were washed with physiological saline for macroscopic examination and were fixed in 10% buffered formalin.

Tissue fragments obtained from the material were processed conventionally and embedded in paraffin to prepare slides containing 5-μm sections. The sections were stained with H&E and picrosirius red for analysis under light microscopy (BX51; Olympus Optical, Tokyo, Japan) at a magnification of ×100. A digital camera (C-7070; Olympus) was used to obtain photomicrographs. To perform a semi-quantitative microscopic analysis, the histological changes found were classified as mild, moderate, or marked.

For a morphometric analysis, three photomicrographs were obtained of non-overlapping fields of the tissues studied. In the tracheal sections, areas containing hyaline cartilage, lamina propria, and ciliated epithelium were selected. In the lung parenchyma, bronchioles, alveoli, and blood vessels were evaluated. The nuclear area was quantified (in pixels) to evaluate the inflammatory process, using Adobe Photoshop CS5 software (Adobe Systems Inc.; San Jose, CA, USA). Collagen deposition was quantified by picrosirius red staining, positive staining corresponding to the presence of type I collagen. Angiogenesis was assessed by counting the number of blood vessels per quadrant of each panoramic photomicrograph, using BioEstat 5.3 software.

A statistical analysis was carried out using the Shapiro-Wilk normality test. After confirmation of normality, ANOVA with Tukey’s post hoc test was used. In cases of non-normality, the Kruskal-Wallis test and Dunn’s post hoc test were used. Results were expressed as group means and standard deviations and as box plots. The level of significance was set at 5%.

The study was approved by the Animal Research Ethics Committee of the Faculdade Adventista da Bahia (Protocol no. 013/2014).

RESULTS

Macroscopic examination of the trachea revealed no changes in tissue color or integrity in any of the groups. The lungs of EG7 and EG21 rats showed focal and diffuse macroscopic changes in different lobes, these changes being related to tissue color and texture.

The histological findings for each group are described below.

In the CG, there were no inflammatory infiltrates or structural tissue changes in the trachea (Figure 2). The lung parenchyma showed no alveolar, septal, or bronchiolar changes and was of normal appearance (Figure 3).

In EG1, a mild inflammatory infiltrate was present in the trachea in 87.5% of the cases. However, in 12.5% of the samples analyzed, the inflammatory response was intense and predominantly focal (Figure 2). In the lung parenchyma, an inflammatory process, consisting of 50% of polymorphonuclear cells, was present in 75% of the cases, and the diffuse form predominated over the focal one. Infiltrates were found in perivascular areas (ranging from mild to moderate) and in peribronchiolar areas. In addition, mild interstitial edema was observed, and there was no collagen deposition (Figure 3).

In EG7, inflammatory infiltrates of varying intensity-mild (in 62.5% of the cases), moderate (in 50.0%), and intense (in 25.0%)-were present in the tracheal tissue (Figure 2). The onset of collagen deposition was demonstrated by the increased acidophilic reaction in the trachea after picrosirius red staining (Figure 2). Microscopic examination of the lung parenchyma revealed an inflammatory process in 87.5% of the cases and a polymorphonuclear cell infiltrate in 62.5%. A mild to intense diffuse inflammatory process was present in 75% of the cases. A perivascular infiltrate pattern was present in 62.5% of the specimens. In addition, perivascular and peribronchiolar collagen deposition was found (Figure 3).

In EG21, a diffuse inflammatory infiltrate was observed in 75% of the cases, being of mild (in 25%) to moderate (in 50%) intensity. No intense inflammatory infiltrates were found (Figure 2). After picrosirius red staining, there was increased acidophilia, indicating the presence of collagen (Figure 2). Histological examination of the lung parenchyma revealed mild to intense diffuse inflammatory infiltrates, with a predominance of mononuclear cells, in 100% of the cases. There was mild perivascular and peribronchiolar inflammation in 50% and 25% of the cases, respectively. Necrosis was observed in 37.5% of the cases and angiogenesis was observed in 100% (p < 0.001) when EG21 was compared with the CG and EG1; in addition, perivascular and peribronchiolar collagen deposition was seen, as was alveolar collagen deposition (Figure 3).

Morphometric and statistical analysis (Figure 4) demonstrated the presence of an inflammatory process in the tracheal tissue of experimental group rats. The mean nuclear area (in pixels) was 379.78 ± 105.65 in the CG, 650.36 ± 147.74 in EG1, 899.18 ± 183.65 in EG7, and 751.96 ± 143.64 in EG21. In comparison with the CG, EG7 showed a more significant inflammatory response (p < 0.05). The data obtained from the morphometric analysis are complementary to the findings of the semi-quantitative analysis.

Morphometry after picrosirius red staining revealed no collagen deposition in the CG and showed a slight progressive, but not statistically significant, increase in acidophilia in EG1 and EG7. However, tracheal tissue collagen deposition was found to be greater in EG21 than in the CG and EG1 (p < 0.01 for both; Figure 4).

Morphometric analysis of the lung parenchyma was performed by determining the mean nuclear area (in pixels). In the CG, the mean nuclear area was 893.13 ± 51.89, which is within normal values. In EG1, polymorphonuclear and mononuclear cellularity started to increase, and the mean nuclear area was 1,373.66 ± 155.43; in EG7, the mean nuclear area reached 2,280.98 ± 744.80 (p < 0.01 in the intergroup comparison). However, the mean nuclear area decreased to 1,251.31 ± 231.75 in EG21, which is suggestive of tissue repair (Figure 5).

Morphometric analysis showed no angiogenesis in the CG, EG1, or EG7. In contrast, in EG21, angiogenesis was detected in 100% of the cases (Figure 5).

DISCUSSION

Our results show that exposure of Wistar rats to emissions from sugar cane burning over different periods of exposure was associated with increased inflammation in tracheal and lung tissues. Focal and diffuse inflammatory polymorphonuclear cell infiltrates were found in the acute phase in the trachea of experimental group rats, especially of EG7 rats. No loss of ciliated epithelium was observed in any of the experimental groups relative to the CG. Tissue fibrosis in the trachea, corresponding to the early stages of the chronic phase, was confirmed in EG21. In the lung parenchyma, alveolar, vascular, and bronchiolar changes were observed in the experimental groups relative to the CG. The time criteria adopted for designating the inflammatory response phases were based on a study of Wistar rats that were administered bleomycin sulfate, in which the inflammatory response was characterized as acute (from day 1 to day 7 after the insult); subacute (from day 7 to day 14 after the insult); and resolving (from day 15 to day 30 after the insult).¹⁷

An experimental study, in which rats received intratracheally-instilled fine PM, observed lung inflammation characterized by macrophage and neutrophil infiltrates, demonstrating that cytokines (IL-12 and IFN-γ) play a key role in injury severity¹⁸; similarly, an experimental rabbit study found an increased recruitment of macrophages and polymorphonuclear cells in the lung parenchyma.¹⁹ In the present study, we found inflammatory changes consisting of polymorphonuclear cells and alveolar macrophages in the lung tissue of rats as early as in EG1.

Tracheal instillation of low doses of PM from sugar cane burning produced changes in the respiratory tract by reducing the thickening of the connective tissue and increasing the production of proinflammatory cytokines and chemokines.⁸ In the present study, morphometry confirmed that emissions from sugar cane burning are able to induce significant and progressive necrotic inflammatory processes, even after short periods of exposure. Alveolar macrophages (after phagocytosis), as well as lung epithelial cells, respond to exposure to PM by increasing inflammatory mediator production, which can lead to certain mechanisms, such as leukocyte proliferation and activation, apoptosis, and endothelial repair.²⁰ These changes are explained by the elements present in smoke; these data confirm our findings, especially in EG7.

It is known that the size of particles emitted from biomass burning has a negative impact on the airways.^21,22 The size of inhaled PM, in terms of varying particle granularity, determines the clinical manifestations in the body. Coarse PM (< 10 µm) is retained in the upper airways and can be removed by ciliary activity; thin PM (< 2.5 µm) and ultrafine particles/nanoparticles (< 0.1 µm) are usually the result of incomplete oxidation of carbon.^22-24 Fine and ultrafine PM have the ability to reach the alveoli and be phagocytosed by alveolar macrophages, having greater deleterious effects, such as changes in lung mechanics, alveolar collapse, and oxidative stress, in rats.^23-26 Chronic exposure to fine particles is strongly associated with higher rates of chronic respiratory disease.³

After direct exposure of mice to dung biomass smoke for 7 consecutive days, a significant increase in cellularity, especially in macrophage cellularity, was observed in the lungs.²⁷ Exposure to emissions from sugar cane burning produced inflammatory infiltrates of varying intensity in the animals of the present study, and, in EG7, there was a more significant inflammatory infiltrate in both tissues of the trachea and lung parenchyma, given that there were areas of more severe inflammation.

Damage to the lung parenchyma after chronic exposure to dung biomass smoke and cigarette smoke includes moderate to marked interstitial inflammation, bronchial and perivascular inflammation, vascular congestion, alveolar destruction, an increase in the number of macrophages, and an increase in vascular wall thickness.³ In the present study, although the exposure was acute only, it was possible to observe that the experimental groups showed a growing change in alveolar structure (septal loss) relative to the CG, with PM being phagocytosed especially in EG1. Areas suggestive of necrosis were identified especially in EG7 and EG21, and angiogenesis was confirmed in EG21.

Rabbits chronically exposed to emissions from biomass and cigarette burning show perivascular inflammation, peribronchiolar inflammation, parenchymal infiltrate, and fibrosis, with respiratory epithelial proliferation and emphysematous changes.²⁸ Using picrosirius red staining, we demonstrated that, in EG7 and EG21, there were areas of tracheal tissue collagen deposition, areas of peribronchiolar and vascular collagen deposition, and diffuse areas of lung parenchymal collagen deposition, which suggest that continued exposure can lead to a tissue fibrotic process.

On the basis of morphological criteria, we found that the changes in alveolar structure in EG7 and the rupture of interalveolar septa in EG21 were consistent with the findings of a rat study that showed that 24.6% of the cigarette smoke-exposed animals had increased alveolar spaces relative to controls, which were not exposed.²⁹

Therefore, the above data allow us to state that acute exposure to emissions from sugar cane burning is able to induce severe damage to the respiratory system. The components of emissions from sugar cane burning trigger polymorphonuclear cell inflammatory processes in the trachea and also induce inflammatory infiltrates and interstitial and alveolar edema in the lung parenchyma of Wistar rats. Changes in alveolar architecture and angiogenesis are also found.

Further research targeting prolonged exposure and determination of proinflammatory marker levels is needed to demonstrate the potential damage caused by chronic exposure to the components of emissions from sugar cane burning, since workers in sugar cane fields and the neighboring population are exposed to these emissions for long periods of their life.

¹Study carried out at the Faculdade de Tecnologia e Ciências da Bahia, Salvador (BA) Brasil.

REFERENCES