EFFECTS OF OUTDOOR VOLLEYBALL
EXERCISE ON CARDIORESPIRATORY
FUNCTION UNDER A HEAVY HAZE
ENVIRONMENT
Hong Wang*
College of Art, Qingdao University of Science & Technology, Qingdao, Shandong,
710061, China
h714628360@126.com
Reception: 31/03/2023 Acceptance: 02/06/2023 Publication: 24/06/2023
Suggested citation:
Wang, H. (2023). Effects of outdoor volleyball exercise on cardiorespiratory
function under a heavy haze environment. 3C TIC. Cuadernos de desarrollo
aplicados a las TIC, 12(2), 360-377.
https://doi.org/10.17993/3ctic.2023.122.360-377
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ABSTRACT
Haze has been one of the originators of the impact on human health. It is noteworthy
that all functions of the human body can decline or even fail in a heavy haze
environment. In this paper, the environmental monitoring website was used to count
the data of meteorological and other natural factors as well as socio-economic
influencing factors in the target cities over the past year. On this basis, the spatial and
temporal distribution patterns of heavy haze weather were analyzed and studied. For
the 100 volunteers who had been exposed to heavy haze pollution for a long time, the
physical activity time of volleyball was classified into four levels using the quadratic
method. Apart from that, a mixed linear model with fixed and random effects was
constructed to explore the effects on cardiorespiratory fitness after outdoor volleyball
exercise under a heavy haze environment. According to the model analysis results,
the outdoor volleyball exercise had a significant interaction effect on pulmonary
ventilation function in men only. Moreover, volleyball could be beneficial to the target
group when the physical activity had not yet reached the level of high-level volleyball
physical activity. This resulted in an improvement of 0.2L, 0.04L, 1.19%, and 0.03L in
their pulmonary ventilation function indexes, respectively. However, the negative
effects of a heavy haze environment were heavier after reaching a high-level degree.
In addition, the indicator kept decreasing, from 2.04L, 1.13L, 63.63%, 1.99L to 1.98L,
1.04L, 60.78%, and 1.83L, respectively.
KEYWORDS
Heavy haze; Outdoor environment; Volleyball; Human cardiorespiratory fitness;
Physical activity level.
INDEX
ABSTRACT
KEYWORDS
1. INTRODUCTION
2. CHARACTERISTICS OF SPATIAL AND TEMPORAL DISTRIBUTION OF HEAVY
HAZE IN THE STUDY AREA
3. RESEARCH ON THE EFFECT OF OUTDOOR VOLLEYBALL ON HUMAN
CARDIORESPIRATORY FITNESS
3.1. Selection of research objectives
3.2. Analytical model of the effect of outdoor volleyball exercise on
cardiorespiratory fitness
4. RESULTS AND ANALYSIS
5. DISCUSSION
6. CONCLUSION
REFERENCES
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1. INTRODUCTION
Haze is one of the weather phenomena of atmospheric pollution. If there is haze in
the air, the air at this time contains a large amount of particulate matter, such as dust,
soot, and dust. These substances make the air more turbid and the visibility level
decreases with it, usually below 10 km [1-3]. There is a clear difference between fog
and haze. Since haze particles are generally distributed in the air in a uniform form,
the visibility in the air is very uniform when haze weather occurs. There is a clear
difference between fog and haze, as haze particles are generally distributed in the air
in a uniform form, so when haze weather occurs, the visibility in the air is very uniform.
Haze contains many particles that are harmful to the human body, and some of them
can enter the interior of the human body directly through the respiratory tract and
cause serious damage to the human body [4-5]. Haze contains mainly sulfuric acid-
like substances and carbon particles. Since it contains more visible light and the
scattering wavelength of these visible lights is longer, the haze seen by the naked eye
is generally orange or yellow [6-8]. Most cities in China generally show an orange-
gray color when the air appears polluted, because black carbon is one of the main
atmospheric pollutants in China [9]. Unlike the effects caused by other severe
weather, when haze occurs it is characterized by a wide area and long duration. Many
harmful substances are contained in the air, especially absorbable particles that can
enter the human body through the respiratory tract and can cause incalculable
damage to humans [10-11].
With the rapid development of China's economy and technological reform, the size
of China's economy has been expanding over time. At the same time, air pollution in
China is increasing, especially in economically and industrially developed cities, and
the number of accidents and deteriorations caused by air pollution is increasing
[12-13]. In the original lexicon, "haze" was a natural phenomenon, which is a
substance that causes an obstacle to visual distance [14-16]. Nowadays, it has
evolved to be caused mainly by the pollution of the environment by human economic
activities, so the protection of the environment should receive more and more
attention [17].
With rapid economic development and rising national living standards, people have
begun to pursue a healthy lifestyle, and more and more people are joining the ranks of
exercise [18]. Due to the large population in China, indoor exercise places cannot
meet the needs of the public, and outdoor exercise has become an important way for
people to participate in exercise [19]. However, due to the aggravation of air pollution
in recent years, whether outdoor exercise should be adhered to under air pollution
conditions has led to extensive discussions [20-22]. The study of air pollution and
exercise was first started by developed Western countries, however, with the rapid
development of industrialization, air pollution in China has become increasingly
serious and the exercise population has gradually increased. Therefore, it is
necessary to investigate the relationship between air pollution and the physiological
health of the outdoor exercise population in China [23-25].
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The effects of air pollution on the physical and mental health of exercising
populations have received international attention. For example: the literature [26]
investigated temporal changes in particulate matter exposure along urban waterfront
trails. A recreational choice framework was used to examine the impact of visitor
perceptions of air quality and health benefits on track usage. The average air quality
during the collection period was "good" to "moderate". The results suggest that these
empirical factors may influence leisure choice depending on other factors, such as
significance. The literature [27] measured exertional spirometry and exertional
expiratory volume in 1 second outdoors before and after two trials of 3200 m running.
Subjective ratings of respiratory distress were quantified after exercise using a 10 cm
visual analog scale. Results validation: PM2.5 differed
18 µg/m3 between trials. 3200
m run time did not differ between trials despite feeling more respiratory discomfort
during the bad air trial compared to the good air trial. There was no significant
difference in post-exercise exertional spirometry between low and high PM2.5
conditions. Ten healthy males were selected in the literature [28] and completed two
90-minute constant load cycling trials under trap or filtered air conditions. Metabolic
profiles were evaluated using non-targeted analysis based on nuclear magnetic
resonance metabolomics. Results showed that metabolic pathways for glycine and
serine metabolism were altered during 30 minutes of exercise under TRAP conditions.
Arginine and proline metabolism at 60 minutes of exercise; glycolysis at 90 minutes of
exercise. The literature [29] was aimed at 80 non-smoking participants aged 16 to 21
years, using a bicycle ergometer for incremental testing, while measuring heart rate
and ventilation per minute. A linear mixed model was constructed using data obtained
from the cardiorespiratory exercise test. Ten individuals were randomly selected as an
external validation group to assess predictive performance using an eight-fold cross-
validation procedure. During the cardiorespiratory exercise test, air pollution
concentrations were monitored and inhalation loads were calculated. Results
validation: The median difference between ventilation measurements and predictions
was 0.3 L/min and the difference between inhalation load based on fit and
measurements was 0.0 to 0.3µg in all participants. In the literature [30], 30 healthy
young men were invited to perform two separate 15-minute submaximal exercise trials
on a cycle ergometer. The trials measured blood pressure, pulse oximetry, spirometry,
and exhaled nitric oxide fraction. The results validated that the decrease in 1-second
exertional expiratory volume/FVC following exercise at high air pollutant
concentrations during the exposure test was significantly and negatively correlated
with SO2, PM10, and PM2.5 concentrations. By collating and summarizing the current
literature, the effects of air pollution on exercise were mainly studied in two aspects:
the effects of air pollution on the physical and mental health of the outdoor exercise
population, and the effects of air pollution on outdoor exercise behavior. However,
most of the studies were conducted mainly on the hazards of air pollution on the
physiological health of the exercise population.
When outdoor exercise is performed under air pollution conditions, it can lead to
increased disease prevalence and reduced life expectancy once lung air pollutant
deposition increases to a certain level. For this reason, in this paper, 100 volunteers
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were selected from regions with a more severe spatial and temporal distribution of
haze, and the level of physical activity generated by outdoor volleyball exercise was
grouped according to their cardiorespiratory fitness and total daily metabolic
equivalent values using a quadratic approach. Based on a simple linear model, the
effects of outdoor volleyball exercise on the heart and lungs in a heavy haze
environment are discussed by combining continuous variables such as systolic blood
pressure and diastolic blood pressure with categorical variables such as volleyball
activity level. The purpose of the study was to increase awareness of
cardiorespiratory health and physical activity in volleyball and to increase the
importance of physical activity and the benefits of changing exercise patterns in a
heavy haze environment.
2. CHARACTERISTICS OF SPATIAL AND TEMPORAL
DISTRIBUTION OF HEAVY HAZE IN THE STUDY
AREA
On the environmental monitoring website, the data of natural and, socio-economic
influencing factors of the target city in the last year were counted to analyze and study
the spatial and temporal distribution pattern of heavy haze weather [31-33]. The
spatial distribution state of particulate matter concentrations in a year was analyzed
based on the PM2.5 and PM10 concentrations counted in the city throughout the year
[34-35]. Figure 1 is made based on the quarterly averages of PM2.5 and PM10
concentrations of polluting particulate matter at eight monitoring sites in the city
throughout the year related to heavy haze weather, using spatial interpolation with
GIS technology. This figure gives the spatial distribution of PM2.5 and PM10
concentration values of particulate matter in the target city for the last year,
respectively [36].
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Figure 1. Spatial interpolation distribution of pollutants in different seasons under heavy haze
environment
As can be seen from Figure 1, the concentration values of particulate matter in the
same quarter have an uneven regional distribution in terms of spatial distribution.
According to the current land use situation of the city, the concentration of polluting
particulate matter decreases gradually from the city center to the outskirts of the city in
a scattering pattern. The distribution of the same polluting particulate matter varies
from season to season, with generally lower overall concentration values in spring and
summer, and generally higher overall concentrations in autumn and winter. The
generally low concentration values of these spring and summer pollutants are mainly
influenced by meteorological conditions. Due to increased precipitation in spring and
summer, rain has a purifying effect on pollutants, while high temperatures and high
humidity in summer are also conducive to the diffusion of pollutants. And the overall
concentration of polluting particulate matter is generally higher in autumn and winter,
mainly due to the influence of pollution sources, and factors such as fireworks during
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the Spring Festival and dust storms in the north. Spatially, the overall pollution
particulate concentration values are gradually decreasing from the city center to the
outskirts of the city in a scattering pattern. The distribution trend of PM2.5 and PM10
concentration values of different pollutants varies with the quarter. However, their
distribution states are similar in the same quarter, while remaining similar to the
distribution states of haze. In summary, the pollutant particulate matter has uneven
distribution in space, the more economically developed the region, the higher the
pollutant concentration value, and vice versa, lower. Temporally, influenced by various
factors such as pollution sources and meteorological elements, there are significant
differences between different months and concentrations, showing cyclical changes,
and mainly concentrated in the autumn and winter seasons.
3. RESEARCH ON THE EFFECT OF OUTDOOR
VOLLEYBALL ON HUMAN CARDIORESPIRATORY
FITNESS
3.1. SELECTION OF RESEARCH OBJECTIVES
To improve the accuracy of the research results, 100 volunteers aged 18 years or
older who participated in the survey in the study area were selected as valid samples
to explore the effect of outdoor volleyball exercise on human cardiorespiratory fitness
in the region with long-term heavy haze pollution. Among them, the data of volunteers
with missing data during the survey were excluded. The mean age of all study
subjects was 28.94±0.55 years, including 64 males with a mean age of 32.11±0.38
years and 36 females with a mean age of 24.95±0.87 years. Physical activity level
subgroups were classified according to the quartiles of the total daily metabolic
equivalent values of the 100 study subjects included. The daily metabolic equivalents
of the study subjects were solved by the following equation.
(1)
Where is the metabolic equivalent of volleyball exercise, and
is the
average daily volleyball time. Figure 2(a) shows that body mass index, 1-second
expiratory volume with force, volume-to-lung capacity ratio, maximum expiratory flow,
and maximum oxygen uptake were greater in men than in women in the total study
population. Quiet heart rate was greater in females than in males. The group sizes of
males and females in different physical activity levels after volleyball exercise
outdoors are shown in Figure 2(b). Due to the large range of physical activity time
data in volleyball, the quartile method was used to classify the physical activity time in
volleyball into four different classes. Those with average daily physical activity time of
0 to 69.4 minutes were classified as low grade, those with average daily physical
activity time of 69.4 minutes to 110.5 minutes were classified as medium grade, those
with average daily physical activity time of 110.5 minutes to 153.1 minutes were
MET =(METn×Hn)
METn
Hn
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classified as high grade, and those with average daily physical activity time of 153.1
minutes or more were classified as very high grade [37].
Figure 2. Schematic diagram of the study population
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3.2. ANALYTICAL MODEL OF THE EFFECT OF OUTDOOR
VOLLEYBALL EXERCISE ON CARDIORESPIRATORY
FITNESS
In this study, a mixed linear model with fixed and random effects was used to
investigate the relationship between volleyball exercise activity level and
cardiorespiratory fitness in a heavy haze environment. The analysis involved
continuous variables such as age, body mass index, systolic blood pressure, diastolic
blood pressure, and volleyball exercise activity level, as well as categorical variables
such as gender, body mass index classification, particulate matter category, and
outdoor volleyball exercise activity level. The construction process of the mixed linear
model is as follows.
A simple linear model was established with systolic or diastolic blood pressure as
the independent variable and other variables as the dependent variables, as follows.
(2)
Where is the dependent variable; is the independent variable;
is the
estimated parameter matrix; and is the error matrix.
Record the statistically significant variables in the simple linear model.
Gradually add a random variable to ensure the significant variables in step 2. At the
same time, the performance of the model is evaluated using the bare pool
informativeness criterion and the Bayesian information criterion auxiliary indicator.
Step 3 is repeated until either the deficit pool informativeness criterion or the Bayesian
information criterion for the potential candidate model is found [38-39].
Based on the potential model in step 3, two or more random variables are gradually
added to determine the significant variables in step 2. At the same time, the bare pool
informativeness criterion and the Bayesian information criterion are applied to the
performance evaluation of the model. This step is repeated until a potential candidate
model is found for either the deficit pool informativeness criterion or the Bayesian
information criterion.
Adjust the random intercept in the random structure until the best model with the
minimum value of the Bayesian information criterion is found.
Compare the models from steps 2, 3, 4, and 5 with the analysis of variance
methods to obtain a significantly improved model. Based on the model structure, the
effects of random variables are represented graphically.
Mixed linear model analysis was performed with systolic and diastolic blood
pressure as dependent variables and age, height, weight, body mass index, metabolic
equivalent, PM2.5-0day, PM2.5-7day, PM2.5-15day, PM2.5-30day, and PM2.5-60day
as independent variables, respectively.
Y=XB +U
Y
B
U
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The Pearson model was used to filter and compare multiple variables, and the
dependent variable with the highest correlation with the cardiopulmonary dependent
variable was selected for modeling to derive the index with the greatest impact on
cardiopulmonary, resulting in the optimal model equation in systolic blood pressure.
(3)
The same modeling approach was used to select the higher correlation variables
for diastolic pressure modeling, and in the diastolic pressure model, the optimal model
was:
(4)
It was found that volleyball motor activity level classification and body mass index
classification were important random terms in both systolic and diastolic models, and
gender was an important random term in the diastolic model. Therefore, based on the
results of the systolic and diastolic blood pressure models, gender, volleyball sports
activity level, and their interactions were emphasized.
4. RESULTS AND ANALYSIS
Using the systolic optimal model and diastolic optimal model, the effects of
volleyball exercise on the cardiopulmonary function of the target subjects under a
heavy haze environment in the recent year were investigated. The model analysis
results of the daily average of each cardiorespiratory function index shown in Figure 3
were obtained.
h y p er v a lu e 1 + age +h eigh t +(1+wei gh t /m et cl a ss) + (1/BMI cl a ss)
h y p er v a lu e 1+p m v a l u e *wei gh t +age + (0 + age /m et cl a ss) + (1/ gen d er)
+(weigh t /BMI cl a ss)
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Figure 3. Effect of volleyball exercise on human cardiopulmonary function under heavy haze
environment
The results of the association test analysis between volleyball exercise and
cardiopulmonary function by gender (see Figure 3(a)). The significance test for quiet
heart rate was 0.68 with a covariance of 0.61. The significance test for quiet systolic
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blood pressure was 0.05 with a covariance of 0.88. The significance test for quiet
diastolic blood pressure was 0.29 with a covariance of 0.76. The significance test for
expiratory volume per second was 2.99 with a covariance of 0.02. The significance
test for expiratory volume per second was 5.01 with a covariance of 0.004. The
significance test value of expiratory volume to spirometry ratio was 3.4 with a
covariance of 0.03. The significance test value of maximum expiratory flow was 3.62
with a covariance of 0.03. The significance test value of maximum oxygen uptake was
0.83 with a covariance of 0.51.
Among them, the significance test values of quiet heart rate, quiet systolic blood
pressure, quiet diastolic blood pressure indexes, and maximum oxygen uptake related
to cardiac function were all less than 1, and the covariance values were all greater
than 0.5. The above data indicate that significant interaction effects were found on
four indexes of pulmonary ventilation function in men: expiratory lung volume with
force, expiratory volume with force in 1 second, expiratory volume to lung volume
ratio, and maximum expiratory flow. However, no interaction effect of volleyball
exercise in a heavy haze environment was found on cardiac function and maximal
oxygen uptake in males. For all cardiopulmonary function indicators in women, the
significance test value for quiet heart rate was 0.68. the covariance was 0.62. the
significance test value for quiet systolic blood pressure was 0.24 and the covariance
was 0.93. The significance test for quiet diastolic blood pressure was 0.69 with a
covariance of 0.6. The significance test for expiratory volume per second was 0.76
with a covariance of 0.6. The significance test for expiratory volume per second was
0.18 with a covariance of 0.87. The significance test for expiratory volume to
spirometry was 0.21 with a covariance of 0.92. The significance test for maximum
expiratory flow was 0.39 with a covariance of 0.84. The significance test for maximum
oxygen uptake was 0.7 and the covariance was 0.67. The significance tests for all
cardiopulmonary function indicators were less than 1 and the covariance was greater
than 0.5, indicating that there was no significant interaction effect of volleyball on
cardiac function, pulmonary ventilation, and maximum oxygen uptake in women in
heavy haze. This revealed that volleyball physical activity in a heavy haze
environment produces different health effects (predominantly on lung function) in
study subjects of different genders, but the mechanisms involved are currently
unclear. The main reason for this is that it is not clear whether the differences between
genders are due to differences in physiological mechanisms or due to different social
attributes. This may also contribute to the fact that no significant differences were
found in pulmonary ventilation function in girls in this study.
Figure 3(b) presents an analysis of cardiopulmonary function indicators (except
quiet heart rate, quiet systolic blood pressure, quiet diastolic blood pressure
indicators, and maximum oxygen uptake) in men within different volleyball physical
activity groups. The results showed that in the high-grade and very high-grade
volleyball physical activity groups, the mean values of 1-second expiratory volume,
expiratory volume to spirometry ratio, and maximum expiratory flow were lower than
those in the low-grade and medium-grade volleyball physical activity groups. For
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significant cardiorespiratory function in the low-grade volleyball physical activity
versus mid-grade volleyball physical activity groups, the longer the volleyball exercise
time, the greater the index values (i.e., 2.72 L > 2.52 L, 1.77 L > 1.73 L, 80.1% >
78.91%, 2.53 L > 2.5 L). For cardiorespiratory fitness that was significant in the high-
grade volleyball physical activity and very high-grade volleyball physical activity
groups, the longer the duration of volleyball exercise, the smaller the index values
(i.e., 1.98 L < 2.04 L, 1.04 L < 1.13 L, 60.78% < 63.63%, 1.83 L < 1.99 L). The reason
for the results of this study may be that the benefits of volleyball exercise on human
cardiorespiratory function outweigh the negative effects of heavy haze when the
physical activity has not yet reached the level of high-grade volleyball physical activity.
At this point, the higher the level of volleyball physical activity, the better the state of
cardiorespiratory function. Volleyball brought greater physical benefits to the target
group by lowering blood pressure and improving pulmonary ventilation and maximum
oxygen uptake in the study subjects. It also completely suppressed the negative
physical effects of fine and respirable particulate matter in a heavy haze environment.
causing the target subject's expiratory lung volume with force, expiratory volume with
force in 1 second, expiratory volume to lung volume ratio, and maximum expiratory
flow rate to increase from 2.52 L, 1.73 L, 78.91%, and 2.5 L to 2.72 L, 1.77 L, 80.1%,
and 2.53 L, respectively. but when physical activity reaches high levels of volleyball
physical activity and above, not only is the respiratory rate typically faster, but also the
probability is that breathing will be done through the mouth. This bypasses the
filtration effect of the nasal cavity, leading to more pollutant inhalation, irritating the
respiratory system, triggering inflammation, or obstructing the airway. At this point, the
positive effects of volleyball on human cardiorespiratory function, such as lowering
blood pressure, are far less than the risk of greater exposure of the human body to
large amounts of particulate matter that accumulate at low altitudes and do not diffuse
easily during breathing at faster respiratory rates. This results in the body's
cardiorespiratory function being far more susceptible to the pollution conditions of a
heavy haze environment than at low levels of volleyball physical activity versus
medium levels of volleyball physical activity. This resulted in a significant decrease in
the target subjects' forceful expiratory lung capacity, 1-second forceful expiratory
volume, expiratory volume to lung capacity ratio, and maximum expiratory flow rate
due to obstructive ventilation dysfunction, obstructive emphysema, respiratory
ventilation dysfunction, restrictive ventilation dysfunction, or mixed ventilation
dysfunction caused by heavy haze, from 2.04 L, 1.13 L, 63.63%, and 1.99 L,
respectively decreased to 1.98 L, 1.04 L, 60.78%, and 1.83 L. In conclusion,
excessive physical activity of volleyball in a heavy haze environment can aggravate
the inhalation of respirable particulate matter, resulting in the negative effects of a
heavy haze environment for the body, overriding the benefits of volleyball for the body.
5. DISCUSSION
For volleyball to achieve its essential role, the hazy environment needs to be
effectively improved, but the improvement process takes time to achieve. During this
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time, volleyball players need to take protective measures to avoid damage to their
cardiopulmonary function. The following measures are proposed for the improvement
of the haze environment and the protection of volleyball:
1.
Volleyball courts are mostly located in the square and other open areas close
to the road so sportsmen are directly affected by the hazards of automobile
exhaust. There are hundreds of undesirable substances in automobile exhaust.
In addition, car exhaust also contains many types of polycyclic aromatic trails,
which contain carcinogenic substances. Therefore, it is important to avoid
inhaling automobile exhaust fumes as much as possible. The government
should take appropriate means to reduce exhaust emissions by formulating
reasonable policies to limit the number of vehicles.
2. Wear a professional mask and try to exercise indoors. In hazy weather, masks
must be worn outside, and professional medical masks should be chosen. It is
recommended to use anti-viral masks, in which the filter layer can filter out
some of the bacteria in the haze. More indoor places such as gymnasiums or
sports activity centers for volleyball can effectively reduce the amount of haze
inhaled.
3.
Minimize the consumption of stimulating foods. Since the air pressure is
relatively low in hazy weather, groups with poor cardiorespiratory fitness should
try not to engage in volleyball or other relatively strenuous exercise. You can
eat more items such as pears and lilies. Garlic and shallots both have
antiseptic effects, and more of the above-mentioned foods can be eaten in
hazy weather to increase immunity.
6. CONCLUSION
Current air pollution levels are becoming increasingly severe, and heavy haze
weather environments are strongly associated with increased morbidity and mortality
from cardiopulmonary disease. People are increasingly concerned about physical
health issues, and more and more people are involved in outdoor physical exercise
and sports. Therefore, in this paper, the study population was selected based on the
spatial and temporal distribution characteristics of heavy haze in the study area.
Based on the quartiles of the daily total metabolic equivalent values of volunteers, the
physical activity level groupings for outdoor volleyball were classified. A mixed linear
model in which the independent variable was systolic or diastolic blood pressure was
used to explore the relationship between the effects of outdoor volleyball exercise on
cardiorespiratory fitness in a heavy haze environment, and three concluding points
were obtained.
1.
Volleyball physical activity in a heavy haze environment produces different
health effects on study subjects of different genders. The significance test
values for male forceful expiratory spirometry, 1-second forceful expiratory
volume, expiratory volume to spirometry ratio, and maximum expiratory flow
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were all greater than 1, and the covariance values were all less than 0.5.
Therefore, there was an interaction effect of volleyball exercise on pulmonary
ventilation function in males. The significance test values of all
cardiopulmonary function indexes in women were less than 1, and the
covariance values were all greater than 0.5, so the interaction effect of
volleyball exercise on women was not significant.
2.
When physical activity has not yet reached the level of high-grade volleyball
physical activity, the benefits of volleyball to human cardiorespiratory function
outweigh the negative effects of heavy haze. Exercise improved pulmonary
ventilation function and maximum oxygen uptake by lowering the blood
pressure of the study subjects, resulting in an increase in their pulmonary
ventilation function index from 2.52 L, 1.73 L, 78.91%, and 2.5 L to 2.72 L, 1.77
L, 80.1%, and 2.53L, respectively.
3.
When physical activity reaches the level of advanced and very high volleyball
physical activity, the filtering effect of the nasal cavity is bypassed due to the
accelerated breathing rate. This resulted in a decrease in the lung ventilation
function index of the target subjects from 2.04 L, 1.13 L, 63.63%, and 1.99 L to
1.98 L, 1.04 L, 60.78%, and 1.83 L, respectively.
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