ANALYSIS OF THE IMPACT OF LAKE
ENVIRONMENTAL WATER POLLUTION ON
THE HEALTH OF OUTDOOR SWIMMERS
BASED ON STIRPAT ENVIRONMENTAL
IMPACT ASSESSMENT MODEL
Xiaogang Gong*
Information and Communication Branch of State Grid Zhejiang Electric Power Co.,
Hangzhou, Zhejiang, 310000, China
gongxiaogang@foxmail.com
Xinyu Wu
Information and Communication Branch of State Grid Zhejiang Electric Power Co.,
Hangzhou, Zhejiang, 310000, China
Xuxiang Zhou
Information and Communication Branch of State Grid Zhejiang Electric Power Co.,
Hangzhou, Zhejiang, 310000, China
Reception: 14/11/2022 Acceptance: 16/01/2023 Publication: 02/03/2023
Suggested citation:
G., Xiaogang, W., Xinyu and Z. Xuxiang. (2023). Analysis of the impact of lake
environmental water pollution on the health of outdoor swimmers based
on STIRPAT environmental impact assessment model. 3C TIC. Cuadernos
de desarrollo aplicados a las TIC, 12(1), 132-150. https://doi.org/
10.17993/3ctic.2023.121.132-150
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
132
ABSTRACT
With the continuous development of China's economy, outdoor swimming has
become an indispensable sport for Chinese people thereupon. However, the pollution
of the outdoor water environment is capable of directly affecting the physical health of
outdoor swimming lovers. Given the above, this paper uses the Stochastic Impacts by
Regression on Population, Affluence, and Technology (STIRPAT) model to analyze
the environmental water pollution of lakes and study the influencing factors and
degree of physical health of outdoor swimming crowds. Moreover, this paper also
identifies the causes of water pollution in two respects, namely water pollution and
human pollution and analyzes from the perspectives of water quality monitoring
environment survey and questionnaire survey. The results show that the primary
factors affecting water quality contain weather, swimming crowd density and
environmental pollution around water areas, lake waters have direct and indirect
effects on human health, and the incidence of eye inflammation, itchy skin, stuffy
nose, sore throat, stomachache, nausea, earache, diarrhea, fever and vomiting are
36.4%, 30.3%, 29.5%, 26.5%, 21.2%, 20.1%, 20.1%, 17.0%, 14.8% and 12.9%
respectively.
KEYWORDS
Water environment pollution; Outdoor swimming; Sports crowd; Influence study;
Water quality monitoring.
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
133
PAPER INDEX
ABSTRACT
KEYWORDS
1. INTRODUCTION
2. MATHEMATICAL MODELS AND DATA SOURCES
2.1. STIRPAT model
2.2. Data sources
3. CHARACTERISTICS AND CAUSES OF WATER POLLUTION
3.1. Characteristics of water environment pollution
3.2. Analysis of causes of water environment pollution
3.2.1. Water pollution
3.2.2. Human pollution
4. RESULTS AND ANALYSIS
4.1. Water quality monitoring and environmental survey results
4.1.1. Water quality monitoring methods
4.1.2. Environmental survey results
4.2. Questionnaire survey and results
4.2.1. Questionnaire survey method
4.2.2. Influence on the Health of the swimming population
4.2.3. Logistic regression analysis of risk factors affecting the health status of
the swimming population
5. DISCUSSION
6. CONCLUSION
7. DATA AVAILABILITY STATEMENT
8. CONFLICT OF INTEREST
REFERENCES
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
134
1. INTRODUCTION
With the continuous progress of science and technology, the ability of human
beings to intervene in nature is getting stronger and stronger. The natural environment
on which human beings depend for survival and development is also under enormous
pressure [1]. Various activities of human society discharge pollutants into the
environment, which not only seriously threaten human health, cause property loss, but
also damage the environmental resources themselves [2-3].
In recent years, the number of environmental pollution damages caused by water
pollution has risen sharply [4-5]. Such as the cadmium pollution incident in Beijing,
Guangdong in December 2005, the arsenic pollution incident in Yueyang, Hunan in
September 2006, the arsenic pollution incident in Yangzonghai in September 2008,
the Yancheng pollution incident in Jiangsu in February 2009, and the arsenic pollution
incident in July 2010. Zijin Mining Pollution Incident and Dalian Oil Spill Incident [6-7].
According to reports from the State Environmental Protection Administration
system, yearbooks, journals, literature and online media, between 2005 and 2010, 95
major environmental pollution accidents were committed. Water pollution incidents
caused by pollutant discharge have become an important type of accident that causes
damage to the water environment [8-9].
In recent years, a large number of scholars at home and abroad have carried out
related research on water environment pollution. Literature [10] has some innovations
in the overall theory of water environmental pollution. They break the traditional way of
thinking about water governance and use the theory of sustainable development to
explore new water pollution management models. They believe that achieving
effective protection and sustainable development is the focus of water pollution control
and improvement. They pointed out that to achieve water pollution control, we must
carry out the overall system and institutional innovation. Literature [11] and [12] put
forward the following viewpoints from the perspective of comprehensive management:
they believe that the management of water environment pollution is an important part
of human production activities. Comprehensive treatment is the most powerful
weapon for water pollution control. Literature [13] introduced the market governance
method into the process of water environment governance, emphasizing the
coordinated governance of various departments. Emission trading theory is a
theoretical development in the process of water environment pollution control. In
terms of governance methods, the literature [14] and [15] creatively put forward a new
concept. He believed that the previous water environment pollution control was an all-
powerful government-style governance. In the process of water pollution control, the
role of market participation has been emphasized. The main role of the people is
emphasized here, and it is hoped that the public can actively participate in water
pollution control. Literature [16] focuses more on the idea that the government guides
the whole society to govern, and believes that the degree of cooperation and
coordination between all parties in the society is an important factor affecting the
realization of high efficiency. References [17] and [18] believe that a government,
market, enterprises, farmers and social organizations can be constructed to
participate in the network governance mechanism of water pollution. Reference [19]
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
135
introduces an environmental penalty function based on the evolutionary game model
analysis. Using this model, the distribution of water pollution loads in the Zarjub River
in northern Iran was analyzed. Reference [20] analyzes the influencing factors of rural
water pollution from the legal level. They argue that there is a Chinese rural water
pollution legislation dependent on the cities. References [21] and [22] compared the
investment in urban and rural environmental pollution control in 2013, and found that
the focus of water environmental pollution control is in cities, while the rural water
environment pollution control lacks investment. The study also shows that the uneven
distribution of urban and rural areas leads to significant differences in the effects of
urban and rural water pollution control. Literature [23], from the perspective of urban
development, believes that the acceleration of urbanization has changed the quality
and spatial distribution of water resources. Reference [24] took Hanji Township, Hubei
Province as a case study object, and tested the water quality of Hanji Township. The
main causes of water pollution are agricultural pollution, industrial pollution, domestic
sewage, and waste pollution. Finally, the management countermeasures and
suggestions are put forward. Reference [25] focuses on the current situation of rural
drainage facilities and proposes that the lack of rural drainage facilities leads to
improper sewage treatment, resulting in serious damage to the rural water
environment. Reference [26] starts from the institutional mechanism of rural water
environmental protection and proposes that the current rural water environmental
protection mechanism has gradually become rigid. Reference [27] starts with the
current situation of rural residents' understanding of water law and finds that rural
residents lack access to knowledge of water law. It can be seen that scholars from all
over the world regard water environment pollution as a major problem that affects the
sustainable development of society and economy and affects people's life and health.
Therefore, while promoting social and economic development, we must also do a
good job in the protection of the water environment. This has become an important
theme of economic development and reform in the new era [28-30].
With the rapid development of China's economy, people pay more and more
attention to the spiritual world. Outdoor sports have become indispensable sport for
the Chinese people. Outdoor swimming is especially sought after by outdoor sports
enthusiasts. Therefore, whether the water environment is polluted or not will directly
affect the health of outdoor swimming enthusiasts. This paper takes the water
environment of a suburban lake in a city in China as an example to study the impact
of typical water environment pollution on outdoor tourism and sports people. The
purpose is to analyze the pollution of the lake water environment in the suburbs of a
city and to study the impact on the outdoor swimming population after the water
environment is polluted.
2. MATHEMATICAL MODELS AND DATA SOURCES
In studying the influencing factors of water environmental pollution, some
researchers use different models to demonstrate. Different scholars have analyzed
the influencing factors and their degree of influence. In recent years, the research on
the STIRPAT model has become more and more extensive, and it is mainly applied to
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
136
environmental problems caused by carbon emissions and energy consumption. In the
research on water environment pollution, some scholars have used the STIRPAT
model to analyze the influence factors and degree of influence of water environment
pollution on the health of the outdoor swimming population.
2.1. STIRPAT MODEL
The STIRPAT model refers to an extensible and random environmental impact
assessment model. This paper will use this model in the subsequent empirical
analysis to empirically analyze the environmental pollution of lakes in the suburbs of a
city, the factors that affect the health of outdoor swimming people and their degree of
influence. The STIRPAT model is an extension of the IPAT model. The initial form of
the model can be expressed as:
(1)
In the above formula, is the environmental pressure,
is the number of
swimmers, is the wealth of a city, and is the technological progress.
The model believes that the environmental pressure is determined by the scale of
the number of swimmers , the affluence of a city , and technological progress .
Due to the limitations of this model in the application, many scholars have modified
the nonlinear regression model STIRPAT model obtained by the IPAT model. The
standard form of the model can be expressed as:
(2)
The above formula, and
respectively represent the same meaning as
formula (1), and
the model influence coefficient and the index of each
variable respectively,
is the random error term. In practical applications, to reduce
the influence of heteroscedasticity, logarithm processing is performed on both sides of
the formula (2). To facilitate the expression of each coefficient, it is expressed by .
After processing, a linear model is obtained. The linear model can be expressed as:
(3)
The above linear model was used to realize the analysis of factors affecting the
health of the outdoor swimming population by water environment pollution.
2.2. DATA SOURCES
Water pollution is mainly caused by population growth, rapid social and economic
development, and accelerated urbanization [31]. To comprehensively study the
influencing factors and degree of influence of China's water environment pollution, this
paper adds industrial structure, water consumption structure, urbanization and other
indicators based on formula (3), so formula (3) is further extended to formula (4), that
is, the extended linear regression equation of the STIRPAT model can be expressed
as:
(4)
I=P×A×T
I
P
A
T
I
A
T
I=aPbAcTde
I,P,A
T
a,b,c
d
e
β
ln I =β0+β1ln P +β2ln A +β3ln T +e
ln I =β0+β1ln P +β2ln A +β3ln T +β4l n ur +β5l n st +β6ln cs
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
137
Formula (4),
is the water environment quality. In this paper, the total amount of
wastewater discharge, COD value and ammonia nitrogen discharge is used as water
pollution indicators; is the population size;
is the wealth level, expressed by per
capita GDP;
is the technical level, expressed by the intensity of wastewater
discharge;
is the urbanization rate, expressed by the proportion of the urban
population to the total population;
is the water consumption structure, expressed by
the proportion of domestic water consumption to total water;
is the industrial
structure, expressed by the industrial output value Expressed as a percentage of
G D P.
When China studies water pollution, the main statistical indicators include total
wastewater discharge, COD discharge and ammonia nitrogen discharge [32].
According to the research on water environment pollution by Chinese scholars, this
paper uses the total amount of wastewater discharge, COD discharge, and ammonia
nitrogen discharge as indicators to measure China's water environment pollution, and
conducts model test analysis with various water environment pollution factors. The
degree of influence of environmental pollution factors on water pollution [33]. The
water environment pollution evaluation index system is shown in Table 1.
Table 1. Evaluation index system of water environment pollution
The data comes from the 2009-2018 "China Statistical Yearbook", "China
Environmental Statistical Yearbook" and the statistical yearbooks of various provinces,
municipalities and autonomous regions.
I
P
A
T
ur
st
cs
Criterion layer Indicator layer Interpretation of indicators
Outdoor swimmers on
the rise
Number of people swimming
outdoors (P) Minimum number of swimmers
Socioeconomic
development
Urban affluence (A) GDP per capita
Techinque level (T) Wastewater discharge intensity
Urbanization rate (ur) The proportion of the number of swimmers to
the total number of people
Industrial structure (cs) Industrial output as a share of GDP
Swimmers swimming
habits Swimming habits (st) The proportion of domestic water
consumption in total water
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
138
3. CHARACTERISTICS AND CAUSES OF WATER
POLLUTION
3.1. CHARACTERISTICS OF WATER ENVIRONMENT
POLLUTION
The water pollutants in the lake area in the suburbs of a city are mainly phosphorus
and nitrogen indicators. Judging from the monitoring results of the four factors of total
phosphorus, total nitrogen, transparency and PH value, which are the evaluation
indicators of the nutritional status of the lake, the lake water in the suburban lake area
of a certain city is still in a state of eutrophication, with the appearance of periodic
intensive growth of aquatic plants and peculiar smell in the water body, resulting in the
deterioration of the lake water environment quality in the suburban lake area of a city
and affecting the landscape of the lake area [34]. In terms of time distribution, the
pollution degree in the suburban lake area of a certain city has strong regularity, and it
mostly occurs between May and July every year, in terms of spatial distribution,
artificial lakeshore areas are the main areas.
3.2. ANALYSIS OF CAUSES OF WATER ENVIRONMENT
POLLUTION
3.2.1. WATER POLLUTION
Water eutrophication is a phenomenon of water pollution caused by excessive
nitrogen, phosphorus and other nutrients in the water body. Crazy growth destroys the
flow of material and energy in the system and gradually deteriorates the water
ecosystem.
In the water body of a suburban lake area of a city, the external input of nutrient
salts and the release of nutrients in the bottom of the lake area are important factors
that cause the water quality in the lake area on the outskirts of a city to show a rich
state, and at the same time, the eutrophication of natural water bodies is related to the
changes in physical factors such as light, temperature, and dissolved oxygen [35].
The water in a lake area in the suburbs of a city is eutrophic, which mostly occurs
from May to July every year (usually during stratification in summer). At this time,
there is sufficient sunshine and the highest ambient temperature during the day is
generally maintained in the range of 25-33
, basically meeting the external
climatic conditions of water eutrophication.
Nutrients such as phosphorus, nitrogen, etc. in the lake water body mainly come
from the following aspects:
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
139
(1) The phosphorus released by the dead aquatic organisms and the decaying
rhizomes of aquatic plants in the lake, and its humus is deposited on the bottom of the
water, resulting in the enrichment of nutrients, and released under specific
environmental conditions, resulting in the water quality of the lake area is rich in
nutrients, this phenomenon is especially directly affected by phosphorus. In the water
body of a lake area on the outskirts of a city, the change in phosphorus content will
directly dominate the production of a certain type or several types of aquatic plants,
and when phosphorus is the limiting factor, the increase of phosphorus will create
favorable conditions for the large reproduction of aquatic organisms such as aquatic
plants, directly affecting the degree of eutrophication of water quality [36].
(2) The mass reproduction and death of aquatic organisms such as aquatic plants
will consume a large amount of oxygen in the water body, resulting in further
deterioration of water quality. The decrease of dissolved oxygen in various water
layers in the lake area was significantly related to the increase in total phosphorus
content. Nutrients at all levels in the lake will release nitrogen and phosphorus when
they secrete, excrete, and transform and release organic matter, which is also the
source of nutrients. During the transformation and release of organic matter, at the
same time as bacteria decompose them, it is returned to water bodies and sediments
to be released under specific environmental conditions. The faster the aquatic plants
reproduce and the more vigorous the activity, the more they will promote the release
of nitrogen and phosphorus in the substrate.
(3) The supply of lakes and lakes in the suburbs of a city mainly comes from the
surface water in the suburbs of a city, and the water also contains excess nitrogen,
which mainly comes from the excessive application of fertilizers, agricultural wastes
and domestic pollutants in agricultural production. Surface water mainly exists in the
form of phosphate [37].
(4) Some tourists have uncivilized travel habits. Tourists throw bait and garbage
into the lake area at will and artificially add phosphorus and nitrogen to the lake area.
3.2.2. HUMAN POLLUTION
Pollution is caused by the swimmer's secretions, excrement, etc. to the water body
when swimming. In addition, it also includes that after people with certain infectious
diseases or bacteria (viruses) enter the swimming pool, pathogenic factors are
brought into the swimming pool, mainly from the digestive tract and body surface of
the swimmer. Such as saliva, sweat, urine, tears and other secretions and excretions.
The specific sources are the following:
(1) Urinary leakage occurs when the bladder contracts involuntarily due to cold
contraction, and the amount of urine leakage for adults is generally 50ml. According to
the survey, those who urinate during swimming account for about 3.5~5.0% of the
swimmers, that is, one person urinates for every 20 swimmers. The more swimmers in
the pool, the higher the urination rate, so urine is one of the main sources of
swimming pool water pollution [38-39].
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
140
(2) Swimmers spit the water from the entrance into the pool together with saliva
from time to time when swimming. The saliva may contain pathogenic bacteria or
viruses, thus causing the pollution of the swimming pool water quality.
(3) Sweat is also a source of pool water pollution. According to Japan's Liuye
report, the average person sweats 100ml/h when swimming in summer, and the
amount of sweat increase with the increase of exercise. Although the amount of tear
and other secretions is small, because there are often a variety of pathogenic factors
such as germs and viruses in these secretions, it is also an important factor in
polluting the water environment.
(4) In addition, the CO2
in the exhaled breath of the swimmer, together with the
secretions and excrement of the human body, can change the PH value of the water
quality in the water environment, thus affecting the sanitation of the water quality.
4. RESULTS AND ANALYSIS
To analyze the impact of water environmental pollution on the outdoor swimming
population, this paper conducted a water quality test on the lake waters in the suburbs
of a city and investigated the waters and the surrounding environment. At the same
time, the outdoor swimming population was divided into a swimming group and a non-
swimming group, and a questionnaire survey and statistical analysis were carried out
for these two groups.
4.1. WATER QUALITY MONITORING AND ENVIRONMENTAL
SURVEY RESULTS
4.1.1. WATER QUALITY MONITORING METHODS
According to the "Technical Regulations for Lake Water Environment
Monitoring" (2002), 3 monitoring points are set up in the suburban lake waters, among
which monitoring point 1 is a peripheral point susceptible to pollution, monitoring point
2 is a crowded area, and monitoring point 3 is a less polluted area. In deep water
points, 2 parallel samples were collected from each monitoring point. From 3 to 5 pm
from May 28 to June 3, 2021, by GB 17378.4-1998 "Lake Monitoring Specification
Part 4: Lake Water Analysis", sampling and microbial and physical index analysis was
carried out, using C200 type automatic water quality analysis Instrument for general
chemical index analysis. Detection indicators include fecal coliforms, color,
transparency, PH, dissolved oxygen, salinity, floating matter and chemical oxygen
consumption (COD).
4.1.2. ENVIRONMENTAL SURVEY RESULTS
There is basically no industrial and agricultural sewage discharge near the lakes in
the suburbs of a city, and there is scattered non-point source pollution, which is mainly
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
141
caused by the domestic garbage brought by restaurants and tourists washed by
rainwater. Therefore, changes in weather conditions and the number of tourists are
the main reasons for the changes in pollutant discharge. The maximum number of
people during the investigation period is 500-800 person-times, and the minimum is
100-200 person-times. 42 lake water samples were collected, and the lake water
chromaticity was normal. The chromaticity of monitoring points 1, 2, and 3 were
(15.00±3.90), (14.28±1.20), and (11.42±1.45) NTU, from near-land point to deep
water. The point gradually becomes smaller; the PH value is 8.01~8.10; the salinity is
31‰~33‰; the transparency is >30cm, the water temperature is normal, and there is
no thermal pollution source around. Table 2 shows the water quality test results of
each monitoring point in the suburban lakes of a city.
Table 2. The water quality test results of each monitoring point in the suburban lakes of a city
Table 2 shows that in terms of dissolved oxygen and oxygen-consuming substance
content, the dissolved oxygen content of monitoring points 1 and 3 are (6.51 ± 2.16)
and (6.71 ± 1.90) mg/L, respectively, reaching the lake water quality class I standard.
Monitoring point 2, the dissolved oxygen content is (5.60±2.01) mg/L, which meets the
water quality standard. The chemical oxygen consumption (COD) of monitoring
points 1, 2, and 3 were (2.70±0.14), (3.40±0.14) and (3.05±0.09) mg/L in turn,
reaching the lake water quality class II standard.
In terms of nitrogen content, inorganic nitrogen can indicate the status of lake water
being polluted by domestic wastewater, etc., and ammonia nitrogen exceeding the
standard indicates the existence of new pollution. The inorganic nitrogen of 2 samples
exceeded the standard of class II lake water, and the exceeding rate was 4.7%,
indicating that the seawater was recently polluted. The nitrate nitrogen content of
monitoring points 1, 2 and 3 is 0.16 mg/L~0.17 mg/L, and the inorganic nitrogen
content is 0.05 mg/L~0.45 mg/L.
In terms of biological indicators, there is no suspended matter in the lake water in
the suburbs of a certain city, and there is white suspended matter in the lake water at
certain times, mainly jellyfish, which are unique to the region in May and June. Fecal
coliforms <156/L, reaching the class I standard of lake water quality.
The results of this survey show that the inorganic nitrogen in the lake water reaches
the standard of lake water category II and meets the requirement of swimming water.
Dissolved oxygen, fecal coliform and PH value can reach the standard of lake water
category . The results of the environmental survey of the lake water show that there
Monitoring
points PH value Chroma
(NTU)
Dissolved
oxygen
(mg/L)
Nitrate
nitrogen
(mg/L)
COD (mg/L)
Inorganic
nitrogen
(mg/L)
Fecal
coliforms
(pcs/L)
Monitoring
points1 8.10±0.08 15.00±3.90 6.51±2.16 0.16±0.02 2.70±0.14 0.21±0.02 36.0±7.60
Monitoring
points2 8.09±0.07 14.28±1.20 5.60±2.01 0.17±0.03 3.40±0.14 0.19±0.02 36.0±6.07
Monitoring
points3 8.01±0.10 11.42±1.45 6.71±1.90 0.16±0.03 3.05±0.09 0.21±0.03 35.0±6.69
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
142
is surface source pollution such as the catering industry in the lake area, and the
dissolved oxygen content in the water is (1.63±0.63) mg/L. The density of swimmers
at monitoring point 2 is the largest, and the dissolved oxygen content in its water is the
lowest, at (5.60±2.01) mg/L. Therefore, the weather, the density of swimmers and the
environment around the lake water are the main factors affecting water quality.
4.2. QUESTIONNAIRE SURVEY AND RESULTS
4.2.1. QUESTIONNAIRE SURVEY METHOD
The field population in a suburban lake was taken as the survey object, and the
questionnaire was formulated and revised according to the actual situation. The
questionnaire contains a total of 42 individual choices, which are divided into two
parts: the on-site questionnaire survey and the follow-up questionnaire after 7 days.
The contents of the investigation included whether there were any changes in the
respiratory tract, digestive tract, eyes, ears, nose, chest tightness, tinea pedis, skin
infection symptoms and changes in mental state, which were completed within 2
consecutive days. The follow-up questionnaire was conducted by telephone, E-mail,
QQ group, WeChat group, etc., and was conducted 7 days after the on-site
investigation.
The investigators of this questionnaire survey are all trained and qualified medical
students. Before the survey, 60 members of the swimming association and 50
students of the school were organized to conduct a preliminary survey, and the
questions in the survey questionnaire were improved. Unify the standards during the
investigation, and eliminate abnormal data during data entry. Monitoring data are
represented by
. Through the above STIRPAT environmental impact
assessment model, the health influencing factors and influence degree of the outdoor
swimming population were assessed. SPSS 10.0 statistical software was used for
data entry, and test and Logistic regression analysis was performed. The difference
was statistically significant .
4.2.2. INFLUENCE ON THE HEALTH OF THE SWIMMING
POPULATION
A total of 500 questionnaires were distributed in this survey, 491 were recovered,
408 were valid questionnaires, and the response rate was over 90%. In this paper, the
population was divided into swimming and non-swimming groups, and on-site
questionnaires were administered to the swimming and non-swimming groups,
respectively. Follow-up questionnaires were conducted again after 7d. The results of
the survey were summarized for both groups and finally, the number of people in both
groups who developed symptoms and the incidence were analyzed. A comparison of
the incidence of different symptoms in the swimming and non-swimming groups is
shown in Figure 1.
¯x±s
x2
P< 0.05
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
143
Figure 1. Comparison of the incidence of different symptoms between the swimming group
and the non-swimming group.
As can be seen from Figure 1, 264 people in the swimming group suffered from
itchy skin, fever, nasal congestion, runny nose, nausea, vomiting, stomach pain, sore
throat, earache, diarrhea and eye inflammation, while the number of people in the
non-swimming group found such symptoms for 144 people. In addition, the number
and incidence of any symptom in the swimming group were higher than those in the
non-swimming group. The most obvious one was: in terms of skin itching symptoms,
the number and incidence of the swimming group were 57% higher than those in the
non-swimming group. people, 14.3%. In terms of nasal congestion and runny nose,
the number and incidence of the swimming group were 51 and 10.7% higher than
those of the non-swimming group. In terms of symptoms of nausea, the number and
incidence of the swimming group were 43 and 13.2% higher than those of the non-
swimming group. In terms of inflammation, the number and incidence of the swimming
group were 57 and 14.3% higher than those of the non-swimming group, respectively.
According to the above data, the number and incidence of skin itching, fever, nasal
congestion, runny nose, nausea, vomiting, stomach pain, sore throat, earache,
diarrhea and eye inflammation in the swimming group were higher than those in the
non-swimming group. The incidences of itching, nasal congestion and runny nose,
nausea, vomiting, stomach pain, sore throat, eye inflammation and diarrhea were
significantly different ( or ), while there was no statistical difference
P< 0.05
P< 0.01
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
144
in the incidence of fever and earache between the two groups. academic significance
().
4.2.3. LOGISTIC REGRESSION ANALYSIS OF RISK FACTORS
AFFECTING THE HEALTH STATUS OF THE SWIMMING
POPULATION
Taking the symptoms of the population (whether there is the respiratory tract,
digestive tract, eyes, ears, nose, chest tightness, tinea pedis, skin infection symptoms
and mental state, etc.), wearing earplugs, swimming goggles, etc.) were used as
independent variables, and a two-class logistic regression analysis was performed.
The logistic regression multivariate analysis of the risk factors for the health status of
the swimming population is shown in Table 3.
Table 3. Logistic regression multivariate analysis of risk factors for the health status of the
swimming population
Table 3 shows that the main risk factors for skin itching symptoms in the population
include swimming (OR value 3.925, 95%CI: 1.830-8.417) and swallowing lake water
(OR value: 4.023, 95%CI: 1.752-9.236). Statistical significance (
), which
indicates that swimming and swallowing lake water sentences can increase the risk of
skin itching in the population; the risk factors for eye inflammation in the population
include swimming (OR value: 2.535, 95%CI: 1.362~4.718) and swimming Without
diving glasses (OR value: 2.433, 95% CI: 1.271-4.661), the difference was statistically
significant ( ), indicating that swimming and swimming without diving glasses
can increase the risk of eye inflammation in the population.
5. DISCUSSION
The disposal of water environmental pollution incidents, especially the restoration
and assessment of water environmental damage, is a blank field in China, and there
is a lack of systematic research on the relevant assessment method systems. This
paper takes the water environment of a lake in the suburbs of a city as an example to
study the impact of the polluted water environment of the lake on the health of outdoor
P< 0.05
Symptom Influencing
factors βvalue SE Wald
value P value OR value 95%CI
Itchy skin
Swim 1.367 389 12.337 0 3.925 1.830-8.417
Swallow lake
water 1.392 424 10.771 1 4.023 1.752-9.236
Eye
inflammation
Swim 0.93 317 8.618 3 2.535 1.362-4.718
Not wearing
diving glasses 889 332 7.193 7 2.433 1.271-4.661
P< 0.01
P< 0.01
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
145
sports swimmers. However, it does not involve the process of China's disposal of
water pollution incidents, as well as the related content of the concept and
assessment method of environmental damage assessment. Therefore, in the future
research direction, it is mainly China's research on the disposal process of water
environmental pollution incidents, the concept and assessment method of
environmental damage assessment, which has important theoretical significance and
technical support for the establishment of environmental damage restoration and
assessment method system, the development of environmental damage assessment
method practice, and the construction of environmental economic policy system. The
protection of the water environment not only protects human survival, social progress
and economic development, but also sustains the need for a good ecological
environment. Lake bathing is best to wear waterproof goggles as well as ear plugs,
etc., use water to rinse the whole body immediately after bathing and use eye drops
and ear drops for prevention if necessary. At the same time, we should strengthen the
monitoring of the density of the swimming crowd and control the surface source
pollution to protect the physical and mental health of the crowd.
6. CONCLUSION
This paper takes the water environment of a suburban lake in a city as an example
to study the impact of the polluted water environment on the health of outdoor sports
swimmers. And analyzed from two aspects of water quality monitoring and
questionnaire survey. Finally, the influencing factors of water environment pollution on
the outdoor tourism population are studied:
(1) Judging from the results of water quality monitoring and environmental
investigation, the inorganic nitrogen in the waters of the lake reaches the class II
standard of lake water, which meets the requirements for swimming water. Dissolved
oxygen, fecal coliform and PH value can reach the class I standard of lake water. The
survey results of the lake water environment show that there is non-point source
pollution such as food and beverages near the lake waters, especially on rainy days,
and the dissolved oxygen content in the water is (1.63±0.63) mg/L. The density of
swimmers at monitoring point 2 was the highest, and the dissolved oxygen content in
its water was the lowest, which was (5.60±2.01) mg/L, which shows that weather,
swimming population density and environmental pollution around the water are the
main factors affecting water quality.
(2) According to the questionnaire survey, lake waters have direct and indirect
effects on people's health (including skin, respiratory tract, stomach, eyes, ears, etc.).
The main symptoms are itchy skin, fever, nasal congestion, runny nose, nausea,
vomiting, stomach pain, sore throat, earache, diarrhea, and eye inflammation.
(3) The results of the questionnaire survey show that polluted lake waters can have
adverse effects on the health of the population. The main manifestations were eye
inflammation at 36.4%, skin itching at 30.3%, nasal congestion and runny nose at
29.5%, sore throat at 26.5%, stomach pain at 21.2%, and nausea at 20.1%, the
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
146
incidence of ear pain was 20.1%, the incidence of diarrhea was 17.0%, the incidence
of fever was 14.8%, and the incidence of vomiting was 12.9%.
It can be seen that the impact of lake water quality on the health of the population is
related to the swimming habits of the swimming population. Lake bathing is best to
wear waterproof goggles as well as ear plugs, etc., use water to rinse the whole body
after bathing and use eye drops and ear drops for prevention if necessary. At the
same time, we should strengthen the monitoring of the density of the swimming crowd
and control the surface source pollution to protect the physical and mental health of
the crowd.
7. DATA AVAILABILITY STATEMENT
The original contributions presented in the study are included in the article/
supplementary material, further inquiries can be directed to the corresponding author.
8. CONFLICT OF INTEREST
The authors declare that the research was conducted in the absence of any
commercial or financial relationships that could be construed as a potential conflict of
interest.
REFERENCES
(1) Tang W, Pei Y, Zheng H, et al. (2022). Twenty years of China's water pollution
control: Experiences and challenges. Chemosphere, 295, 133875.
(2) Ren L, Lu Z, Xia X, et al. (2022). Metagenomics reveals bacterioplankton
community adaptation to long-term thermal pollution through the strategy
of functional regulation in a subtropical bay. Water Research, 216, 118298.
(3) He J, Zhang Y, Ni F, et al. (2022). Understanding and characteristics of
coagulation removal of composite pollution of microplastic and
norfloxacin during water treatment. Science of The Total Environment, 831,
154826.
(4) Yang J, Strokal M, Kroeze C, et al. (2022). What is the pollution limit?
Comparing nutrient loads with thresholds to improve water quality in Lake
Baiyangdian. Science of The Total Environment, 807, 150710.
(5) Riedel T, C Kübeck, Quirin M. (2022). Legacy nitrate and trace metal (Mn, Ni,
As, Cd, U) pollution in anaerobic groundwater: Quantifying potential health
risk from "the other nitrate problem". Applied Geochemistry, 139, 105254.
(6) Yan C, Qu Z, Wang J, et al. (2022). Microalgal bioremediation of heavy metal
pollution in water: Recent advances, challenges, and prospects.
Chemosphere, 286(3), 131870.
(7) Niu Y H, Wang L, Wang Z, et al. (2022). High-frequency monitoring of
neonicotinoids dynamics in soil-water systems during hydrological
processes. Environmental Pollution, 292, 118219.
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
147
(8) Yu X, Huang W, Wang Y, et al. (2022). Microplastic pollution in the
environment and organisms of Xiangshan Bay, East China Sea: An area of
intensive mariculture. Water Research, 212, 118117.
(9) Yang Q, Liu Y, Wang L, et al. (2022). Cerium exposure in Lake Taihu water
aggravates microcystin pollution via enhancing endocytosis of Microcystis
aeruginosa. Environmental Pollution, 292, 118308.
(10) Liu Y, Wang P, Gojenko B, et al. (2021). A review of water pollution arising
from agriculture and mining activities in Central Asia: Facts, causes and
effects. Environmental Pollution, 291, 118209.
(11) Zhou, Z., Liu, J., Zhou, N., Xu, J., He, L., & Jiang, X. (2021). Does the "10-Point
Water Plan" reduce the intensity of industrial water pollution? Quasi-
experimental evidence from China. Journal of Environmental Management,
295, 113048.
(12) Wang, H., Yang, Q., Ma, H., Zou, Z., & Wang, L. (2021). Chemical
compositions evolution of groundwater and its pollution characterization
due to agricultural activities in Yinchuan Plain, northwest China.
Environmental Research, 200, 111449.
(13) Dai, L., Lu, Q., Zhou, H., & Jiang, L. (2021). Tuning oxygenated functional
groups on biochar for water pollution control: A critical review. Journal of
Hazardous Materials, 420(Part 1), 126547.
(14) Zhang, Q. Q., Xing, C., Cai, Y. Y., Yu, K., & Liu, X. (2021).
How much do human
and livestock actually contribute to steroids emission and surface water
pollution from past to the future: A global research. Science of The Total
Environment, 772, 145558.
(15) Ishii, E., Watanabe, Y., Agusa, T., Fujihara, J., Yasuda, T., & Mizukawa, K.
(2021). Acesulfame as a suitable sewer tracer on groundwater pollution: A
case study before and after the 2016 Mw 7.0 Kumamoto earthquakes.
Science of The Total Environment, 754, 142409.
(16) Ranjbar, R., Shariati, F. P., Tavakoli, O., & Dorraji, M. S. (2021). Fabrication of a
new reactor design to apply freshwater mussel Anodonta cygnea for
biological removal of water pollution. Aquaculture, 737077.
(17) Meng, X., Peng, X., Xue, J., Gao, C., & Liu, Y. (2021). A biomass-derived, all-
day-round solar evaporation platform for harvesting clean water from
microplastic pollution. Journal of Materials Chemistry A, 9.
(18) Haskins, D. L., Brown, M. K., Qin, C., Adams, L., & Hecker, M. (2021). Multi-
decadal trends in mercury and methylmercury concentrations in the brown
watersnake (Nerodia taxispilota). Environmental Pollution, 274, 116722.
(19) Oehler, T., Ramasamy, M., George, M. E., & Reniers, A. J. (2021). Tropical
Beaches Attenuate Groundwater Nitrogen Pollution Flowing to the Ocean.
Environmental Science and Technology, 55(12).
(20) He, S., Wu, J., Wang, D., & Wen, Y. (2021). Predictive modeling of
groundwater nitrate pollution and evaluating its main impact factors using
random forest. Chemosphere, 290(2), 133388.
(21) Xia C, Liu G, Wang Z, et al. Distribution of hydrogen and oxygen stable isotopes
and pollution indicators in water during a monsoon transitional period in Min
River Basin[J]. Science of The Total Environment, 2021:146780.
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
148
(22) Kumar S. Water resources pollution associated with risks of heavy metals
from Vatukoula Goldmine region, Fiji. Journal of Environmental Management,
2021.
(23) Payus C, Geoffrey I, Oliver A. (2018). Retracted: Determination of free
chlorine content in indoor and outdoor swimming pool sports complex.
(24) Smith, C. C., Löf, G., & Jones, R. (2019). Measurement and analysis of
evaporation from an inactive outdoor swimming pool. Solar Energy, 53(1),
3-7.
(25) Simard, S., Tardif, R., & Rodriguez, M. J. (2017). Variability of chlorination by-
product occurrence in water of indoor and outdoor swimming pools. Water
research: A journal of the international water association.
(26) Yao, S. (2020). An investigation of haloacetic acid occurrence in indoor and
outdoor swimming pools in Beijing China. IOP Conference Series: Earth and
Environmental Science, 467(1), 012136 (7pp).
(27) Pérez, P. A., Ballesteros-Gómez, A., Crespo-Lopez, M. E., et al. (2022). The role
of outdoor and indoor air quality in the spread of SARS-CoV-2: Overview
and recommendations by the research group on COVID-19 and particulate
matter (RESCOP commission). Environmental Research.
(28) Allen, J. M., Plewa, M. J., Wagner, E. D., et al. (2021). Making Swimming
Pools Safer: Does Copper-Silver Ionization with Chlorine Lower the
Toxicity and Disinfection Byproduct Formation? Environmental Science &
Technology, 55(5).
(29) Anugerah, A. R., Muttaqin, P. S., & Purnama, D. A. (2021). Effect of Large-
Scale Social Restriction (PSBB) during COVID-19 on Outdoor Air Quality:
Evidence from Five Cities in DKI Jakarta Province, Indonesia.
Environmental Research, 197(Special Issue), 111164.
(30) Belosi, F., Conte, M., Gianelle, V., et al. (2021). On the concentration of SARS-
CoV-2 in outdoor air and the interaction with pre-existing atmospheric
particles. Environmental Research, 193, 110603.
(31) Li M, Lana C C, Tan C S, et al. (2021). Association of time outdoors and
patterns of light exposure with myopia in children. British Journal of
Ophthalmology.
(32) Hamid N A, Alexander N, Suer R, et al. (2020). Targeted outdoor residual
spraying, autodissemination devices and their combination against Aedes
mosquitoes: field implementation in a Malaysian urban setting - ERRATUM
.
Bulletin of Entomological Research, 110(6), 1.
(33) Rozema A D, Mathijssen J, Van K, et al. (2019). Results of outdoor smoking
bans at secondary schools on adolescents smoking behaviour: a quasi-
experimental study. The European Journal of Public Health, 29(4).
(34) Gartrell B D, Battley P F, Clumpner C, et al. (2019). Captive husbandry and
veterinary care of seabirds during the MV Rena oil spill response. Wildlife
Research, 46(7), 610.
(35) Magalhaes S, Baumgartner J, Weichenthal S. (2018). Impacts of exposure to
black carbon, elemental carbon, and ultrafine particles from indoor and
outdoor sources on blood pressure in adults: A review of epidemiological
evidence. Environmental Research, 161(FEB.), 345-353.
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
149
(36) Wyse A, Rodrigues A, dos Santos A, et al. (2017). Pregnancy swimming
causes short- and long-term neuroprotection against hypoxia-ischemia in
very immature rats. Pediatric Research.
(37) Yoon I J, Hong J W. (2017). Safety Equipment for Swimming Beaches in
Korea: Implications for Management. Journal of Coastal Research, 79, 1-5.
(38) Juárez, F. F., Esenarro, D., Díaz, M., & Frayssinet, M. (2021). Model based on
balanced scorecard applied to the strategic plan of a peruvian public
entity. 3C Empresa. Investigación y pensamiento crítico, 10(4), 127-147. https://
doi.org/10.17993/3cemp.2021.100448.127-147
(39) Chen, H., Peng, X., & Chen, C. (2022). Corporate social responsibility
fulfilment, product-market competition and debt risk: Evidence from China.
Applied Mathematics and Nonlinear Sciences, 7(2), 757-772. https://doi.org/
10.2478/AMNS.2021.2.00163
https://doi.org/10.17993/3ctic.2023.121.132-150
3C TIC. Cuadernos de desarrollo aplicados a las TIC. ISSN: 2254-6529
Ed.42 | Iss.12 | N.1 January - March 2023
150