ARTICLE INFO

Article Type

Original Research

Authors

Bahmanpour   H. (*1)
Naghibi   SH (2)
Abdi   H. (2)






(*1) Department of Environment, Faculty of Engineering, Shahrood Branch, Islamic Azad University, Shahrood, Iran
(2) Department of Physical Education, Faculty of Human Sciences, Shahrood Branch, Islamic Azad University, Shahrood, Iran

Correspondence

Address: Shahrood Branch of Islamic Azad University, Daneshgah Boulevard, Shahrood, Iran Postal Code: 3619943189
Phone: +98 (21) 44838161
Fax: +98 (21) 88546377
hooman.bahmanpour@gmail.com

Article History

Received:  March  25, 2020
Accepted:  May 11, 2020
ePublished:  May 30, 2020

BRIEF TEXT




Air pollution is one of the most important factors influencing human life [Arnesano et al., 2016]. It is the fourth-factor threatening human life in the world [WHO, 2017]. The athletes absorb more pollutants because of their higher activity, which leads to early fatigue [Mohaghegh & Hajian, 2013]. According to the recorded data, the percentage of people with respiratory problems increases up to 60% in severely polluted days [Ghanbari & Azizi, 2007]. Bahmanpour et al. (2013) show no stable and regular pattern in distributing the pollutants in Tehran, and the eastern part of the city is not in an optimal condition [Rohani et al., 2017]. The sports sites' air pollution risk assessment in Tehran shows a high risk of pollution [Nameni et al., 2019].

This study aimed to assess the environmental risk of Tehran's sports sites in terms of Carbon Monoxide pollution.

The research type is not mentioned.

The current research is carried out in the outdoor sports sites in northeast of Tehran (regions 4, 7, 8, and 13) from 2018, April to 2019, April

The needed data gathered from five active stations in the studied area.

There are no devices and materials mentioned.

Carbon Monoxide hourly concentration The hourly Carbon Monoxide in assessment stations is 2.39 in Aqdasiyeh station, 2.11 in Piroozi station, 2.30 in Drous station, and 2.13 in Setad Bohran 2.16 in Golbarg station. Chart 1 shows the hourly concentration of Carbon Monoxide in the studied stations in different seasons of 2018.AQI and PSI indicators assessment AQI and PSI are two international reference indicators to assess air pollution by measuring all air pollutants. The number of polluted days (PSI>100) in each station is shown in Chart. This Chart assesses the air quality in the studied stations using the air pollutants indicators and shows Piroozi station has the least air quality (53.42% polluted days in a year), while Aqdasiyeh has the highest air quality (15.61% polluted days in a year). Aqdasiyeh has had the most number of days with fresh air (77days), and Piroozi has had the least days with fresh air (7 days). Although the "hazardous" air quality grade is recorded for none of the stations, "unhealthy" and "unhealthy for sensitive groups" account for 30% of the days in 2018. As it is shown in Chart 3, the average daily amount of Carbon Monoxide is far less than the national standard (7ppm). The map of Carbon Monoxide pollutant distribution and concentration in the studied area is drawn in Figure1. The map in Figure 2 was, eventually, prepared by overlaying the sports sites location layer and Carbon Monoxide distribution layer. Environmental risk assessment in the sports sites in the studied area The environmental risk of Carbon Monoxide in the sports sites was assessed using William Fine method guideline. Two different scenarios were proposed to assess the environmental risk of the emission of air pollutants in the studied area and their impact on the sports sites, according to Table 5. Risk level determination (consequences, exposure, and probability) for Carbon Monoxide according to the number of days without pollution; Risk level determination (consequences, exposure, and probability) for all pollutants using AQI/PSI indicators and according to 30% polluted days in the year measuring the rising amount of Carboxyhemoglobin in the blood in exchange for the increase of the amount of 〖VO〗_2max in the equation of y=0.6575x+1.8355. Finally, this factor was evaluated using William Fine method as below: Risk probability × risk consequences × exposure To sum up, Carbon Monoxide's risk is low in scenario A, and the hazard should be controlled, but the risk grade in scenario B is moderate. A summary of the managerial practices compatible with the situation is shown in Table 6. According to the results and findings, it can be concluded that 12 sports sites out of 48 studied sites are located in the most polluted areas. Figure 3 shows the number of sports sites in each air pollution grade and shows the risk level.

The result of the current study is consistent with Rohani et al. (2002) and Brunekreef & Holtage (2002) in terms of the methodology and concluded results. Nevertheless, it is not consistent with the results of Bahmanpour et al. (2013) regarding the air pollution emission in Tehran. The current research results do not approve Nameni et al.'s (2019) results regarding the environmental risk of Carbon Monoxide.

There are some suggestions to solve the problem such as finding better timing for doing exercise, choose more compatible sports in time of high air pollution, designing the sports sites with moving roofs that cover the outdoor spaces in time of high air pollution, the use of air purifiers and air conditioners in sports sites, and raising awareness of the public about the air pollution in these sites. It helps the athletes to choose the sports sites more carefully.

There is no limitation reported.

Almost 12 sports sites in the studied area are directly exposed to air pollutants, and as the athletes are more prone to severe air pollution damages, some managerial practices are needed to improve such land uses quality.

The authors thank Ms. Atousa Halajian for their help in drawing the maps.

None.

None.

The current research is carried out using personal funds.

TABLES and CHARTS

Show attach file


CITIATION LINKS

[1]Arnesano M, Revel GM, Seri FA (2016). A tool for the optimal sensor placement to optimize temperature monitoring in large sports spaces. Automation in Construction. 68:223–234.
[2]Allen HH, Chia-wei H, Tsai-Chi K, Wei-Cheng W (2009). Risk evaluation of green components to hazardous substance using FMEA and FAHP. Expert Systems with Applications. 36(3):7142-7147.
[3]Ghanbari H, Azizi GH (2007). Numerical simulation of Tehran air pollution behavior based on wind pattern. Natural Geographic Researchs. 68:15-32. [Persian]
[4]Bahmanpour H, Askari Rabori A, Gholami M (2013). The qualitative and quantitative evaluation of urban parks and green spaces in city of Tehran. Advances in Environmental Biology. 7(11):3474-3481. [Persian]
[5]Blair C, Walls J, Davies NW, Jacobson GA (2010). Volatile organic compounds in runners near a roadway: increased blood levels after short-duration exercise. British Journal of Sports Medicine. 44:731-735.
[6]Bono R, Degan R, Pazzi M, Romanazzi V, Rovere R (2006). Benzene and formaldehyde in air of two winter olympic venues of Torino 2006. Enviroment International. 36(3):268-275.
[7]Brunekreef ST, Holgate S (2002). Air pollution and health. The Lancet Conference Alerts. 360 (9341):1233–1242.
[8]Campbell M, Li Q, Gingrich S, Macfarlene R, Cheng S (2005). Should people be physically active outdoors on smog alert days? Canadian Journal of Public Health. 96:24-28.
[9]Carlisle AJ, Sharp NC (2001). Exercise and outdoor ambient air pollution. British Journal of Sports Medicine. 35(4):214-222.
[10]Daisey JM, Angell WJ, Apte MG (2003). Indoor air quality, ventilation and health symptoms in schools: analysis of existing information. Indoor Air. 13(1):53–64.
[11]Florida-James G, Donaldson K, Stone V (2004). Athens 2004: The pollution climate and athletic performance. Journal Sports Science. 22(10):967-80.
[12]Folinsbee LJ (2001). Air pollution: Acute and chronic effects. 2nd ed. London: The Royal Society of Medicine.
[13]Holzer K (2012). Respiratory symptoms during exercise. In: Brukner P, Brukner and Khan clinical editor. sports medicine.4th ed. McGraw-Hill.
[14]O'Brien TD, Noyes J, Spencer LH, Kubis HP, Hastings RP, Whitaker R (2016). Systematic review of physical activity and exercise interventions to improve health, fitness and well-being of children and young people who use wheelchairs. BMJ Open Sport & Exercise Medicine. 2(1).
[15]International Agency for Research on Cancer [Internet]. International Agency for Research on Cancer, Latest world cancer statistics Global cancer burden raises to 14.1 million new cases in 2012: Marked increase in breast cancers must be addressed. [Published 2013, 3 March; Cited 2013, 15 May]. France: IARC Publications. Available From: https://www.who.int/
[16]Kim YM, Harrad S, Harrison R (2001). Concentrations and sources of volatile organic compounds in urban domestic and public microenvironments. Environmental Science & Technology. 35(6):147-53.
[17]Lippi G, Guidi GC, Maffulli N (2008). Air pollution and sports performance in Beijing. International Journal of Sports Medicine. 29(8):696-898.
[18]Mohaghegh S, Hajian M (2013). Sport and air pollution. Journal of Medical Council of Iran. 31(3):237-249.
[19]Nameni A, Tayebi-Sani SM, Fahiminejad A, Morsal B (2019). Environmental risk assessment of sports complexes in Tehran within Air Pollutant. Quarterly Journal of Human Geographic. 11(2):164-179. [Persian]
[20]Nasibullina A (2015). Education for sustainable development and environmental ethics. Procedia - Social and Behavioral Sciences. 214:1077-1082.
[21]Rohani A, Tayebi Sani SM, Bahmanpour H, Morsal B (2017). Spatial assessment and environmental sustainability assessment of Tehran Shemiran sports complexes in connection with zoning of air pollution: in the direction of sustainable development and environmental protection. Quarterly of Geography (Regional Planning). 8(1):215-236.
[22]Raub JA, Benignus VA (2002). Carbon monoxide and the nervous system. Neuroscience & Biobehavioral Reviews. 26(8):925-940.
[23]Swain DP, Brawner CA (2014). ACSM's resource manual for guidelines for exercise testing and prescription. Philadelphia: Wolters Kluwer Health/Lippincott Williams & Wilkins Publisher.
[24]TAQCC (2016). Teharan air quality control company. Report of Tehranz, Tehran Municipality, Nashr-e- Shahr. pp 265.
[25]United States Environmental Protection Agency [Internet]. An examination of EPA risk assessment principles and practices. [Published 2004, 17 March; Cited 2006, 4 November]. Washington, D.C: USEPA Publications. Available From: https://www.epa.gov/
[26]Vedal S, Brauer M, White RJ (2003). Air pollution and daily mortality in a city with low levels of pollution. Environ Health Prospect. 111(1):45-51.
[27]Wark K, Warner CF, Davis WT (1998). Air pollution: Its origin and control. 3rd ed. London: Pearson.
[28]WB (2015). Air pollution cost in global, World Bank Reports.
[29]World Health Organization [Internet]. Air quality and health. [Published 2017, 7 January; Cited 2019, 3 March]. Geneva: WHO Publications. Available From: https://www.who.int/
[30]Wu D, Xu Y, Zhang S (2015). Will joint regional air pollution control be more cost-effective? An empirical study of China's Beijing Tianjin Hebei region. Journal of Environmental Management. 149:27-36.
[31]Zammori F, Gabbrielli R (2012). ANP/RPN: A multi criteria evaluation of the risk priority number. Quality and Reliability Engineering International. 28(1):104-85.