Clean air is important for human health and well-being, air pollution has increased in many parts worldwide and thus posing a significant threat people’s health. In Kenya, the traffic police officers who constantly un covered stand on road junctions continuously expose themselves to motor vehicle emissions, greatly risking their health. This study collected qualitative data and quantitative data analysed police person’s perceptions of the health impact of motor vehicle emissions on traffic police in Nairobi, Kenya. The respondents were sampled from among the traffic police officers who normally control traffic in Nairobi CBD. Pretested questionnaires were used to collect data. The study showed that police officers were aware of the effects that the motor vehicle air pollution could have on their health. About 98.1% of respondents indicated that they are affected by motor vehicle pollution. On average, about 30% of the police officers are off duty due to sickness while 82.2% had been greatly affected by exposure to motor vehicle pollution. 58.9% new cases of the health effects related to motor vehicle emission constant though majority did not take any measures. They obtained this knowledge and experience from their colleagues suffering from respiratory diseases; reporting frequent occurrence of health problems thought to arise acquaintance to motor vehicle emissions. The study accomplishes that there is an association between the amounts spent manning traffic and contact to high levels of pollution. The traffic officers have associated illnesses such as respiratory problems, asthma, cancer and other diseases that are pollution related to the high emissions of motor vehicle pollution in the Central business district.
Dominant part of the present vehicles utilize inward combustion engines that consume gas or other petroleum products; and disregard to supplant worn or deteriorated segments by Motorists which result in poor engine performance, higher fuel utilization, motor harm and excess emissions 1, 2. During combustion, various vaporous materials and pollutions are produced. These ignition side-effects are discharged into the environment as fumes gasses. Among the gasses stand nitrogen oxides, carbon monoxide, sulfur dioxide, lead and particulate matters that contaminate the atmosphere. It has been affirmed that, in creating nations of the world, vehicular development has been to a great extent unchecked by natural managing bodies making large amounts of contamination 3. One of the main worries of air contamination is the unfavorable wellbeing it has on wellbeing. Confirmation focuses to air contamination that shoots from transport as an essential supporter of ill health.
In Kenya, every person is eligible to a clean and healthy atmosphere and he or she is indebted to enhance it. The entitlement to a clean and healthy environment includes the access by persons in Kenya to the various public elements or segments of the environment for recreational, educational, health, spiritual and cultural purposes 4. World Health Organization battles that perfect air is a fundamental necessity for human wellbeing and prosperity despite the fact that air contamination keeps on representing a noteworthy risk to wellbeing around the world. As indicated by their appraisal of the weight of ailment because of air contamination, more than two million unexpected losses happening every year can be ascribed to the impacts of urban open air and indoor air contamination caused by the consuming of petroleum products 5. The greater part of these ailment troubles, specifically respiratory complexities, are borne by the populaces of creating nations Kenya included 5, currently urban air pollution is increasing.
The traffic police department’ mandate ensure that drivers on the road comply with the traffic Act and related subsidiary legislations. A majority of the traffic police staff have to spend much of their time on the roads while on duty. In these circumstances therefore, they are exposed to particulate matter and exhaust gases emitted by the vehicles on the road. This situation is worsened during peak hours when the traffic is heavy and more pollutants are released into the ambient air. This may affect their health in a variety of ways including irritation of eyes, nose and throat 6.
Vehicular emission has long run negative health consequences for those who are continuously exposed to it. This is a rather broad group including almost all the citizens of a metropolis. However, the impact varies and it depends on the direct contact with vehicular emission. The traffic police personnel’s of the city are a very vulnerable group in this regard. Standing long time in the city junctions facing the vehicles directly has a direct negative effect on them 7.
The environment conscious is very low in developing countries such as Kenya. Pollution hazard rarely come into the rational choice of the traffic men. Moreover the policemen’s duty is divided between on the road and off the road periods. Obviously the former involves a far greater health hazard with direct exposure to the vehicular emissions. These duty allocations are determined by the higher authorities with little consideration of the policemen health. Given this scenario, it is only the traffic officers themselves that can mitigate their health losses by taking measures to ameliorate the detrimental effect of air pollution. It is alongside this contextual that this study required to analyze the perception of motor vehicle emissions pollution impact on the health of traffic police in Nairobi, Kenya.
The study was carried out in the city of Nairobi, the capital city and the largest urban centre in Kenya and the one having the highest number of motor vehicles. The city is situated 140 kilometers south of equator and 500 kilometers west of the Indian Ocean at . It occupies 696km2 at an altitude of 1,661 meters above sea level (Nairobi county website, 2016 www.nairobi.go.ke/home/about-the-county).
2.2. Study PopulationThe descriptive exploratory study was targeted the traffic police working within the CBD and its outskirts. Severely congested roundabouts, within the CBD and its outskirts, were selected purposefully for the study. These are the Kamukunji, Railways terminals, University way and Uhuru Highway roundabouts manned by a population of 127 traffic police officers. Self-administered questionnaires were distributed to all the 127 participants. In addition, five (5) senior ranking officers participated in a key informant discussion. All the officers participated in the study. In respect of the proposed study, the researcher enlisted the services of traffic police leaders that is, the Base Commanders to help in the identification of the Traffic police officers according to their seniority of year of employment and work experience. It provided for equal chances of selection of individuals of similar level of experience.
2.3. Survey InstrumentThe study used a self-administered English language questionnaire to collect data, all traffic police officers being sufficiently literate as evidenced by the entry qualifications.
The questionnaire was pretested with 8 traffic police officers of Kamukunji police Station who were not used in the actual study. The pretesting feedback helped establish internal consistency of the questionnaire. Before the self-administering of the questionnaires, traffic police officers were briefed on the purpose of the study. Thirty to forty five minutes were allowed for each respondent to fill in the answers in the presence of the researcher and his assistants. The questionnaires were collected immediately they were filled and validated and where necessary clarification sought from the respondent.
It was noted that on average an officer spends 10 hours manning traffic on a roundabout every week. About 98.1% of respondents indicated that they are affected by motor vehicle pollution whereas only 1.9% said that they are not affected. For those who agreed that manning the roundabout exposed them to motor vehicle air pollution, they gave the following as their reasons; The police execute their duties for extended hours along the roundabout and therefore are most of the time vulnerable to smoke from vehicles (proportions); Traffic police officers work at the roundabout without any protective gear hence making them unprotected to things like smoke and dust (proportions); During work the police are exposed to a lot of smoke from moving vehicles (proportions); The fact that there are many traffic police officers working at the roundabouts who have had respiratory problems.
On average, at any one time, about 30% of the respondents are off duty due to sickness (Figure 1) for period 1-3 days per week, which translate to about 4-12 days, were month on sick leave.
Majority of the respondents (82.2%) said that they had been greatly affected by exposure to motor vehicle pollution, 15% (moderate), 0.9% (Small) and 1.9% had not been affected (See Figure 1).
Compared to other police officers performing other core duties, the traffic officers are at a higher health risk. The findings revealed that 75.7% of the officers rated their risks as very high as compared to other officers, 23.4% (high) whereas only 0.9% rated their risks as low. See Figure 2.
Most of the respondents agreed to have known another traffic officer who have had illnesses related to motor vehicle air pollution in the past one year (58.9%) and in the past three months (40.2%). (See Table 2).
On assessment of other air pollution that could affect their health the results indicated that 12.1 % of the respondents were smokers among which 42.9% had once been advised by health professionals to quit smoking and 28.6% had been smoking first thing in the morning as an ‘eye opener’ and smoking an average of 6 sticks of cigarettes per day (See Table 3).
A cross tabulation was made to establish the relationship between smoking and the effects of motor vehicle pollution. Of the 39.3% people who had ever had diseases associated with motor vehicle air pollution, 16% of them did smoke. This means that 61.5% of those who smoked had ever suffered from a disease associated with motor vehicle air pollution. The 12.3% of the officers who smoke may in general look like a small number compared to those who don’t smoke. However, taken on their own, and comparing them to those who have ever suffered a disease associated with Motor Vehicle air pollution, it becomes clear that smoking can be a cause for their illnesses. (See Figure 3).
On preparedness of adverse health effects it was found that majority 47.7% were not prepared for adverse health effects that could result from motor vehicle emissions, 32.7 indicated they were little prepared, 8.4% were prepared. (See Figure 4).
On preparedness on motor vehicle pollution, about 50.5% indicated that their stations were not prepared, 34.7% (a little prepared), 8.9% (prepared) while only 5.9% claimed to have been very prepared, 5.6 were well prepared while another 5.6% were unaware of any effects. (See Figure 5).
The traffic department is a department within the Kenya Police Service that is charged with ensuring that drivers on the road comply with the traffic Act and related subsidiary legislations. A majority of the traffic police staff have to spend much of their time on the roads while on duty. Traffic officers spend the about eight hours or more on the road while only few spend 8 hours or less while discharging their duties. The average hours spent on the road by traffic officers is 10 hours. However, when an officer falls sick or has to leave because of other reasons, his or her duties must be taken over by other officers. Due to the limited number of officers, at times one repeats a shift. Majority of the officers interviewed stated that they spend most part of their day manning traffic.
This study is in line with a study carried out by Bell, 8, that demonstrated that the health effects of any pollutant in an individual is directly dependent on the exposure period and toxicity of the pollutant. Nanda Kumar et al., 9, in their study among 80 TPO’s in Tirupati, India observed that there was a significant statistical correlation between period of exposure and an increase in admission rate for respiratory disorders. They observed that traffic police personnel who were occupationally exposed for longer period in their life reported to have more number of admissions than traffic police with less exposure periods. (See Table 4).
The table above on cross tabulation indicates that areas with high pollution levels are railways and Kamukunji. In railways there is high concentration of Matatu (23) unladen (35.4%) and Large bus (45 seaters) unladen (31.2%). Kamukunji also had high concentration of Matatu (23) unladen (11.9%) and Large bus (45 seaters) unladen (16.5%). This is because most of this cars use diesel and Diesel tail pipe is a foremost contributor to particulate matter (PM) pollution. Additionally large bus passenger vehicles are a main pollution contributor, producing substantial amounts of nitrogen oxides, carbon monoxide, and other contamination (See Table 4).
Areas found to have low pollution were University way and Uhuru highway. University way has high concentration of Car & Taxi (46.8%) and large cars 4WD & Jeeps (25.8%). While Uhuru highway was found to have high concentration of Car & Taxi (54.6%) and large cars 4WD & Jeeps (22.7%). The vehicles in this areas use mainly fuels which has substantial volumes of nitrogen oxides, carbon monoxide, and other pollution. The emissions from cars are low.
Comparable studies done demonstrated that overwhelming heavy-duty vehicles tried in Germany and Finland produced around 210mg NOx for each kilometer driven, not as much as a large portion of the 500mg/km directed out by present day diesel autos that meet the most noteworthy "Euro 6" standard. In any case, the transports and trucks have bigger motors and consume more diesel per kilometer, implying that autos deliver 10 times more NOx for each litre of fuel.
In this study majority of the traffic police did not smoke cigarette. This is an indication that any health effects were to a great extent attributed to automobile air pollution and not to smoking. These results agree with the 2012 World Health Statistic that indicated that current daily tobacco smoking in Kenya is estimated at 9.3% 10. These results also concur with the findings of Sharat et al., 11, who had observed from his study that there was a significant decline in various parameters examined such as forced vital capacity (FVC), forced expiratory volume in one second (FEV), and peak expiratory flow rate (PEFR) on the exposed nonsmoking TPO’s when compared with the controls.
On the number of years worked, the study found that on average, traffic police officers worked for 5 years in the traffic department. This therefore exposes them for long periods on daily basis to the effects of automobile air pollution. Thus traffic officers are vulnerable of being affected by the toxins with constant exposure. These results compares well with those of Braback, L., A. Breborowicz, S. Dreborg, A. knursson, H pieklik, and B. Bjorksten. 28, also reported in Switzerland, that there existed a relationship amid long-standing exposure to ambient air pollution and respiratory symptoms. Similar trends were observed by the investigator where there was more number of admissions among the traffic police personnel who were exposed for 6 years. Also Michael and Konstantinos 12 and Gauderman and others 13 all argued and demonstrated that the health effects of any pollutant is dependent on the period of exposure and the target organ affected.
The study showed a significant reduction in lung function in police workers working in the high traffic generated pollution 29. Another study found that changes during exercise testing that included decreased gross mechanical efficiency and a decrease in the amount of keep fit period at an anaerobic threshold and highest effort compared to those whose exposure was less. In addition, those working in chronic air pollution had a higher frequency of respiratory allergies 30. Substantial evidence and research involving combustion-related fine particulate inhalation exposure concludes that air pollution is harmful to human health. Long haul exposures have been related with cardiovascular mortality, different blood markers of cardiovascular hazard, histopathological markers of subclinical unending lung damage and subclinical atherosclerosis. Here and now exposures to particulate matter in the atmosphere have been related with cardiovascular mortality and healing facility affirmations, stroke mortality, myocardial areas of localized necrosis, confirmation of aspiratory and orderly aggravation and oxidative anxiety, modified heart autonomic capacity and blood vessel vasoconstriction 31.
As Traffic moves slowly, slow moving vehicles emit more carbon monoxide, the problem is more surmounted in Nairobi. This co-effect is toxic to human’s body. It reacts with the hemoglobin of blood and affects oxygen supply to the brain. Thus it causes death 14. One of the major causes for road congestion and therefore, vehicular emission is the massive increase in the vehicular pollution plying in and around Nairobi city. Due to this huge vehicular pollution growth, the energy demand (both diesel and petrol) increased manifold. One of the major factors that determine vehicular emission is the speed of the vehicles. According to the eminent scientist there exists a critical speed at which the emission is less of the vehicles. If the speed is well below or well above that critical one then the emission will rise significantly. So vehicle emissions are one of the significant constituents in ambient pollution. Citing a study by NEERI 15 they found that the main concentration levels for various atmospheric pollutants have increased in all the major cities.
In Kenya, legal Notice No. 60 of 2007 16 provides the recommended long term exposure limits as follows, 50 ppm for CO, 5000 ppm for CO2, 3 ppm for NO2 while short term exposure limits are given as 300 ppm for CO, 15000 ppm for CO2 and 5 ppm for NO2 respectively. WHO 17 also provides long term exposure limits for CO and NO2 as 9 ppm and 0.072 ppm respectively while short term exposure limits for the same gases are given as 26 ppm for CO and 0.12 ppm for NO2.
Other reports also indicate that cancer among the urban population in Kenya between the periods 2000 to 2002 was on an upward trend 18 and malaria was the primary source of illness followed closely by diseases of respiratory infections in the year 2005, 2006 and 2007 respectively according to Ministry of Health Kenya records 2008. Statistics in Kenya also show that about 50 Kenyans die on daily basis from various forms of cancer and about 80,000 cases of cancer are diagnosed each year in the world 19. The reports, however, failed to give the underlying factors for cancer and respiratory ailments. This phenomenon clearly exposes gloomy situation in Kenya.
The tiny evidence accessible on automobile air pollution in Nairobi suggests great pollution emissions 20, 21, 22. Similarly Mulaku and Kamau 23 demonstrated that a similar situation and condition prevailed within Nairobi. In most cases, air pollution increases in direct proportion with the increase of the number of vehicles 24 in the absence of clear policies in the management of emissions from these motor vehicles. Vehicle age and lack of regular maintenance, poor infrastructure and economic inability are factors that were found to aggravate air pollution situations in urban centres especially the Central Business District 25.
The developing countries suffer more than the developed countries from air pollution which happens from vehicle emissions. Vehicle emissions have high level of leads have led to a great environmental danger in many places in the world. For them the problem is becoming more acute as the numbers of motor vehicles are growing rapidly. Example in Delhi’s, vehicular pollution is responsible for 64 percent of the pollutants thus the inhabitants inhale a lot of polluted air 26.
The traffic officers have associated illnesses such as respiratory problems, asthma, cancer and other diseases that are pollution related, to the high emissions of motor vehicle pollution in the CBD. The police men take long hours manning their duty stations, and due to low number, majority does not take their days off and therefore they are highly exposed.
It is recommended that structures be put in place to take care of police officers, who have suffered from the effects of motor vehicle air pollution. The study recommends that the traffic department should establish and implement a system of rotation of duties for the officer’s e.g alteration of field work with office work, so as to reduce the exposure.
The study recommends that exposure can also be reduced by providing the traffic police officers with suitable personal protective devices such as masks and plain glasses to prevent lung and eye irritations. They should also be trained on their use, the type of air pollutions and associated health hazards and preventive measures required.
The financial support of the study was done by the author.
The author declares he has no competing interests.
The author wishes to express heartfelt gratitude to all traffic police officers in Nairobi County for their supports throughout the study. In due observance of protocol in this thesis am also obliged to my immediate supervisors Dr. Thuita Thenya, Prof. Raphael G Wahome, Dr. Kiemo Karatu and Prof, Michael Gatari, for their tireless effort to make sure I inscribed this paper. In general those whom I could not mention in this paper I also recognize your well aspirations and your academic input through your cherished counsel.
Ethical issues (Including plagiarism, Informed Consent, misconduct, data fabrication and/ or falsification, double publication and/ or submission, redundancy, etc) have been completely observed by the author.
[1] | Prather, M. J., Catastrophic loss of stratospheric ozone in dense volcanic clouds, J. Geophys. Res., 97, 10,187-10,191, 1995. | ||
In article | View Article | ||
[2] | Martin, S.T., 2003. Kinetics of heterogeneous ice nucleation on the surfaces of mineral dust cores inserted into aqueous ammonium sulfate particles. J. Phys. Chem. A 107 (9), 1296-1306. | ||
In article | View Article | ||
[3] | Hansen, W. Monitoring urban air exposure of bus drivers and mail carriers in Denmark. In: Chiyotani K et al., eds. Advances in the prevention of occupational respiratory diseases. Amsterdam, Elsevier Science: 2006; 1055-1060. | ||
In article | |||
[4] | GOK. National Climate Change Response Strategy. Government Printer. 2009 | ||
In article | |||
[5] | WHO. WHO Air quality guidelines for particulate matter, ozone, Nitrogen Dioxide and sulfur dioxide: Global Update 2002 (Document ref No. WHO/SDE/PHE/OEH/06.02). | ||
In article | |||
[6] | Anderson HR et al., Meta-analysis of time-series studies and panel studies of particulate matter (PM) and ozone (O3): report of a WHO task group. Copenhagen, WHO Regional Office for Europe 2004. | ||
In article | View Article | ||
[7] | Barman, N. Kumar, R. Singh, G.C. Kisku, A.H. Khan, M.M. Kidwai, R.C.Murthy, M.P.S. Negi, P. Pandey, A.K. Verma, G. Jain, S.K. Bhargava Assessment of urban air pollution and it's probable health impact Journal of Environmental Biology, 31; 2010; pp. 913-920. | ||
In article | PubMed | ||
[8] | Bell ML,. Hospital admissions and chemical composition of fine particle air pollution. Am J RespirCrit Care Med 2006; 179: 1115-1120. | ||
In article | View Article PubMed | ||
[9] | Nanda Kumar, H., T. Dohmen, Thomas, A. Falk. D. Huffman, and U. Sunde, “Crosssectional earnings risk and occupational sorting: The role of risk attitudes,” Labour Economics, 14(6) (2009), 926-937. | ||
In article | View Article | ||
[10] | Gathura, G. Men pay price for risky life styles. Daily Nation, Friday 18th May2012. pp10. | ||
In article | |||
[11] | Sharat, G.; Shallu, M.; Avnish, K. and Kamal, D. S. Respiratory effects of air pollutants among nonsmoking traffic policemen of Patiala, India. Lung India, Vol.28, No. 4, October-December, 2011, pp. 253-257. | ||
In article | View Article PubMed | ||
[12] | Michael, K. and Konstantinos, H. "Short-Term Affects of Air Pollution Levels on Pulmonary Function of Young Adults". The Internet Journal of PulmonaryMedicine 2008; 9 (2). pp 7. | ||
In article | |||
[13] | Gauderman, W. J.; McConnell, R.; Gilliland, F.; London, S.; Thomas, D. and Avon, E. Association between air pollution and lung function growth in Southern 2000. | ||
In article | View Article | ||
[14] | Banerjee, S and Bhattacharyya, R. (-ed) Environmental Economics: An Indian Perspective, (Chapter-4) Oxford University Press, New Delhi. 2001. | ||
In article | |||
[15] | NEERI Uncertainty estimation in analysis of particulate-bound mercury in different size fractions of PM 10 in ambient air 2005. | ||
In article | View Article | ||
[16] | GOK. The Factories and Other places of Work (Hazardous Substances) Rules 2007. Legal Notice No. 60 of 2007. Government Printer. 2007. | ||
In article | |||
[17] | WHO. (2000). Air quality guidelines for Europe, 2nd ed. Copenhagen, WHO Regional Office for Europe, 2000 (WHO Regional Publications, European Series, No. 91), pp 33. | ||
In article | View Article | ||
[18] | Korir, A.; Mutuma, G. and Omach, J. Cancer in Urban Population of Kenya, Nairobi Cancer Registry. Kenya Medical Research Institute report on cancer. 2008. | ||
In article | |||
[19] | Olick, F. Slow Progress in halting disease claim many lives. The Standard,Tuesday 8th November 2011. | ||
In article | |||
[20] | Gatebe, C.K.,. Estimation of Carbon Monoxide, Hydrocarbons and Oxides of Nitrogen from motor vehicles in Nairobi. M.Sc. Thesis, University of Nairobi 1992. | ||
In article | |||
[21] | Karue, J., A.M. Kinyua and A.H.S. El-Busaidy, Measured components in total suspended particulate matter in a Kenyan Urban Area. Atmos. Environ. Burb, 1992; 26(4): 505-511. | ||
In article | View Article | ||
[22] | Gatebe, C.K., A.M. Kinyua, M.J. Mangala, R. Kwach, L.N. Njau, E.A. Mukolwe and D.M. Maina,. Determination of suspended particulate matter of major significance to human health using nuclear techniques in Kenya. J. Radioanal. Nucl. Ch., 1996; 203(1): 125-134. | ||
In article | View Article | ||
[23] | Mulaku, G. C. and Kamau, L. W. Mapping and Analysis of Air Pollution in Nairobi, Kenya, International Conference on Spatial Information for Sustainable Development Nairobi, Kenya, 2-5 October 2001 | ||
In article | |||
[24] | Odhiambo, G. O.; Kinyua, A. M.; Gatebe, C. K. and Awange, J. Motor Vehicle Pollution in Nairobi, Kenya. Research Journal of Environmental and Earth Sciences 2(4): 178-187, 2010 | ||
In article | |||
[25] | Maina, D.M.; Gatari, M. J.; Bundi, P. and Muturi, H. Impact of Road Transport on Air Quality in Kenya. Roadside Survey in the Cities of Mombasa and Nairobi. Unpublished. 2015. | ||
In article | |||
[26] | Bhattacharyya (-ed) Environmental Economics: An Indian Perspective, (Chapter-4) Oxford University Press, New Delhi.2002. | ||
In article | |||
[27] | G.D’amato, R. Pawankar, C. vitale, et al. climate change and Air pollution: effects and respiratory allergy. Allergy Asthma immunol Res.8 (2016), pp.391-395. | ||
In article | View Article PubMed | ||
[28] | Braback, L., A. Breborowicz, S. Dreborg, A. knursson, H pieklik, and B. Bjorksten. 1994 Atopic sensitization and respiratory sympotoms among polish and Swedish school children. Allegy 24: 826-835. | ||
In article | View Article | ||
[29] | Liwsrisakun C, Tungkanakorn S, Liewhiran A, Yutabootr Y, Praramontol T. Effects of air pollution on lung function: A study in traffic policemen in Chiang Mai. Chiang Mai Med Bull. 2002; 41: 89-94. | ||
In article | |||
[30] | Proietti L, Mastruzzo C, Palmero F, Vancheri C, Lisitano N, Crimi N. Prevalence of respiratory symptoms, reduction in lung function and allergic sensitization in a group of traffic police officers exposed to urban pollution. Med Lav. 2005; 96: 24-32. | ||
In article | PubMed | ||
[31] | Kariisa M, Foraker R, Pennell M, et al.. Short- and long-term effects of ambient ozone and fine particulate matter on the respiratory health of chronic obstructive pulmonary disease subjects. Arch Environ Occup Health. 2015; 70(1):56–62. | ||
In article | View Article PubMed | ||
[32] | Kenya National Bureau of Statistics (KNBS) and ICF Macro. 2010. Kenya Demographic and Health Survey 2008-09. Calverton, Maryland: KNBS and ICF Macro. | ||
In article | |||
Published with license by Science and Education Publishing, Copyright © 2017 Samson Murangiri Mukaria, Thuita Thenya, Raphael G Wahome, Kiemo Karatu and Michael Gatari
This work is licensed under a Creative Commons Attribution 4.0 International License. To view a copy of this license, visit https://creativecommons.org/licenses/by/4.0/
[1] | Prather, M. J., Catastrophic loss of stratospheric ozone in dense volcanic clouds, J. Geophys. Res., 97, 10,187-10,191, 1995. | ||
In article | View Article | ||
[2] | Martin, S.T., 2003. Kinetics of heterogeneous ice nucleation on the surfaces of mineral dust cores inserted into aqueous ammonium sulfate particles. J. Phys. Chem. A 107 (9), 1296-1306. | ||
In article | View Article | ||
[3] | Hansen, W. Monitoring urban air exposure of bus drivers and mail carriers in Denmark. In: Chiyotani K et al., eds. Advances in the prevention of occupational respiratory diseases. Amsterdam, Elsevier Science: 2006; 1055-1060. | ||
In article | |||
[4] | GOK. National Climate Change Response Strategy. Government Printer. 2009 | ||
In article | |||
[5] | WHO. WHO Air quality guidelines for particulate matter, ozone, Nitrogen Dioxide and sulfur dioxide: Global Update 2002 (Document ref No. WHO/SDE/PHE/OEH/06.02). | ||
In article | |||
[6] | Anderson HR et al., Meta-analysis of time-series studies and panel studies of particulate matter (PM) and ozone (O3): report of a WHO task group. Copenhagen, WHO Regional Office for Europe 2004. | ||
In article | View Article | ||
[7] | Barman, N. Kumar, R. Singh, G.C. Kisku, A.H. Khan, M.M. Kidwai, R.C.Murthy, M.P.S. Negi, P. Pandey, A.K. Verma, G. Jain, S.K. Bhargava Assessment of urban air pollution and it's probable health impact Journal of Environmental Biology, 31; 2010; pp. 913-920. | ||
In article | PubMed | ||
[8] | Bell ML,. Hospital admissions and chemical composition of fine particle air pollution. Am J RespirCrit Care Med 2006; 179: 1115-1120. | ||
In article | View Article PubMed | ||
[9] | Nanda Kumar, H., T. Dohmen, Thomas, A. Falk. D. Huffman, and U. Sunde, “Crosssectional earnings risk and occupational sorting: The role of risk attitudes,” Labour Economics, 14(6) (2009), 926-937. | ||
In article | View Article | ||
[10] | Gathura, G. Men pay price for risky life styles. Daily Nation, Friday 18th May2012. pp10. | ||
In article | |||
[11] | Sharat, G.; Shallu, M.; Avnish, K. and Kamal, D. S. Respiratory effects of air pollutants among nonsmoking traffic policemen of Patiala, India. Lung India, Vol.28, No. 4, October-December, 2011, pp. 253-257. | ||
In article | View Article PubMed | ||
[12] | Michael, K. and Konstantinos, H. "Short-Term Affects of Air Pollution Levels on Pulmonary Function of Young Adults". The Internet Journal of PulmonaryMedicine 2008; 9 (2). pp 7. | ||
In article | |||
[13] | Gauderman, W. J.; McConnell, R.; Gilliland, F.; London, S.; Thomas, D. and Avon, E. Association between air pollution and lung function growth in Southern 2000. | ||
In article | View Article | ||
[14] | Banerjee, S and Bhattacharyya, R. (-ed) Environmental Economics: An Indian Perspective, (Chapter-4) Oxford University Press, New Delhi. 2001. | ||
In article | |||
[15] | NEERI Uncertainty estimation in analysis of particulate-bound mercury in different size fractions of PM 10 in ambient air 2005. | ||
In article | View Article | ||
[16] | GOK. The Factories and Other places of Work (Hazardous Substances) Rules 2007. Legal Notice No. 60 of 2007. Government Printer. 2007. | ||
In article | |||
[17] | WHO. (2000). Air quality guidelines for Europe, 2nd ed. Copenhagen, WHO Regional Office for Europe, 2000 (WHO Regional Publications, European Series, No. 91), pp 33. | ||
In article | View Article | ||
[18] | Korir, A.; Mutuma, G. and Omach, J. Cancer in Urban Population of Kenya, Nairobi Cancer Registry. Kenya Medical Research Institute report on cancer. 2008. | ||
In article | |||
[19] | Olick, F. Slow Progress in halting disease claim many lives. The Standard,Tuesday 8th November 2011. | ||
In article | |||
[20] | Gatebe, C.K.,. Estimation of Carbon Monoxide, Hydrocarbons and Oxides of Nitrogen from motor vehicles in Nairobi. M.Sc. Thesis, University of Nairobi 1992. | ||
In article | |||
[21] | Karue, J., A.M. Kinyua and A.H.S. El-Busaidy, Measured components in total suspended particulate matter in a Kenyan Urban Area. Atmos. Environ. Burb, 1992; 26(4): 505-511. | ||
In article | View Article | ||
[22] | Gatebe, C.K., A.M. Kinyua, M.J. Mangala, R. Kwach, L.N. Njau, E.A. Mukolwe and D.M. Maina,. Determination of suspended particulate matter of major significance to human health using nuclear techniques in Kenya. J. Radioanal. Nucl. Ch., 1996; 203(1): 125-134. | ||
In article | View Article | ||
[23] | Mulaku, G. C. and Kamau, L. W. Mapping and Analysis of Air Pollution in Nairobi, Kenya, International Conference on Spatial Information for Sustainable Development Nairobi, Kenya, 2-5 October 2001 | ||
In article | |||
[24] | Odhiambo, G. O.; Kinyua, A. M.; Gatebe, C. K. and Awange, J. Motor Vehicle Pollution in Nairobi, Kenya. Research Journal of Environmental and Earth Sciences 2(4): 178-187, 2010 | ||
In article | |||
[25] | Maina, D.M.; Gatari, M. J.; Bundi, P. and Muturi, H. Impact of Road Transport on Air Quality in Kenya. Roadside Survey in the Cities of Mombasa and Nairobi. Unpublished. 2015. | ||
In article | |||
[26] | Bhattacharyya (-ed) Environmental Economics: An Indian Perspective, (Chapter-4) Oxford University Press, New Delhi.2002. | ||
In article | |||
[27] | G.D’amato, R. Pawankar, C. vitale, et al. climate change and Air pollution: effects and respiratory allergy. Allergy Asthma immunol Res.8 (2016), pp.391-395. | ||
In article | View Article PubMed | ||
[28] | Braback, L., A. Breborowicz, S. Dreborg, A. knursson, H pieklik, and B. Bjorksten. 1994 Atopic sensitization and respiratory sympotoms among polish and Swedish school children. Allegy 24: 826-835. | ||
In article | View Article | ||
[29] | Liwsrisakun C, Tungkanakorn S, Liewhiran A, Yutabootr Y, Praramontol T. Effects of air pollution on lung function: A study in traffic policemen in Chiang Mai. Chiang Mai Med Bull. 2002; 41: 89-94. | ||
In article | |||
[30] | Proietti L, Mastruzzo C, Palmero F, Vancheri C, Lisitano N, Crimi N. Prevalence of respiratory symptoms, reduction in lung function and allergic sensitization in a group of traffic police officers exposed to urban pollution. Med Lav. 2005; 96: 24-32. | ||
In article | PubMed | ||
[31] | Kariisa M, Foraker R, Pennell M, et al.. Short- and long-term effects of ambient ozone and fine particulate matter on the respiratory health of chronic obstructive pulmonary disease subjects. Arch Environ Occup Health. 2015; 70(1):56–62. | ||
In article | View Article PubMed | ||
[32] | Kenya National Bureau of Statistics (KNBS) and ICF Macro. 2010. Kenya Demographic and Health Survey 2008-09. Calverton, Maryland: KNBS and ICF Macro. | ||
In article | |||