World Environment

p-ISSN: 2163-1573    e-ISSN: 2163-1581

2013;  3(4): 133-137

doi:10.5923/j.env.20130304.02

Determination of Carbon Monoxide Concentration in Industrial and Commercial Areas of Kano Metropolis, Kano State, Nigeria

Bernard Emmanuel

Department of Chemistry, Federal College of Education (Technical) Bichi P.M.B 3473, Kano, Nigeria

Correspondence to: Bernard Emmanuel, Department of Chemistry, Federal College of Education (Technical) Bichi P.M.B 3473, Kano, Nigeria.

Email:

Copyright © 2012 Scientific & Academic Publishing. All Rights Reserved.

Abstract

The incomplete combustion of organic fossil fuels such as oil, gas or coal is a common source of carbon monoxide (CO) pollution in the environment and when inhaled into the body it combines with the blood, preventing it from absorbing oxygen, causing illness and even death at high concentration. A mean value of 14.13 parts per million ( ppm) was observed for the Metropolis, while the highest mean value of 18.00 ppm for Bata a highly crowded commercial area followed by a mean value of 16.92ppm for Sharada industrial layout with Sabon Gari having a mean of 9.67 ppm, the least mean value of 8.52 ppm was detected at Challawa. The study indicated that Kano Metropolis dwellers were generally exposed to higher levels of CO which is above the World Health Organisation (WHO) permitted value of less than 9ppm over an 8 hour period. It is recommended that the government should make urgent efforts to improve power generation, since this will reduce dependence on generators for power supply and increase awareness of health risks from exposure amongst others.

Keywords: Determination, Carbon Monoxide, Concentration, Industrial, Commercial, Metropolis

Cite this paper: Bernard Emmanuel, Determination of Carbon Monoxide Concentration in Industrial and Commercial Areas of Kano Metropolis, Kano State, Nigeria, World Environment, Vol. 3 No. 4, 2013, pp. 133-137. doi: 10.5923/j.env.20130304.02.

1. Introduction

Carbon monoxide (CO) is a colorless, odorless, tasteless, nonirritating and toxic gas that is slightly lighter than air. It is present in small amounts in the atmosphere, chiefly as a product of volcanic activity, industrial processes, human and animal respiration, cigarette smoke, natural and man-made fires (such as forest and bushfires). The burning of fossil fuels is the principal source of CO pollution in most industrial, commercial and large urban areas. Incomplete oxidation during combustion of fuels like wood, coal, oil, paraffin, natural gas, trash and unvented gas or kerosene heaters may cause high concentrations of CO in air. Auto truck or bus exhaust from attached garages, nearby roads, or parking areas can also be a source. Because natural sources of carbon monoxide are so variable from year to year, it is extremely difficult to accurately measure natural emissions of the gas. In the atmosphere it is spatially variable, short lived, having an indirect radiative forcing effect by the formation of methane and ground-level ozone[1][2][3][4]. Through natural processes in the atmosphere, it is eventually oxidized to carbon dioxide.
At lower levels of exposure, CO causes mild effects that are often mistaken for the flu. They include fatigue, dizziness, irregular breathing, disorientation, cherry red lips, nausea, headache, paleness, and coughing. The effects of CO exposure can vary greatly from person to person depending on age, overall health condition, the concentration of the gas and length of exposure. Because it is impossible to see, taste or smell the toxic fumes, CO can kill one before one is aware of its existence. In human CO is naturally produced by the action of heme oxygenase 1 and 2 on the heme from hemoglobin breakdown. This process produces a certain amount of carboxyhemoglobin (COHb) in normal persons, even if they do not breathe any carbon monoxide[5][6][7].
In the United States and other parts of the world CO is noted as the leading cause of poisoning mortality and may be responsible for more than half of all fatal poisonings worldwide. It is the most common type of fatal air poisoning in many countries. It combines with hemoglobin to produce COHb, which is ineffective for delivering oxygen to bodily tissues. The percentage of hemoglobin inactivated by CO depends on the amount of air breathed, the concentration of CO in air, and length of exposure.[8][9][10][11][12]
The USA Centers for Disease Control and Prevention reported that from 1968 to 1998, non–fire-related CO poisoning caused or contributed to 116,703 deaths, 70.6% of which were due to motor vehicle exhaust, and 29% of which were unintentional. An estimated 5000 to 6000 people die in the United States each year as a result of CO exposure. The rate of accidental deaths seems to have declined from 1513 per year in 1979 to approximately 500 to 600 per year in the 1990s, likely owing to the widespread use of catalytic converters on automobiles and improved emissions policies. The Clean Air Act gives state and local government primary responsibility for regulating pollution from power plants, factories, and other “stationary sources.” The Environmental Protection Agency (EPA) has primary responsibility for “mobile source” pollution control. The EPA motor vehicle program has achieved considerable success in reducing carbon monoxide emissions. EPA standards in the early 1970’s prompted automakers to improve basic engine design. By 1975, most new cars were equipped with catalytic converters designed to convert carbon monoxide to carbon dioxide. Catalysts typically reduce CO emissions by about of 80 percent. In the early 1980’s, automakers introduced more sophisticated converters, plus onboard computers and oxygen sensors to help optimize the efficiency of the catalytic converter.
While ambient carbon monoxide levels have dropped, despite large increases in the number of vehicles on the road and the number of miles they travel in developed nations the reverse is the case of developing world like Nigeria. It is argued that this is an important current source of health inequality between the developed and developing nations created partly by the massive importation of used automobiles.[9][13][14][15]
The World Health Organization’s (WHO) guidelines values and periods of time-weighted average for carbon monoxide exposure are expressed at four averaging times, determined in such a way that the COHb. level of 2.5% is not exceeded, even when a normal subject engages in light or moderate exercise as follows: 87ppm for 15 min, 52ppm for 30 min, 26ppm for 1 h, 9ppm for 8 h[16][17]
In Kano Metropolis there has been several cases of death recorded in connection with CO poisoning especially when people find themselves sleeping in same room with or close to a power generating set and in the event of fire outbreak. This has made it very relevant to ascertain the level of CO present in the industrial and commercial areas in Kano metropolis and to enlighten the populaces of the danger of high concentration of CO.

2. Materials and Method

2.1. Study Area

The study was carried out at different industrial and commercial areas where some of the most heavily populated and industrialized areas of Kano Metropolis, Kano State of Nigeria. Samples of Carbon Monoxide were measured. A total of one hundred and ninety seven (197) samples were taken between September, 2012 and January, 2013 on a continuous basis throughout the sampling period. The sample sites are: Bata (the east of the City) surrounded by Sabon-Gari to the North. Sabon-Gari is located west of Mallam Aminu Kano International airport, while the industrial areas Sharada is outside the City walls, and Challawa industrial area is bounded by rail line south-west of the City walls.

2.2. Instrumentation

The Crowcon-Gasman “TO” detection instrument was used. The Gasman “TO” is designed to monitor for the presence of specific toxic gases, and is certified to EEx ia IIC T3/T4. Temperature classification T3 applies if the unit is fitted with the Crowcon rechargeable battery pack, while the T4 applies if the unit is fitted with disposable batteries. To adjust the span of the “TO” version gas of known concentration and reliable delivery systems to the sensor are required. The calibration gas test kits, comprising gas mixtures, either in disposable cylinders, regulator, and tube and calibration adaptors were used. The calibration adaptor was fitted into the top of the sensor housing and the gas cylinder valve was opened. The gas flow rate was set to sensor 0.5l/min and the reading on the display was allowed to stabilize. The CAL preset was adjusted so that the display indicated the concentration shown on the cylinder. With the units

3. Results and Discussion

The present study shows the ambient carbon monoxide (CO) inputs in the industrial and commercial areas of Kano State. With the exception of Challawa with a mean of 8.93ppm, it was observed that the concentration of CO is higher than the internationally permitted standard of below 9ppm over an 8 hour average period.[18]. The monitored zones were divided into four having Sharada and Challawa industrial layouts as industrial area because of the high concentration of industries and industrial activities, while Bata and Sabon Gari were designated commercial areas due to the high concentration of commercial/business activities. The mean, standard deviation and coefficient of variation for CO gas in the metropolis are shown in Table 1.
Table 1. Carbon Monoxide Concentration in Industrial and Commercial Areas of Kano State
     
The frequency distribution pattern for CO gas concentration in the Metropolis is shown in Fig.1a; the distribution is skewed towards high frequency of low concentration. It was observed that the Metropolis has a mean value and standard deviation of 14.13 ± 012.12ppm. The observed distribution pattern can be attributed to the use of private power generator plants for electric supply as a substitute for the inconsistent Power Holding Company of Nigeria (PHCN) supply for both industrial and business activities as well as high vehicular movements with most vehicles poorly managed/serviced.[19][20].[21] Fig 1b shows the frequency distribution for Sharada industrial layout and it is skewed toward a high frequency of low concentration with a mean value and standard deviation of 16.92 ± 012.72ppm with the highest single value of above 65ppm at some points, this outcome can be attributed to very high concentration of factories in full production emitting smoke from their power generation plants coupled with heavy traffic. Challawa industrial layout had a mean value and standard deviation of 8.52 ± 8.22ppm it is skewed towards high frequency of low concentration as shown in Fig. 1c.. Challawa’s lower value below standard permission of 9ppm over an 8 hour period can be attributed to the proper layout of the area with fewer industries in involved in actual production. Vehicular movement is relative lower than Sharada industrial layout emission level when compared. Considering the commercial areas it was observed that Bata has a mean and standard deviation values of 18.00 ± 9.50ppm which is skewed towards high frequency of low concentration as shown in Fig. 1d. This observation can be attributed to extremely high concentration of private power generation sets as almost every business outlet owns one and the heavy vehicular movement with periodic traffic obstructions. Sabon Gari has a mean and standard deviation of 9.67 ± 5.44ppm, as shown in Fig. 1e when compared with Bata though with many generating sets and vehicular movement but not concentrated in a particular area there by giving room for dispersal of the generated gases.
Figure 1a. Frequency Distribution Pattern for Metropolis
Figure 1b. Frequency Distribution Pattern for Sharada
Figure 1c. Frequency Distribution Pattern for Challawa
Figure 1d. Frequency Distribution Pattern for Bata
Figure 1e. Frequency Distribution Pattern Sabon Gari
It is apparent that human beings have been responsible for most of this increase in CO due to a tremendous dependence on machine and equipment that burn fossil fuels such as automobiles and generators as well as enhanced chemical processes carried out in factories and power plants.
Ambient concentrations of carbon monoxide, can be detrimental to human health and welfare, depending on the levels that occur in areas where humans live and work and on the susceptibility of exposed individuals to potentially adverse effects. The workplace is an important setting for carbon monoxide exposures. In general, apart from commuting to and from work, exposures at work exceed carbon monoxide exposures during no work periods. Occupational and non-occupational exposures may overlay one another and result in a higher concentration of carbon monoxide in the blood. Certain industrial processes can expose workers to carbon monoxide produced directly or as a byproduct.
However, the observed values are not likely to reduce but grow worst because, the current state of National Power supply is not encouraging and more industries and commercial/business outfits are flourishing with more companies and individuals acquiring more automobiles.[19] [20]

4. Conclusions

In Nigeria, with a developing economy fuel combustion in cars and by the numerous electric power generating sets which serve as more reliable source of power due to the epileptic power supply from the national power company - Power Holding Company of Nigeria (PHCN) the massive importation of electric power generating sets for both industrial and domestic use and importation of used automobiles that are poorly maintained / serviced will most certainly increase the CO emissions. It is responsible for a large percentage of the accidental poisonings and deaths reported throughout the world each year. Certain conditions exist in both the indoor and outdoor environments that cause a small percentage of the population to become exposed to dangerous levels of carbon monoxide. Outdoors, concentrations of carbon monoxide are highest near street intersections, in congested traffic, near exhaust gases from internal combustion engines and from industrial sources, and in poorly ventilated areas.[19]
Preventive measures to be taken include avoiding running of any internal combustion engine equipment in an enclosed space such as a closed garage. Also noisy engine often indicate a faulty exhaust system. Check the system and have it repaired if there is a blown-out gasket, loose exhaust manifold, leaking exhaust pipe connections or holes in the muffler, Make sure that fuel-burning equipment is installed by qualified, licensed or trained persons. Such installation should conform to all local codes and standards. Prompt automakers to improve basic engine design and equip automobile with catalytic converters designed to convert carbon monoxide to carbon dioxide. Introduction of more sophisticated converters, plus onboard computers and oxygen sensors to help optimize the efficiency of the catalytic converter and the addition of oxygen-containing compounds to gasoline which has the effect of “leaning out” the air-to-fuel ratio, thereby promoting complete fuel combustion. In the US this typically reduced carbon monoxide emissions upwards of 80 percent,[1][9][19] and it is attainable here in Kano.
To manage the effect of CO havocs, educating the general population, especially those with cardiovascular and respiratory diseases, about the risk of CO exposure, improving monitoring of CO in the workplace and in public places (streets, shops, restaurants, car parks) and government making urgent efforts to improve power generation, since this will reduce people’s dependence on generators for power supply, encouraging the development of better methods for carbon monoxide detection and promotion of the use of carbon monoxide detectors; catalytic converters on automobiles and improved emissions policies will go a long way to make the Kano Metropolis more pleasant to its inhabitants.[13]

References

[1]  Astrid Sigel, Roland K. O. Sigel (2009). Metal-Carbon Bond in Enzymes and Cofactors. Royal Society of Chemistry.
[2]  Nelson, LH (2002). "Carbon Monoxide". Goldfrank's toxicologic emergencies (7th ed.). New York: McGraw-Hill. pp. 1689–1704.
[3]  Marc B, Bouchez-Buvry A, Wepierre JL, Boniol L, Vaquero P, Garnier M (June 2001). "Carbon-monoxide poisoning in young drug addicts due to indoor use of a gasoline-powered generator". Journal of Clinical Forensic Medicine 8 (2): 54–56.
[4]  James Carrick White (1989). Global climate change linkages: acid rain, air quality, and stratospheric ozone. Springer. p. 106.
[5]  Verma, A; Hirsch, D.; Glatt, C.; Ronnett, G.; Snyder, S. (1993). "Carbon monoxide: A putative neural messenger". Science 259 (5093): 381–384.
[6]  Kolata, Gina (1993). "Carbon Monoxide Gas Is Used by Brain Cells As a Neurotransmitter" The New York Times. Retrieved April 12, 2013.
[7]  Li, L; Hsu, A; Moore, P K (2009). "Actions and interactions of nitric oxide, carbon monoxide and hydrogen sulphide in the cardiovascular system and in inflammation--a tale of three gases!" Pharmacology & therapeutics 123 (3): 386–400.
[8]  Goldfrank LR, Flomenbaum NE, Lewin NA, Howland MA, Hoffman RS, Nelson LS, (2002). Goldfrank’s toxicologic emergencies. 7th edition. New York: McGraw-Hill.
[9]  Cobb N, and Etzel R A. (1991) Unintentional carbon monoxide-related deaths in the United States, 1979 through 1988. JAMA ;266:659–63.
[10]  Raub JA, Mathieu-Nolf M, Hampson NB, Thom SR. (2000) Carbon monoxide poisoning—a public health perspective. Toxicology;145:1–14.
[11]  Omaye ST. (2002). "Metabolic modulation of carbon monoxide toxicity". Toxicology 180 (2): 139–150.
[12]  Hardy K R, and Thom S R (1994). "Pathophysiology and treatment of carbon monoxide poisoning". Journal of Toxicology. Clinical Toxicology 32 (6): 613–629.
[13]  Mott J A, Wolfe M I, Alverson C J, Macdonald S C, Bailey C R, Ball L B, (2002). National vehicle emissions policies and practices and declining US carbon monoxide-related mortality. JAMA; ;288:988–95.
[14]  Mah J C. (1998) Non-fire carbon monoxide deaths and injuries associated with the use of consumer produces: annual estimates—1998 annual estimates. Bethesda, MD: US Consumer Product Safety Commission.
[15]  Banjoko, S. O; Olatunde ,O M; Ogunkola, I. O; Mynapelli K C S (2008) Ambient carbon monoxide andcarboxyhaemoglobin levels in Ibadan City, Nigeria: A source of health inequality between developed and developing nations? Journal of Environmental Health Research. Vol 7 (1) London, SE1 8DJ
[16]  Vossberg B, and Skolnick J. (1999) The role of catalytic converters in automobile carbon monoxide poisoning: a case report. Chest ;115:580–1.
[17]  Tikuisis, P; Kane, D M; McLellan, T M; Buick, F; Fairburn, S M (1992). "Rate of formation of carboxyhemoglobin in exercising humans exposed to carbon monoxide". Journal of Applied Physiology 72 (4): 1311–9.
[18]  World Health Organisation (WHO) (2000). Carbon monoxide. WHO Air quality guidelines 2nd edition. WHO Regional office for Europe. Copenhagen.
[19]  World Health Organisation (1999): Carbon monoxide, Environmental Health Criteria 213. Genera: World Health Organisation.
[20]  Ayodele, J .T and Emmanuel, B (2007) Methane in Kano Atmosphere, Caspian Journal of Environmental Science. University of Guilan, I. R, Iran. Vol. 3 No. 2: 133 – 141.
[21]  Ayodele, J .T and Emmanuel, B. (2008) Nitrogen Dioxide in Kano Atmosphere, ChemClass Journal,: Chemical Society of Nigeria, Zaria. Vol., 5, 135 – 143.