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INTERNATIONAL JOURNAL OF ENVIRONMENTAL SCIENCES Volume 5, No 4, 2015 © Copyright by the authors - Licensee IPA- Under Creative Commons license 3.0 Research article ISSN 0976 – 4402 Comparison of particulate matter levels in major urban centres in Eastern Nigeria Ngele, S.O1, Onwu, F.K 2 1- Department of Industrial Chemistry, Ebonyi State University, Abakaliki, Nigeria 2- Department of Chemistry, Michael Okpara University of Agriculture, Umudike, Abia State, Nigeria. [email protected] doi:10.6088/ijes.2014050100071 ABSTRACT This study investigated the particulate matter (PM) load, total suspended particulate matter (TSP) and PM of diameter ≤ ten micrometers (PM10)) in ten urban centres in South-Eastern Nigeria in the dry and wet seasons from December, 2008 to September, 2009 using particulate counter instrument. The results showed that the cities' seasonal mean TSP ranged from103.31±22.26 to1260.25±608.59 and 28.69±4.77 to 555.13±304.57 µg.m- 3 in the dry and wet seasons respectively. The corresponding range for the dry and wet seasonal means of PM10 was 14.38±3.01 to 288.06±129.79 µg.m-3 respectively. Comparatively the cities had PM load in the order: Onitsha > Aba > Umuahia > Owerri > Enugu > Nsukka > Abakaliki > Nnewi > Afikpo > Orlu. Four cities representing 40% of the cities studied namely: Nnewi, Abakaliki, Afikpo and Orlu recorded dry seasonal mean TSP values within the WHO annual guideline limit of 150-230 µgm-3 for combined exposure to TSP and SO2 , while other cities had dry seasonal TSP mean values above the limit. The dry seasonal mean PM10 levels in all the cities exceeded the US annual National Ambient Air Quality Standard (NAAQS) of 50 µg.m-3. The Correlation matrix showed that the TSP seasonal means (dry and wet) correlated positively with that of the PM10 (p<0.05) while the student t-test statistics showed that the dry seasonal means (TSP and PM10) were statistically significant from that of the wet season (p<0.05). The study concluded that recording high values (which exceeded the recommended annual guideline limit) of these pollutants in these cities portends public health risk particularly to people dwelling in the affected cities. Keywords: Ambient air, Environmental pollution, monitoring, particulate matter, SouthEastern Nigeria. 1. Introduction Nigeria presently has neither National ambient air quality standard (NAAQS) nor air monitoring stations for measuring the concentration of pollutants in the ambient air as obtainable in most developed countries. The availability of base line data on regional and national levels is necessary for the establishment of NAAQS and air quality management and control. The paucity of information regarding air quality in major cities in Nigerian environment has attracted researchers’ attention of late. Majority of the previously published works on environmental issues tilted greatly in favour of the water and soil segment of the environment. This development is in line with what the World Bank research group observed, that starting from the lowest level of development, environmental regulation increases steadily with income per capita and follow a characteristic trend of natural resources protection through regulation of water pollution to air pollution control (World bank policy Received on December 2014 Published on January 2015 765 Comparison of particulate matter levels in major urban centres in Eastern Nigeria working paper, 1995). The recent upsurge in the quantum of research in the air environment may stem from increased awareness on the negative consequences of air pollution on public health, biotic and material component of the environment. For instance, air pollution particularly particulate matter has been implicated in the aggravation of respiratory and cardiovascular diseases (philip and Graham, 2005; Norris et al., 1999; Pope, 2000; Samet et al., 2000; Ong et al., 1991), retardation in growth and yield of plants (Prajapati, 2008), reduction in visibility (EPA, 1979; Kim et al., 2006) and deterioration of the physical environment (Ferm et al., 2006). This awareness has been powered more by the globalization of information made possible by the advent of internet communication technology (ICT). Furthermore, researchers assume that as developing countries strive to develop and expand their industries, the developed multinationals shift their production /manufacturing activities to developing economies in search of relatively cheaper labour and less stiff environmental regulations and as a result air pollution is most likely to progressively increase in the developing countries. Air pollution has been simply defined as the presence in the ambient (outdoor) atmosphere of one or more contaminants or combination thereof in such quantities and of such duration as may be or tend to be injurious to humans, plants, property or animal life, or which unreasonably interfere with the comfort of life, property or the conduct of business (US public Health service). Air pollutants include: sulphur oxides, nitrogen oxides, carbon monoxide, gaseous hydrocarbons, dust, smoke, fumes, aerosols (particulates) and radioactive materials. These potential air pollutants are usually present in the atmosphere at low level concentration (background level) and are considered to be harmless but are regarded as pollutants when their levels in atmosphere relatively exceed the background level and hence become harmful (RAO, 1991; Mirslav and Vladimir, 1998). Air pollutants are categorized as primary and secondary. Primary pollutants are those that are emitted directly from the sources while secondary pollutants are those that are formed in the atmosphere by chemical and photochemical interactions among primary pollutants and normal atmospheric constituents (Miroslav and Vladimir, 1998; Sodhi, 2005). The sources of these air pollutants are grouped into natural and anthropogenic sources. Typical natural sources include: volcanoes (SO2, HCl, CO2, dust particles), bog and marshes (H2S), lightning (NOx) and sea spray (sea salts). The anthropogenic sources include: vehicular traffic emissions (CO, SO2, NOx, hydrocarbons), emissions from electric power generation plants (SO2,NOx), volatile organic compounds (VOCs), emissions from agricultural activities and solid waste burning, emissions from bush and forest fires, emissions from mining and quarry activities, emissions from domestic heating and alternative electric power generation during power outages from public power supply (Gomez et al., 2005; EU, 1997; Oluyemi et al., 1994; Fennelly, 1976). Suspended particulate matter is an important source of air pollutant (Miroslav and Vladimir, 1998). It consists of finely divided solids or liquids such as smoke, dust, fumes, mist, smog and sprays (Sodhi, 2005). Particulate matter in the ambient air usually consists of discrete particles ranging in size from molecular clusters of 0.005 µm to coarse particles in the order of 100 µm (Sodhi 2005; Shendell and Naeher, 2002). Processes that emit particulate matter into the atmosphere include: volcanic eruptions, geochemical sources, windblown dust, soil re-suspension, spray from marine sources, power plant emissions, agricultural and industrial emissions, vehicular emissions (Commission of European communities, 2005; Sodhi, 2005; Gomez et al., 2005). In Nigeria, data on ambient air concentration of particulate matter is lacking for many urban cities and scanty for some others, hence the need to monitor it to build baseline data for the south-eastern part of the country. Available data of random sampling by researchers and consultants in some urban centres in the country showed that Ngele, S.O, Onwu, F.K International Journal of Environmental Sciences, Volume 5 No.4, 2015 766 Comparison of particulate matter levels in major urban centres in Eastern Nigeria while some cities such as Lagos, Kano, PortHarcourt, Calabar etc., have PM load above the WHO recommended limit (Olukayode, 2005; Akeredolu, 1989; Koku and Osuntogun, 1999; Ikamaise et al., 2001; Azuka, 1985), other cities such as Abakaliki and Ogoja have PM levels within the limit (Ngele, 2009; Ngele, 2012). This study aims at providing baseline data on the PM levels (TSP andPM10) of ten major cities in south- eastern part of Nigeria. 2. Material and methods 2.1 The study area The study covered two major cities each in Anambra, Enugu, Ebonyi, Abia, Imo (all in south- eastern Nigeria). The area is located within latitudes (4º-6.5º) N and longitudes (5º-9º) E (Microsoft Ecanta, 2007). The area has an approximate population of 16,382,029 according to the 2006 census figure. The climatic condition is tropical, characterized by wet and dry seasons. The wet season sets in between April and October while the dry season is usually between November and March (Strachler and Strahler, 1977) Table 1: Sampling Location, Name and GPS Coordinates S/No 1 City Aba Site Name Osisioma junction 2 Umuahia Gate / Warri Street 3 Nnewi Izuchukwu junction 4 Onitsha Upper Iweka 5 Abakaliki Akanu Ibiam Roundabout 6 Afikpo Eke Market 7 Enugu 8 Nsukka Chris Chemist/Ogbete market Junction Peace Mass Park, Nsukka 9 Orlu 10 Owerri Owerri Road / International Market junction Govt House / Modotel Junction Coordinates N050 07.051 E0070 19.811 N050 32.061 E0070 29.651 N060 01.101 E0060 55.091 N060 08.041 E0060 47.481 N060 18.581 E0080 05.411 N050 52.961 E0070 56.181 N060 26.321 E0070 29.241 N060 50.921 E0070 23.901 N050 47.331 E0070 01.901 N050 30.541 E0070 02.181 2.2 Sampling site selection In each of the States, two major cities were selected for study. The cities studied were Abakaliki and Afikpo (Ebonyi State), Enugu and Nsukka (Enugu State), Onitsha and Nnewi (Anambra State), Owerri and Orlu (Imo State), Umuahia and Aba (Abia State). In each of the cities, a site was chosen in the ‘heart’ of the city based on visible human activities, high population density and traffic volume. The coordinates of each site was measured with Garmin global position system, model etrex H (Taiwan). Ngele, S.O, Onwu, F.K International Journal of Environmental Sciences, Volume 5 No.4, 2015 767 Comparison of particulate matter levels in major urban centres in Eastern Nigeria 2.3 Monitoring protocol The suspended particulate matter (SPM) concentration in the ambient air of the monitored sites was determined by means of a digital read out photometric -laser particle counter, Aerocet Model 531-9800 Rev. C (Metone Inc. U.S.A.). The instrument has in-built particle count data for eight different particle size ranges including total suspended particulate (TSP), PM10, PM2.5 and proprietary algorithm to derive the mass concentration for particulate sampled. The sampler was held at a height of 2 m above ground level, human breathing zone (EC, 2005) and the ambient air PM concentration reading recorded as displayed on the instrument's screen. Sampling time for each parameter was two minutes (that is time taken from switch on of parameter nub to display of reading on the screen). The frequency of the monitoring was such that a site was monitored one day in a week for twelve hours (6.00 am6.00 pm) at an interval of thirty minutes for four months (16 weeks) in the dry season, December, 2008 to March, 2009 and four months in the wet season, June-September, 2009. The hourly mean level for the twelve hours per day per week of each parameter was averaged and the mean for the 16 weeks computed to obtain the seasonal mean for the parameters using statistical package for social science (SPSS) software, version 17. Invernizi et al., 2011, had earlier reported the use of the Aerocet-531 instrument in the measurement of black carbon concentration (of the following PM sizes: PM10, PM2.5 and PM1) as an indicator of air quality benefits of traffic restriction policies within the ecopass zone in Milan, Italy 3. Result and Conclusion The results of the TSP and PM10 concentrations and their computed seasonal means are presented in Tables 2 and 3 and their seasonal variations depicted in Figs. 1A and 2A, while their trends across the cities within the period of the study are shown in Figs. 1B, 1C and 2B, 2C. Figure 1A: Variations of TSP concentrations in Ambient Air between the dry and wet seasons across cities in South-Eastern Nigeria. Ngele, S.O, Onwu, F.K International Journal of Environmental Sciences, Volume 5 No.4, 2015 768 Comparison of particulate matter levels in major urban centres in Eastern Nigeria Figure 1B: Comparison of Dry Season TSP concentration within the months of Dec. 2008 to March 2009. Figure 1C: Comparison of Wet Season TSP concentration within the months of June – September, 2009. Table 2: Weekly levels and seasonal mean TSP (µg m-3) in dry and wet seasons in the cities monitored Week 1 2 3 4 5 6 7 8 9 10 ABA D W 704 180 721 186 924 185 960 121 1786 156 1088 63 829 84 913 103 692 86 652 97 UMU D W 446 114 476 126 517 106 1006 86 1551 100 1314 70 422 55 476 80 517 68 421 90 NNEWI D W 142 60 126 55 134 38 127 25 162 67 141 60 156 54 133 26 141 80 128 70 ONITSHA D W 1271 581 1211 627 1200 608 2379 781 2408 779 2244 813 1564 981 1034 841 1126 801 1231 807 Ngele, S.O, Onwu, F.K International Journal of Environmental Sciences, Volume 5 No.4, 2015 ABAKALIKI D W 211 121 179 89 182 124 400 76 377 86 364 40 257 46 120 48 140 50 150 45 769 Comparison of particulate matter levels in major urban centres in Eastern Nigeria 11 12 13 14 15 16 x S 1036 101 463 76 104 61 1028 510 132 28 840 80 385 60 96 49 960 136 100 54 345 112 426 43 73 50 641 121 150 21 385 68 345 53 81 60 437 141 96 65 312 75 107 50 76 62 556 229 120 56 318 118 186 44 99 58 874 126 98 52 781.56 113.44 566.13 76.31 119.94 54.69 1260.25 555.13 192.25 62.56 370.61 41.69 388.79 25.62 28.14 14.73 608.59 304.57 102.84 29.71 Table 2 Continued Week 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 x S AFIKPO D W 101 40 115 42 96 45 120 50 150 52 130 41 124 43 102 32 122 37 98 22 86 25 64 30 75 36 97 33 88 34 85 32 103.31 37.13 22.26 8.32 ENUGU D W 550 120 560 160 427 122 533 150 450 108 315 104 325 102 307 121 146 133 130 50 180 40 150 42 120 46 150 37 130 22 140 30 288.31 86.69 167.46 46.97 NSUK D W 201 53 221 60 302 70 365 46 249 170 280 86 267 109 239 120 206 42 246 53 224 42 326 60 208 40 156 36 127 38 121 46 233.63 66.94 66.82 37.15 ORLU D W 150 32 160 30 165 32 172 37 180 35 216 25 165 30 157 24 148 28 146 32 140 20 130 25 125 30 105 32 100 25 108 22 147.94 28.69 30.23 4.77 OWERRI D W 290 50 308 45 296 38 314 37 360 40 380 35 443 36 460 40 413 42 390 35 313 45 321 30 296 30 240 28 248 28 236 30 331.75 36.81 69.37 6.63 Foot note: D = Dry Season; W = Wet season, x = mean and S = Standard deviation. Figure 2A: Variations of PM10 concentrations in Ambient Air between the dry and wet seasons across cities in South-Eastern Nigeria Ngele, S.O, Onwu, F.K International Journal of Environmental Sciences, Volume 5 No.4, 2015 770 Comparison of particulate matter levels in major urban centres in Eastern Nigeria Figure 2B: Comparison of Dry Season PM10 concentration within the months of Dec. 2008 to March 2009 Figure 2C: Comparison of Wet Season PM10 concentration within the months of June – September, 2009 Table 3: Weekly levels and seasonal mean PM10 (µg m-3) in dry and wet seasons in the cities monitored Week 1 2 3 4 5 6 7 8 9 ABA D W 604 106 678 124 727 117 711 121 901 107 975 106 811 120 846 100 684 90 UMUAHIA D W 376 120 481 134 810 106 840 100 889 90 720 60 911 80 387 60 312 70 NNEWI D W 106 44 122 51 87 24 98 30 96 31 89 34 96 29 78 30 73 28 ONITSHA D W 1320 427 1460 408 1600 419 1433 400 1283 383 1109 375 1175 364 1086 208 1101 276 ABAKALIKI D W 107 82 100 73 148 76 155 68 158 48 147 41 123 64 126 60 128 58 Ngele, S.O, Onwu, F.K International Journal of Environmental Sciences, Volume 5 No.4, 2015 771 Comparison of particulate matter levels in major urban centres in Eastern Nigeria 10 11 12 13 14 15 16 x S 637 580 564 498 367 470 335 649.25 181.47 83 83 87 79 75 89 66 97.06 18.04 354 287 248 172 180 243 271 467.56 269.08 75 66 60 51 85 72 53 80.13 24.32 78 76 80 70 74 63 64 84.38 16.03 25 24 28 26 25 23 21 29.56 7.87 896 235 120 982 211 115 960 136 106 96 121 112 88 101 82 81 98 120 81 95 117 921.34 266.06 122.75 532.60 129.79 20.78 45 41 40 39 38 36 29 52.38 16.36 Table 3 Continued Week 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 x S AFIKPO D W 128 60 100 64 136 61 140 58 142 54 152 50 102 52 96 48 95 47 90 42 84 38 76 29 72 32 70 24 56 25 52 21 99.44 44.06 31.67 14.29 ENUGU D W 247 46 253 48 270 48 308 60 309 51 233 40 207 42 362 30 172 29 162 30 108 20 107 18 152 20 90 18 75 16 96 18 196.94 33.38 89.77 14.46 NSUKKA D W 170 60 200 71 206 80 220 68 200 62 210 65 286 60 301 40 254 36 100 32 100 30 120 42 190 28 180 27 110 23 146 21 187.06 46.56 61.75 19.51 ORLU D W 105 12 100 10 120 14 102 14 120 18 90 15 88 12 86 18 86 14 80 15 80 12 60 20 70 18 68 16 80 10 86 12 88.81 14.38 17.09 3.01 OWERRI D W 110 120 121 100 136 102 160 102 158 101 171 90 280 83 310 86 323 82 286 76 260 85 277 75 240 98 236 90 285 85 244 78 224.81 90.81 70.90 12.13 The highest dry and wet seasonal mean TSP concentrations of 1260.25±608.59 and 555.13±304.37 µg.m-3 were recorded in Onitsha Urban, while the least values of 103.31±22.26 and 37.13±8.32 µg.m-3 and 119.94±28.14 and 54.69±14.73 µg.m-3 were recorded at Afikpo and Nnewi urbans respectively (Table 2). It can be seen from the results of TSP that urban areas that are relatively larger in size, higher in traffic volume, population density and built-up areas (Onitsha, Aba, Umuahia, Owerri and Enugu) ranked higher in their TSP levels whereas the smaller cities (Orlu, Afikpo and Nnewi) trail behind. This is in agreement with similar study which reported higher TSP values in Lagos, Nigeria relative to less urbanized city of Ile-Ife, south-west Nigeria (Ikamaise et al, 2001). The general (with few irregularities) dry season trends of the TSP levels across the cities within the period of the study showed gradual rise within the first eight weeks with the peaking in the fourth to sixth week followed by dipping from tenth week (Fig. 1B). The peaking of the TSP in this study corresponds with the peak of harmattan (usually between the middle of December to January ending in the south-east Nigeria) characterized by high levels of dust in the ambient air due to the dust laden south-east trade wind from the sahara desert that prevails within this period. Similarly, in the wet season, the TSP presented higher levels in the first four weeks (June) (Fig. 1C) corresponding to the commencement of Ngele, S.O, Onwu, F.K International Journal of Environmental Sciences, Volume 5 No.4, 2015 772 Comparison of particulate matter levels in major urban centres in Eastern Nigeria the rainy season and dipping afterwards as the rainy season deepens due to wet precipitation. The levels of TSP obtained in this study (in most of the cities) were generally above those recorded in European countries (European Commission, 1997) but within those reported in Pakistan (JICA/PAKEPA Report, 2002; Masfin, 2005) but below that reported for Lagos, Nigeria (koku and osuntogun, 2007; Akeredolu et al., 2004). Onitsha also recorded the highest seasonal mean PM10 values of 921.34±532.60 and 266.08±129.79 µg.m-3 during the dry and wet seasons respectively while the least seasonal mean values were obtained in Nnewi and Orlu for the dry and wet seasons respectively (Table 3). The trends of the PM10 (Figs. 2B and 2C) during the study period across the cities were similar to that exhibited by the TSP. The dry and wet seasonal levels of PM10 correlates significantly with TSP (P< 0.05) in all the cities monitored while the student t-test statistics showed significant difference between the dry and wet seasonal mean level across the cities (p<0.05). The PM10 seasonal mean in all the cities (except Orlu in the wet season) exceeded the WHO annual average guideline value of 20 µg.m-3. The seasonal mean range of PM10 in this study (14.38±3.01921.34±532.60 µg.m-3) was above the values reported for various European Countries (European Commission Report, 1997) and 170-260 µg.m-3 reported in Calabar, Cross River State, Nigeria (Abam and Unachukwu, 2009) but were within the 24-hour mean levels of 149-340 µg.m-3 reported for cities in Pakistan with the exceptions of Onitsha, Aba and Umuahia (JICA/PAKEPA Report, 2002). It can be concluded that within the period of the study, Onitsha urban relative to other cities studied had the highest ambient air level of the coarse particulate. It is noteworthy that greater percentage of the cities studied had particulate matter load that were above the guideline limit and this calls for concern in view of the human health risk associated with particulate matter pollution. 4. References 1. 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