Analysis of Potentially Toxic Metals in Airborne Cement Dust Around Sagamu, Southwestern Nigeria
This study analyzed the concentration levels of potentially toxic and harmful elements contained in the airborne cement dust generated in the vicinity and farther away 500 m in the conventional four cardinal directions from the West African Portland Cement Company (WAPCO) factory mill, Sagamu. The results indicated that the concentration range of these toxic elements fall between 40.0 and 280,000 μg g1 in the cement dust samples. Also, the concentration range of these toxic elements in 1 L of air samples varies between 0.01 μg g1 and 29.92 μg L1. The results generally show elevated concentrations of all the elements when compared with USA threshold limit of particulate metal concentration (e.g., Pb (1.5 g m3); Cd (0.004-0.026 g m3) in the air. These elements in the airborne cement dusts may pose a great threat to the health of plants, animals and residents in and around the factory and also to workers and visitors to the factory.
Cement production is characterized by particulate air pollutant and essentially dust. Aina (1990) observed that 80% of atmospheric pollution comes from industrial emission in which cement and steel factories are more pervasive. It has also been observed that out of the 360 pounds/ton of cement produced, majority of them are from cement kiln. Besides, cement dusts are produced during blasting of raw materials, grinding of cement clinker and packaging or loading of finished cement (Bankole, 2003). Dusts according to Fenelly (1975) have wide range of sizes, usually less than 30 mm in diameter and varied in chemistry. Unlike dust from acidic rock quarries which are relatively inert, dust from the limestone according to Everest (1980) are highly alkaline with pH varying between 6.0 and 12.0 (Cawse et al., 1989; Arslan and BoyBay, 1990) and also contain metal constituents that have direct toxic effect (Darley, 1966). Some of the numerous components of cement dust include alumina, silica, polychlorinated dioxins and furans, mercury, antimony, cadmium, lead, zinc, chromium, arsenic and manganese (NPI, 1991). Majority of these constituents are Potentially Harmful Elements (PHEs) to the biotic components of the environment. Despite these adverse effects, cement is widely used in building and construction works as a key ingredient in concrete products. It is a binding agent that holds sand and other aggregates together in a hard stone like mass. Portland cement accounts for about 95% of the cement produced in North America. It is also, together with blended cement, the most commonly used cement in Nigeria. Production of Portland cement requires primary raw materials like limestone, chalk, cement rock and corals; secondary materials like shale, clays, sand and siltstones. Other required materials include iron ore, bauxite, fly ash and red alluvium. Production of cement is achieved by wet processing method. This study investigate the concentration levels of potentially harmful toxic metals in the air and cement dust generated in the vicinity and farther away (i.e., 500 m) in the four cardinal directions from the West African Portland Cement (WAPCO) mill, Sagamu area of southwestern Nigeria. From the results the pollution indices of these metals are determined and mitigation measures are suggested.
MATERIALS AND METHODS
The study area: Sagamu, the third largest settlement in Ogun state after
Abeokuta and Ijebu Ode, is located within latitude 6°50' and 7°00' N
and longitude 3°45' and 4°00' E. Sagamu works, the second works of WAPCO
where this study was carried out is strategically located within the system
of urban centers. It is 63 km southeast of Abeokuta, 72 km southeast of Ibadan,
67 km northwest of Lagos and 32 km west of Ijebu ode. The area stands on a low-lying
gently undulating terrain with altitude ranging between 30 and 61 m above sea
level. The area is characterized by high annual temperature, high rainfall,
high evapotranspiration and high relative humidity which makes it to be classified
as humid tropical region (Iloeje, 1981; Oguntoyinbo et al., 1983; Akanni
in Onakomaya, 1992).
Geological setting: According to Kehinde-Phillips (1992), geology of Ogun state in which sagamu - the study area is a part, comprises of sedimentary rocks which underlie approximately three-quarters of the whole surface area of the state stretching from the northwest to the southeast and Basement complex rocks which underlie the remaining one-quarter of the surface of the state. The basement complex according to Jones and Hockey (1964) is made up of magmatite-gneiss complex, the schist belt and the older granites which are 800 to 500 million years in age (Hurley et al., 1967). These rocks are well displayed in Odeda, Abeokuta, Igbo-ora, Ijebu Igbo etc. The sedimentary rocks of Ogun state consist of Abeokuta formation (Rayment, 1965; Adegoke, 1969) later known as Abeokuta group-consisting of Ise Formation, Afowo formation and Araromi formation (Omatsola and Adegoke, 1981). The Abeokuta group which is Neocomian to Maastrichtian in age is overlain by Ewekoro formation which is Paleocene in age and Ilaro formation of Eocene age. Ewekoro formation is highly fossiliferous and consists of economic deposits of limestone that is presently quarried by WAPCO in Ewekoro and Sagamu, respectively.
Field sampling techniques: A total of thirty six (36) dust and air
samples collected at interval of 100m from the mill (i.e., 0.0 m) using air
sampler disc mounted with 4.5 micron filter paper were analyzed in this study.
The air sampler was used to sample the dust in the air at different points (i.e.,
100, 200, 300 and 500 m) from the mill, which serve as the reference point (i.e.,
0.0 m) along each of the cardinal points (i.e., east, west, south and north).
The dust from the air was sucked into a 4.5 microns filter paper placed in a
disc having an air inlet attached to a battery controlled air pump. The sampling
of the air was carried out on a height of 1.5 m above the ground for a period
of 2 hrs at each point. The airflow rate at each point of sampling was recorded.
Each filter paper on which the air dust particles were collected was stored
into a sampling disc at the site and taken to laboratory for analysis. Dust
samples collected at intervals of 100, 200, 300 and 500 m in each of the four
cardinal points from the mills over a period of four months was also analyzed
to compliment the air sample results.
Laboratory analysis: Each filter paper containing the dust particulates were measured and from the weight obtained the initial weights of the filter papers were deducted in order to obtain the weight of dust collected from each point. Each filter paper was digested along with the dust on it using concentrated nitric acid and distilled water at a ratio 1:2 (i.e., 15 mL of acid to 10 mL of water) in a conical flask and placed on a heating mantle. The resultant solutions were made up to the 50 mL mark in a volumetric flask. A blank digestion was also carried out as a check. The digested samples were analyzed for the arsenic (As), cadmium (Cd), cobalt (Co), lead (Pb), aluminium (Al), iron (Fe), zinc (Zn) and chromium (Cr) using Atomic Absorption Spectrometer (AAS).
Data interpretation: The data obtained from the chemical analysis were subjected to statistical treatment using correlation coefficient matrices. This was carried out in order to establish element association and probable source of dispersion or pollution. From the data was deduced concentration ranges of the elements; their mean concentrations and standard deviations were also calculated. Besides, the clustered bar charts were produced to show the elemental concentration in both the air and the dust and also Pollution Index (PI) was calculated for each toxic pollutant in order to determine their load in air and dust media and their potential hazards.
RESULTS AND DISCUSSION
The data (Table 1 and 2) show a considerable
abundance of the toxic metals at the cement works and its surrounding environments.
However, it was discovered that the concentrations of all the metals are higher
at the 500 m locations than at the 100 m locations especially in the southern
and western directions of the mills. This probably implies that resident time
and mobility of the metals in the air would have resulted into the metals settling
down at distances further away from the main source. Thus, the farther the distance
the higher the deposition. Besides, the higher concentration of elements recorded
in both the western and southern directions of the reference point (i.e., the
mill) can also be attributed to the presence of the quarry at the southern end
and production activities in the western part of the mill which invariably have
increased the quantity of the dusts and also elemental concentrations at these
|| Elemental concentrations of metals from dust samples
|W-West, S-South , E-East and N-North
|| Elemental concentrations of metals from air samples
|W-West, S-South, E-East and N-North
||Statistical parameters for elemental concentrations of metals
in dust samples
||Statistical parameters for elemental concentrations of metals
in 1 L of air samples
Simple descriptive statistical analysis of elemental concentrations of metals
in the dust samples indicates the highest mean concentrations for arsenic (27614.41
μg L1) followed by aluminium (7, 265.40 μg L1)
and also least for chromium (221.24 μg L1) (Table
3). The same analysis for 1 L of air samples recorded the highest mean concentration
for arsenic (3.97 μg L1) followed by chromium (2.38 μg
L1) and least for iron (0.13 μg L1) (Table
Further statistical analysis indicated a very strong correlation between the
elements analyzed in the samples from the study area. Table 5
shows a positive relationship between almost all the metals except zinc, which
shows a negative relationship with arsenic, cobalt and chromium. The relationship
between the metals in the dust samples is most significant at the level of 0.01
(i.e., p>0.01) while correlation between zinc and aluminium is only significant
at the level of 0.02 (i.e., p>0.02). The same pattern of relationship between
the metals in the dust samples was also observed in the air samples (Table
6) except that in addition, zinc shows a negative relationship with calcium
in the air sample medium. Also, the correlation between the metals in the air
samples is only and very strongly significant at the level of 0.01 (i.e., p>0.01).
Both cobalt and chromium show very strong significant relationship at a level
of 0.01 (i.e., p>0.01) with all the metals except zinc. Also, very strong
and significant correlation exists between nearly all the elements analyzed
and calcium which is one of the main components of cement. However, the situation
is not the same with iron which shows a weak correlation (i.e., p>0.082)
and a very weak correlation (i.e., p>0.81) with calcium and also zinc which
shows a very weak correlation (i.e., p>0.24) and (p>0.73) with calcium
in both the dust samples and air samples, respectively.
|| Correlation coefficient matrix of analyzed elements In the
|**Correlation is significant at the 0.01 level; *Correlation
is significant at the 0.05 level
|| Correlation Coefficient Matrix of Analyzed Elements In the
|** Correlation is significant at the 0.01 level
||Clustered chart of mean element concentration of dust smaple
This implies that all other elements are from the same source (i.e., cement
dust). Since iron and zinc gives a very strong correlation (i.e., p>0.00)
with one another in both the dust and air samples, it then suggests that they
are from the same source. The strong correlation between iron and aluminium
(p>0.003 and p>0.007), zinc and aluminium (p>0.02 and p>0.05) in
dust and air samples could be as a result of contamination from the precipitator
stack due to rust. Generally, the values obtained from the study site far exceed
the stipulated standard of PM 2.5 (particulate matter less than 2.5 μm
in diameter) for personal exposure (CARB, 2002) and also exceed personal exposure
levels for PM in Alberta (Norman, 2002). The clustered bar charts (Fig.
1 and 2) confirm the trending pattern of high concentration
of the elements in both the dust and air samples along the southern and western
directions of the cement mill.
||Clustered chart of mean element concentration of air smaple
Also, the pollution index employed in this study defines the extent or degree
of pollution of the toxic elements in air and dust collected from the study
area. It is calculated using the ratio of average elemental concentration in
air or dust to the standard of element in air. The pollution indices less than
2 (i.e., PI<2) in this study are considered not significant while those above
2 (i.e., PI>2) are significant. The charts of pollution indices (Fig.
3) for the study area indicate lead (Pb) as the greatest pollutant in all
the four directions followed by arsenic (As) in the air and dust along the southern
and western directions. Similarly, cobalt (Co) is relatively pronounced in the
air and dust collected in the northern and eastern directions.
The health effect of toxic metals in air and dust from cement factory on human is better appreciated if one consider the fact that an active person typically inhales 10, 000 to 20, 000 L of air daily (i.e., 7 to 14 L per min). This intake increases with vigorous exercise (Derek, 1996).
|| Pollution indices for toxic element in air and dust samples
from the study area
As air is taken into body so also are the particulate and gaseous pollutants. During the inhalation and exhalation, these pollutants can inflame, sensitize and even scar the lungs and tissues. The pollutants may enter the numerous tiny air sacs deep inside the lungs and also the blood stream thereby affecting several other organs than lung. These elevated concentrations of arsenic, cadmium, chromium, cobalt and lead in both southern and western part of the mill may account for more health problems among the inhabitants of the communities in these two wind directions than those in the northern and eastern portion of the mill where the concentration of these metals are low in the airborne dust. Many of the possible serious health problems of these airborne dust pollutants on human include asthma, irritation of the lungs, bronchitis, cancer, pneumonia, decreased resistance to respiratory and early death (EPA, 2001).
Apart from the direct health problem on man, adverse effect of airborne dust pollutant on the ecosystem in general are ozone layer depletion, green house effects and acid rain (Mellanby, 1988). Specifically, dust from cement factory adversely affect the forest ecosystem, soil enzyme, fungi and bacteria population within the vicinity of the factory (Khosla and Parmer, 1988). It increases the soil pH and sulphur and also affect phosphorous quantity and behaviour thereby affecting seed germination. Dust from cement factories according to Amira (2002) is capable of changing salt content of water hence seriously disrupting aquatic communities and also decrease quality of water used for drinking and irrigation purpose. Cement dust is capable of increasing water turbidity and reducing light penetration. It can also result in deficiency of certain minerals and environmental factors like extreme water hardness or elevation of carbon dioxide which will give rise to other pathological conditions (Landolt, 1975). Sree Rangaswani et al. (1973) observed that deposition of cement dust on herbaceous plants and fruit crops can cause effects that range from blocked stomata, reduced number of plant leaf and injury to complete reduction in vegetative growth and reproductive structures.
CONCLUSIONS AND RECOMMENDATION
This study has shown that there is significant emissions of airborne pollutant into the environment around WAPCO works Sagamu, up to 500 m distances from the mill in the four cardinal directions. This emission is capable of posing a serious health risk to workers and residents even at a distance of 500 m away from the mill. Besides, the presence in high concentrations of these toxic metals in the generated cement dusts are indicators of possible lethal effect on both the terrestrial and aquatic habitat with resultant negative impact on all the living organisms. The emitted cement dust can also affect soil property and quality of water resources in the study area. However, the use of electric precipitator for dust removal and recycling is recommended. Compliance with the new standard of 20 mg m3 and proper monitoring of air emission of cement dust in the area will help in reducing the impact of airborne pollutant on the environment. Use of safety wears in workplace and premises of the factory to ensure the good health of the workers and factory visitors is advocated.
Adegoke, O.S., 1969. Eocene stratigraphy of Southern Nigeria. Bureau Recherches Geologiques Minieres Mem., 3: 23-48.
Aina, E.O., 1990. Halting industrial pollution in Nigeria, Which way? FEPA Monograph, 2: 15-15.
Akanni, C.O., 1992. Climate. In: Ogun State in Maps, Onakomaya, S.O., K. Oyesiku and J. Jegede (Eds.). Rex Charles Publisher, Ibadan, pp: 187.
Amira, J.O., 2002. The environmental effects of limestone mining and cement dust on sagamu metropolis. M.Sc. Thesis, University of Ado-Ekiti, pp: 125.
Arslan, M. and M. BoyBay, 1990. A study on the characterization of dust fall. Atmos. Envrion., 24: 2667-2671.
Bankole, O.D., 2003. Assessment of particulate air pollutants from cement factory dust (A case study of WAPCO, Sagamu works). B.Sc. Thesis, University of Agriculture, Abeokuta, pp: 52.
Cawse, P.A., S.J. Baker and R.A. Page, 1984. The influence of particulate matter and rainwater acidity and chemical composition. UK Atomic Energy Authority Report R13478, HMSO, London.
Darley, E.F., 1966. Studies on the effect of cement-kiln dust on vegetation. J. Air Pollut. Centre Associ., 16: 145-150.
CrossRef | Direct Link |
Derek, E., 1996. Managing Urban Air Quality. Earthscan Publications Ltd., London, pp: 30-52.
Environmental Protection Agency (EPA), 2001. Office of air and radiation manual. Physician for Social Responsibility, USA Air Quality, pp: 51-60.
Everest, K.R., 1980. Distribution and Properties of road dust along the northern portion of the haul road. Environmental Engineering and Ecological Baseline Investigations along the Yukon River. Research Engineering Lab; CRREL, Report 80-99, pp: 101.
Fenelly, P.F., 1975. Primary and secondary particulates as pollutants. J. Air Poll. Contr. Ass., 25: 697-704.
Hurley, P.M. and J.R. Rank, 1967. Test of continental drift by comparison of radiometric ages. Science, 157: 495-500.
Iloeje, N.P., 1981. A New Geography of Nigeria. Longman, Nigeria, pp: 201.
Jones, C.A. and H.A. Hockey, 1964. Geology of part of South Western Nigeria. GSN Bull., 31: 63-72.
Khosla, P.K. and Y.S. Parmer, 1988. Effect of particulate air pollution on shorea robusta forest ecosystem. pp: 1-3
Landolt, M.L., 1975. Visceral Granuloma and Nephrocalcinosis of Trout. In: The Pathology of Fishes, Ribelin, W.R. and G. Mighki (Eds.). University of Wisconson Press, Madison Wis., pp: 793-801.
Mellanby, K., 1988. Air pollution, acid rain and the environment. The WATT Committee on Energy Report, No. 18, pp: 129.
National Pollutant Inventory (NPI), 1991. Emission estimation technique manual for cement manufacturing. pp: 1-5.
Norman, A.L., 2002. Air quality downwind of sour gas flaring and processing operations west of calgary, alberta, Canada. Medical Geology Newsletter, No.
Oguntoyinbo, J.S., O.O. Areola and M. Filani, 1983. A Geography of Nigeria Development. 2nd Edn., Heinemann Education Books Nigeria Ltd., Nigeria, pp: 456.
Omatsola, M.E. and O.S. Adegoke, 1981. Tectonic evolution and cretaceous stratigraphy of the Dahomey basin. J. Min. Geol., 18: 130-137.
Oyesiku, O.O., 1992. Ogun State in Maps. Rex Charles Publishers, Ibadan, pp: 187.
Rayment, R.A., 1965. Aspect of the geology of Nigeria. Ibadan University Press, Tehran, pp: 145.
Sree, S.R., C. Padmanghan, R. Jambulingar and M. Gurunathan, 1973. Effect of cement on plant ecotypes. Madras Agric. J., 60: 1766-1770.