Comparative%20Assessment%20of%20Soils%20in%20Automobile%20Repair%20and%20Non-Automobile%20Repair%20Sites%20in%20Abakaliki,%20Southeastern%20Nigeria%20By%20Njoku,%20C.%20and%20Ngene,%20P.N.%20Department%20of%20Soil%20Science%20and%20Environmental%20Management,%20Ebonyi%20State%20University,%20P.M.B.%20053, - PowerPoint PPT Presentation

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Comparative%20Assessment%20of%20Soils%20in%20Automobile%20Repair%20and%20Non-Automobile%20Repair%20Sites%20in%20Abakaliki,%20Southeastern%20Nigeria%20By%20Njoku,%20C.%20and%20Ngene,%20P.N.%20Department%20of%20Soil%20Science%20and%20Environmental%20Management,%20Ebonyi%20State%20University,%20P.M.B.%20053,

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... obvious since the soil is contaminated with automobile fuels that are composed of hydrocarbon and PAHs (Atlas, 1981; McMurry, 2000; Clayden and Greeves 2001). – PowerPoint PPT presentation

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Title: Comparative%20Assessment%20of%20Soils%20in%20Automobile%20Repair%20and%20Non-Automobile%20Repair%20Sites%20in%20Abakaliki,%20Southeastern%20Nigeria%20By%20Njoku,%20C.%20and%20Ngene,%20P.N.%20Department%20of%20Soil%20Science%20and%20Environmental%20Management,%20Ebonyi%20State%20University,%20P.M.B.%20053,


1
Comparative Assessment of Soils in Automobile
Repair and Non-Automobile Repair Sites in
Abakaliki, Southeastern NigeriaByNjoku, C.
and Ngene, P.N.Department of Soil Science and
Environmental Management, Ebonyi State
University, P.M.B. 053, Abakaliki, Nigeria
2
ABSTRACT
  • An experiment was conducted at automobile repair
    and non-automobile repair sites in Abakaliki to
    compare the selected chemical properties of soils
    of automobile repair and non-automobile repair
    sites.
  • A survey of the study area was carried out and
    automobile repair and non-automobile repair sites
    were selected.
  • Five replicates soil samples each were collected
    at 0 30 cm depth in each sites.
  • Data collected were analysed using standard error
    of the mean.
  • Results of the study showed that automobile
    repair site recorded higher total organic carbon,
    C/N ratio and total exchangeable acidity than
    non-automobile repair site.
  • On the other hand, lower pH, total N, available
    P, Ca, Mg, K, Na, total exchangeable bases,
    effective cation exchangeable capacity and base
    saturation were observed in automobile repair
    site than non-automobile repair site.
  • Soils of automobile repair sites are not good for
    crop production since they are low in plant
    nutrients

3
Key Words
  • Automobile repair site
  • Oil
  • Plant nutrient
  • Soil
  • Wastes

4
Aims
  • The aim of this study is to compare the selected
    chemical properties of soils of automobile repair
    and non-automobile repair sites in Abakaliki,
    southeastern Nigeria.

5
Materials and Methods
  • Site description and soil sampling
  • Laboratory Analysis
  • Data Analysis

6
Site Description and Soil Sampling
  • Ten automobile repair sites spreading within
    Abakaliki metropolis were surveyed and the
    automobile repair site at Ogoja road, opposite
    Abakaliki rice mill and adjacent College of
    Agricultural Science, Ebonyi State University was
    selected.
  • This site is a major and the biggest automobile
    repair site in Abakaliki.
  • An arable land at Ebonyi State University,
    Faculty of Agriculture and Natural Resources
    Management Research Farm was used as
    non-automobile repair sites.
  • Abakaliki lies at latitude 6o 19 N and longitude
    8o 06 E in the derived savannah of the southeast
    agro-ecological zone of Nigeria.
  • It has a mean annual rainfall of 1700 1800 mm.
  • The rainfall pattern is bimodal between April
    July and September November with short spell in
    August.
  • According to Ofomata (1975) the minimum and
    maximum temperatures of the area are 27oC and
    31oC respectively.
  • The relative humidity of the area is between 60
    80. The soil belongs to the order Ultisol and is
    classified as Typic Haplustult (FDALR, 1985).
  • Soil samples were obtained in five replicates at
    each site at depths of 0 to 30 cm using soil
    auger. Each sample was immediately placed in a
    fresh plastic bag and tightly sealed. All the
    samples were transported to the laboratory where
    on arrival, analytical procedure commenced in
    earnest.

7
Laboratory Analysis
  • The pH of the soil was determined using a
    suspension of soil and distilled water in the
    ratio of 25 soil water (McLean, 1982).
  • Total nitrogen was determined using modified
    kjeldahl digestion procedure (Bremmer and
    Mulvaney, 1982).
  • Organic carbon was determined by the method of
    Nelson and Sommers (1982).
  • Available phosphorus was determined by Bray 11
    method (Olsen and Sommers, 1982).
  • Exchangeable bases were determined using Chapman
    (1982) method.
  • Exchangeable acidity was determined by the
    titration method (Juo, 1979).
  • Effective cation exchange capacity and base
    saturation were determined by the summation and
    calculation, respectively (Njoku and Mbah (2012)

8
Data Analysis
  • Statistical analysis of the data was carried out
    using standard error of the mean (Steel and
    Torrie, 1980).

9
Result and Discussion
  • The results of selected chemical properties of
    soils of automobile repair and non-automobile
    repair sites are presented in table 1.

10
  • Table 1 Selected chemical properties of soils of
    automobile repair and non-automobile repair sites
  • Parameter Automobile Repair site
    Non-automobile Repair site
  • pH (H2O) 4.310.011
    5.960.005
  • Organic Carbon () 1.950.015
    0.940.020
  • Total Nitrogen () 0.150.017
    0.170.011
  • C/N Ratio 13.000.012
    5.230.003
  • Available P (mgkg-1) 7.080.05
    10.260.015
  • Ca (cmol()kg-1) 4.640.005
    5.070.005
  • Mg (cmol()kg-1) 1.560.017
    3.710.017
  • K (cmol()kg-1) 0.110.005
    0.180.003
  • Na (cmol()kg-1) 0.180.009
    0.250.013
  • TEA (cmol()kg-1) 1.390.006
    1.220.012
  • TEB (cmol()kg-1) 6.490.013
    9.210.014
  • ECEC (cmol()kg-1) 7.880.003
    10.430.011
  • BS () 82.36 0.011
    88.300.006

11
pH
  • Automobile repair site recorded the lower pH
    value of 4.31.
  • This observed pH value in automobile repair site
    was lower than that of non-automobile repair site
    by 28.
  • This lower pH observed in automobile repair site
    than non-automobile repair site may be as a
    result of acidic automobile wastes that entered
    the soil and increasing its acidity.

12
Organic Carbon and C/N Ratio
  • On the other hand, higher organic carbon, and C/N
    ratio were recorded in automobile repair site
    than non-automobile repair site.
  • These higher values of organic carbon and C/N
    ratio may be attributed to the presence of spent
    lubricant oil and petroleum products that are
    among the wastes produced in automobile repair
    sites.
  • The high amount of organic matter in the studied
    soil samples is quite obvious since the soil is
    contaminated with automobile fuels that are
    composed of hydrocarbon and PAHs (Atlas, 1981
    McMurry, 2000 Clayden and Greeves 2001).
  • Similarly, this result was inline with Bahuguna
    et al. (2011) who noted that the soil samples
    from automobile repair work stations demonstrated
    significantly higher total organic carbon, total
    PAHs contents and soil temperature while showing
    lower moisture contents and bacterial counts.

13
Total N, Available P, Exchangeable bases and
Total Exchangeable acidity
  • The results also showed lower total N, available
    P, Ca, Mg, K, Na, TEB, ECEC, BS and higher TEA in
    automobile repair site than non-automobile repair
    site.
  • These are plant nutrients which when they are
    lacking in soils will reduced the quality of the
    soils and the yield of crops growing in that
    soil.
  • Thus, the soils of automobile repair site are not
    good for crop production and should be put into
    alternative use.

14
Conclusion
  • This study showed that the soils of automobile
    repair site are of low quality.
  • It is high in organic carbon, low in soil major
    nutrients and pH.
  • Therefore, such soils should not be used for
    crop production but should be used for other
    non-agricultural ventures.

15
References
  • Atlas R.M (1981). Microbial degradation of
    petroleum hydrocarbons An
  • Environmental Perspective, Microbiological
    Reviews 45, pp 180 209.
  • Bahuguna.A., Lily.M.K., Munjal.A. , Singh.R.N.
    and Dangwal.K. (2011). A study on the physico
    chemical analysis of automobile contaminated soil
    of Uttarakhand, India International Journal of
    Environmental Sciences Vol.2 (2) 380 388.
  • Bremmer J.M. and Mulvaney (1982). Nitrogen total.
    In Page A. et al. (eds) Methods of Soil
    Analysis. Part 2. ASA, Madison, Wisconsin 595
    624.
  • Chapman H.D. (1982). Total exchangeable bases. In
    C.A. Black (ed). Methods of Soil Analysis Part
    11 ASA Madison, Wisconsin 902 904.
  • Clayden, J. and Greeves, N (2001).Organic
    Chemistry Oxford. pp 21.
  • Federal Ministry of Agriculture and Natural
    resources Management (1985). Reconnaissance soil
    survey of Anambra State Nigeria Soil Report
    FDALR, Kaduna.

16
References Continued
  • Federal Ministry of Agriculture and Natural
    resources Management (1990). Soils of Nigeria and
    rating for soil date interpretation in the
    tropics FDALR publication, Kaduna.
  • Jou N.S.R. (1979). Selected methods of soil and
    plant analysis, IITA Ibadan Manual Series 1, 97
    98.
  • Mbah C.N., Idike F.I. and Njoku C. (2011).
    Accumulation of pollutants in an ultisol amended
    with burnt and unburnt rice milled wastes J.
    Agric and Biol. Sc., 043 047.
  • Mclean E.O. (1982). Soil pH and lime
    requirements. In Page A.L. (eds) Methods of Soil
    Analysis Part 2. Chemical and microbial
    properties. Agronomy Series No. 9 ASA, SSSA
    Madison, W.I. USA.
  • McMurry, J (2000).Organic Chemistry. (5th ed.)
    Cole Thomson Learning, pp 75 81.
  • Nelson D.W. and Sommers L.E. (1982). Total
    carbon, organic carbon and organic matter. In
    Method of Soil Analysis Part 2. (ed) Page A.L.,
    Miller R.H., Keeney D.R. and Madison W.I.
    Ame.Soc. Argon pp 539 579.

17
References Continued
  • Nkwopara U.N., Eshett E.T., Onwerenadu E.U.,
    Osuji G.E. and Ndukwu B.N. (2008). Selected
    properties of soils formed under different
    lithologies in southeastern Nigeria Proc. 42nd
    Annual Conf. Agricultural Society of Nigeria 434
    437.
  • Njoku, C. and Mbah, C.N. (2012). Effect of burnt
    and unburnt rice husk dust on maize yield and
    soil physico-chemical properties of an ultisol
    in Nigeria, Biol. Agric. and Horti. Vol. 1, 1
    12.
  • Nwite J.N., Mbah, C.N., Igwe T.S. and Njoku C.
    (2009). Prediction of productivity of spent
    lubricant oil uncontaminated and contaminated
    soil amended with organic wastes using modified
    productivity index in Abakaliki Nigeria Nature
    and Science 7 (7) 100 112.
  • Ofomata, G. E. (1975). Nigeria in maps. Eastern
    States. In G. E. K. Ofomata ed. Ethiope Pub.
    House. Benin City. Pp 45 46.
  • Olsen S.R. and Sommers L.E. (1982). Phosphorus.
    In Method of Soil Analysis Part 2. (ed) Page
    A.L., Miller R.H., Keeney D.R. and Madison W.I.
    Ame.Soc. Argon pp 1572.
  • Steel, R.G.D. and Torrie, J.A. (1980). Principle
    and procedures of statistics A Biological
    Approach, McGraw-Hill Companies, Inc. New York,
    USA.

18
References Continued
  • Vuoti S. P., Valimarki J., Kwokequen J. and
    Tahuaja P. (2005). Biogradabilities of some Crain
    oils in groundwater as determined by the
    repitometric BOD in oxitop method, Bio analytical
    Chemistry 381 (2) 445 450.
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