Research Article | | Peer-Reviewed

Ecological Assessment of Soil Samples Around Refuse Dump Sites Within the Metropolis of Enugu State, Nigeria

Received: 29 March 2024     Accepted: 27 May 2024     Published: 29 September 2024
Views:       Downloads:
Abstract

This study looked at assessing the impact of solid wastes within Enugu metropolis on heavy metal concentrations and otherphysicochemical properties of soil samples from the site locations. Physicochemical analysis of the soil from the respectiverefusedump sites showed pH of 4.24, 6.3 and 5.87 respectively in the presence of the control experiment which maintained atpH of 7.6 throughout the experiment. Soil conductivity of the respective refuses ites within Enugu municipal showed a progressive increase of soil conductivity. Mineral contents were found in the following order: Cl>Ca>Mg>K>PO3. Heavy metals of Hg, As and Cd were found at below detectable limit range (BDL) in both the sampled soils from the respective refuse dumpsite andcontrol experiment. Cu, and Pb were significantly high in all the sampled soil from the dumpsites however, Cd was only detected in the soil sample from refuse dump III. Fe showed a progressive decrease across the dumpsites oil samples.

Published in International Journal of Environmental Chemistry (Volume 8, Issue 2)
DOI 10.11648/j.ijec.20240802.11
Page(s) 30-36
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2024. Published by Science Publishing Group

Keywords

Physicochemical, Heavy Metals, Dump Site, Minerals

1. Introduction
Solid wastes persistent in their ecological niche significantly have varying degree of impact within the ecological cosm . Functional dynamics of ecosystem reveals the significance of these wastes upon their bioavailability in the environment. Impact assessment study shows the effect of these wastes through biochemodynamics upon interaction with the environment . Upon many significant properties of the ecosystem affected by solid waste; trace metals stand to the test of significant clinical and health implicated elements of these waste .
As reported by Oparaji et al. , they stated that resultant effect of these waste largely depends on characteristic nature of these solids waste, their timing biochemical transformation within their accumulated niches and original nature of accumulator composites.
Trace metals due to their relativity in abundance and bioavaiability are metals with relatively high atomic mass and thus which reflect in their atomic weights examples includes Arsenic, beryllium, cadmium, chromium, lead, manganese, mercury, nickel, and selenium . They take part in bio-geochemical reactions and are transported between compartments by natural processes, the rate of which are at times greatly altered by human activities .
Heavy metals are connected with severe health abnormalities such as nephrotoxicity, neurotoxicity and malignancies of various types Lead (Pb) interferes with haem biosynthesis . It inhibits the activity of 2-amino laevulinic acid dehydratase which leads to accumulation of protoporphyrin in the red blood cell .
The average volume of waste generated daily by human activities and in some serendipity state depends on the availability of the composite quantity, the cultural level and type, and the economic conditions. In thereof, successive impact of these wastes especially the majorly solid waste due their persistence in the surrounding is of oblivion to eco-toxicology records . The present study investigate the presence of heavy metals and variations in the properties of soil samples around certain selected refuse dump sites within Enugu metropolis of Enugu state.
2. Material and Methods
2.1. Materials
All the reagents, equipment used in the present study were of analytical grade and products of BDh, May and Baker, Sigma Alrich. The equipments are calibrated at each use.
2.2. Methods
2.2.1. Collection of the Experimental Samples
Arable soils were collected directly from three refuse dump sites within the metropolis of Enugu state (Long.140N, SE 4) Nigeria as described by Ezenwelu et al. . These sites were popularly for heavy anthropogenic activities of refuse collections and disposals. The soil was collected in clean sterile sample containers and was taken to the lab for further experiments.
2.2.2. Determination of Physicochemical Properties of the Soil
Physicochemical properties of the respective soils were determined as described in the Journal of ATSDR, (2009). The following physicochemical properties were determined:
1) Soil pH profiling test
2) Soil conductivity test
3) Determination of macro and micro contents of the soil: Potassium ion (K), Chloride ion
4) Concentration of chloride ion in both mixtures were deduced from the formula:
Chloride: 100 mEq/L=VA – VB X M X 70,900Vol. ml.
Where VA= Volume of the standard solution; VB= Volume of the blank solution, M= molarity of the standard solution.
2.2.3. Calcium Hardness
CaCO3 content (mg/Kg)=VxE (CaCO3) x 10050
Calciummetal (mg/kg)=Tx 400.5 x 1.0550
T= titre value.
V= titre volume
E= equimolar concentration
2.2.4. Magnesium Hardness
Magnesium (as mg/l) = (T–C) x 0.243
Where; T= total hardness mg/l (as CaCO3)
C= Calcium hardness mg/l (as CaCO3)
2.2.5. Total Organic Carbon Contents
TOC (mg) = Vb- VsX 16,000/ vol. of sample used
Total organic matter content (TOM) = 1.23 X TOC
Vs= total volume of standard
Vb= total volume of blank
2.2.6. Determination of Heavy Metal Concentrations in the Soil Samples
Heavy metals in the soil samples were determined as described by Oparaji et al. ; Rantama (2018). Prior to the analysis, the respective soil were digested in an acid treatment of aqua regia, aqua fortis and hydrofluoric acid partitioned concentrations (HNO3, HCl and HF in the ratio 3:2:1) and heated on a hot plate. The digested sample were dissolved and filtered. The filtrates were subjected to heavy metal determinations using the atomic absorption spectrophotometer machine. Equivalent values of the determined metal were read off from the standard curve.
3. Results and Discussion
Tables 1, 2, 3 below respectively show the physicochemical properties of soil sample from the respective dump sites within Enugu metropolis. From the table the samples, there are significant variations in the physicochemical features of the soil samples within the grouped dump sites and the control experiment. Soil phosphorus was considered insignificant in refuse dump site I at P.> 0.05. Dissolved mineral contents of Ca, K, Mg, P and Cl were considered insignificant (P>0.05) in the experimented soil samples from refuse dump site I, II and III. Physical parameters were considered significant in the experimented soil samples.
Table 1. Physicochemical properties of soil samples from refuse dump site I.

Physiochemical parameters

Control experiment

Soil sample

pH

7.6±0.01

6.62±0.03

Soil Conductance

610±0.04

1134±0.12

Chloride ion (Mg/g)

433±0.03

1143.18±0.21

Phosphorus (Mg/g)

1.78±0.05

1.43±0.3

Magnesium (Mg/g)

6.27±0.011

16.04±0.05

Potassium (Mg/g)

7.22±0.021

16.28±0.03

Total hydrocarbon (THC) (Mg/g)

672.34±0.04

1309.06±0.4

Total Organic Carbon (TOC) (Mg/g)

78.45±0.06

127.12±0.22

Total Organic Matter (TOM) (mg/g)

96.45±0.06

156.36±0.01

N=2mean±SD

Table 2. Physicochemical properties of soil samples from refuse dump site II.

Physiochemical parameters

Control experiment

Soil sample

pH

7.6±0.01

6.16±0.22

Soil Conductance

610±0.04

1219±0.32

Chloride ion (Mg/g)

433±0.03

1265.09±0.42

Phosphorus (Mg/g)

1.78±0.05

0.94±0.4

Magnesium (Mg/g)

6.27±0.011

13.28±0.01

Potassium (Mg/g)

7.22±0.021

18.63±0.14

Calcium (Mg/g)

16.34±0.04

41.06±0.04

Total hydrocarbon (THC) (Mg/g)

672.34±0.04

1342.21±0.3

Total Organic Carbon (TOC) (Mg/g)

78.45±0.06

131.43±0.45

Total Organic Matter (TOM) (mg/g)

96.45±0.06

161.65±0.11

N=2mean±SD
Table 3. Physicochemical properties of soil samples from refuse dumpsite III.

Physiochemical parameters

Control experiment

Soil sample

pH

7.6±0.01

5.87±0.34

Soil Conductance

610±0.04

965±0.02

Chloride ion (Mg/g)

433±0.03

1056.45±0.25

Phosphorus (Mg/g)

1.78±0.05

4.04±0.04

Magnesium (Mg/g)

6.27±0.011

10.13±0.44

Potassium (Mg/g)

7.22±0.021

08.21±0.11

Calcium (Mg/g)

16.34±0.04

42.11±0.52

Total hydrocarbon (THC) (Mg/g)

672.34±0.04

1102.34±0.33

Total Organic Carbon (TOC) (Mg/g)

78.45±0.06

112.41±0.35

Total Organic Matter (TOM) (mg/g)

96.45±0.06

138.26±0.42

N=2mean±SD

Physicochemical analysis of the soil from the respective refuse dumpsites showed pH of 4.24, 6.3 and 5.87 respectively in the presence of the control experiment which maintained a pH of 7.6 throughout the experiment. This can be attributed to the nature of the contaminant in the soil such as oil and other acidic compounds (oleic, benzoic acids) as stated in the proceedings of the ASTDR . Soil conductivity of the respective refuse sites within Enugu municipal showed a progressive increase of soil conductivity.
Dissolved mineral contents were found in the following order: Cl>Ca>Mg>K>PO3. Solid wastes as stated by Vallero contain numerous minerals which impound in any receiving body and increase the physicochemical properties of the body. However, Oparaji et al. reported as a significant concentration of Ca and Mg in their analysis on inorganic ions dynamisms in soil samples from Fordoes terminal, Portharcourt, Rivers state. In their suggestions they went further to state that this significant increase can be attributed to the quarry and other anthropogenic activities going on the given location.
Table 4. Heavy Metals Concentrations Solid Wastes from the Respective Dump Sites.

Heavymetals

Control

Dumpsite I

Dumpsite II

Dumpsite III

Iron (Mg/g)

4.11± 0.02

28.76± 0.14

24.52± 0.12

35.62± 0.2

Cadmium (Mg/g)

BDL

BDL

BDL

0.12±0.2

Mercury (Mg/g)

BDL

BDL

BDL

BDL

Arsenic (Mg/g)

BDL

BDL

BDL

BDL

Lead (Mg/g)

1.09±0.4

4.17±0.17

12.24±0.1

14.35±0.25

Copper (Mg/g)

21.21±0.1

44.3±0.2

32.33±0.3

40.20±0.5

N=2
Analysis of Heavy Metal Concentrations
The table below shows the heavy metals concentrations from the respective solid wastes sample from dump sites within Enugu east L.G.A Enugu state. From the table toxicant implicated heavy metals were found at below detectable limit in all the sampled soils except for cadmium which were found in solid waste from dump site III. Heavy metals like Fe, Cu were relatively in abundance compared to the control experiment. Heavy metals such as Cd, Hg, and As were below detectable limit in the both the control and experimented solid waste samples from dump sites I, II and IV respectively; however, Pb was not recorded in the control experiment. Fe and Pb was significantly (P<0.05) high in the experimented soil refuse dump site samples when compared with the control experiment but considered insignificant (P>0.05) among the test experiment.
Heavy metals of Hg, As and Cd were found at below detectable limit range (BDL) in both the sampled soils from the respective refuse dumpsite and control experiment. Concentration of Cu and Pb increases across the refuse dumpsite except for Fe which showed an upward decrease. Cd among the relative toxic trace metals was seen only in dump site III but was below detectable limit in dump site I and II, respectively. Valero in the biosystem approach of heavy metal pollutions and toxicities stated that presence of these transition metals within any biological niches can be resultant manifestation of biochemodynamism of jetty activity, beneath soil pollutions from volcanisation effects and other physical interactions of the soils and other ecosystems.
The progressive decrease in the concentration of Fe can be attributed by the availability of masking elements such as oxygen, sulphur and other ligands which competitively bind to iron and diminishes their bioavailability. The result was in correlation with findings of Khalid et al. in their study on soil pollution and lead bioaccumulations revealed higher quotients of heavy metals like Fe, Pb and Cu in the soil while heavy metals of Hg, As, Cd were found below detectable limits in the soil.
4. Conclusion
The present research through experimental approach(es) has shown with empirical the presence of certain recalcitrants in soil samples around three refuse dumpsites within Enugu municipal, Enugu state, Nigeria. Solid wastes from the respective waste sites showed impact on the surrounding soil as were estimated compared to the control experiment. The afore with data will provide the health and risk assessment of inhabitants of concerned localities moreso the present study has shown the level of pollution of the community agricultural soil and a guide to environmentalist in curbing indiscriminate refuse dumping around dense metropolis.
Abbreviations

Pb

Lead

Zn

Zinc

Cu

Copper

BDL

Below Detectable Limit

mg/g

Milligram Per Gram

Funding Information
This work was solely funded by Nwanjoku, H.C.
Ethics
Authors declared no ethical issues that may arise after the publication of this manuscript.
Author’s Contributions
Nwanjoku Chioma Helen: Conceived and designed the experiments, performed the experiment and processed the data, analyzed the data and wrote the manuscript.
Edeoga Cyril Onyeka: Co-supervised the research and revised the manuscript.
Emeka Henry Oparaji: processed the data and revised the manuscript.
Ameh Godwin Ikechukwu: Designed the experiment, read the manuscript and processed the data.
Conflicts of Interest
The authors declare no conflicts of interest.
References
[1] Abdel-Shafy H. and Mansour, M. (2018). Solid waste issue: Sources, composition, disposal, recycling, and valorization. Egyptian Journal of Petroleum, 27(4): 1275-1290.
[2] Abdullah, A., Salamatinia, B., Mootabadi, H. and Bhatia, S. (2019). Current status and policies on biodiesel industry in Malaysia as the world’s leading producer of palm oil. Energy Policy, 37(12): 5440-5448.
[3] Agency for Toxic Substance Development and Disease Registry (ATSDR) (2009). Documentary on toxicological profile of total petroleum hydrocarbon contaminations. Agency for toxic substance and disease registry, division of toxicology and toxicology information branch, Atlanta Georgia.
[4] Amin, N., Allobaidy, E. and Ahmad, T. (2015). Contamination of soil with heavy metals from industrial effluent and their translocation in green vegetables of Peshawar, Pakistan. RSC Advance, 5: 14322–14329.
[5] Antonino, R., Fook, B., Lima, V., Rached, R., Lima, E., Lima, R., Covas, C. and Fook, M. (2017). Preparation and characterization of chitosan Obtained from shells of Shrimp (Litopenaeusvannamei Boone). Marine Drugs, 15(5): 141.
[6] Bánfalvi, G. (2011). "Heavy Metals, Trace Elements and their Cellular Effects". In Bánfalvi, G. Cellular Effects of Heavy Metals. Springer, 3–28.
[7] Chen, Z., Ngo, H. and Guo, W. (2013). A critical review on the end uses of recycled water. Critical Review on Environmental Science and Technology, 43: 1446–1516.
[8] Chiemchaisri, C., Juanga, J. and Visvanathan, C. (2007). Municipal solid waste management in Thailand and disposal emission inventory. Environmental Monitoring and Assessment, 135: 13-20.
[9] Chukwu, M. and Adams, E. (2016). Effect of Generator (Exhaust) Fumes on the Growth and Development of Lycopersicum esculentus (Tomato). Journal of Applied Environmental Science and Management, 20 (2) 335– 340.
[10] De Groot, R., Alkemade, R., Braat, L., Hein, L. and Willemen, L. (2010). Challenges in integrating the concept of ecosystem services and values in landscape planning, management and decision making. Ecol. Complex. 7: 260–272.
[11] Dyer P. (2009). The 1900 Arsenic Poisoning Epidemic. Brewery History, (130): 65–85.
[12] Ejedegba O., Onyeneke, E. and Oviasogie, P. (2007). Characterisation of lipase isolated from coconut seed under different nutrient conditions. African Journal of Biotechnology, 6: 723-727.
[13] Environmental protection agency (EPA) (2008). Report on integrating management of watershed and coastal line. USA environmental protection unit. 7th Edn. Washington DC.
[14] EPA Method 8270D (2010) (SW-846) Semivolatile Organic Compounds by Gas Chromatography/mass Spectrometry (GC/MS), Revision 4.
[15] Evanko, C. and Dzombak, A. (1997). "Remediation of Metals-Contaminated Soils and Groundwater". Technology Evaluation Report (Pittsburgh PA: Ground-water Remediation Technologies Center). TE 97-0-1.
[16] Evanko, C. and Dzombak, A. (2017). Remediation of Metals-Contaminated Soils and Groundwater. Technology Evaluation Report (Pittsburgh PA: Ground-water Remediation Technologies Center). TE 97-0-1.
[17] Ezenwelu, C., Aribodor, O., Ezeonyejiaku, C., Okafor, S. and Oparaji, E. (2022). Assessment of physicochemical properties and microbial loading index of soil samples from mgbuka market, Anambra state. Journal of Environmental Pollution and Management, 12: 134-176.
[18] Harvey, J., Handley, K. and Taylor, P. (2017). "Identification of the Sources of Metal (Lead) Contamination in Drinking Waters in North-Eastern Tasmania Using Lead Isotopic Compositions". Environmental Science and Pollution Research, 22: 12276–12288.
[19] Karak T., Bhagat, R. and Bhattacharyya, P. (2012). Municipal solid waste generation, composition, and management: The world scenario. Critical Reviews in Environmental Science and Technology. 42: 1509-1630.
[20] Khalid, S., Shahid, M., Dumat, C., Niazi, N., Bibi, I., Gul Bakhat, H., Abbas, G., Murtaza, B. and Javeed, H. (2017). Influence of groundwater and wastewater irrigation on lead accumulation in soil and vegetables: Implications for health risk assessment and phytoremediation. International Journal Phytoremediation, 19: 1037–1046.
[21] Kulczycka, J., Mineral, T., Lelek, L., Mineral, T. and Lewandowska, A. (2016). Life cycle assessment of municipal solid waste management—Comparison of results using different LCA models. Polish Journal of Environmental Studies. 24: 125-140.
[22] Kutty, S., Ngatenah, S., Isa, M. and Malakahmad, A. (2019). A nutrients removal from municipal wastewater treatment plant effluent using Eichhornia crassipes. World Academy of Science, Engineering and Technology, 36: 828-833.
[23] Lee, K. (2018). Earthworms. Their Ecology and Relationships with Soils and Land Use; Academic Press: Orlando, FL, USA, ISBN 0124408605.
[24] Markou, G., Chatzipavlidis, I. and Georgakakis, D. (2016). Cultivation of arthrospira (Spirulina) platensis in olive-oil mill wastewater treated with sodium hypochlorite. Bioresources Technology, 112: 234-241.
[25] Miao, K., Cortazar, E., Bartolome, L. and Arrasate, S. (2001). Distribution and bioaccumulation of PAHs in the UNESCO protected natural reserve of Urdaibai, Bay of Biscay. Chemosphere, 72(10): 1467-1474.
[26] Morris, R. (1952). Determination of Iron in water in presence of heavy metals. Analytical Chemistry, 24(8): 1376-1378.
[27] Narodoslawsky, M. and Krotscheck, C. (2015). The sustainable process index (SPI): Evaluating processes according to environmental compatibility. Journal of Hazardous Materials. 41: 383-397.
[28] Niederl-Schmidinger A. and Narodoslawsky, M. 2008. Life cycle assessment as an engineer’s tool? Journal of Cleaner Production, 16: 245-252.
[29] OLF (2007) Environmental report 2007. The Norwegian Oil Industry Association (OLF). Stavanger, Norway 63 p.
[30] Onen, S., Kucuksezgin, F. andKocak, F. (2011). Temporal And Spatial Bio monitoring of Heavy Metals in Eastern Aegean Costal Waters Using Amphitrite. Air pollution bulletin, 62: 2548-2556.
[31] Onugbolu, C. and Adieze I. (2016). Assessment of emulsification potentials of hydrocarbon utilizing fungi isolates isolated from a crude oil polluted at FUTO, owerri. Nigerian Journal of Microbiology, 30(1): 3225-3234.
[32] Oparaji, E., Nweze, E., Arinzechukwu, O., Anosike, J., Agbo, K and Arazu, V. (2017). Estimation of polycyclic aliphatic hydrocarbons and total petroleum hydrocarbons in aquatic fauna from forcados terminal rivers, Portharcourt, Rivers state. Journal of Environmental and Analytical toxicology, 7(6): 1123-1176.
[33] Osei A. (2001). New School Chemistry. 3rdedn, Africa Feb Publishers, 368-402.
[34] OSPAR Commission (2000). Quality Status Report 2000. London: OSPAR.
[35] Prioreschi, P. (1998). Roman Medicine. A History of Medicine III. Horatius Press, ISBN 1888456035.
[36] Pritchard, J. (2010). "Wal-Mart Pulls Miley Cyrus Jewelry After Cadmium Tests". USA Today.
[37] Pucknat, W. (ed.) (1981). Health Impacts of Polynuclear Aromatic Hydrocarbons. Environmental Health Review No. 5. Noyes Data Corp., Park Ridge, New Jersey, 271 pp.
[38] Rabie, A. and Ghallab, A. (2006). Heavy-metal fractionation and distribution in soil profiles short-term-irrigated with sewage wastewater. Chemistry and Ecology, 22: 267–278.
[39] Rantamaki, P.(1997). Release and Retention of Selected Polycyclic Aromatic Hydrocarbons (PAHs) and their Methylated Derivatives by the Common Mussel (Mytilusedulis) in the Brakish Water of the Baltic Sea. Chemosphere, 35: 487-502.
[40] Redmond MC, Valentine DL (2012) Natural Gas and Temperature Structured a Microbial Community Response to the Deepwater Horizon Oil Spill. Proc. Proceedings from National Acadamy of Science. USA,
[41] Retnam, A. and Zakari, P. (2010). Hydrocarbon and heavy metal pollutions in aqua culture. Proceedings of Postgraduate Colloquim.
[42] Ramachandra, T., Bharath, H., Kulkarni, G. and Han, S. (2018). Municipal solid waste: Generation, composition and GHG emissions in Bangalore, India. Renewable and Sustainable Energy Reviews, 82: 1122-1136.
[43] Scaglia, B. and Adani, F. (2018). Sustainable landfill and biological stability of municipal solid waste. In: Lavelle JR, editor. Waste Management: Research, Technology and Developments. USA: Nova Science Publishers, Inc. pp. 193-223.
[44] Scaglia, B., Salati, S., Di, A., Carrera, A., Tambone, F. and Adani F. (2013). Short mechanical biological treatment of municipal solid waste allows landfill impact reduction saving waste energy content. Bioresource Technology, 143: 131- 138.
[45] Shah, K. (2020). Basics of Solid and Hazardous Waste Management Technology; Upper Saddle River, N. J.: Prentice Hall.
[46] Shekdar A. (2009). Sustainable solid waste management: An integrated approach for Asian countries. Waste Management. 29: 1438-1448.
[47] Tarmudi, Z., Abdullah, M. and Tap, A. (2012). An overview of municipal solid wastes generation in Malaysia. Jurnal Teknologi, 51: 1-15.
[48] USEPA. (1987). Appendix A to 40 CFR Part 423. United States Environmental Protection Agency. Available on the html:
[49] Valerro D. (2010). Environmental biotechnology: A Biosystems approach. 4th edition. Pp. 1245-1453.
[50] Wange, S., Paletto, M., Commendatore, M. andEsteves, L. (2016). Hydrocarbon Levels in Sediments and Bivalve Mollusks from Bahía Nueva (Patagonia, Argentina): An Assessment of Probable Origin and Bioaccumulation Factors. Marine Pollution Bulletin, 56: 2082-2105.
[51] World Health Organisation. (1997). Non-heterocyclic polycyclic aromatic hydrocarbons. World Health Organization, International Programme on Chemical Safety (Environmental Health Criteria 202), Geneva.
[52] Zhang, D., Tan, S. and Gersberg, R. (2010). Municipal solid waste management in China: Status, problems and challenges. Journal of Environmental Management. 91: 1623-1633.
Cite This Article
  • APA Style

    Helen, N. C., Ikechukwu, A. G., Onyeka, E. C., Oparaji, E. H. (2024). Ecological Assessment of Soil Samples Around Refuse Dump Sites Within the Metropolis of Enugu State, Nigeria. International Journal of Environmental Chemistry, 8(2), 30-36. https://doi.org/10.11648/j.ijec.20240802.11

    Copy | Download

    ACS Style

    Helen, N. C.; Ikechukwu, A. G.; Onyeka, E. C.; Oparaji, E. H. Ecological Assessment of Soil Samples Around Refuse Dump Sites Within the Metropolis of Enugu State, Nigeria. Int. J. Environ. Chem. 2024, 8(2), 30-36. doi: 10.11648/j.ijec.20240802.11

    Copy | Download

    AMA Style

    Helen NC, Ikechukwu AG, Onyeka EC, Oparaji EH. Ecological Assessment of Soil Samples Around Refuse Dump Sites Within the Metropolis of Enugu State, Nigeria. Int J Environ Chem. 2024;8(2):30-36. doi: 10.11648/j.ijec.20240802.11

    Copy | Download

  • @article{10.11648/j.ijec.20240802.11,
      author = {Nwanjoku Chioma Helen and Ameh Godwin Ikechukwu and Edeoga Cyril Onyeka and Emeka Henry Oparaji},
      title = {Ecological Assessment of Soil Samples Around Refuse Dump Sites Within the Metropolis of Enugu State, Nigeria
    },
      journal = {International Journal of Environmental Chemistry},
      volume = {8},
      number = {2},
      pages = {30-36},
      doi = {10.11648/j.ijec.20240802.11},
      url = {https://doi.org/10.11648/j.ijec.20240802.11},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ijec.20240802.11},
      abstract = {This study looked at assessing the impact of solid wastes within Enugu metropolis on heavy metal concentrations and otherphysicochemical properties of soil samples from the site locations. Physicochemical analysis of the soil from the respectiverefusedump sites showed pH of 4.24, 6.3 and 5.87 respectively in the presence of the control experiment which maintained atpH of 7.6 throughout the experiment. Soil conductivity of the respective refuses ites within Enugu municipal showed a progressive increase of soil conductivity. Mineral contents were found in the following order: Cl>Ca>Mg>K>PO3. Heavy metals of Hg, As and Cd were found at below detectable limit range (BDL) in both the sampled soils from the respective refuse dumpsite andcontrol experiment. Cu, and Pb were significantly high in all the sampled soil from the dumpsites however, Cd was only detected in the soil sample from refuse dump III. Fe showed a progressive decrease across the dumpsites oil samples.
    },
     year = {2024}
    }
    

    Copy | Download

  • TY  - JOUR
    T1  - Ecological Assessment of Soil Samples Around Refuse Dump Sites Within the Metropolis of Enugu State, Nigeria
    
    AU  - Nwanjoku Chioma Helen
    AU  - Ameh Godwin Ikechukwu
    AU  - Edeoga Cyril Onyeka
    AU  - Emeka Henry Oparaji
    Y1  - 2024/09/29
    PY  - 2024
    N1  - https://doi.org/10.11648/j.ijec.20240802.11
    DO  - 10.11648/j.ijec.20240802.11
    T2  - International Journal of Environmental Chemistry
    JF  - International Journal of Environmental Chemistry
    JO  - International Journal of Environmental Chemistry
    SP  - 30
    EP  - 36
    PB  - Science Publishing Group
    SN  - 2640-1460
    UR  - https://doi.org/10.11648/j.ijec.20240802.11
    AB  - This study looked at assessing the impact of solid wastes within Enugu metropolis on heavy metal concentrations and otherphysicochemical properties of soil samples from the site locations. Physicochemical analysis of the soil from the respectiverefusedump sites showed pH of 4.24, 6.3 and 5.87 respectively in the presence of the control experiment which maintained atpH of 7.6 throughout the experiment. Soil conductivity of the respective refuses ites within Enugu municipal showed a progressive increase of soil conductivity. Mineral contents were found in the following order: Cl>Ca>Mg>K>PO3. Heavy metals of Hg, As and Cd were found at below detectable limit range (BDL) in both the sampled soils from the respective refuse dumpsite andcontrol experiment. Cu, and Pb were significantly high in all the sampled soil from the dumpsites however, Cd was only detected in the soil sample from refuse dump III. Fe showed a progressive decrease across the dumpsites oil samples.
    
    VL  - 8
    IS  - 2
    ER  - 

    Copy | Download

Author Information
  • Department of Applied Biology, Enugu State University of Science and Technology, Enugu, Nigeria; Department of Medical Microbiology, Faculty of Clinical Science, University of Nigeria Teaching Hospital, Enugu, Nigeria

  • Department of Applied Biology, Enugu State University of Science and Technology, Enugu, Nigeria

  • Department of Applied Biology, Enugu State University of Science and Technology, Enugu, Nigeria

  • Department of Biochemistry, University of Nigeria, Nsukka, Nigeria