Browse

Journals By Subject

Life Sciences, Agriculture & Food
Chemistry
Medicine & Health
Materials Science
Mathematics & Physics
Electrical & Computer Science
Earth, Energy & Environment
Architecture & Civil Engineering
Education
Economics & Management
Humanities & Social Sciences
Multidisciplinary

Books

Publish Conference Abstract Books
Upcoming Conference Abstract Books
Published Conference Abstract Books
Publish Your Books
Upcoming Books
Published Books

Proceedings

Events

Events
Five Types of Conference Publications

Join

Join as Editorial Board Member
Become a Reviewer

Information

For Authors
For Reviewers
For Editors
For Conference Organizers
For Librarians
Article Processing Charges
Special Issue Guidelines
Editorial Process
Manuscript Transfers
Peer Review at SciencePG
Open Access
Copyright and License
Ethical Guidelines
Submit an Article
Research Article | | Peer-Reviewed

Effect of Neem Seed Ash on the Geotechnical Properties of Lateritic Soil

Tijanee Sharifdeen Adebayo*,  Abdulrauf Kabir
Published in Journal of Civil, Construction and Environmental Engineering (Volume 10, Issue 6)
Received: 11 October 2025     Accepted: 21 October 2025     Published: 5 November 2025
Views:       Downloads:
Download PDF
Abstract

The impact of Neem Seed Ash (NSA) on the geotechnical properties of three clay soil samples classified as MH and CH by the Unified Soil Classification System is investigated in this study. The results of preliminary testing indicated moderate plasticity and load-bearing capacity, with natural moisture levels ranging from 7.2% to 9.38%, specific gravities from 2.66 to 2.75, and California Bearing Ratio (CBR) values from 13.42% to 19.8%. According to ASTM C618’s Class C classification, NSA's pozzolanic content of 52.01% was determined by chemical analysis. The engineering properties of the soils were significantly improved by NSA integration. As the NSA content rose, the specific gravity decreased, demonstrating the admixture's decreased density. Indicating improved soil workability and decreased plasticity, Atterberg limits showed a significant decline: liquid limits decreased from 37% to 12%, plastic limits from 27% to 11%, and the plasticity index from 14% to 2%. The maximum dry density increased to 2.37 g/cm3 at 6% NSA substitution, according to compaction tests, and the optimal moisture content decreased from 16% to 9.6%, indicating increased compaction efficiency. With 8% NSA replacement, the CBR values increased dramatically, reaching 44.1%, indicating a notable improvement in strength. These findings confirm that NSA is an effective stabilizing agent for difficult clay soils, enhancing their mechanical properties and potentially reducing environmental impacts and building costs. The study supports the use of NSA as an economical and environmentally friendly additive for stabilizing geotechnical soil.

Published in Journal of Civil, Construction and Environmental Engineering (Volume 10, Issue 6)
DOI 10.11648/j.jccee.20251006.11
Page(s) 207-215
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), 2025. Published by Science Publishing Group
Previous article
Keywords

Neem Seed Ash, Lateritic Soils, California Bearing Ratio, Maximum Dry Density, Fly-ash

1. Introduction
Lateritic soil with remarkable engineering features is frequently sought after by contractors building various engineering constructions
[1, 2]
. In actuality, it is often difficult to identify such soils, especially since many construction sites are predominantly made up of lateritic soil, some of which are known to have high clay content in their native state. Engineers all throughout the world have frequently expressed concern about this issue. To overcome this issue, different strategies are available; one option is to scarify the current soil and immediately replace it with a brought-in material, or to stabilize the existing soil in place. However, given the financial elements of site logistics, haulage distances, and the transportation of imported components, scarification and substitution with foreign resources may not always be cost-effective and may frequently increase building costs. Unlike stabilization, cost is reduced while achieving sustainability
[3]
. Soil stabilization is essentially the process of changing the soil's properties by applying chemically reactive chemicals. This improves the soil's engineering qualities, both physical and chemical. Chemical soil stabilization alters the soil's consistency, swelling properties, grain size distribution, unconsolidated compressive strength (UCS), and California bearing ratio (CBR)
[4, 5]
. Numerous research have recently been undertaken on the use of chemical additives such as cement, lime, and fly ash in the treatment of clay-rich
[6-8]
.
Despite these outstanding results, the cost of using this traditional addition is substantial, as are the environmental effects it produces during manufacturing. As a result, researchers face the difficult task of investigating alternate methods for soil stabilization. The global surge in urban populations has led in an increase in trash production across all aspects of human activity
[9]
. Careless trash disposal is quickly becoming a major concern in Nigeria, with agricultural waste accounting for the majority of the waste generated
[10-12]
. According to Agamuthu
[13]
, around 998 million tonnes of agricultural waste are produced each year. These findings have prompted academics to focus further on converting these minerals for usage as a soil augmentation resource in building. However, initiatives aimed at achieving environmental sustainability have prompted the investigation of various sustainable materials (agricultural waste materials) as effective alternatives for improving lateritic soil, as opposed to traditional approaches that use cement and lime for soil improvement
[9, 14, 15]
.
Numerous research have shown that agricultural waste is an effective substitute for traditional materials in improving soil quality
[16-19]
. Agricultural waste refers to the byproducts produced during the production and handling of unprocessed agricultural products such as fruits, vegetables, livestock, poultry, dairy products and crops. Neem Seed Husk is a byproduct of the industrial processing of Neem Seed for oil extraction and fertilizer manufacturing
[20-22]
. To make neem-based fertilizer, first extract neem oil, and then use the resultant cake to make organic fertilizer. A little portion of seed husk is crushed and used into fertilizer, while the majority goes to waste
[23, 24]
. However, neem seed husk waste causes disposal challenges in neem oil processing plants, resulting in severe ecological and environmental contamination when discarded, causing serious threats to human health and other living species
[25-28]
. This demands the utilization of neem seed husk waste.
2. Materials and Methodology
2.1. Laterite
This was taken from three different areas in AjaseIpo village, packaged, and ramped to keep its natural moisture content for measuring purposes. The samples were collected from AjaseIpo town using GPS coordinates (latitude: 8.2333, longitude: 4.8167) at a depth of 900mm after the overlying soil was removed. The natural moisture content was determined using FMWH (2000) criteria for road construction.
2.2. Neem Seed
The neem seed husk was received from Yammfy Farms Nigeria Limited, located on Offa-Ilemona Road in Offa, Kwara State, Nigeria. Following collecting, the husks were carefully placed in sack bags, properly sealed, and tagged for onward transport to the laboratory. Inside the lab, the husks were rigorously cleansed to remove any impurities or pollutants. They were then sun-dried for 24 hours to ensure complete moisture removal. The remaining contaminants were then manually chosen, and the husks were cut into smaller fragments of around 2.00 mm in size. The prepared Neem Seed Husk underwent controlled calcination at temperatures ranging from 700°C to 900°C. The obtained Neem seed Ash (NSA) was then ground into finer particles that could pass through a 63 mm sieve and was kept in a cool, dry place for later use.
2.3. Sample Preparation
Laterite soil samples were oven-dried for 24 hours at 60 ºC to preserve their clay mineral properties. To modify the laterite soil, varying volumes of Neem Seed Ash (NSA) were injected at rates of 2%, 4%, 6%, 8%, and 10% (by weight). The ingredients were thoroughly mixed to ensure close mixing. The mixed samples were allowed to cure for 48 hours before being remixed to achieve a uniform consistency for testing..
2.4. Testing Experiment
Specific gravity, Atterberg limits, compaction, particle size distribution (sieve analysis), and California Bearing Ratio (CBR) were among the laboratory experiments conducted on soils and Neem Seed Ash (NSA) stabilized soils. Neem Seed Ash was used to stabilize clay soil in compliance with BS 1924 guidelines.
3. Results and Discussion
3.1. Preliminary Test Results on Soil Samples
Table 1 summarizes the results of the preliminary geotechnical tests, such as natural moisture content, specific gravity, Atterberg limits, compaction, and CBR, which were conducted only on clay soil.
Table 1. Results of Preliminary Test on Soil Samples.

Properties

Soil 1

Soil 2

Soil 3

Natural Moisture Content

8.4

9.38

7.2

Grain Specific Gravity, Gs

2.66

2.71

2.75

Liquid Limit (LL)%

33

37

35

Plastic Limit (PL)%

27

27

21

Plasticity Index (PI)%

6

10

14

Sand

34.29%

36.79%

17.12%

Silt

58.49%

44.23%

60.34%

Clay

7.2%

18.98%

22.54%

Effective Diameter, (D10) mm

0.054

0.023

0.019

Coefficient of Uniformity (Cu)

20

15

18

UCSC Soil Classification

MH

MH

CH

AASHTOSoil Classification

A-6

A-6

A-7-6

Maximum Dry Density (g/cm3)

2.33

2.39

1.40

Optimum Moisture Content (%l)

16

13.5

7.1

California Bearing Ratio (%)

19.8

17.1

13.42
The natural moisture levels of soil samples A, B, C are 8.4%, 9.38%, and 7.2%, indicating that all the soil samples are relatively dry. The specific gravity of the soil is recorded at 2.66 for soil sample 1, 2.71 for soil sample 2, and 2.75 for soil sample 3; these figures suggest that all soil samples possess moderately high specific gravity. Upon compaction of the soil samples, soil sample 1 exhibits a Maximum Dry Density of 2.33 with an optimum moisture content (OMC) of 16%, soil sample 2 presents a Maximum Dry Density of 2.39 at an optimum moisture content (OMC) of 13.5%, while soil sample 3 reflects a Maximum Dry Density of 1.40 with an optimum moisture content (OMC) of 7.1%. This indicates that the soil possesses considerable weight per unit volume under compression, which is beneficial for load-bearing structures.
The Unified Soil Classification System identifies the three soil samples as MH (Sandy Silt), MH (Sandy Silt), and CH (Clayey Silt), while the AASHTO classification categorizes them as A-6, A-6, and A-7-6, respectively. The soil samples show a Liquid limit from 33 to 37%, a Plastic limit from 21 to 27%, and a Plasticity index from 6% to 14%. All of this suggests that every soil sample exhibits moderate plasticity.
3.2. Chemical Composition of Neem Seed Ash (Nsa)
The chemical analysis tests were done to determine the oxide composition of Neem Seed Ash (NSA). This was carried out at Rolab research Centre Ibadan.
Table 2. Oxides Cmposition of NSA.

Chemical Constitutients

Neem Seed Ash (NSA) (%)

SiO2

36.5

Al2O3

3.37

Fe2O3

12.14

CaO

18.08

MgO

3.2

K2O

9.45

Na2O

0.05

SO3

2.09

Loss on Ignition (LOI)

7.50
Table 2 showed the chemical composition of Neem Seed Ash (NSA). The chemical constituents include Calcium oxides (CaO), Potassium oxides (K2O), Silica (SiO2), Alumina (Al2O3) and Ferric Oxide (Fe2O3) amongst others and Loss on Ignition (LOI) as 36.5%, 3.37%, 12.14%, 18.08%, 3.25, 9.45%, 0.05%, 2.09% and 7.50% respectively. From Table 2, the pozzolan content (i.e. combination of SiO2+ Al2O3 +Fe2O3) of Neem Seed Ash (NSA) is 52.01% which is greater than 50% specified for Class C pozollan. Thus, the Neem Seed Ash (NSA) meets the requirement for Class C pozzolan.
3.3. Specific Gravity
The specific gravity of the Neem Seed Ash (NSA) is 2.35. The specific gravity of the mixes of soil samples with the Neem Seed Ash are shown in Table 3 and Figure 1. There was reduction in specific gravity of mixes of soil sample 1 from 2.66 to 2.53, Soil Sample 2 from 2.71 to 2.55 and soil sample 3 from 2.75 to 2.63. It was observed that there is significant reduction in the specific gravity of all the soil samples as the Neem Seed Ash Content increases.
Table 3. Result for specific gravity test.

Test

Specific Gravity (Gs)

% NSA Replacement

0%

2%

4%

6%

8%

Sample 1

2.66

2.61

2.63

2.59

2.53

Sample 2

2.71

2.65

2.62

2.58

2.55

Sample 3

2.75

2.79

2.68

2.72

2.63
Figure 1. Specific Gravity of Modified Soil Samples.
3.4. Atterberg Limit Test
The Atterberg limit tests which include the liquid limit tests, plastic limit tests and plasticity index tests are carried out in accordance with BS 1377. The Atterberg tests were done for the three natural soil samples 1, 2 and 3 which are regarded as 0% and also for the stabilized (addition of Neem Seed Ash) soil samples at an increment of 2%, 4%, 6% and 8% for soil sample 1, 2 and 3 as shown in Table 4, Figure 2 and Figure 3.
Table 4. Result of Atterberg Limits Tests.

Test

Atterberg Limit (%)

Sample

1

2

3

% Replacement

0%

2%

4%

6%

8%

0%

2%

4%

6%

8%

0%

2%

4%

6%

8%

Liquid Limit

33

23

20

21

12

37

29

25

23

12

35

21

21

26

18

Plastic limit

27

19

18

14

11

27

24

16

19

11

21

17

16

21

16

Plasticity index

6

4

2

7

1

10

5

9

4

1

14

4

5

5

2
Figure 2. Liquid Limit of Modified Soil Sample.
Figure 3. Plastic Limit of Modified Soil Sample.
Neem Seed Ash (NSA) changes the Atterberg limits of the soils. An increase in NSA from 0%-8%, the liquid limit, plastic limit and plasticity index of all soil samples reduces from 37% to 12%, 27% to 11% and 10% to 1%. The reduction in plastic index is expected because Neem Seed Ash (NSA) are cohesion-less material. Thus an inclusion of Neem Seed Ash (NSA) reduces the Atterberg limits of the clay soils. Thus, this is an indication there is an improvement in the consistency of the soil.
3.5. Compaction
In determining the Optimum Moisture Content (OMC) and Maximum Dry Density (MDD), the compaction test was performed on the soil samples andmodified soil samples using the Standard Proctor test compaction method. The average value of the Optimum Moisture Content (OMC) and Maximum Dry Density (MDD) are shown in Table 5 and presented in Figure 4 and Figure 5 respectively.
Table 5. Result of Compaction test.

Sample

Sample 1

Sample 2

Sample 3

% Neem Seed Ash (NSA) Replacement

MDD (g/cm3)

OMC (g/cm3)

MDD (g/cm3)

OMC (g/cm3)

MDD (g/cm3)

OMC (g/cm3)

0%

2.33

16

2.39

13.5

1.40

8.2

2%

2.34

11.0

2.43

11

1.48

7.9

4%

2.35

11.5

2.21

13

1.58

7.6

6%

2.37

9.6

2.37

9.8

2.13

7.1

8%

1.53

11.0

2.10

7.1

1.58

7.2
Figure 4. Maximum Dry Density (MDD) of Modified Soil Samples.
Figure 5. Optimum Moisture Content of Modified Soil Samples.
Neem Seed Ash (NSA) changes the compaction characteristics of the soils. An increase in NSA from 0%-8%, the maximum dry density of all soil samples increases up to 6%Neem Seed Ash (NSA) replacement, but beyond 6% it reduces. Similarly, the optimum moisture content (OMC) of all soil sample reduces as the Neem Seed Ash content increases in the soil mixes. The reduction in maximum dry density is attributed to the fact that Neem Seed Ash (NSA) is a cohesion-less material and of low specific gravity. Also, the addition of Neem Seed Ash (NSA) reduces the optimum moisture content (OMC) because the surface area and water absorption rate of the soil samples are diminished. Thus, increase in the maximum dry density (MDD) and reduction in the optimum moisture content (OMC) is a pointer there is an improvement in the mechanical properties of the modified clay soil.
3.6. California Bearing Ratio
The average value of the soaked California Bearing Ratio (CBR) test results are shown in Table 6 and presented in Figure 6.
Table 6. Result of CBR Test.

1

2

3

% NSA Replacement

CBR Value (%)

CBR Value (%)

CBR Value (%)

0%

19.8

17.1

13.42

2%

29.4

26.6

22.5

4%

32.5

34.0

34.2

6%

34.6

35.2

36.4

8%

38.3

44.1

36.9
Figure 6. California Bearing Ratio of Modified Soil Sample.
Neem Seed Ash (NSA) changes the California bearing ratio (CBR) of the soils. An increase in NSA from 0%-8%, the California bearing ratio (CBR) of all soil samples increases The increase in California bearing ratio (CBR) is attributed to the fact that Neem Seed Ash (NSA) is made up of coarser material and its pozzolanic reaction. Thus, increase California bearing ratio (CBR) in is a pointer there is an improvement in the mechanical properties of the modified soil samples.
4. Conclusion
This study examines the impact of Neem Seed Ash (NSA) on the geotechnical characteristics of three soil samples collected from various sites. The three soil samples examined in this study were categorized as MH, MH, and CH according to the USCS soil classification system. The materials vary from sandy silt to clayey silt with high plasticity according to general classification. The results from the chemical composition test indicate that the Neem Seed Ash (NSA) is classified as Fly-Ash type C according to ASTM C618. Furthermore, it was demonstrated that incorporating Neem Seed Ash (NSA) admixture enhanced the engineering characteristics of the clay soils. The plasticity index, including liquid limits, plastic limits, and plastic index, decreases. The decrease in the plasticity index indicates that the soil characteristics and its operability have been enhanced. The OMC decreases, while the values of MDD and CBR rise.
In conclusion, Neem Seed Ash can act as effective alternatives to amend and stabilize troublesome clay soils, thereby aiding in lowering construction expenses, minimizing environmental risks, and ultimately enhancing the geotechnical characteristics of clay soils.
Abbreviations

MH

Silty Clay

CH

High Plasticity Clay

CBR

California Bearing Ratio

NSA

Neem SeedAsh

ASTM

American Society for Testing and Materials

MDD

Maximum Dry Density

OMC

Optimum Moisture Content

FMWH

Federal Ministry of Works and Housing

BS

Bristish Standard

Gs

Specific Gravity

LL

Liquid Limit

PL

Plastic Limit

PI

Plasticity Index

D10

Effective Diameter

Cu

Coefficient of Uniformity

UCSC

Unified Soil Classification System

AASHTO

American Association of State Highway and Transportation Officials
Conflicts of Interest
The authors declare no conflicts of interest.
References
[1] Gidigasu, M. (Ed.). (2012). Laterite soil engineering: pedogenesis and engineering principles (Vol. 9). Elsevier.
[2] Etim, R. K., Ekpo, D. U., Udofia, G. E., &Attah, I. C. (2022). Evaluation of lateritic soil stabilized with lime and periwinkle shell ash (PSA) admixture bound for sustainable road materials. Innovative Infrastructure Solutions, 7(1), 62.
[3] Beckham, T. L., & Hopkins, T. C. (1997). Stabilization of subgrade soil using hydrated lime product. Kentucky: Kentucky Transportation Center.
[4] Umar, I. H., Abubakar, S., Lin, H., & Hassan, J. I. (2025). Metakaolin as a soil stabilizing admixture: A comprehensive analysis of California bearing ratio and consolidation behavior using experimental and machine learning approaches. Earth Science Informatics, 18(2), 200.
[5] Matajinimvar, S., Choobbasti, A. J., &Kutanaei, S. S. (2025). The effect of construction moisture content on the mechanical, shear and environmental characteristics of clay stabilized with cement and CS: A micro and macro study. Case Studies in Construction Materials, 22, e04818.
[6] Andavan, S., &Pagadala, V. K. (2020). A study on soil stabilization by addition of fly ash and lime. Materials Today: Proceedings, 22, 1125-1129.
[7] Mahedi, M., Cetin, B., & White, D. J. (2020). Cement, lime, and fly ashes in stabilizing expansive soils: Performance evaluation and comparison. Journal of Materials in Civil Engineering, 32(7), 04020177.
[8] Ali, H. F. H., & Mohammed, A. S. (2024). Modeling the effect of chemical additives on clay soil plasticity: novel analysis of oxide contributions in fly ash and cement treatments. Modeling Earth Systems and Environment, 1-30.
[9] Adeboje, A. O., Bankole, S. O., Apata, A. C., Olawuyi, O. A., &Busari, A. A. (2022). Modification of lateritic soil with selected agricultural waste materials for sustainable road pavement construction. International Journal of Pavement Research and Technology, 15(6), 1327-1339.
[10] Nnaji, C. C. (2015). Status of municipal solid waste generation and disposal in Nigeria. Management of Environmental Quality: An International Journal, 26(1), 53-71.
[11] Ogunmakinde, O. E., Sher, W., &Maund, K. (2019). An assessment of material waste disposal methods in the Nigerian construction industry. Recycling, 4(1), 13.
[12] Balogun, W. O. & Otunola, O. O. The Use of Yam Peel Ash as Partial Replacement of Cement Towards Achieving Low Cost Housing. American Journal of Construction and Building Materials, 2021, 5(1), 15-21.
[13] Agamuthu, P. (2009, November). Challenges and opportunities in agro-waste management: An Asian perspective. In Inaugural meeting of first regional 3R forum in Asia (Vol. 11, p. 12). University of Malasiya.
[14] James, J., &Pandian, P. K. (2016). Industrial wastes as auxiliary additives to cement/lime stabilization of soils. Advances in Civil Engineering, 2016(1), 1267391.
[15] Sharma, A., & Sharma, R. K. (2021). Sub-grade characteristics of soil stabilized with agricultural waste, constructional waste, and lime. Bulletin of Engineering Geology and the Environment, 80(3), 2473-2484.
[16] Olonode, K. A. (2010). Prospect of Agro-by-products as pozzolans in concrete for low-cost housing delivery in Nigeria. In Proceedings of the International Conference of the ObafemiAwolowo University, Faculty of Technolgy (Vol. 1, pp. 217-221).
[17] Oluremi, J. R., Adedokun, S. I., &Osuolale, O. M. (2012). Stabilization of poor lateritic soils with coconut husk ash. International Journal of Engineering Research and Technology, 1(8), 1-9.
[18] Ako, T., & Yusuf, I. (2016). Effect of palm kernel shell ash on compaction characteristics of a lateritic soil. Webs Journal of Science and Engineering Application, 5(1), 449-455.
[19] Ishola, K., Olawuyi, O. A., Bello, A. A., &Yohanna, P. (2019). Effect of plantain peel ash on the strength properties of tropical red soil. Nigeria Research Journal of Engineering and Environmental Sciences, 4(1), 447-459.
[20] Lokanadhan, S., Muthukrishnan, P., &Jeyaraman, S. (2012). Neem products and their agricultural applications. Journal of Biopesticides, 5, 72.
[21] Adepoju, T. F. (2020). Optimization processes of biodiesel production from pig and neem (Azadirachtaindica a. Juss) seeds blend oil using alternative catalysts from waste biomass. Industrial Crops and Products, 149, 112334.
[22] Neto, F. S., MeloNeta, M., Sousa, A., Damasceno, L., Sousa, B., Medeiros, S., Melo, R., Lopes, A., Santos, J. and Rios, M., (2023). Analysis of the Fuel Properties of the Seed Shell of the Neem Plant (Azadirachtaindica). Processes, 11(8), p. 2442.
[23] Fragassa, C., Vannucchi de Camargo, F., &Santulli, C. (2024). Sustainable biocomposites: Harnessing the potential of waste seed-based fillers in eco-friendly materials. Sustainability, 16(4), 1526.
[24] Gupta, A. K. (2022). Use of neem and neem based products in organic farming. Indian Farming, 72(1).
[25] Iqbal, N., Sharma, R., Hazra, D. K., Dubey, S., Kumar, N., Agrawal, A., & Kumar, J. (2021). Successful utilization of waste cooking oil in Neem oil based fungicide formulation as an economic and eco-friendly green solvent for sustainable waste management. Journal of cleaner production, 288, 125631.
[26] Nuruddeen, M. M. (2013), Influence of Neem Seed Husk Ash on the Tensile Strength of Concrete, American Journal, Volume-02, Issue-12, Pp-171-174.

www.ajer.org

[27] Oyegoke, T., Oyegoke, A. F., Fasanya, O. O., & Ibrahim, A. A. G. (2023). State of agro-wastes management in Nigeria: Status, Implications, and way Forward. In Waste Recovery and Management (pp. 241-272). CRC Press.
[28] Sharma, R., &Kole, C. (2019). Utilization of neem and neem products in agriculture. In The Neem Genome (pp. 31-48). Cham: Springer International Publishing.
Cite This Article
Plain Text BibTeX RIS

  • APA Style

    Adebayo, T. S., Kabir, A. (2025). Effect of Neem Seed Ash on the Geotechnical Properties of Lateritic Soil. Journal of Civil, Construction and Environmental Engineering, 10(6), 207-215. https://doi.org/10.11648/j.jccee.20251006.11

    Copy | Download

    ACS Style

    Adebayo, T. S.; Kabir, A. Effect of Neem Seed Ash on the Geotechnical Properties of Lateritic Soil. J. Civ. Constr. Environ. Eng. 2025, 10(6), 207-215. doi: 10.11648/j.jccee.20251006.11

    Copy | Download

    AMA Style

    Adebayo TS, Kabir A. Effect of Neem Seed Ash on the Geotechnical Properties of Lateritic Soil. J Civ Constr Environ Eng. 2025;10(6):207-215. doi: 10.11648/j.jccee.20251006.11

    Copy | Download 

  • @article{10.11648/j.jccee.20251006.11,
  author = {Tijanee Sharifdeen Adebayo and Abdulrauf Kabir},
  title = {Effect of Neem Seed Ash on the Geotechnical Properties of Lateritic Soil
},
  journal = {Journal of Civil, Construction and Environmental Engineering},
  volume = {10},
  number = {6},
  pages = {207-215},
  doi = {10.11648/j.jccee.20251006.11},
  url = {https://doi.org/10.11648/j.jccee.20251006.11},
  eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.jccee.20251006.11},
  abstract = {The impact of Neem Seed Ash (NSA) on the geotechnical properties of three clay soil samples classified as MH and CH by the Unified Soil Classification System is investigated in this study. The results of preliminary testing indicated moderate plasticity and load-bearing capacity, with natural moisture levels ranging from 7.2% to 9.38%, specific gravities from 2.66 to 2.75, and California Bearing Ratio (CBR) values from 13.42% to 19.8%. According to ASTM C618’s Class C classification, NSA's pozzolanic content of 52.01% was determined by chemical analysis. The engineering properties of the soils were significantly improved by NSA integration. As the NSA content rose, the specific gravity decreased, demonstrating the admixture's decreased density. Indicating improved soil workability and decreased plasticity, Atterberg limits showed a significant decline: liquid limits decreased from 37% to 12%, plastic limits from 27% to 11%, and the plasticity index from 14% to 2%. The maximum dry density increased to 2.37 g/cm3 at 6% NSA substitution, according to compaction tests, and the optimal moisture content decreased from 16% to 9.6%, indicating increased compaction efficiency. With 8% NSA replacement, the CBR values increased dramatically, reaching 44.1%, indicating a notable improvement in strength. These findings confirm that NSA is an effective stabilizing agent for difficult clay soils, enhancing their mechanical properties and potentially reducing environmental impacts and building costs. The study supports the use of NSA as an economical and environmentally friendly additive for stabilizing geotechnical soil.},
 year = {2025}
}

    Copy | Download 

  • TY  - JOUR
T1  - Effect of Neem Seed Ash on the Geotechnical Properties of Lateritic Soil

AU  - Tijanee Sharifdeen Adebayo
AU  - Abdulrauf Kabir
Y1  - 2025/11/05
PY  - 2025
N1  - https://doi.org/10.11648/j.jccee.20251006.11
DO  - 10.11648/j.jccee.20251006.11
T2  - Journal of Civil, Construction and Environmental Engineering
JF  - Journal of Civil, Construction and Environmental Engineering
JO  - Journal of Civil, Construction and Environmental Engineering
SP  - 207
EP  - 215
PB  - Science Publishing Group
SN  - 2637-3890
UR  - https://doi.org/10.11648/j.jccee.20251006.11
AB  - The impact of Neem Seed Ash (NSA) on the geotechnical properties of three clay soil samples classified as MH and CH by the Unified Soil Classification System is investigated in this study. The results of preliminary testing indicated moderate plasticity and load-bearing capacity, with natural moisture levels ranging from 7.2% to 9.38%, specific gravities from 2.66 to 2.75, and California Bearing Ratio (CBR) values from 13.42% to 19.8%. According to ASTM C618’s Class C classification, NSA's pozzolanic content of 52.01% was determined by chemical analysis. The engineering properties of the soils were significantly improved by NSA integration. As the NSA content rose, the specific gravity decreased, demonstrating the admixture's decreased density. Indicating improved soil workability and decreased plasticity, Atterberg limits showed a significant decline: liquid limits decreased from 37% to 12%, plastic limits from 27% to 11%, and the plasticity index from 14% to 2%. The maximum dry density increased to 2.37 g/cm3 at 6% NSA substitution, according to compaction tests, and the optimal moisture content decreased from 16% to 9.6%, indicating increased compaction efficiency. With 8% NSA replacement, the CBR values increased dramatically, reaching 44.1%, indicating a notable improvement in strength. These findings confirm that NSA is an effective stabilizing agent for difficult clay soils, enhancing their mechanical properties and potentially reducing environmental impacts and building costs. The study supports the use of NSA as an economical and environmentally friendly additive for stabilizing geotechnical soil.
VL  - 10
IS  - 6
ER  -

    Copy | Download

Author Information
Download PDF
Submit an Article
  • Abstract
  • Keywords

  • Document Sections

    1. 1. Introduction
    2. 2. Materials and Methodology
    3. 3. Results and Discussion
    4. 4. Conclusion
    Show Full Outline
  • Abbreviations
  • Conflicts of Interest
  • References
  • Cite This Article
  • Author Information

About Us

Science Publishing Group (SciencePG) is an Open Access publisher, with more than 300 online, peer-reviewed journals covering a wide range of academic disciplines.

Learn More About SciencePG

Products

Information

Important Link

Copyright © 2012 -- 2025 Science Publishing Group – All rights reserved.