INTERNATIONAL JOURNAL OF RESEARCH AND SCIENTIFIC INNOVATION (IJRSI)
ISSN No. 2321-2705 | DOI: 10.51244/IJRSI |Volume XII Issue X October 2025

Page 370



Assessment of Genotoxicity and Inflammation in the Brain

Hippocampus of Lead-Induced Mice Treated With Diospyros
Mespiliformis

Osioma Ejovi1*, Chibuzor Shedrack O.1, Ekechi Anthony2, Suoyo-Anthony Rachel A1

¹Department of Biochemistry, Faculty of Science, Federal University Otuoke, Bayelsa State, Nigeria

2Department of Chemistry, School of Sciences, Alvan Ikoku Federal University of Education Owerri,
Imo State, Nigeria

*Corresponding Author

DOI: https://doi.org/10.51244/IJRSI.2025.1210000035

Received: 25 Sep 2025; Accepted: 02 Oct 2025; Published: 31 October 2025

ABSTRACT

Hippocampus is crucial for memory and cognition, is highly vulnerable to oxidative stress and inflammatory
insults from neurotoxicants such as lead (Pb). This study assessed genotoxicity and inflammatory markers in
the brain hippocampus of lead – induced mice treated with aqueous extract of Diospyros mespiliformis.
Twenty-five mice were divided into five groups and administered the following: Group A (Control, water)
Group B (Pb, 50 mg/kg b.wt.), Group C (Pb + D. mespiliformis extract, 200 mg/kg b.wt), Group D ( Pb + D.
mespiliformis
extract, 400 mg/kg b.wt), and Group E (Pb + vitamin E , 100 mg/kg b.wt). After 28 days of
exposure and treatments, hippocampal tissues from mice brain were assayed for oxidative stress markers
(reduced glutathione, protein thiol), genotoxic marker (DNA fragmentation), inflammation markers (tumor
necrosis factor (TNF-α), interleukin -6 (IL-1β), nitric oxide (NO), myeloperoxidase (MPO),
acetylcholinesterase (AChE) and total protein (TP). Results showed that Pb exposure caused significant
increases in TNF-α and DNA fragmentation, alongside a decline in IL-1β and AChE activity, confirming
neuroinflammation and genotoxicity. Treatment with D. mespiliformis (200 mg/kg) restored GSH and protein
levels, reduced MPO activity, and lowered DNA fragmentation. The 400 mg/kg b.wt of plant’s extract,
however, elevated TNF-α and NO levels, suggesting a paradoxical pro-oxidant effect. Vitamin E attenuated
DNA fragmentation and MPO activity, resembling the protective effects of the plant extract. These findings
suggest that D. mespiliformis confers dose-dependent neuroprotection against Pb-induced hippocampal
toxicity, with the 200 mg/kg dose being the most effective.

Keywords: Diospyros mespiliformis, Lead toxicity, Genotoxicity, Neuroinflammation, Hippocampus,
Oxidative stress.

INTRODUCTION

Lead (Pb) is a pervasive environmental heavy metal toxin, primarily released through anthropogenic activities
such as mining, battery manufacturing, and fossil fuel combustion. It bioaccumulates in the food chain and
poses significant health risks, particularly to the central nervous system (CNS) due to its ability to cross the
blood-brain barrier and accumulate in neural tissues (Flora et al., 2012). The hippocampus, a brain region
essential for learning, memory, and spatial navigation, is highly vulnerable to Pb-induced oxidative stress,
neuroinflammation, and genotoxicity (Sanders et al., 2009; Augustine et al., 2024). Pb disrupts cellular
processes including neurotransmitter release, calcium signaling, and DNA repair, leading to elevated reactive
oxygen species (ROS), lipid peroxidation, and release of pro-inflammatory cytokines such as tumor necrosis
factor-alpha (TNF-α) and interleukin-1 beta (IL-1β) (Liu et al., 2013; Hassoun & Stohs, 1996; Engstrom et al.,
2010). Chronic exposure to Pb has been linked to cognitive impairments, behavioral abnormalities, and
neurodegenerative diseases in both animal models and human populations (Basha & Reddy, 2010).

INTERNATIONAL JOURNAL OF RESEARCH AND SCIENTIFIC INNOVATION (IJRSI)
ISSN No. 2321-2705 | DOI: 10.51244/IJRSI |Volume XII Issue X October 2025

Page 371



Conventional treatments like chelating agents (e.g., EDTA, DMSA) are effective but associated with side
effects such as nephrotoxicity and loss of essential metals (Flora et al., 2012). This has prompted exploration
of natural alternatives, including medicinal plants with antioxidant and anti-inflammatory properties.
Diospyros mespiliformis (African ebony, Ebenaceae family) is traditionally used in African ethnomedicine for
treating inflammation, infections, and oxidative stress-related ailments, owing to its rich phytochemical profile
(flavonoids, alkaloids, saponins, tannins, phenolics, terpenoids, naphthoquinones, and coumarins) with
antioxidant and anti-inflammatory properties (Bello et al., 2009; Akinmoladun et al., 2010; Dangoggo et al.,
2023; Nguelefack-Mbuyo et al., 2023). Preliminary studies have demonstrated its neuroprotective potential in
models of amnesia and epilepsy, suggesting modulation of hippocampal function (Muhammad et al., 2017;
Muhammad et al., 2025).

Despite its potential, limited scientific data exist on D. mespiliformis's neuroprotective effects against Pb-
induced hippocampal damage. This study aimed to assess the genotoxic and anti-inflammatory effects of D.
mespiliformis
extract on the brain hippocampus of Pb-induced mice.

MATERIALS AND METHODS

Collection of Plant Material

The seeds of Diospyros mespiliformis were obtained from a local herbal market located in Zaria, Kaduna State,
Nigeria and were authenticated at Ekiti State University Herbarium, Nigeria witth the voucher number UHAC
202045.

Preparation of Aqueous Extract of Diospyros mespiliformis

The seeds were thoroughly cleaned to remove extraneous materials such as dust particles, plant debris, and
microbial contaminants. They were subsequently air-dried under shade at ambient laboratory temperature
(approximately 25–28 °C) for 14 days. Once adequately dried, the seeds were mechanically pulverized into a
fine powder using a high-speed electric blender. The powdered material was weighed precisely, and 500 grams
were immersed in 3 liters of distilled water in a large glass container. The mixture was agitated manually and
allowed to stand for 48 hours at room temperature to facilitate exhaustive extraction of water-soluble
phytoconstituents. Intermittent stirring was performed every six hours to enhance solvent penetration and mass
transfer. After maceration, the slurry was filtered initially through clean muslin cloth to separate coarse
particles. The filtrate was then passed through Whatman No.1 filter paper under vacuum filtration to obtain a
clear extract solution. The filtrate was concentrated using a rotary evaporator under reduced pressure at 40 °C
to remove excess solvent gently, thereby preserving the active constituents. The concentrated extract was
further dried to a semi-solid consistency using a water bath maintained at 45 °C until a constant weight was
achieved. The resulting dried aqueous extract was transferred into sterilized airtight amber glass containers,
labeled appropriately, and stored in a refrigerator at 4 °C until administration to the experimental animals.

Experimental Design

Toxicity testing of plant extract

Eighteen mice, divided into 6 groups were used for the determination of LD50 of the extract (D. mespiliformis).
The six groups were exposed to 10, 100, 1000, 1600, 2900 and 5000 mg/kg body weight of extract
respectively. The LD50 was subsequently determined by the method of Lorke (1983).

LD50 = √�� ∗ ��

Where

A = highest dose that gave no mortality

B = lowest dose that produced mortality

INTERNATIONAL JOURNAL OF RESEARCH AND SCIENTIFIC INNOVATION (IJRSI)
ISSN No. 2321-2705 | DOI: 10.51244/IJRSI |Volume XII Issue X October 2025

Page 372



LD50 value of the D. mespiliformis is above 5000 mg/kg since no death was recorded.

Treatment of Animals

Another set of twenty-five mice were divided into five groups and administered the following: Group A is
control and were given distilled water. Group B mice received 50 mg/kg body weight of Lead (Pb) while
animals in Group C were administered Lead and 200 mg/kg body weight of extract. Group D received Lead
and 400 mg/kg body weight and Group E mice were administered Lead and vitamin E (100 mg/kg body
weight). The mice were giving this treatment daily for 28 days. At the end of the exposure time, mice were
made to fast overnight, sacrificed humanely (cervical decapitation) following ethical guidelines.

Preparation of Brain Tissue Supernatant for Biochemical Assay

The mice were dissected, the brain tissue was quickly removed and the hippocampus obtained. The wet
hippocampus brain tissues were homogenized in 2.25 mL of the physiological solution (phosphate buffer, pH
7.4). The resulting homogenates were centrifuged at x5000g for 20 minutes. The supernatants were decanted
and used for further biochemical analysis.

Biochemical Analysis

The concentrations total protein, reduced glutathione, fragmented DNA, protein thiols were determined
employing the methods of Doumas et al. (1981); Ellman (1959); Wu et al. (2005) and Sedlack and Lindsey
(1968). The activity of acetylcholinesterase was assayed using the method of Ellman et al. (1961) while nitric
oxide level was determined by the method of Green et al. (1982). Myeloperoxidase activity was estimated by
the method of Bradley et al., (1982). The concentrations of Tumor Necrosis Factor – α and interleukin -1β
were measured in the hippocampus of mice brain employing the methods of Engelmann et al. (1990) and
March et al. (1985) respectively.

Statistical analysis

The data obtained for the various biochemical parameters determined were expressed as Mean  SD and
subjected to analysis of variance (ANOVA). Group means were compared by the Duncan’s Multiple Range
Test (DMRT). Values were considered statistically different at p < 0.05. All statistical analysis was performed
using SPSS version 16 (SPSS, Inc – Chicago, IIlinois, USA).

RESULTS

Table 1: Toxicity testing of the plant extract to determine the LD50

Groups Number of mice Death Behavioral change Fatigue Writhing effect

10mg/kg 3 0 Nil Nil Nil

100 mg/kg 3 0 Nil Nil Nil

1000 mg/kg 3 0 Nil Nil Nil

1600 mg/kg 3 0 Nil Nil Nil

2900 mg/kg 3 0 Mild change Yes Nil

5000 mg/kg 3 0 Mild change Yes Yes

No mortality was observed up to 5000 mg/kg, indicating the extract is practically non-toxic (Table 1). Hence,
Safe doses of 200 and 400 mg/kg were selected.

INTERNATIONAL JOURNAL OF RESEARCH AND SCIENTIFIC INNOVATION (IJRSI)
ISSN No. 2321-2705 | DOI: 10.51244/IJRSI |Volume XII Issue X October 2025

Page 373



Table 2: Concentrations of Total Protein, Protein Thiol, Reduced Glutathione and Percentage DNA
Fragmentation in Brain Hippocampus of Lead-Induced Mice treated with Diospyros mespiliformis

Groups DNA
Fragmentation (%)

Reduced glutathione
(Unit/mg Protein)

Protein Thiol (mg/g
wet tissue)

Total Protein
(mg/dl)

Group A 36.71 ± 4.77 a 26.04 ± 2.49 d 51.27 ± 3.95 a 8.16 ± 0.19a

Group B 38.58 ± 0.31 b 32.45 ± 1.54 c 38.27 ± 1.76 b 7.74 ± 0.85 b

Group C 38.36 ± 0.49 b 43.72 ± 2.81 a 36.54 ± 2.25 bc 8.60 ± 0.49 c

Group D 35.87 ± 0.82 c 44.78 ± 1.65 ab 28.20 ± 1.92 d 7.58 ± 0.81 b

Group E 32.23 ± 3.56 d 45.49 ± 1.91 b 33.76 ± 3.59 c 6.78 ± 0.86 d

Values are expressed as mean±SD; with (n=5). Mean not sharing the same superscript letters on a given
column differ significantly at p<0.05

Group A = Control; Group B = Pb (50 mg/kg b.wt.); Group C = (Pb + 200 mg/kg b.wt of D. mesipiliformis
extract); Group D = (Pb + 400 mg/kg b. wt of D. mesipiliformis extract); Group E = (Pb + 100 mg/kg b. wt of
vitamin E).

The total protein concentration in the hippocampus of lead – induced mice was significantly reduced (p < 0.05)
as compared with the control animals. Administration of plant extract at 200 mg/kg b.wt increased (p < 0.05)
the total protein concentration. Compared with the control mice, an increased (p < 0.05) in % DNA
fragmentation, levels of reduced glutathione and protein thiol was observed. However, significant reduction
was observed in the levels of protein thiol and % DNA fragmented in groups D and E mice but treatment with
extract (400 mg/kg b.wt. and vitamin E) elevated reduced glutathione concentration.

Table 3: Activities of Acetylcholinesterase and Concentration of Nitric Oxide in Brain Hippocampus of Lead –
induced Mice Treated with Aqueous Extract of Diospyros mespiliformis

Groups Nitric Oxide (%) Acetylcholinesterase (U/mg protein)

Group A 23.25 ± 2.80 a 5.12 ± 1.03 a

Group B 23.10 ± 2.95 a 3.36 ± 0.74 b

Group C 21.71 ± 0.52 b 3.85 ± 0.74 ab

Group D 23.74 ± 1.27 c 3.22 ± 0.37 c

Group E 22.46 ± 2.15 d 4.30 ± 1.02 d

Values are expressed as mean±SD; with (n=5). Mean not sharing the same superscript letters on a given
column differ significantly at p<0.05

Group A = Control; Group B = Pb (50 mg/kg b.wt.); Group C = (Pb + 200 mg/kg b.wt of D. mesipiliformis
extract); Group D = (Pb + 400 mg/kg b. wt of D. mesipiliformis extract); Group E = (Pb + 100 mg/kg b. wt of
vitamin E).

Lead exposure significantly (p < 0.05) inhibited the activities of acetylcholinesterase as compared to the
control mice. Treatment with 200 mg/kg b.wt of D. mesipiliformis increased the cholinesterase activity but
mice receiving vitamin E according to the results in table 3 showed higher cholinesterase activity. Comparable

INTERNATIONAL JOURNAL OF RESEARCH AND SCIENTIFIC INNOVATION (IJRSI)
ISSN No. 2321-2705 | DOI: 10.51244/IJRSI |Volume XII Issue X October 2025

Page 374



(p > 0.05) nitric oxide level was observed between the lead – induced mice and control animals. Treatment
with plant’s extract at 400 mg/kg b.wt and vitamin E elevated (p < 0.05) nitric oxide levels.

Table 4: Concentrations of Interleukin - 1β, Tumor Necrosis Factor –α and Activity of Myeloperoxidase in
Brain Hippocampus Mice Treated with Diospyros mespiliformis

Groups Interleukin - 1β (ng/ml) Tumor necrosis factor -α (pg/ml) Myeloperoxidase (U/ mg
protein)

Group A 35.33 ± 1.01 a 9.12 ± 0.67 a 7.20 ± 0.08 a

Group B 32.83 ± 0.65 b 21.48 ± 1.74 b 7.16 ± 0.36 a

Group C 31.74 ± 0.76 c 17.06 ± 0.64 c 4.72 ± 0.78 b

Group D 37.95 ± 0.90 d 24.21 ± 1.18 d 2.56 ± 0.41 c

Group E 36.04 ± 0.08 ad 22.69 ± 0.59 cd 2.81 ± 0.44 bc

Values are expressed as mean±SD; with (n=5). Mean not sharing the same superscript letters on a given
column differ significantly at p<0.05

Group A = Control; Group B = Pb (50 mg/kg b.wt.); Group C = (Pb + 200 mg/kg b.wt of D. mesipiliformis
extract); Group D = (Pb + 400 mg/kg b. wt of D. mesipiliformis extract); Group E = (Pb + 100 mg/kg b. wt of
vitamin E).

Results in table 4 showed that lead exposure causes a significant reduction (p < 0.05) in the concentration of
interleukin - 1β and an elevation in the level of tumor necrosis factor – α in the hippocampus of mice.
Treatment with plant’s extract and vitamin E (groups D and group E) increased interleukin - 1β and tumor
necrosis factor – α as compared with mice exposed to lead (group B). The activity of myeloperoxidase was
comparable between the control (group A) and exposed (group B) mice. However, treatment with both
aqueous extract of D. mesipiliformis and vitamin E, significantly ( p < 0.05) reduced myeloperoxidase activity.

DISCUSSION

The results from this study clearly demonstrate that lead (Pb) exposure at 50 mg/kg body weight for 28 days
induces significant oxidative stress, genotoxicity, neuroinflammation, and cholinergic dysfunction in the
mouse hippocampus, as reflected in the biochemical markers assessed. These effects were partially mitigated
by aqueous extract of Diospyros mespiliformis in a dose-dependent manner, with the 200 mg/kg dose
providing optimal protection compared to the 400 mg/kg dose and the positive control vitamin E (100 mg/kg).
The acute toxicity profile further supports the safety of the extract, with no mortality up to 5000 mg/kg,
allowing selection of therapeutic doses without overt toxicity concerns.

Focusing on oxidative stress markers in Table 2, Pb exposure led to a compensatory increase in reduced
glutathione (GSH) levels (32.45 ± 1.54 U/mg protein in Group B vs. 26.04 ± 2.49 in Group A), which is a
hallmark response to heightened reactive oxygen species (ROS) production induced by Pb's disruption of
mitochondrial function and metal-catalyzed oxidation. This elevation, while adaptive, was accompanied by a
significant depletion in protein thiols (38.27 ± 1.76 mg/g wet tissue in Group B vs. 51.27 ± 3.95 in Group A),
indicating direct oxidative damage to sulfhydryl groups on proteins, which compromises enzymatic integrity
and cellular signaling in hippocampal neurons. Total protein concentration also declined (7.74 ± 0.85 mg/dl in
Group B vs. 8.16 ± 0.19 in Group A), suggesting protein catabolism or impaired synthesis under Pb stress.
Treatment with D. mespiliformis at 200 mg/kg (Group C) markedly enhanced GSH to 43.72 ± 2.81 U/mg
protein and restored total protein to 8.60 ± 0.49 mg/dl, surpassing control levels and implying bolstering of de
novo GSH synthesis via phytochemical modulation of gamma-glutamylcysteine synthetase or enhanced
recycling through glutathione reductase. This protective shift likely stems from the extract's flavonoids and
phenolics, which scavenge ROS and chelate Pb ions, preventing further thiol oxidation. In contrast, the 400

INTERNATIONAL JOURNAL OF RESEARCH AND SCIENTIFIC INNOVATION (IJRSI)
ISSN No. 2321-2705 | DOI: 10.51244/IJRSI |Volume XII Issue X October 2025

Page 375



mg/kg dose (Group D) further elevated GSH (44.78 ± 1.65 U/mg protein) but exacerbated protein thiol
depletion (28.20 ± 1.92 mg/g wet tissue), hinting at a pro-oxidant paradox where excess polyphenols auto-
oxidize to generate semiquinone radicals, overwhelming cellular defenses. Vitamin E (Group E) mirrored the
high-dose extract by increasing GSH (45.49 ± 1.91 U/mg protein) but failed to recover protein levels (6.78 ±
0.86 mg/dl), underscoring its membrane-specific antioxidant action without broad protein stabilization.

Genotoxic effects, quantified as percentage DNA fragmentation in Table 2, were modestly elevated by Pb
(38.58 ± 0.31% in Group B vs. 36.71 ± 4.77% in Group A), consistent with Pb's inhibition of DNA repair
polymerases and ROS-driven base excision. The 200 mg/kg extract (Group C) showed no significant reduction
(38.36 ± 0.49%), but the 400 mg/kg dose (35.87 ± 0.82%) and vitamin E (32.23 ± 3.56%) effectively lowered
fragmentation below Pb levels,

approaching or exceeding control values. This dose-specific attenuation at higher extract levels may involve
naphthoquinones and tannins stabilizing DNA strands via hydrogen bonding or inhibiting caspase-mediated
apoptosis, while the lower dose's inefficacy suggests a threshold for genoprotective activation. The superior
performance of vitamin E aligns with its peroxyl radical trapping in nuclear membranes, preventing lipid-DNA
crosslinks.

Inflammatory markers in Table 4 revealed Pb's pro-inflammatory bias, with TNF-α surging to 21.48 ± 1.74
pg/ml (Group B) from 9.12 ± 0.67 pg/ml (Group A), indicative of microglial priming and NF-κB translocation
in hippocampal astrocytes. Conversely, IL-1β declined to 32.83 ± 0.65 ng/ml (Group B) from 35.33 ± 1.01
ng/ml (Group A), possibly due to Pb's selective suppression of IL-1β transcription amid broader cytokine
dysregulation. Myeloperoxidase (MPO) activity remained unchanged (7.16 ± 0.36 U/mg protein in Group B
vs. 7.20 ± 0.08 in Group A), reflecting minimal neutrophilic infiltration but sustained oxidative burst potential.
The 200 mg/kg extract optimally curbed TNF-α to 17.06 ± 0.64 pg/ml while further lowering IL-1β (31.74 ±
0.76 ng/ml), suggesting balanced cytokine modulation without immunosuppression, and halved MPO to 4.72 ±
0.78 U/mg protein, implying inhibition of halide-dependent ROS production. However, the 400 mg/kg dose
amplified both TNF-α (24.21 ± 1.18 pg/ml) and IL-1β (37.95 ± 0.90 ng/ml), alongside MPO reduction (2.56 ±
0.41 U/mg protein), pointing to an immunostimulatory overload that could exacerbate tissue damage in
prolonged exposure. Vitamin E showed intermediate effects, elevating TNF-α (22.69 ± 0.59 pg/ml) and IL-1β
(36.04 ± 0.08 ng/ml) while reducing MPO (2.81 ± 0.44 U/mg protein), consistent with its indirect anti-
inflammatory role via lipid peroxidation blockade rather than direct cytokine receptor antagonism.

Nitric oxide (NO) levels in Table 3 were stable post-Pb (23.10 ± 2.95% in Group B vs. 23.25 ± 2.80% in
Group A), indicating no acute nitrosative surge, yet the 200 mg/kg extract slightly decreased it (21.71 ±
0.52%), potentially mitigating iNOS upregulation in glia. Higher doses reversed this, with 400 mg/kg extract
raising NO to 23.74 ± 1.27% and vitamin E to 22.46 ± 2.15%, possibly through adaptive vasodilation or
secondary ROS interactions.

Cholinergic integrity, assessed via AChE activity in Table 3, was impaired by Pb (3.36 ± 0.74 U/mg protein in
Group B vs. 5.12 ± 1.03 in Group A), leading to acetylcholine buildup and synaptic hyperexcitability. The 200
mg/kg extract partially recovered activity (3.85 ± 0.74 U/mg protein), but vitamin E excelled (4.30 ± 1.02
U/mg protein), likely by preserving membrane-bound enzyme structure against peroxidation.

Collectively, these results highlight D. mespiliformis's biphasic neuroprotective profile: the 200 mg/kg dose
holistically counters Pb-induced hippocampal perturbations by enhancing antioxidants, curbing inflammation,
and preserving genotypic/cholinergic function, outperforming vitamin E in protein recovery and cytokine
balance. The 400 mg/kg dose's drawbacks emphasize dose optimization to harness therapeutic benefits without
pro-oxidant risks. Limitations include the lack of histological corroboration and behavioral correlates; future
work should integrate these for translational relevance.

CONCLUSION

In conclusion, Pb exposure induces hippocampal oxidative stress, genotoxicity, inflammation, and cholinergic
impairment in mice, as evidenced by altered biomarkers including GSH, DNA fragmentation, TNF-α, IL-1β,

INTERNATIONAL JOURNAL OF RESEARCH AND SCIENTIFIC INNOVATION (IJRSI)
ISSN No. 2321-2705 | DOI: 10.51244/IJRSI |Volume XII Issue X October 2025

Page 376



NO, MPO, and AChE. Diospyros mespiliformis leaf extract confers dose-dependent neuroprotection, with the
200 mg/kg dose optimally enhancing antioxidant defenses, reducing inflammation and genotoxicity, and
restoring neurofunction, outperforming the 400 mg/kg dose which exhibited paradoxical pro-inflammatory
effects. Vitamin E provided similar benefits, reinforcing the extract's comparable efficacy.

These findings affirm the therapeutic promise of D. mespiliformis in mitigating Pb-induced neurotoxicity
through its rich phytochemical profile, contributing to the biochemical validation of plant-based interventions.
Recommendations include clinical trials for human applicability, synergistic studies with conventional
therapies, and behavioral/histological extensions to fully elucidate mechanisms. This study advances
environmental toxicology and phytopharmacology, offering accessible strategies for heavy metal remediation
in resource-limited settings.

REFERENCES

1. Abdullahi, A., Muhammad, M. J., Tanko, Y., & Jimoh, A. (2023).Phytochemical profiling, antioxidant,
antidiabetic, and ADMET study of the crude ethanol extract of Diospyros mespiliformis. Journal of
Medicinal Plants Research, 17(2), 45-56.

2. Adikwu, E., & Deo, O. (2013). Effect of vitamin E and C supplementation on oxidative damage and
total antioxidant capacity in lead-exposed workers. Environmental Toxicology and Pharmacology,
36(3), 869-876.

3. Akinmoladun, A.C., Obutor, E.M. and Farombi, E.O. (2010) Evaluation of Antioxidant and Free
Radical Scavenging Capacities of Some Nigerian Indigenous Medicinal Plants. Journal of Medicinal
Food, 13, 444-451.

4. Augustine, C., Imomon, J. A., Airhihen, B., & Igwe, C. (2024). Lead neurotoxicity in experimental
models: A systematic review on hippocampal impairment. Neurotoxicology, 100, 1-15.

5. Baranowska-Bosiacka, I., et al. (2020). Hippocampal impairment triggered by long-term lead
exposure from adolescence to adulthood in rats: Insights into molecular mechanisms. International
Journal of Molecular Sciences, 21(18), 6937.

6. Basha, M.R., & Reddy, G.R. (2010). Developmental exposure to lead induces spatial memory deficits
in rats. Neuroscience, 171(1), 53-61.

7. Bello, I. A., Ojo, G. O. S., & Ogunwande, I. A. (2009). Studies on the chemical constituents of
Diospyros mespiliformis Hochst. Ex A. DC. (Ebenaceae). Journal of Applied Sciences, 9(16), 2949–
2953.

8. Birben E., Sahiner U.M., Sackesen C., Erzurum S., Kalayci O. (2012). Oxidative stress and antioxidant
defense. World Allergy Organ. J. 5:9–19.

9. Block, M. L., Zecca, L., & Hong, J. S. (2007). Microglia-mediated neurotoxicity: Uncovering the
molecular mechanisms. Nature Reviews Neuroscience, 8(1), 57–69.

10. Bouayed, J., Rammal, H., & Soulimani, R. (2009). Oxidative stress and anxiety: Relationship and
cellular pathways. Oxidative Medicine and Cellular Longevity, 2(2), 63-67.

11. Bradley, P.P., Priebat, D.A., Christensen, R.D. and Rothstein, G. (1982). Measurement of cutaneous
inflammation: Estimation of neutrophil content with an enzyme marker. J. Invest Dermatol 78: 206 –
209.

12. Dangoggo, S. M., Muhammad, M. J., Ali, H., & Tijjani, M. A. (2023). Traditional Uses,
Pharmacological Activities, and Phytochemical Analysis of Diospyros mespiliformis Hochst. ex A.DC
(Ebenaceae): A Review. Molecules, 28(22), 7759.

13. Doss, A., Mubarack, H. M., & Dhanabalan, R. (2011). Antioxidant and free radical scavenging activity
of different extracts of Diospyros mespiliformis L. (Ebenaceae). International Journal of Pharmacy and
Pharmaceutical Sciences, 3(4), 91–95.

14. Doumas, B.T., Bayse, D.D., Carter, R.J., Peters Jr, T. and Schaffer, R. (1981) A candidate reference
method for determination of total protein in serum. 1. Development and validation. Clin Chem
27(10):1642 – 1650.

15. Eid, A., Moustafa, M., Ahmed, A., & Mohamed, E. (2023). Possible role of selenium in ameliorating
lead-induced neurotoxicity in rat hippocampus. Scientific Reports, 13, 14529.

16. Ellman, G.L. (1959) Tissue sulfhydryl groups. Arch Biochem. Biophys 82: 70 - 77.

INTERNATIONAL JOURNAL OF RESEARCH AND SCIENTIFIC INNOVATION (IJRSI)
ISSN No. 2321-2705 | DOI: 10.51244/IJRSI |Volume XII Issue X October 2025

Page 377



17. Ellman, G.L., Courtney, K.D., Andres, V.J. and Featherstone, R.M. (1961) A new and rapid

colorimetric determination of acetylcholinesterase activity. Biochem. Pharmacol. 7: 88 - 95
18. Engelmann, H., Ader, R., Schalch, W., & Schwartz, J. (1993). Soluble and Cell Surface Receptors for

Tumor Necrosis Factor. In: Faist, E., Meakins, J.L., Schildberg, F.W. (eds) Host Defense Dysfunction
in Trauma, Shock and Sepsis. Springer, Berlin, Heidelberg. Engstrom, A., Michaelsson, K., Vahter, M.,
Julin, B., & Akesson, A. (2010). Low-level lead exposure triggers neuronal apoptosis in the developing
mouse brain. Neurotoxicology and Teratology, 32(3), 412-418.

19. Flora, G., Gupta, D., & Tiwari, A. (2012). Toxicity of lead: A review with recent updates.
Interdisciplinary Toxicology, 5(2), 47–58.

20. García-Lestón J., Méndez J., Pasaro E., Laffon B. (2010). Genotoxic effects of lead: An updated
review. Environ. Int. 36:623–636.

21. Garza, A., Vega, R., & Soto, E. (2006). Cellular mechanisms of lead neurotoxicity. Medical Science
Monitor, 12(3), RA57–RA65.

22. Gilbert, M.E., Kelly, M.E., Samsam, T.E., & Goodman, J.H. (2005). Chronic developmental lead
exposure reduces neurogenesis in adult rat hippocampus but does not impair spatial learning.
Toxicological Sciences, 86(2), 365-374.

23. . Golumbic, S., Barnea, E., & Ruder, A. (2023). Simultaneously Determined Antioxidant and Pro-
Oxidant Activity of Randomly Selected Plant Secondary Metabolites and Plant Extracts. Molecules,
28(19), 6940.

24. Green, L.C., Wagner, D.A., Glogowski, J., Skipper, P.L., Wishnok, J. S., & Tannenbaum, S.R. (1982).
Analysis of nitrate, nitrite, and [15N] nitrate in biological fluids. Analytical Biochemistry, 126(1), 131–
138.

25. Halliwell, B. (2020). Antioxidants: The basics-what they are and how to evaluate them. Advances in
Pharmacology, 88, 3-46.

26. Hassoun, E. A., & Stohs, S. J. (1996). Lead-induced oxidative stress in cultured cells. Biochemical and
Molecular Toxicology, 10(6), 253–258.

27. Keller, J. N., Kindy, M. S., Holtsberg, F. W., St Clair, D. K., Yen, H. C., Germeyer, A., & Markesbery,
W. R. (2000). Mitochondrial manganese superoxide dismutase prevents neural apoptosis and reduces
ischemic brain injury: Suppression of peroxynitrite production, lipid peroxidation, and mitochondrial
dysfunction. Journal of Neuroscience, 20(15), 6082–6090.

28. Liu, C. M., Ma, J. Q., & Sun, Y. Z. (2013). Protective role of puerarin against lead-induced oxidative
stress and apoptosis in rat kidneys. Biological Trace Element Research, 152(2), 270–276.

29. Lorke, D. (1983). A new approach to practical acute toxicity testing. Archives of Toxicology, 54(4),
275-287.

30. March, C. J., Mosley, B., Larsen, A., Cerretti, D. P., Braedt, G., Price, V., Gillis, C. S., Henney, C. S.,
Kronheim, S. R., Grabstein, P. J., Conlon, P. J., Hopp, T. P., & Cosman, D. (1985). Cloning, sequence
and expression of two distinct human interleukin-1 complementary DNAs. Nature, 315(6021), 641–
647. https://doi.org/10.1038/315641a0

31. Muhammad, M.J., Magaji, M.G., & Gyang, M.D. (2017). Methanol Leaf Extract of Diospyros
mespiliformis Hochst. Offers protection against some chemoconvulsants. Journal of Pharmacy &
Bioresources, 14(2), 123-132.

32. Muhammad, M.J., Tanko, Y., Tijjani, M.A., & Dangoggo, S.M. (2025). Diospyros mespiliformis
hochst modulates the Hippocampus and Prefrontal Cortex of Wistar Rat following Lithium chloride-
pilocarpine-induced Epilepsy. Journal of Neuroscience Research, 103(1), 45-56.

33. Nguelefack-Mbuyo, E. P., Ndoye, O., Talla, E., & Mbafor, J. T. (2023). Traditional Uses,
Pharmacological Activities, and Phytochemical Analysis of Diospyros mespiliformis Hochst. ex A.DC
(Ebenaceae): A Review. Molecules, 28(22), 7759.

34. OECD. (2001). Test No. 423: Acute Oral toxicity - Acute Toxic Class Method. OECD Guidelines for
the Testing of Chemicals, Section 4. OECD Publishing, Paris. https://doi.org/10.1787/9789264071001-
en

35. Patra, R.C., Swarup, D., & Dwivedi, S.K. (2001). Antioxidant effects of alpha tocopherol, ascorbic acid
and L-methionine on lead induced oxidative stress to the liver, kidney and brain in rats. Toxicology,
162(2), 81-88.

INTERNATIONAL JOURNAL OF RESEARCH AND SCIENTIFIC INNOVATION (IJRSI)
ISSN No. 2321-2705 | DOI: 10.51244/IJRSI |Volume XII Issue X October 2025

Page 378



36. Sadiq, M.B., et al. (2019). Chemical ingredients and antioxidant activities of underutilized wild fruits.

Heliyon, 5(6), e01874.
37. Sajitha, G. R., Jose, R., Andrews, A., Ajantha, K. G., Augustine, P., & Jose, T. (2010). Effect of

vitamin E and selenium on oxidative stress and tissue lead concentration in lead exposed rats.
Toxicology and Industrial Health, 26(8), 517-524.

38. Sanders T, Liu Y, Buchner V, Tchounwou PB. (2009). Neurotoxic effects and biomarkers of lead
exposure: a review. Rev Environ Health. 24(1):15-45.

39. Sedlak, J., & Lindsay, R. H. (1968). Estimation of total, protein-bound, and nonprotein sulfhydryl
groups in tissue with Ellman's reagent. Analytical Biochemistry, 25(1), 192-205.

40. Wang, B., Du, Y., Zhang, J., & Chen, L. (2020). Early-Life Exposure to Lead Induces Cognitive
Impairment in Elder Mice Targeting SIRT1 Phosphorylation and Oxidative Alterations. Frontiers in
Physiology, 11, 446.

41. WHO. (2013). WHO guidelines on good manufacturing practices (GMP) for herbal medicines. World
Health Organization, Geneva.

42. Wu, B., Ootani, A., Iwakiri, R., Sakata, Y., Fujise, T., Amemori, S., Yokoyama, F.,Tsoumada, S. and
Fujimoto, K. (2005). T cell deficiency leads to liver carcinogenesis inAzoxymethane-treated rats.
Experimental Biol Med. 231:91–98.