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A mitochondria targeting Ir(III) complex triggers ferroptosis and autophagy for cancer therapy: A case of aggregation enhanced PDT strategy for metal complexes
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© 2025 IJCRT | Volume 13, Issue 6 June 2025 | ISSN: 2320-2882
Computational Analysis For The Prediction Of
Key Genes Affected By The Exposure Of
Microplastics
Ananya Singh, Prachi Srivastava
Amity institute of biotechnology
Amity University Uttar Pradesh, Lucknow, India
ABSTRACT:
Humans and other biological entities are at a great risk from microplastics, which are ubiquitous in both marine
and terrestrial ecosystems. Their capacity to transport and absorb harmful substances is demonstrated by recent
research, which suggests that they may be the source of a number of health problems. By offering insights into
the fundamental molecular processes and aiding in the development of abatement techniques, computational
biology has emerged as a critical method for identifying important genes impacted by microplastic exposure.
This work uses databases and bioinformatics methods, such as MalaCard, GeneCard, and OMIM to find and
examine the genes that are affected by exposure to microplastics. Additionally, utilizing 12 distinct cytohubba
characteristics, the protein-protein interaction networks were examined in order to identify the hub gene.
"TNF" protein was identified as the key regulator of the network. A list of phytochemicals was also carefully
selected after a thorough review of the literature in order to determine which ones would be useful in protecting
against the exposure to microplastics. Using ADMETLab 3.0, the drug-like properties of these phytochemicals
were tested. The structure of the key hub gene, that is, TNF was modeled using Swiss-Model. Molecular
docking studies were done to explore the potential of phytochemicals against TNF. Molecular docking studies
revealed the potential role of “Ellagic Acid” that has the highest binding energy of “-9.36” in the management
of microplastics exposure in human. This study underscores the pervasive threat of microplastics to both human
health and the environment, highlighting their ability to transport harmful substances. Computational biology
has played a pivotal role in identifying key genes affected by microplastic exposure, with TNF emerging as a
critical regulator. Through molecular modeling and docking studies, Ellagic Acid shows promising potential
as a therapeutic agent against microplastic-induced health risks.
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Keywords: Network biology, Computational biology, TNF, Mircoplastic, Molecular modeling, Exposure
management, Gingerol, Binding energy.
INTODUCTION:
At the moment, microplastics stand to be one of the most pervasive environmental problems, with some
potential adverse impacts on ecosystems and human health. These small plastic particles, less than 5 mm in
size, come from sources similar to breaking down larger plastic items, industrial activities, and decaying of
plastic wastes. Because they are so small and nondigestible, microplastics can easily be consumed by many
organisms at all trophic levels of the food chain, fast becoming of concern to the environment.
While the physical and chemical consequences of microplastic pollution have been extensively studied, their
biological effects, particularly at the molecular level, remain largely unexplored. Understanding how
microplastics influence gene expression in organisms is crucial for assessing their ecological ramifications
comprehensively. Traditional experimental approaches are often limited in their ability to capture the complex
and dynamic nature of gene expression alterations induced by microplastic exposure across diverse species
and environmental conditions.
Environmental MPs are able to enter the human body, pass through biological barriers, and be further
distributed in the organism. [R. Dris et al., M. Bläsing et al.] The accumulation of MPs in tissues can lead to a
variety of adverse effects: from oxidative stress and immunological inflammation to cellular damage,
endothelial leakiness, neurotoxicity, and metabolic problems. The MPs' unique features in physical and
chemical characteristics can make the central nervous system sensitive to them even with the blood-brain
barrier. The reports by [B. Chai et al., S. Feng et al., and T.A. Kurniawan et al.] relate that the damaging of the
BBB, neurological function impairment, and transfer of MPs into the brain can occur. These effects may
potentially accelerate the development and progression of neurodevelopmental and neurodegenerative
diseases. Nevertheless, most of the research works have focused on the general risks of microplastics to the
human body, with few studies involving their neurotoxic effects. The more recent reviews focus mainly on
summarizing the neurotoxic effects either in different test subjects or the behavior of microplastics within a
cell. [C.G. Avio et al.], [G. Erni-Cassola et al.] Further research into the neural diseases MPs can provoke is
required.
Literature published between 2000 and 2024 was retrieved by an online search of the Web of Science databases
with the support of the following keywords: Microplastics, nanoplastics, environmental risk, neurotoxicity,
human exposure, and neurological illnesses compose a series of interconnected concerns. In this work, focusing
on neurotoxic effects on human health as a result of MPs and NPs, we have done an overview of the literature.
A general overview on MPs and NPs as a risk for human health and the environment by [J.C. Prata],
mechanisms opening MPs' and NPs' passage into the brain by [H.A. Leslie et al.], neurotoxic effects of MPs
and NPs on abnormalities in neurodevelopment and neurodegeneration by [K. Yin et al.], and lastly, by [J.Q.
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Jiang], possible mechanisms by which MPs and NPs cause neurotoxicity. This will help in increasing the
knowledge regarding the strength of connection of MPs and NPs with the developing neurodevelopmental and
neurodegenerative disorders. Plastic pollution and its health effects are a concern not just for human health but
for sustainable development of the ecosystem itself.
We hereby propose a computational framework for predicting key genes affected by microplastic exposure.
Our approach will harness the power of bioinformatics, equipped with cutting-edge data-driven methodologies,
to integrate multi-omics information. It applies transcriptomics, proteomics, and metabolomics in the study of
molecular mechanisms underlying microplastic toxicity. This large dataset, acquired either from model
organisms or environmental samples, will be analyzed to identify conserved molecular signatures associated
with microplastic exposure that would facilitate cross-species comparisons and generalizations.
The utilization of computational methods offers several advantages in studying microplastic-induced gene
expression changes. Firstly, it enables the simultaneous analysis of multiple datasets, allowing for a
comprehensive assessment of gene expression alterations across different biological systems. Secondly, by
employing machine learning algorithms and network-based approaches, we can uncover hidden patterns and
interactions within complex biological data, elucidating the intricate regulatory networks modulated by
microplastic exposure. Lastly, computational predictions can guide experimental studies by prioritizing
candidate genes and pathways for further validation, thereby accelerating the discovery of novel biomarkers
and therapeutic targets for mitigating microplastic pollution.
In summary, this computational analysis holds promise in advancing our understanding of the molecular
responses to microplastic exposure, shedding light on the potential risks posed by microplastics to
environmental and human health. By elucidating the underlying mechanisms driving microplastic toxicity, our
findings may inform regulatory policies and management strategies aimed at mitigating the impacts of
microplastic pollution on ecosystems worldwide.
Plastic contamination has been one of the most challenging materials in the world over the recent past. Ten
percent of the globally produced plastics each year end up in water as wastes. According to Borrelle et al.,
plasty can fragment slowly, resulting in secondary microplastics measuring between 0.1 µm and 5 mm and
secondary nanoplastics of less than 100 nm. It has recently been demonstrated that up to 16 million nano- and
microplastic particles per liter can be detected in polypropylene baby feeding bottles.[ Li and associates],
While A single source can release 3.1 billion nanoplastics and 11.6 billion microplastic teabag in boiling
water.[Hernandez and others], [A. Mirzaie et al.] Besides, very usual food packaging, such as paper cups, takeout boxes, and instant noodle packets releases the nanoplastics into the environment.[ Li and co-workers],
These nanoparticles, following their ingestion, become capable of entering the body tissues and producing
devastating toxicological effects[ Li et al.]., [S.-L. Hsieh et al.], [W. Lin et al.], Nano- and microplastics have
just been identified in human blood, organs, placenta, and breast milk and in the gastrointestinal tract pointing
to a worrisome association with major health disorders, such as diabetes and obesity, cognitive impairment,
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and neurodegenerative diseases like PD and AD [N. Benseny-Cases et al.], [C. Lazzari et al.], and. With about
6 million cases in the With 30 million cases worldwide and a considerable number in the United States,
Alzheimer's disease is the most common neurological condition. [N. Benseny-Cases et al.]. The second most
common type of dementia, Parkinson's disease, affects 6 million adults over 65 and is projected more than to
quadruple to 12 million cases in the world by 2040. [Dorsey et al.], [C. Lazzari et al.] Dorsey et al. More than
90% of the huge population affected by these diseases consists of sporadic cases. Though Aβ in Alzheimer's
disease and α-synuclein in Parkinson's disease have been demonstrated to be the main causes due to abnormal
aggregation of amyloid proteins, there is a growing consensus that exposure to common but ill-defined
environmental toxins could be the cause for the steep rise of these neurological disorders.A variety of biota,
including fish, mollusks, crustaceans, nematodes, and rats, have recently had the neurotoxicity of nanoplastics
clarified [M. Pang et al.], [Dorsey et al.], [Hernandez], [A. Mirzaie et al.], [W. Lin et al.], [H.A. Leslie et al.].
Neurotoxic effects, for instance, have been reported when fish and bivalves are directly exposed to nanoplastics
through the food chain. [W. Li et al.], [Kopatz and associates] When nanoplastic particles were introduced into
drinking water in mice, they were able to pass through the blood-brain barrier and reach brain in just two
hours—something that was not the case with bigger particles. Kopatz and associates, 15 It has been discovered
that tiny polystyrene (PS) nanoparticles exhibit clear neurotoxicity by blocking AChE activities, leading to a
considerable how the particles are absorbed by cells and accumulate in the mouse brain.[S.-L. Hsieh et al.]
The neurotoxicity of nanoplastics has been shown to be dose-dependent, with low-dose nanoplastics either
showing no neurotoxicity at all or very little. There is now no information available on how much nanoplastics
are present in the brain, influenced by the capabilities of detection methods. On on the other hand, it is expected
that the brain would have very little nanoplastic due to the blood-brain barrier. The association between the
neurotoxicity of nanoplastics and their impact in brain illnesses is left with a significant information gap. In
order to close this gap, research on the neurotoxicity of nanoplastics themselves must go beyond where it is at
the moment. Rather, it is necessary to study the regulation mechanism pertaining to the the in vivo effects and
roles of amyloid proteins in the brain diseases, with a focus on the impact of naturally low-toxic nanoplastics.
More crucially, our research has highlighted the fact that by interacting with essential proteins, even less
harmful exogenous chemicals can have a very toxic effect. In order to clarify the complex interactions between
environmental toxins and brain illnesses, it provides a useful basis for future research initiatives.
LITERATURE REVIEW:
Numerous technologies for networking are constantly being created as the information era progresses. Network
drug discovery is gaining pace as an integration of pharmacology and information network, based on system
biology, bioinformatics, and high-throughput histology [Z. H. Liu, .Q. Zhang et al.]. In 2007, Andrew L.
Hopkins introduced the idea of network pharmacology [A. L. Hopkins]. In accordance with the low
effectiveness of highly selective single-target medications, it blends network biology with polypharmacology
[A. L. Hopkins]. From a vast quantity of data, network pharmacies allows us to immediately discover
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medications and disease targets as well as comprehend the processes and routes that connect them [B. Zhang,
X. Zhu et al.]. It is a useful approach. These days, the range of applications for network pharmacology is
growing and includes investigating the fundamental pharmacologic effects of medications on illnesses and
their causes [S. Y. Guo et al., R. Wu et al.], examine the practical significance of TCM [L. L. Zhan et al.] and
its implementation of TCM [S. Han et al., C. Y. Ung et al.].
DrugBank [D. S. Wishar et al.], STITCH [M. Kuhn et al.], and TCM chemical knowledge databases [M. Zhang
et al.] are examples of common tools used in network pharmacology. These databases contain information
about pharmaceutical molecules, and other databases related to active ingredients include PubChem [T. Cheng
et al.], ChEMBL [G. Papadatos et al.], KEGG [J. Wixon et al.], and Target database. Gene-related databases
include OMIM [A. Hamosh et al.], protein-related databases like HPRD [. S. Keshava Prasad et al.], BioGRID
[B. Lehne et al.],and DIP [K. R. Brown et al.], and databases related to biomolecular interactions include
HPRD, BIND [. Jurisica et al.], DIP, HAPPI [J. Y. Chen et al.], MINT [T. Schlitt et al.], STRING [D.
Szklarczyk et al.], and PDZBase [L. Skrabane et al.]. You may utilize any of them to locate the information
you need. Additional tools, such as Cytoscape, Pajek, VisANT, GUESS, WIDAS, PATIKA, PATIKAweb,
and CADLIVE, are required in addition to these databases [. Shannon, E. Adar et al.]. Currently, VisANT,
GUESS, Pajek, and Cytoscape are the most used network evaluation programs in the field of TCM research.
Designing incredibly selective ligands that can prevent side effects has been the primary emphasis of drug
development over the past few decades, according to the prevalent paradigm of "one gene, one drug, one
disease" [F. Sams-Dodd]. Yet, the clinical attrition rate of novel therapeutic candidates might approach 30%
due to their lack of safety and effectiveness [I. Kola et al.]. Further research using large-scale functional
genomics investigations has shown that just 34% of single-gene knockouts resulted in illness or death [M. E.
Hillenmeyer et al.], while many single-gene knockouts have no influence on the phenotype [B. P. Zambrowicz
et al.]. Changes to a single molecular component are not the focus of systems biology, a contemporary trend
in neuroscience study that looks at the intricate relationships within biological structures holistically [H.
Kitano, U. Sauer et al.].
Network phȃrmȃcology is a system biology-based methodology; it replaces, according to A. L. Hopkins and
A. L. Hopkins, the corollary of rational drug design of "magic bullets" with the search for multitarget drugs
that act on biological networks as "magic shotguns". It challenges the dominant assumption of single-target
drug discovery because of increased understanding of the role of network biology systems. Chinese herbal
medicines include natural medicines discovered by the ancient Chinese, evolved through at least 3000 years
of uninterrupted clinical practice. Generally, CHM can cure diseases only through the synergistic effects of a
great deal of compounds and herbal formulae, which mainly work on integrative and holistic ways [G. A. Luo
et al.]. The rising need for elucidating pharmacologic processes, possible therapeutic effectiveness, and clinical
toxicity are significant concerns that must be addressed, nevertheless, given the expanding acceptance and
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immense possibility of CHM. The concept of drug discovery based on thorough investigation and synthetic
evaluation may be integrated in a novel way with the technique and technologies of network pharmacology.
Undoubtedly, this idea aligns with the traits of TCM's syndrome distinction and the holistic approach to treating
CHM [Z. H. Liu et al.].
The computational study of alterations in gene expression brought on by exposure to microplastics has become
a growing area of interest in recent studies. Smaller than 5 mm plastic particles are known as microplastics,
and they are a major environmental hazard to human health and marine life alike. Studies have indicated that
these particles have the ability to cause inflammation, oxidative stress, and other detrimental effects on cells.
Some of the most important recent advances in civilization, such as contemporary technology and medical
enhancements like single-use syringes and modern prostheses, can be attributed to plastics since they are
strong, affordable, and manufactured quickly [Kautish et al.]. Yet, because up to 70% of the world's plastic
gets disposed of improperly in landfills or the environment, the enormous rise in plastic manufacturing has
also resulted in a serious pollution issue [Jabeen, F et al.]. It is known that plastics in the environment may
absorb toxic substances [5,6,7], harbor invasive species like viruses [Prata, J.C, Cole, M et al.], and be
consumed by marine life [Wright, S.L, Duarte, A.C et al.].
Apart from the aforementioned detrimental effects, it has been demonstrated that plastics subjected to
environmental variables including ultraviolet light, oxidation, and physical abrasion lead to the creation of
microplastics, [da Costa, J.P]. Microplastics enter the human body through inhalation of textiles, synthetic
rubber tires, and plastic covers. One can consume MPs straight with the intake of water, seafood, and consumer
goods like apparel, toothpaste, salt, sugar, honey, beer, and all types of food stored in plastic bottles, plastic
wraps, or cans-cartons. In addition to other detrimental effects, MPs have been shown to upregulate proinflammatory cytokines [Li, B, Wang, X et al.], impair cell viability [Halimu, G, Palaniappan, S et al.], cause
oxidative stress [Qiao, R, Gonzalez-Gil, G et al.], and change energy metabolism [Limonta, G, Jin, Y. et al.].
The lungs [Jenner, L.C, Carvalho-Oliveira, R et al.], blood [Leslie, H.A, Guan, Q et al.], cirrhotic liver tissues
[Tamminga, M], human feces [Köppel, S, Luo, T et al.], and even breastmilk [Ragusa, A et al.] have all been
found to include MPs more recently. It has become more crucial to comprehend the health effects of
microplastics exposure in mammals as a result of these findings and the fact that a significant amount of MPs
research is still conducted in marine models. Age is another factor that may affect the outcome of MP exposure,
but there are currently very few research that address the potential negative consequences of MP exposure on
mammal brain health. Therefore, we offered to study the impact of MP exposure on C57BL/6J mice of different
ages, with a particular emphasis on the impacts on neurobehavior, inflammatory response, translocation, and
MP build-up in several tissues, including the brain.
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Since their invention and subsequent widespread manufacturing in the mid-1950s, plastics have become
incredibly popular in business and daily life [Miranda, M.N et al.]. Plastics' chemical makeup makes it possible
to produce goods that are both temperature- and chemical-resistant as well as durable building materials (like
polyvinyl chloride [PVC] pipework). Polychlorinated biphenyls (PCBs) and persistent organic pollutants
(POPs) are two hazardous chemicals that plastics may transport due to their hydrophobic nature. PVC,
polypropylene (PP), low density polyethylene (LDPE), high density polyethylene (HDPE), and polyethylene
terephthalate (PET) are a few of the most popular polymers. These polymers are utilized in many different
goods (such as implants, electronics, apparel, furniture, and pipes).
Mostly through physical-chemical degradation, plastics break down into ever-tinier fragments as they weather
in the environment. By microbial deterioration, plastics can also break apart. This finding, together with the
chemical characteristics of plastic, such their hydrophobicity and capacity to draw in other hydrophobic
particles, led to a surge in the study of microplastics, or plastic particles smaller than 5 mm, starting in 2015.
Any length, breadth, or height of the plastics under study that is 5 mm or less is a regularly used measure for
identifying plastics as microplastics [Jovanović et al., B, Stapleton, P.A]. The origin of microplastics can also
be used to categorize them as main or secondary [Piao, M et al.]. Primary microplastics, which are often found
in the textile and pharmaceutical sectors, are polymers that are produced with a dimension of 5 mm or less.
Plastic trash, including plastic bags, weathers and fragments in the environment to generate secondary
microplastics [Liu, H et al.]. Every year, about 14.5 million tons of plastic garbage, including clothing and
packaging, are generated in the US [Xia, J et al.]. Plastics can be spread via a variety of operations and
procedures, such as agricultural methods and the use of water and wastewater systems. From 2014, the field
of microplastics research has exploded. The effects of microplastics on the environment across the world and
the possible risks they may bring to plants and animals are being studied by interdisciplinary sectors ranging
from engineering and exposure sciences to biology and chemistry. In order to improve our comprehension of
the effects of microplastics on the environment and human health, we have devised a technique for classifying
the microplastic literature and identifying knowledge gaps for this scoping study.
MATERIAL AND METHOD:
NCBI:
https://www.ncbi.nlm.nih.gov/.
National Center for Biotechnology Information (NCBI) is a service of the National Institutes of Health (NIH),
which is home to the United States National Library of Medicine (NLM). The NCBI was established in 1988
and provides access to biological and genetic data to support these academic disciplines. It has a huge collection
of databases, such as BLAST for sequence comparison, PubMed for biomedical literature, and GenBank for
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DNA sequence collections. The resources and tools provided by NCBI enable research by providing extensive,
integrated data and computational resources for the analysis of genetic, genomic, and biological data.
Fig.1. Welcome to the NCBI Home Page
Pubchem:
https://pubchem.ncbi.nlm.nih.gov/.
Chemical compounds and their actions on biological tests are included in the publicly available database
PubChem. The National Center for Biotechnology Information (NCBI), a branch of the National Library of
Medicine in the US, is in charge of maintaining it. For research and development in chemistry, biology, and
medicine, PubChem is a valuable resource that offers details on the biological functions of tiny molecules.
By using PubChem, chemists may look up compounds with certain features and obtain comprehensive
chemical information. Researchers studying biology can examine the interactions between various substances
and biological systems. By examining the biological activity of substances, pharmacologists can utilize the
database to find possible medication candidates.
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Fig.2. Welcome to the PubChem Home Page
ADMETLAB:
https://admet.scbdd.com/.
ADMETlab is a web-based platform for the in silico prediction of various properties of a compound with
respect to its absorption, distribution, metabolism, excretion, and toxicity. It provides accurate, comprehensive
ADMET predictions, thus helping in drug discovery and development research. Utilizing ADMETlab,
Pharmaceutical Researchers can forecast the pharmacokinetic characteristics of novel drug candidates,
assisting in the early detection of any problems throughout the drug development process.
In order to help develop molecules with advantageous pharmacokinetic profiles, Chemists are able to assess
the ADMET features of synthetic drugs.Assisting with safety evaluations, toxicologists are able to forecast the
toxicity of chemical substances.
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Fig.3. Welcome to the ADMETLab Home Page
CYTOSCAPE:
https://cytoscape.org/.
Intricate networks may be shown and combined with any type of attribute data using an open-source program
called Cytoscape. It is extensively employed in systems biology, bioinformatics, and other disciplines that
demand network analysis and visualization.
Bioinformaticians may assist in identifying important nodes and pathways by visualizing and analyzing
molecular
interaction
networks
using
Cytoscape.
Systems biologists may investigate the intricate relationships found in biological systems by integrating several
forms
of
omics
data
into
networks.
Social scientists may comprehend linkages and impacts within a society by visualizing and analyzing social
networks.
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Fig.4. Welcome to the Cytoscape Home Page
SWISS MODEL:
https://swissmodel.expasy.org/](https://swissmodel.expasy.org/
An intuitive user interface for creating protein models from known templates is the goal of the automated
structure of protein homology-modeling system SWISS-MODEL. Automating template selection, alignment,
and model construction streamlines the process of predicting protein structures. The Template Library finds
appropriate templates by searching through an extensive library of protein structures that have been identified
via experimentation (found in PDB). Evaluation of Model Quality provides instruments for evaluating the
quality of models, such as GMQE (Global Model Quality Estimation) and QMEAN (Qualitative Model Energy
Analysis). Easy-to-use Interface Serves a broad spectrum of users, from novices to seasoned academics, and
provides both programmatic and web-based use. Users can oversee several modeling projects and monitor their
development with the help of project management. Analyses and Graphics incorporates visual aids for
examining and assessing structural characteristics into the models.
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Fig.5. Welcome to the SWISS-MODEL Home Page
SEAMDOCK:
https://bioserv.rpbs.univ-paris-diderot.fr/services/SeamDock/
SeamDock is a molecular docking software used for predicting the binding affinity and interaction modes
between small molecules and their protein targets. Incredibly Accurate Docking high accuracy ligand binding
conformation most likely to occur using sophisticated algorithms. Easy-to-use Interface enables the setup of
docking experiments, the visualization of data, and the analysis of interactions using a simple interface.
Detailed Scoring Features optimizes docking findings by evaluating binding affinity through the use of several
scoring systems. It is possible to mimic induced fit along with additional conformational changes with the
support of flexible manipulation of ligands and protein structures. Combining Tools with One Another Allows
for enhanced capability through seamless integration with existing cheminformatics and bioinformatics
technologies. Combined Processing Suitable for virtual screening of huge chemical libraries, it enables highthroughput docking simulations.
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Fig.6. Welcome to the SeaDock Home Page
METHODOLOGY:
GENE
IDENTIFICATION
PROTEINPROTEIN
NETWORK
PROTEIN
MODELING
LIBRARY
PREPARATION
VIRTUAL
SCREENING
MOLECULAR
MODELING
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Gene Identification:
We used bioinformatics tools like MalaCard, GeneCard, and OMIM to identify genes affected by exposure to
microplastics. These databases helped us pinpoint specific genes that are potentially impacted by microplastic
pollution.
Protein-Protein Network:
To understand how these genes interact within biological systems, we constructed protein-protein interaction
networks using 12 different cytohubba characteristics. This analysis identified TNF (Tumor Necrosis Factor)
as a central hub gene, suggesting it plays a crucial role in the network affected by microplastic exposure.
Protein Modeling:
Using Swiss-Model, we generated a 3D structure model of TNF, the key hub gene identified in our proteinprotein interaction network analysis. This modeling provided insights into the structural details of TNF, aiding
in further computational studies.
Library Preparation:
From a thorough review of the literature, we compiled a list of phytochemicals known for their potential
protective effects against microplastic exposure. These compounds were selected based on their documented
bioactivity and safety profiles.
Virtual Screening:
We assessed the drug-like properties of the selected phytochemicals using ADMETLab 3.0. This step helped
us evaluate their absorption, distribution, metabolism, excretion, and toxicity characteristics, crucial for
identifying potential therapeutic agents.
Molecular Modeling:
The binding interactions between TNF and the chosen phytochemicals were investigated by molecular docking
experiments. Ellagic Acid emerged as the most promising compound, showing strong binding affinity with
TNF (binding energy of -9.36). This suggests Ellagic Acid’s potential as a therapeutic agent against health
risks associated with microplastic exposure.
RESULT:
Gene Identification and Network Analysis
We utilized bioinformatics tools, including MalaCard a detailed resource that compiles information on
human diseases and their related genes, GeneCard a comprehensive database offering information on all
documented and anticipated human genes and OMIM an extensive resource on human genes and their
genetic traits, to identify genes potentially affected by microplastic exposure. This way we were able to
gather a lot of information on genes influenced by exposure to microplastics.
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Network Analysis
Our analysis revealed a set of genes whose expressions may be influenced by the presence of microplastics in
the environment. The discovery of TNF crucial genes among others, involved a critical analysis that isolated a
number of genes whose expressions could be influenced by microplastics in the environment. These findings
underscore the genetic pathways through which microplastics could exert their biological effects.
MalaCard3.pdf
GeneCard.pdf
OMIM.pdf
Genes Compiled from MalaCard, GeneCard, and OMIM Databases
Protein-Protein Interaction Network
To elucidate the functional relationships among the identified genes, we constructed protein-protein interaction
networks using 12 distinct cytohubba characteristics. Our analysis highlighted TNF (Tumor Necrosis Factor)
as a central hub gene within this network. TNF emerged as a key regulator, suggesting its pivotal role in
mediating cellular responses to microplastic-induced stress.
MC
DM
MN
Degr EPC
Bottle
EcCentr Close
Radi
Betwe
Stres
ClustringCo
C
NC
C
ee
Neck
icity
ness
ality
eness
s
efficient
UBC
GAP
GAP
GAPD
GAP
TM2D1
DH
DH
H
DH
SNAP25 ACT
ACT
ACTB
ACT
CCL CCL GAP
GAP
GAP
CXCL
2
DH
DH
DH
8
CD4 CCR ACT
ACT
ACT
GAPD
11
6
B
B
B
H
CX
CD2
IL6
IL6
IL6
CD4
CL8
7
ICA
CX
TP5
TP5
TP5
M1
CR3
3
3
3
IFN
IL16 EGF
EGF
EGF
R
R
AKT
AKT
1
1
G
R
IL10 IL33 AKT
1
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XYLT2
B
B
B
SOX2
IL6
IL6
APP
APP
COLGALT1
APP
RPSA
TP53
TP53
TP53
IL6
TMEM126B
IL2
TSC1
EGFR EGF
EGFR
TP53
TMEM230
AKT1
AKT
REG1A
R
TP53
CALM1
AKT1 AKT
1
1
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IL1
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IL7
IL1B IL1B IL1B AKT1
HLA-B
IL1B
IL1B
ALB
ALB
NSMAF
IL1
SEL
ALB
ALB
TNF
TNF
PSMA7
ALB
ALB
TNF
TNF
MST1
B
E
IL6
TLR
TNF
TNF
INS
CCL2
HNRNP
TNF
TNF
CTNN
CTN
TTBK1
B1
NB1
A
5
A2B1
Table.1. CytoHubba Parameters Overview: 12 Key Metrics for Network Analysis
Fig.7. Visualization of Gene Network: Interactions and Connections
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Fig.8. Gene Network Visualization Based on MCC Parameter: Identifying Key Interactions
Fig.9. Gene Network Visualization Based on DMNC Parameter: Identifying Key Interactions
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Fig.10. Gene Network Visualization Based on MNC Parameter: Identifying Key Interactions
Fig.11. Gene Network Visualization Based on DEGREE Parameter: Identifying Key Interactions
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Fig.12. Gene Network Visualization Based on EPC Parameter: Identifying Key Interactions
Fig.13. Gene Network Visualization Based on BottleNeck Parameter: Identifying Key Interactions
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Fig.14. Gene Network Visualization Based on EcCENTRICITY Parameter: Identifying Key Interactions
Fig.15. Gene Network Visualization Based on CLOSENESS Parameter: Identifying Key Interactions
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Fig.16. Gene Network Visualization Based on RADIALITY Parameter: Identifying Key Interactions
Fig.17. Gene Network Visualization Based on BETWEENESS Parameter: Identifying Key Interactions
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Fig.18. Gene Network Visualization Based on STRESS Parameter: Identifying Key Interactions
Fig.19. Gene Network Visualization Based on CLUSTERING CO-EFFICIENT Parameter: Identifying Key
Interactions
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Phytochemical Screening
To identify phytochemicals with potential protective effects against microplastic toxicity, we conducted a
comprehensive literature review. This review centered on natural compounds renowned for their antioxidative,
anti-inflammatory, and detoxifying qualities. We drew from scientific journals, databases, and previous studies
on phytochemicals and their health benefits. From this literature review, we compiled a list of phytochemicals
that showed promising effects against environmental toxins and stressors.
ADMET Analysis
Using ADMETLab 3.0, we evaluated the drug-like properties of these phytochemicals, focusing on their
bioavailability and safety profiles. The screening process revealed several promising candidates with good
pharmacokinetic properties that are worth further investigation.
Phyto
Source
Scienti
Canonical Smile
Lipins
compoun s
fic
ki
ds
Names
Rule
Curcumi
Turme
Curcu
COC1=C(C=CC(=C1)C=CC(=O)CC(=O)C=CC2=CC(=C(C=C2)
ACCE
n
ric
ma
O)OC)O
PTED
C1=CC(=CC=C1C=CC2=CC(=CC(=C2)O)O)O
ACCE
longa
Resverat
Grapes
rol
Vitis
vinifer
PTED
a
Querceti
Onions Allium
n
&
cepa &
Apple
Malus
C1=CC(=C(C=C1C2=C(C(=O)C3=C(C=C(C=C3O2)O)O)O)O)O ACCE
PTED
domest
ica
Genistei
Soybea Glycin
n
ns
e max
Luteolin
Celery
Apium
&
graveol
Green
ens
Pepper
Capsic
s
um
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C1=CC(=CC=C1C2=COC3=CC(=CC(=C3C2=O)O)O)O
ACCE
PTED
C1=CC(=C(C=C1C2=CC(=O)C3=C(C=C(C=C3O2)O)O)O)O
ACCE
PTED
&
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annuu
m
Apigenin Parsley Petrose
&
C1=CC(=CC=C1C2=CC(=O)C3=C(C=C(C=C3O2)O)O)O
linum
ACCE
PTED
Chamo crispu
mile
m
&
Matric
aria
chamo
milla
Kaempfe
Kale & Brassic
rol
Brocco a
li
C1=CC(=CC=C1C2=C(C(=O)C3=C(C=C(C=C3O2)O)O)O)O
ACCE
PTED
olerace
a
&
Brassic
a
olerace
a
vsar.ita
lica
Catechin
Green
Camell
C1C(C(OC2=CC(=CC(=C21)O)O)C3=CC(=C(C=C3)O)O)O
Tea & ia
Cacao
ACCE
PTED
sinesis
&
Theobr
oma
cacao
Naringen Grapef
Citrus
in
paradis
ruits
C1C(OC2=CC(=CC(=C2C1=O)O)O)C3=CC=C(C=C3)O
ACCE
PTED
i
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Sulforap
Brocco Brassic
hane
li
CS(=O)CCCCN=C=S
& a
ACCE
PTED
Brusse
olerace
ls
a
Sprout
var.itali
s
ca
&
Brassic
a
olerace
a
var.ge
mmifer
a
Berberin
Golden Hydras
COC1=C(C2=C[N+]3=C(C=C2C=C1)C4=CC5=C(C=C4CC3)O
ACCE
e
seal
CO5)OC
PTED
tis
canade
nis
Ginsenos Ginsen
Panax
CC(=CCCC(C)(C1CCC2(C1CCC3C2(CCC4C3(CCC(C4(C)C)O) ACCE
ide
ginsen
C)C)C)O)C
PTED
CC1=CC(=O)C(=CC1=O)C(C)C
ACCE
g
g
Thymoq
Black
Nigella
uinone
Cucum sativa
PTED
in
Apigenin Parsley Petrose
C1=CC(=CC=C1C2=CC(=O)C3=C(C=C(C=C3O2)O)O)O
lium
ACCE
PTED
crispu
m
Gingerol
Ginger
Zingib
CCCCCC(CC(=O)CCC1=CC(=C(C=C1)O)OC)O
er
ACCE
PTED
officin
ale
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Ursolic
Holy
Ocimu
CC1CCC2(CCC3(C(=CCC4C3(CCC5C4(CCC(C5(C)C)O)C)C)C ACCE
Acid
Basil
m
2C1C)C)C(=O)O
PTED
C1CCN(CC1)C(=O)C=CC=CC2=CC3=C(C=C2)OCO3
ACCE
sanctu
m
Piperine
Black
Piper
Pepper
nigrum
PTED
Ellagic
Pomeg
Punica
C1=C2C3=C(C(=C1O)O)OC(=O)C4=CC(=C(C(=C43)OC2=O)O ACCE
Acid
ranates
granatu
)O
PTED
m
Rosmari
Rosem
Rosma
C1=CC(=C(C=C1CC(C(=O)O)OC(=O)C=CC2=CC(=C(C=C2)O
ACCE
nic Acid
ary
rinus
)O)O)O
PTED
CC1CCC2C13CC(=C(C)C)C(O3)(C=C2C)O
ACCE
officin
alis
Curcume
Curcu
Turmer
nol
ma
ic
Specie
family
PTED
s
Betulinic
Birch
Betulla
CC(=C)C1CCC2(C1C3CCC4C5(CCC(C(C5CCC4(C3(CC2)C)C) ACCE
Acid
Trees
species
(C)C)O)C)C(=O)O
PTED
Emodin
Rhubar Rheum
CC1=CC2=C(C(=C1)O)C(=O)C3=C(C2=O)C=C(C=C3O)O
ACCE
b
& palmat
Aloe
um
vera
Aloe
PTED
&
barbad
ensis
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Chloroge Coffee
Coffea
C1C(C(C(CC1(C(=O)O)O)OC(=O)C=CC2=CC(=C(C=C2)O)O)
ACCE
nic Acid
&
species
O)O
PTED
Bluebe
&
rries
Vaccin
CC(=O)C1=CC(=C(C=C1)O)OC
ACCE
ium
corymb
osum
Apocyni
Picrorh Polygo
n
iza
num
Kurroa
cuspida
&
tum
PTED
Japane
se
Knotw
eed
Gallocat
Green
Camell
echin
Tea
ia
C1C(C(OC2=CC(=CC(=C21)O)O)C3=CC(=C(C(=C3)O)O)O)O
ACCE
PTED
sinesis
Epigallo
catechin
gallate
Green
Tea
Camelli
a
sinesis
C1C(C(OC2=CC(=CC(=C21)O)O)C3=CC(=C(C(=C3)O)O)
O)OC(=O)C4=CC(=C(C(=C4)O)O)O
REJE
Hesperi
din
Orang
es
Citrus
sinesis
CC1C(C(C(C(O1)OCC2C(C(C(C(O2)OC3=CC(=C4C(=O)C
C(OC4=C3)C5=CC(=C(C=C5)OC)O)O)O)O)O)O)O)O
REJE
Lycopen
e
Tomat
oes
Solanu
m
lycoper
sicum
CC(=CCCC(=CC=CC(=CC=CC(=CC=CC=C(C)C=CC=C(C)
C=CC=C(C)CCC=C(C)C)C)C)C)C
REJE
Oleurop
ein
Olive
Leaves
Olea
europa
ea
CC=C1C(C(=COC1OC2C(C(C(C(O2)CO)O)O)O)C(=O)OC)
CC(=O)OCCC3=CC(=C(C=C3)O)O
REJE
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CTED
CTED
CTED
CTED
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Baicalin
Chines
e
Skullca
p
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Scutell
aria
baicale
nsis
C1=CC=C(C=C1)C2=CC(=O)C3=C(C(=C(C=C3O2)OC4C(
C(C(C(O4)C(=O)O)O)O)O)O)O
REJE
CTED
Table.2. Screening of Phytochemicals with ADMET Analysis Results
Protein Modeling and Molecular Docking Studies
We generated a 3D structural model of TNF using Swiss-Model to gain insights into its molecular architecture.
Subsequently, molecular docking studies were conducted to predict the binding affinities between TNF and
selected phytochemicals. Among these compounds, Ellagic Acid exhibited the highest binding energy (-9.36
kcal/mol), suggesting strong potential as a therapeutic agent against microplastic-induced health risks.
Fig.20. "Structural Model of TNF Gene Generated with Swiss Model: Insights and Analysis"
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PHYTOCHEMICALS NAMAE
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Curcumin
BINDING
ENERGY
AMINO
RESIDUE
© 2025
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Issue 6ACID
June 2025
| ISSN: 2320-2882
-6.13
L105, L119, N106, D121, R107,
N122
Resveratrol
-7.35
L169, F200, V93, A94, P96, N110,
F220, N168, H91, C11, C13
Quercetin
-6.44
Q201, L112 ,N106, R108, N110,
L113, A111, A109
Genistein
-7.39
K188, Q178, R179, P176, T181,
E186, E192, K174, S175, C177
Luteolin
-6.7
V93, A94, P96, F220, A109, A109,
R108, S223, N110, G224
Apigenin
-7.03
V93,A94, P96, R108, A109, F220,
V226, G224, G224
Kaempferol
-6.69
V93,
A94,
P96,
R108,
A109,
F220,V226,G224, S223
Catechin
-7.32
K188, W190, Q178, R179, P176,
T181, E186, C177, A187
Naringenin
-7.96
T181, K188, W190, Q178, R179,
E180, E186, S175, P176, G144,
C177, S175, P182
Sulforaphane
-5.62
P193, Y195, I194
Berberine
-7.25
K188, Q178, P176, T181, S175, E192
Ginsenoside
-6.52
K87, P88, A232, S85, S128, P84
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Thymoquinone
-6.35
V93, F220, S223, V226, R108
Apigenin
-7.03
V93, A94, P96, R108, A109, F220,
V226, G224, S223
Gingerol
-4.51
A185, K188, Q178, R179, P189,
G144, W190
Ursolic Acid
-8.23
N95, Q103, L105, L119, N122
Piperine
-7.73
K188, W190, Q178, R179, T181,
E186, S175
Ellagic Acid
-9.36
V93, A94, A109, N110, F220, V226,
R108, G224, S223
Rosmarinic Acid
-7.02
K188, R179, T181, E180, E186, C145
Curcumenol
-7.92
K188, W190, Q178, G144
Betulinic Acid
-9.17
K141, E99, Y217, F220, A221, L218,
Q143,G142, D219
Emodin
-8.15
V93, A94, P96, A109, N110, F220,
V226, G224, R108, S223
Chlorogenic Acid
-5.26
R107, L113, E118, N106, L119,
G116
Apocynin
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-6.44
Y195, Q137, P193, I194
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Gallocatechin
-7.41
V93, A94, P96, R108, F220,A109,
V226, N168, S223, N110,
Table.3. Binding Energy and Amino Acid Residue Interactions of Phytochemicals
Top Docking Results Based on Highest Binding Energy
Fig.21. Ellagic Acid (-9.36)
Fig.22. Curcumin (-6.13)
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Fig.23. Resveratrol(-7.35)
Fig.24. Quercetin(-6.44)
Fig.25. Genistein(-7.39)
Fig.26. Luteolin(- 6.7)
Fig.27.Apigenin
(-7.03)
Fig.28.Kaempferol(-6.69).
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Fig.29. Catechin (-7.32)
Fig.31. Sulforaphane (-5.62)
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Fig.30. Naringenin (-7.96)
Fig.32. Berberine (-7.25)
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Fig.33. Ginsenoside (-6.52)
Fig.35. Apigenin (-7.03)
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Fig.34.Thymoquinone(-6.35)
Fig.36.Gingerol(-4.51)
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Fig.37. Ursolic Acid (-8.23)
Fig.38.Piperine(-7.73)
Fig.39.Rosmarinic Acid (-7.02)
Fig.40.Curcumenol(-7.92)
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Fig.41. Betulinic Acid (-9.17)
Fig.42.Emodin(-
8.15)
Fig.43. Chlorogenic Acid (-5.26)
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Fig.44. Apocynin (-6.44)
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Fig.45. Gallocatechin (-7.41)
DISCUSSION:
Our study delves into the impact of microplastic exposure on gene expression, identifying TNF as a crucial
hub gene within affected protein-protein interaction networks. By using bioinformatics tools like MalaCard,
GeneCard, and OMIM, we pinpointed key genes influenced by microplastic pollution. TNF's central role in
these networks underscores its significance in the biological response to microplastics. Through Swiss-Model,
we visualized the 3D structure of TNF, enhancing our understanding of its functional mechanisms. We then
curated a library of phytochemicals with potential protective effects and evaluated their ADMET properties
using ADMETLab 3.0. Molecular docking studies revealed Ellagic Acid as a promising therapeutic candidate,
showing a strong binding affinity with TNF. These findings highlight Ellagic Acid’s potential to mitigate health
risks posed by microplastic exposure, paving the way for further research into effective interventions.
CONCLUSION:
Microplastics pose a significant threat to human health and the environment, primarily through their ability to
transport and absorb harmful substances. Our study employed computational biology techniques to investigate
the impact of microplastic exposure at the molecular level.
Through gene identification and network analysis, we identified key genes, with TNF (Tumor Necrosis Factor)
emerging as a critical regulator in protein-protein interaction networks affected by microplastics. This
highlights TNF's potential role in mediating biological responses to microplastic-induced stress.
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Furthermore, our screening of phytochemicals revealed Ellagic Acid as a promising candidate for mitigating
microplastic toxicity. Molecular docking studies demonstrated Ellagic Acid's strong binding affinity to TNF,
suggesting its potential as a therapeutic agent against microplastic-induced health risks.
Overall, our findings underscore the pervasive threat of microplastics and highlight the importance of
computational biology in identifying potential interventions. Further research is warranted to validate these
findings and explore the broader implications for environmental and human health.
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10. Feng, S., Lu, H., Tian, P., Xue, Y., Lu, J., Tang, M., & Feng, W. (2020). Analysis of microplastics
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