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GaiaGuard: A Satellite-Based Smart Monitoring and Alert System for Natural Resources Protection

DOI : https://doi.org/10.5281/zenodo.19661867
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GaiaGuard: A Satellite-Based Smart Monitoring and Alert System for Natural Resources Protection

Ch. Vyshnavi, G. Shyamala, G. Spoorthi

Department of CSE Data Science, Sreenidhi Institute of Science and Technology (Autonomous) Yamnampet, Ghatkesar, Hyderabad 501301, Telangana, India

Guide: Dr. Md Jaffar Saqid, Associate Professor & Head, Dept. of CSE-DS

Abstract – The rapid depletion of natural resources including forests, water bodies, and ecological land zones due to illegal deforestation, encroachments, and unregulated land-use changes has emerged as a critical environmental crisis. This paper presents GaiaGuard, a full-stack satellite-based smart monitoring and alert system designed for real-time detection and reporting of environmental changes using remote sensing. The system integrates Google Earth Engine (GEE) Sentinel-2 imagery, Normalized Difference Vegetation Index (NDVI) analysis, and a rule-based classification engine to categorize detected changes into three severity levels: Low, Moderate, and Critical. A Human-in-the-Loop (HITL) admin verification mechanism filters false positives before triggering automated multi-channel alerts via email (Flask-Mail) and SMS (Twilio) to forest departments, NGOs, and district authorities. Evaluated across six districts of Telangana, India, GaiaGuard achieves a macro-averaged F1 score of 92.5% and reduces false positive alert rates from 17.8% to 3.1% through HITL verification. The system generates structured satellite evidence reports to support legal enforcement actions, requiring no geospatial expertise from end users.

Keywords – satellite monitoring; remote sensing; NDVI; Google Earth Engine; Sentinel-2; change detection; environmental protection; natural resource management; rule-based classification; human-in-the-loop; Twilio; Flask; React.js; deforestation detection; Telangana

  1. INTRODUCTION

    Natural resources such as forests, water bodies, and land ecosystems form the ecological backbone of human civilization. According to the United Nations Environment Programme (UNEP), the world loses approximately 10 million hectares of forest annually due to logging, agricultural expansion, and illegal encroachments [1]. In India, Telangana alone recorded over 2,500 complaints of forest encroachment between 2018 and 2023, of which fewer than 30 percent were acted upon within an acceptable timeframe [2]. This delay is largely attributable to the severe limitations of traditional monitoring mechanisms.

    Conventional approaches to environmental surveillance rely on periodic manual surveys, helicopter flyovers, and satellite data that must be interpreted by trained geospatial analysts. These methods suffer from high latency, limited geographic coverage, and substantial operational cost. Critically, they are incapable of detecting sudden or small-scale changes precisely the type of activity associated with illegal deforestation and land grabbing before irreversible ecological damage occurs [3].

    To address this gap, this paper presents GaiaGuard, a satellite-based smart monitoring and alert system that operationalizes environmental surveillance for non-expert stakeholders including forest officials, NGO workers, and district administrators. GaiaGuard leverages freely available Copernicus Sentinel-2 imagery processed through Google Earth Engine (GEE) to generate before-and-after NDVI comparisons within a constrained temporal window of up to three days. Detected changes are classified automatically using

    rule-based thresholds and, when significant, routed through a Human-in-the-Loop (HITL) verification panel before automated alerts are dispatched to relevant authorities.

    The primary contributions of this work are: (1) an end-to- end environmental change detection pipeline integrating GEE, NDVI-based analysis, and rule-based classification; (2) a monsoon-aware dynamic NDVI threshold mechanism that reduces seasonal false positives; (3) a HITL admin verification layer that improves alert precision from 82.2% to 96.9%; (4) a fully automated multi-channel alert system (email + SMS) with role-based authority mapping per Telangana region; and (5) automated structured evidence report generation supporting legal enforcement workflows.

    The paper is structured as follows. Section II presents a comprehensive literature review with DOI references. Section III describes the system architecture and design. Section IV covers UML-based system modeling. Section V details implementation. Section VI presents results and comparative evaluation with 8 performance tables. Section VII concludes with future directions.

  2. LITERATURE REVIEW

    This section reviews foundational and contemporary research across five thematic pillars directly relevant to GaiaGuard: satellite change detection, NDVI-based vegetation monitoring, deforestation and land-use change monitoring, environmental alert systems, and human-in-the-loop verification frameworks.

    1. Remote Sensing and Satellite Change Detection

      Coppin et al. [4] provided a landmark survey of digital change detection techniques in remote sensing, establishing theoretical foundations for bitemporal image comparison, image differencing, principal component analysis (PCA), and post-classification comparison. They demonstrated that no single technique universally outperforms others; context- specific selection is essential. Zhu and Woodcock [5] proposed the Continuous Change Detection and Classification (CCDC) algorithm using Landsat time-series, achieving an overall accuracy of 90.3% across multiple land-cover types (DOI: 10.1016/j.rse.2014.01.011). However, CCDC requires dense time-series data unavailable at GaiaGuard's three-day resolution. Singh [6] reviewed multitemporal remote sensing for land-use change detection, highlighting that image differencing is effective for short-period analysis, directly informing GaiaGuard's temporal window design.

    2. NDVI-Based Vegetation Monitoring

      Tucker [7] introduced the Normalized Difference Vegetation Index (NDVI) as a robust, dimensionless measure of green vegetation density using near-infrared (NIR) and red reflectance bands, establishing its utility for large-area vegetation mapping (DOI: 10.1016/0034-4257(79)90013-0). NDVI values range from 1 to +1, with dense healthy vegetation typically yielding values above 0.5. Pettorelli et al.

      [8] demonstrated that NDVI is sensitive to phenological variation, moisture stress, and land-cover change, and proposed species-specific thresholding strategies (DOI: 10.1016/j.tree.2005.05.011) a principle adapted in GaiaGuard's monsoon-aware threshold module. Verbesselt et al. [9] developed BFAST for detecting change in time-series vegetation data, whose seasonality decomposition informed GaiaGuard's monsoon period differentiation logic (DOI: 10.1016/j.rse.2009.08.014).

    3. Deforestation and Land-Use Change Monitoring

      Hansen et al. [10] produced the first high-resolution (30 m) global forest change map using Landsat imagery processed in GEE, quantifying a net global forest loss of 2.3 million km² for 20002012 (DOI: 10.1126/science.1244693). Their work established GEE as a scalable satellite data processing platform and demonstrated the feasibility of automated forest loss detection at national scale. Chen et al. [11] proposed a sub-pixel change detection framework for Sentinel-2 achieving an F1 of

      0.86 on mixed land-cover test sites (DOI: 10.1016/j.rse.2022.112799). Their use of Sentinel-2 bands B4 and B8 forNDVI calculation is directly adopted in GaiaGuard. Gao et al. [12] recommended median compositing over a 37- day window to minimize cloud contamination, consistent with GaiaGuard's retrieval strategy.

    4. Environmental Alert and Notification Systems

      Demir et al. [13] reviewed geospatial data management platforms for disaster response, emphasizing the necessity of automated alerting pipelines connecting satellite-detected events to field responders (DOI: 10.1109/CVPRW.2018.00031). Their architectural recommendations informed GaiaGuard's alert dispatch module. Wan et al. [14] demonstrated that satellite-to-authority latency can be reduced to under 90 seconds using asynchronous alert queues integrated with SMS gateways (DOI:

      10.1109/ACCESS.2019.2941862). GaiaGuard adopts a similar asynchronous dispatching architecture.

    5. Human-in-the-Loop (HITL) Verification

      Monarch [15] provided a comprehensive treatment of human-in-the-loop machine learning, demonstrating that incorporating expert validation checkpoints reduces false positive rates by 3560% in environmental classification tasks. Tsui et al. [16] evaluated HITL verification in satellite change detection workflows and found that a single-reviewer manual check reduced erroneous alert rates from 18.4% to 3.2% in a deforestation monitoring context, while adding a median latency of only 14 minutes per case (DOI: 10.1016/j.rse.2021.112474). These findings validate GaiaGuard's decision to employ HITL verification specifically for moderate and critical cases.

    6. Geospatial Web Platforms

      Gorelick et al. [17] documented GEE's planetary-scale data catalogue hosting over 60 petabytes of geospatial data including Sentinel-2, Landsat, and MODIS datasets (DOI: 10.1016/j.rse.2017.06.031). GEE's Python API is the data access backbone of GaiaGuard. Tamiminia et al. [18] benchmarked GEE-based classification workflows against traditional desktop GIS and found a 14Ă— reduction in processing time for regional analysis tasks (DOI: 10.1016/j.isprsjprs.2020.04.011), validating GEE as the appropriate processing engine.

    7. Summary of Literature and Research Gap

    Table I highlights a clear research gap: no existing system integrates short window NDVI change detection, severity classification, HITL verification, multi-channel alerts, and evidence reporting in a single non-expert web app.

    TABLE I

    Reference

    Method / System

    Dataset

    Key Result

    Limitatio n vs GaiaGuar d

    Coppin et al. [4]

    Change Detection Survey

    Landsat

    8592% OA

    No alert/UI

    Zhu & Woodcock [5]

    CCDC Time-Series

    Landsat

    OA 90.3%

    Needs dense TS

    Tucker [7]

    NDVI Foundations

    Landsat MSS

    NDVI

    defined

    No change classify

    Pettorelli et al. [8]

    NDVI Monitoring

    MODIS

    Phenology

    -aware

    No user interface

    Verbesselt et al. [9]

    BFAST Breakpoint

    Landsat

    Seasonal CD

    Complex setup

    Hansen et al. [10]

    Global Forest Change

    Landsat 7/8

    2.3M km² mapped

    Annual res.; no alert

    Chen et al. [11]

    Sub-pixel CD

    Sentinel-2

    F1 = 0.86

    No HITL or alert

    Wan et al. [14]

    Forest Fire IoT Alert

    IoT+Satell ite

    <90 s

    latency

    Fire only; no CD

    Tsui et al. [16]

    HITL

    Deforestation

    Sentinel-2

    FP:

    18.43.2

    %

    No web UI

    Gorelick et al. [17]

    Google Earth Engine

    Multi- source

    60 PB

    catalogue

    Needs coding skills

    Literature Review Summary and Research Gap Analysis

    GaiaGuard (Ours)

    NDVI+Rule+HITL

    +Alert

    Sentinel- 2/GEE

    F1 92.5%

    See future work

  3. SYSTEM ARCHITECTURE AND DESIGN

    GaiaGuard is built on a three-tier Model-View-Controller (MVC) architecture comprising a React.js Presentation Layer, a Python Flask Application Layer, and an PostgreSQL Data Layer. All inter-tier communication occurs through stateless RESTful HTTP/JSON APIs, enabling independent scaling of each component and straightforward migration to microservices in the future.

    1. Presentation Layer

      The frontend is developed using React.js 18 with Vite as the build tool and Tailwind CSS for utility-first responsive styling. Interactive map-based ROI selection is powered by Leaflet.js with OpenStreetMap tile overlays. The Axios HTTP client manages authenticated API calls with JWT Bearer token injection. The interface presents results as side-by-side before/after satellite image panels, color-coded severity badges, and downloadable PDF evidence reports, requiring no geospatial expertise from the user.

    2. Application Layer

      The backend exposes 12 RESTful API endpoints built on Python 3.11 and Flask 3.0. Authentication is handled via Flask- JWT-Extended with 24-hour access tokens. Satellite data is retrieved and processed through the Google Earth Engine Python API. NDVI calculation and change classification are performed server-side using NumPy. Alert dispatch integrates Flask-Mail (SMTP/TLS) and the Twilio REST API for SMS. All operations are logged via Python's standard logging module with rotating file handlers.

    3. Data Layer

      The database uses PostgreSQL managed through Flask- SQLAlchemy ORM, with four primary tables: (1) users credentials, roles, session metadata; (2) analyses ROI coordinates, date parameters, NDVI values, classification results; (3) contacts role-based authority contacts per Telangana district slug; (4) reports generated evidence document metadata. The schema follows third normal form (3NF) and is designed for straightforward migration to PostgreSQL.

      Fig. 1. GaiaGuard Three-Tier System Architecture

    4. System Workflow

    The operational workflow comprises nine sequential stages:

    (1) user authenticates and selects ROI via the Leaflet map interface; (2) user inputs a start date; system auto-derives Period 2; (3) frontend dispatches POST /api/analyse with JWT;

    (4) backend queries GEE for Sentinel-2 median composites for both periods; (5) NDVI is calculated; mean NDVI drop percentage is computed; (6) rule-based classifier assigns Low/Moderate/Critical status; (7) for Moderate or Critical results, admin dashboard flags the case for HITL review; (8) admin confirms or dismisses; on confirmation, alert dispatcher fires multi-channel notifications; (9) structured evidence PDF is generated and stored.

  4. SYSTEM MODELING

    The GaiaGuard system is formally modeled through four standard UML diagrams that collectively represent structural composition, actor interactions, temporal message flow, and process control logic.

    1. Class Diagram

      The class diagram (Fig. 2) depicts core domain entities and relationships. Principal classes include User, Region, Analysis, Contact, Report, and AlertLog. The Analysis class aggregates Region and is associated with one Report and zero-to-many AlertLog entries. The User class is specialized into RegularUser and AdminUser via inheritance.

      Fig. 2. UML Class Diagram

    2. Use Case Diagram

      The use case diagram (Fig. 3) identifies two primary actors: the RegularUser and the Administrator. RegularUser use cases include Register/Login, Select ROI, View Before/After Images, View Classification Result, and Download Report. Administrator use cases extend these with Review Flagged Analysis, Confirm/Dismiss Change, Trigger Alert, and Manage Contacts.

      Fig. 3. UML Use Case Diagram

    3. Sequence Diagram

      The sequence diagram (Fig. 4) traces the message exchange lifecycle for a complete analysis request across the Browser, React Frontend, Flask API, GEE Engine, Analysis Module, Classification Engine, Admin Panel, Alert Dispatcher, and Notification Channels (Email/SMS).

      Fig. 4. UML Sequence Diagram

    4. Activity Diagram

    The activity diagram (Fig. 5) captures the conditional branching logic governing classification routing and alert dispatch, including the fork node that parallelizes email, SMS, and fax notification channels after admin confirmation.

    Fig. 5. UML Activity Diagram

  5. IMPLEMENTATION

    1. Technology Stack

      Table II provides a complete summary of all technologies used in GaiaGuard across all system layers.

      TABLE II

      GaiaGuard Complete Technology Stack

      Layer

      Technology

      Version

      Purpose

      Frontend

      React.js

      18.2

      Dynamic single-page application UI

      Frontend

      Vite

      4.4

      Build tool with hot module replacement

      Frontend

      Tailwind CSS

      3.3

      Utility-first responsive styling

      Frontend

      Leaflet.js

      1.9

      Interactive map-based ROI selection

      Frontend

      Axios

      1.4

      HTTP client for authenticated API calls

      Backend

      Python

      3.11

      Primary backend language

      Backend

      Flask

      3.0

      Lightweight REST API framework

      Backend

      Flask- SQLAlchemy

      3.1

      ORM for database abstraction

      Backend

      Flask-JWT- Extended

      4.5

      JWT authentication and sessions

      Backend

      Flask-Mail

      0.9

      SMTP/TLS email alert dispatch

      Backend

      Twilio SDK

      8.2

      SMS alert delivery to authorities

      Satellite

      Google Earth Engine

      0.1.374

      Satellite imagery retrieval

      Satellite

      Copernicus Sentinel-2

      L2A (SR)

      10 m resolution NDVI imagery

      Data Proc.

      NumPy

      1.24

      NDVI calculation and statistics

      Database

      PostgreSQL

      3.43

      Relational data store (dev/prod)

      Security

      JWT (HS256)

      RFC 7519

      Stateless session management

      Dev Tools

      Git / GitHub

      Version control and collaboration

      Dev Tools

      Postman

      10.x

      REST API testing and debugging

    2. Satellite Data Retrieval

      Sentinel-2 Level-2A (surface reflectance) imagery is retrieved from the COPERNICUS/S2_SR GEE collection. The system filters by region bounding box and date range, applies a 20% cloud pixel filter, then computes a median composite. NDVI is derived from bands B8 (NIR, 842 nm) and B4 (Red, 665 nm): NDVI = (B8 B4) / (B8 + B4).

      import ee; ee.Initialize()

      def get_satellite_image(region, start, end): coll = ee.ImageCollection("COPERNICUS/S2_SR")

      .filterBounds(region)

      .filterDate(start, end)

      .filter(ee.Filter.lt("CLOUDY_PIXEL_PERCENTAGE",20))

    3. NDVI Change Detection and Classification

      The change detection engine computes the mean NDVI of the before and after composites over the user-defined ROI polygon. The NDVI loss percentage is: loss_pct = ((ndvi_before ndvi_after) / ndvi_before) Ă— 100. Monsoon- aware thresholding (JuneSeptember) dynamically adjusts classification cutoffs to account for natural seasonal NDVI variability and reduce false positives.

      def classify_status(loss_pct: float) -> str: if loss_pct < Config.MODERATE_MIN_PCT: # 10%

      return "Normal"

      if loss_pct < Config.CRITICAL_MIN_PCT: # 25% return "Moderate Change"

      return "Critical Loss"

    4. Multi-Channel Alert Dispatch

      Upon admin confirmation of illegal activity, the alert system simultaneously dispatches email (Flask-Mail SMTP/TLS), SMS (Twilio REST API), and fax log notifications to all role-mapped contacts for the affected Telangana district. Contacts are stored per region slug for four roles: forest_department, ngo, human_resources, and authority.

      def send_illegal_alerts(analysis: dict) -> dict: contacts = list_contacts_for_region(

      analysis["region_slug"]) for c in contacts:

      if c["phone"]: _sms(sms_text, c["phone"])

      if c["email"]: _email(subj, body, c["email"])

    5. Database Schema

    Figs. 68 show the primary user-facing outputs of GaiaGuard across a test scenario involving a monitored forest region in Telangana.

    Fig. 6. GaiaGuard Main Dashboard Interface

    TABLE III

    Database Schema Key Entities and Attributes

    Table

    Primary Key

    Foreign Keys

    Key Attributes

    users

    id (INT)

    email, password_hash, role, is_active,

    created_at

    analyses

    id (INT)

    user_idusers

    region_slug, roi_geojson, p1_start, p1_end, ndvi_before, ndvi_after, loss_pct, status

    contacts

    id (INT)

    region_slug, role, name,

    organization, phone, email, fax

    reports

    id (INT)

    analysis_idanalyses

    file_path, generated_at, download_count

    alert_logs

    id (INT)

    analysis_idanalyses

    channel, recipient, sent_at, delivery_success

    Fig. 7. ROI Selection and Date Range Input Interface

    Fig. 8. Before-and-After Satellite Image Comparison Panel

    B. Classification Performance

    Table IV reports classification performance per severity category across 45 test cases with ground-truth labels assigned by a domain expert.

    TABLE IV

    Category

    TP

    FP

    FN

    Precision

    Recall

    F1

    Normal

    16

    1

    0

    94.1%

    100.0%

    97.0%

    Moderate

    12

    2

    1

    85.7%

    92.3%

    88.9%

    Critical

    11

    0

    2

    100%

    84.6%

    91.7%

    Macro Average

    39

    3

    3

    93.3%

    92.3%

    92.5%

    Classification Performance by Severity Category

  6. RESULTS AND EVALUATION

    This section presents the results of GaiaGuard evaluated across 45 manually verified test cases covering six Telangana districts, along with comparative analysis against existing platforms.

    A. System Output Screens

    The overall macro-averaged F1 score of 92.5% demonstrates the effectiveness of the NDVI differencing approach. The perfect precision on the Critical category is significant for an enforcement-oriented system, ensuring no false critical alerts burden authorities. Two critical cases were

    Monsoon-Aware Thresholding

    No

    No

    No

    Yes

    ROI Selection via Map UI

    Yes

    Yes

    Yes

    Yes

    Sentinel-2 Imagery Support

    Yes

    Yes

    Yes

    Yes

    Free / Open- Source Tier

    Yes

    No

    Yes

    Yes

    <=3-Day

    Temporal Window

    Yes

    Yes

    No

    Yes

    missed (FN=2) due to cloud contamination exceeding the 20% filter; integration of Sentinel-1 SAR imagery is identified as a priority future enhancement.

    C. Impact of HITL Verification

    Table V quantifies the contribution of the HITL admin verification layer to overall alert precision across the 45 test cases.

    TABLE V

    Impact of Human-in-the-Loop Verification on Alert Precision

    Metric

    Without HITL

    WITH HITL

    False Positive Alert Rate

    17.8%

    3.1%

    Erroneous Authority Notifications

    8 / 45

    1 / 45

    Alert Precision

    82.2%

    96.9%

    Admin Review Latency (median)

    N/A

    11.4 min

    Cases Escalated to Authorities

    29

    22 (verified only)

    D. Alert System Performance

    Table VI reports performance of the multi-channel alert dispatch system across 22 verified test cases requiring authority notification.

    F. System Performance Benchmarks

    Table VIII reports computational performance measured on a standard workstation (Intel Core i5-12th Gen, 8 GB RAM, 100 Mbps internet connection).

    TABLE VIII

    System Performance Benchmarks

    Operation

    Avg. Time

    Notes

    GEE Sentinel-2 Image Retrieval

    4.3 s

    Median composite, 3- day window

    NDVI Calculation (per ROI)

    0.8 s

    Server-side NumPy vectorized

    Rule-Based Classification

    <0.01 s

    Deterministic threshold logic

    PDF Evidence Report Generation

    1.2 s

    ReportLab / WeasyPrint

    SMS Dispatch via Twilio

    4.2 s

    Network latency dependent

    Email Dispatch via Flask- Mail

    8.1 s

    Per recipient, SMTP/TLS

    End-to-End (detect to classify)

    5.3 s

    Excluding HITL wait time

    Full Pipeline (incl. alert)

    19.6 s

    Post admin verification

    TABLE VI

    A

    lert Dispatch Performance Across Notification Channels

    Channel

    Sent

    Delivered

    Avg. Delivery Latency

    SMS via Twilio REST API

    22

    21 (95.5%)

    4.2 seconds

    Email via Flask- Mail (SMTP)

    88

    86 (97.7%)

    8.1 seconds

    E. Feature Comparison with Existing Platforms

    Table VII benchmarks GaiaGuard against three widely used geospatial monitoring platforms across twelve operational feature dimensions.

    TABLE VII

    Feature Comparison: GaiaGuard vs. Existing Monitoring Platforms

    Feature / Capability

    GEE

    Sent. Hub

    SERVIR

    GaiaGuard

    Non-Expert Web Interface

    No

    No

    Yes

    Yes

    Automated NDVI Change Detection

    No

    Yes

    Yes

    Yes

    Severity Classification (3- class)

    No

    No

    Yes

    Yes

    HITL Admin Verification

    No

    No

    No

    Yes

    SMS + Email Alerts to

    <>Authorities

    No

    No

    No

    Yes

    Evidence Report Generation

    No

    No

    Yes

    Yes

    Role-Based Authority Contacts

    No

    No

    No

    Yes

  7. CONCLUSIONS

This paper presented GaiaGuard, a satellite-based smart monitoring and alert system for natural resources protection that operationalizes environmental surveillance for non-expert stakeholders in Telangana, India. Three principal technical contributions are made: (1) a monsoon-aware NDVI differencing engine built on GEE Sentinel-2 imagery that classifies environmental changes into Low/Moderate/Critical categories with a macro-averaged F1 of 92.5%; (2) a Human- in-the-Loop admin verification layer that reduced false positive alert rates from 17.8% to 3.1%; and (3) a real-time multi- channel notification system achieving 95.5% SMS and 97.7% email delivery to role-mapped authorities within under 15 seconds of admin confirmation.

Comparative evaluation against Google Earth Engine, Sentinel Hub, and SERVIR confirmed that GaiaGuard is the only platform surveyed providing the complete operational feature set: non-expert UI, severity classification, HITL verification, multi-channel alerts, authority contact management, monsoon-aware thresholding, and automated evidence reporting all within a single integrated web application.

Planned future enhancements include: (i) integration of Sentinel-1 SAR imagery for cloud-independent change

detection; (ii) deep learning semantic segmentation (U-Net, DeepLab v3+) for finer classification granularity; (iii) time- series trend analysis for early warning of gradual deforestation;

(iv) real-time GEE streaming; (v) mobile PWA for field officer use; and (vi) expansion to all 33 Telangana districts with integration into the Forest Department portal.

ACKNOWLEDGMENT

The authors thank Dr. Md Jaffar Sadiq, Head of the Department of CSE-Data Science and internal guide, and Dr. Naadem Divya, Project Coordinator, at Sreenidhi Institute of Science and Technology for their invaluable technical guidance. The authors also thank the Principal, Dr. T. Ch. Siva Reddy, for providing excellent research infrastructure. This work was carried out as part of the Major Project, B.Tech CSE- Data Science, Academic Year 2025-2026.

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