Submitted:
21 September 2025
Posted:
23 September 2025
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Abstract
Keywords:
1. Introduction
2. Methodology
2.1. Literature Search Strategy
2.2. Data Sources and Databases
- Academic Databases: Searches were conducted on prominent platforms including Google Scholar, Web of Science, and Scopus. These databases provided extensive coverage of global peer-reviewed articles across ecology, conservation science, remote sensing, and computer science disciplines.
- Institutional Repositories and Reports: Given the specific focus on Pakistan, institutional reports and grey literature were gathered from government and non-governmental organizations. Notably, data and publications from the National Council for Conservation of Wildlife (NCCW), Islamabad Wildlife Management Board (IWMB), WWF-Pakistan, International Union for Conservation of Nature (IUCN) Pakistan, the Pakistan Wildlife Foundation (PWF), and the Zoological Society of Pakistan (ZSP) were reviewed to provide localized context.
- Preprint Servers: To capture the latest research pending formal peer review, preprint archives such as arXiv were also consulted, especially for studies involving novel machine learning applications in wildlife monitoring.
2.3. Keywords and Search Terms
- “Wildlife monitoring”
- “Camera traps + Machine Learning (ML)”
- “Remote sensing wildlife”
- “Acoustic monitoring wildlife”
- “Bio-loggers wildlife”
- “Pakistan wildlife technology”
2.4. Inclusion and Exclusion Criteria
- Empirical studies or reviews that employed one or more of the following technologies: camera traps, drones/UAVs, remote sensing, bio-loggers, or machine learning algorithms.
- Research focused on wildlife population monitoring, behavioral studies, movement ecology, or human-wildlife conflict mitigation.
- Studies conducted globally but with particular attention to applications within Pakistan.
- Publications from 2018 to mid-2025 to reflect contemporary practices, with allowance for seminal earlier works explicitly referenced.
3. Technological Methods in Wildlife Monitoring
3.1. Camera Traps and Artificial Intelligence (AI)
3.2. Remote Sensing, Satellite Imagery, and Drones
3.3. Bio-Loggers, Telemetry, and GPS Tracking
3.4. Acoustic Monitoring
4. Comparison of Technologies
Comparison of Wildlife Monitoring Technologies
5. Global Case Studies (2022–2025)
5.1. Serengeti-Mara Migration Census Using Satellite Imagery + Deep Learning

5.2. Drone Sampling for Roe Deer in Austria

5.3. Real-Time Detection of Ground-Nesting Birds in Wales

5.4. Mega Detector for Large-Scale Camera Trap Image Classification
| Case Study | Region | Species / Focus | Technology Used | Key Outcomes |
| Serengeti Migration Monitoring | East Africa | Wildebeest, Zebra | Satellite + Deep Learning (CNNs) | F1 score ~84.75%; scalable census over large terrain |
| Roe Deer Density Estimation | Austria | Roe Deer | Drones (thermal + RGB), REM modeling | Accurate population estimates; better than camera traps |
| Curlew Nest Monitoring | Wales, UK | Ground-nesting Birds | YOLOv10 + Real-Time Monitoring | High detection accuracy; supports nest protection |
| Mega Detector Image Classification | Multi-region | Multiple species (animals, humans) | AI-based object detection (Mega Detector v4) | Classified >300,000 images; 90%+ accuracy |
6. Wildlife Monitoring in Pakistan: Current Status and Case Studies
6.1. Snow Leopard Conflict Mitigation in Gilgit-Baltistan

6.2. Camera Trap Monitoring in Margalla Hills National Park (MHNP)

6.3. Satellite Tagging of Indus River Dolphins

6.4. Gaps and Challenges in Pakistan's Monitoring Landscape
- Lack of drone-based monitoring studies: Although drones have been proposed for habitat mapping and anti-poaching patrols, few peer-reviewed studies exist that demonstrate their effective application within Pakistan's conservation areas.
- Minimal use of acoustic monitoring: Passive acoustic sensors, widely used globally for birds, bats, and amphibians, are rarely utilized or documented in the Pakistani context, despite suitable environments in northern forests and southern wetlands.
- Limited data sharing and open-access repositories: There is a lack of centralized, open-access wildlife datasets for Pakistan, hindering collaborative research and machine learning training opportunities.
- NGO-led or donor-dependent initiatives: Most technologically advanced projects are initiated and managed by non-governmental organizations (WWF, IUCN-Pakistan) or funded through short-term international donor grants, leading to sustainability concerns.
| Project / Case Study | Region | Technology Used | Key Species | Key Outcome |
| Snow Leopard Conflict Mitigation | Gilgit-Baltistan | AI-enabled camera traps | Panthera uncia | Zero livestock losses reported in targeted localities |
| Camera Trap Monitoring in MHNP | Islamabad | Infrared camera traps | Leopards, deer | Behavioral data in response to human activity |
| Satellite Tracking of Indus River Dolphins | Indus River (Sindh) | Satellite telemetry | Platanista gangetica minor | Movement data for habitat management |
| Drone Monitoring (planned, few pilots only) | Various (unpublished) | UAVs / drones | Not species-specific | Few published results; underutilized |
| Acoustic Monitoring | No major case studies | Passive acoustic sensors | Birds, bats | Technology remains unused or undocumented |
7. Challenges and Limitations
7.1. Technical and Operational Barriers
- Power supply and battery life remain major limitations, particularly for long-term deployments in areas with heavy snowfall, high heat, or monsoon rains. Devices often fail due to condensation, temperature fluctuations, or physical damage.
- Data storage and limited internet connectivity in remote areas restrict real-time data transmission, making centralized monitoring difficult.
- Machine learning models used for species recognition depend on high-quality annotated datasets. In low-data regions like Pakistan, species misclassification, especially among similar-looking taxa, remains a persistent issue.
- Drone regulations and import restrictions, along with delays in obtaining aerial flight permissions, limit the scalability of drone-based surveys.
7.2. Environmental and Species-Specific Issues
- Dense vegetation or forest canopy obstructs visibility for both satellite sensors and aerial drones, particularly in montane or riverine ecosystems.
- Cryptic, nocturnal, or highly mobile species are less likely to be detected via standard camera traps or visual drone surveys. Animals that camouflage well or exhibit low movement frequencies can be underrepresented in data.
- Behavioral seasonality, such as migration or hibernation, means that short-term monitoring may yield incomplete insights. Longitudinal studies are therefore essential, requiring sustainable resources and consistent fieldwork.
7.3. Socio-Ethical and Community Engagement Concerns
- In conflict-prone areas, devices such as camera traps may raise community concerns, especially where they inadvertently capture images of people. This raises privacy and ethical issues.
- If local communities do not perceive direct benefits, such as alerts to predator presence or compensation for livestock losses, they may become resistant to technology deployment.
- Genuine community participation—through shared decision-making, training, or incentive-based schemes—is often lacking, reducing long-term viability.
7.4. Capacity, Policy, and Funding Constraints
- Many institutions lack trained personnel in machine learning, image analysis, drone operations, or satellite data interpretation.
- The cost of equipment, such as GPS collars, thermal cameras, and drones, combined with high maintenance and replacement costs, makes projects dependent on external funding.
- There is an absence of centralized wildlife monitoring policies in Pakistan. No unified regulatory body oversees the ethical deployment of surveillance technology or data governance for biodiversity.
- Short-term donor-funded initiatives, while impactful, often fail to create sustainable systems or transfer skills and knowledge locally.
8. Opportunities and Future Directions
8.1. Integrated Multi-Sensor Monitoring Systems
- Camera traps can be paired with passive acoustic sensors to detect both visual and auditory presence.
- Bio-loggers can record movement, while drones capture landscape-level changes.
- Remote sensing (NDVI, LULC maps) can help contextualize data for modeling habitat use.
8.2. Edge AI and TinyML
- This is especially valuable in Pakistan’s remote areas, where satellite internet or stable 4G connectivity is often unavailable.
- Real-time alert systems—notifications when predators approach livestock—can improve human-wildlife coexistence.
8.3. Open-Source Platforms and Local Data Sharing
- Building a Pakistan-specific annotated dataset—covering native species like the snow leopard, hog deer, chinkara, and Indus dolphin—would enable locally tuned machine learning models.
- Encouraging institutions to publish and share camera trap datasets, acoustic recordings, and telemetry outputs will foster cross-project collaboration.
8.4. Expanding Drone Applications
- Monitoring migration corridors, illegal deforestation, wetlands, and nesting sites.
- Detecting nocturnal mammals using infrared thermal imagery.
- Mapping habitat fragmentation and human encroachment.
8.5. Citizen Science and Community Participation
- Programs where villagers help maintain camera traps, report animal sightings, or assist in acoustic data collection have been successfully piloted in India and Nepal.
- In Pakistan, such efforts can build early-warning networks for human-wildlife conflict zones and assist in ground truthing of remotely sensed data.
8.6. Policy, Regulation, and Ethical Frameworks
- Drone permits for conservation use should be streamlined and subsidized.
- Data privacy protocols must be implemented, especially when human subjects are inadvertently recorded.
- Ethical treatment and animal welfare regulations must be enforced in projects involving tagging or collaring.
8.7. Training and Institutional Capacity Building
- Interdisciplinary university courses combining ecology, computer science, and data science are needed.
- Workshops, certificate programs, and field training for rangers, students, and NGO staff should be institutionalized.
- International partnerships with organizations such as WWF, ZSL, and Google Earth Engine can facilitate technology transfer and co-creation.
9. Limitations of This Review Paper
9.1. Reliance on Published and Accessible Sources
- For example, community-led conservation efforts or pilot uses of drones in provincial reserves may not yet be documented or disseminated widely.
- Similarly, technical reports by NGOs or provincial departments may remain inaccessible due to language, platform, or archival limitations.
9.2. Lag in Capturing Rapid Technological Advancements
- Tools such as new versions of YOLO, transformer-based vision models, or novel bio-logger designs may already be in use or tested but not yet included in formal academic literature.
- Additionally, open-source models updated on GitHub or preprint servers (arXiv) are sometimes ahead of traditional publication cycles, leading to potential temporal gaps in this synthesis.
9.3. Geographic and Infrastructure Bias in the Literature
- Studies from countries with robust scientific institutions (USA, UK, Germany, Kenya, South Africa, Australia) are better represented.
- In contrast, conflict-affected regions, remote mountainous zones, or countries with limited research funding, such as parts of Balochistan, Khyber Pakhtunkhwa, and rural Sindh, are underrepresented due to data scarcity.
9.4. Language and Access Constraints
- For instance, provincial wildlife department reports or community conservation documentation written solely in regional languages may not be included.
- Furthermore, paywalled journal articles not available through open-access repositories may have been excluded due to access limitations.
9.5. Methodological Exclusions
- Purely theoretical models, simulations, or reviews without field application were excluded.
- Studies prior to 2018 were only included if considered seminal or foundational.
10. Conclusion
- The development of integrated, multi-sensor monitoring systems that combine visual, acoustic, and spatial data for comprehensive insights.
- Local capacity building, including interdisciplinary training programs in ecology, remote sensing, and artificial intelligence.
- Promotion of open-access data platforms and national-level species annotation datasets to improve machine learning model performance.
- Establishment of clear regulatory and ethical frameworks, particularly for drone use, data privacy, and animal welfare.
- Encouragement of community engagement and participatory monitoring models that foster local stewardship and long-term conservation outcomes.
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| Technology | Strengths | Limitations | Applications in Pakistan |
| Camera Traps + AI | Non-invasive, 24/7 monitoring, AI enables automation of species identification | High cost, requires training data, false triggers | Snow leopard monitoring in Gilgit-Baltistan; Margalla Hills leopard tracking |
| Remote Sensing / Drones | Covers large areas, habitat and land-use change detection | Limited resolution under canopy, requires processing expertise | Forest monitoring and habitat mapping under planning (limited published applications) |
| Bio-loggers / Telemetry | Detailed movement and behavior tracking, migratory studies | Expensive, invasive, small sample sizes | Indus river dolphin satellite tracking; few large-scale applications |
| Acoustic Monitoring | Ideal for vocal species (birds, bats), continuous monitoring | Affected by noise, data interpretation complex | Underutilized; opportunity for birds and bats in remote regions of Pakistan |
| Machine Learning / AI | Handles large datasets efficiently, automates image/audio analysis | Requires high-quality datasets, computational resources | Used in WWF-Pakistan camera trap project for snow leopard detection |
| Technology | Key Strengths | Weaknesses / Limitations | Suitability in Pakistan |
| Camera Traps + AI | - Continuous monitoring, 24/7 operation - Captures rare/cryptic species - Automated species classification |
- High installation and maintenance costs - High number of false positives ("empty shots") - Requires robust ML models and image training datasets - Battery and memory issues in remote areas |
- Proven success in Gilgit-Baltistan - Valuable for leopards, deer, and mountain ungulates - Can be expanded in remote and mountainous areas |
| Remote Sensing & Drones | - Wide-area habitat mapping - Land use change detection - Rapid deployment - non-intrusive |
- Satellite imagery expensive - Cloud cover limits use - Drones face canopy visibility issues - Legal barriers to drone use - Requires data processing expertise |
- Underutilized but promising - Suitable for aerial surveys in deserts, mountain zones, and national parks - Need regulatory and technical support |
| Bio-loggers / Telemetry | - Provides fine-scale movement and behavior data - Useful for migratory and aquatic species |
- High cost per animal - Requires animal capture (ethical concerns) - Small sample sizes - Limited battery life - Requires data retrieval systems |
- Used for Indus dolphin tracking - Can be extended to ungulates, raptors, and marine species - Needs stronger infrastructure and permitting systems |
| Acoustic Monitoring | - Effective in poor visibility or dense vegetation - Non-invasive - Good for vocalizing species |
- Difficult to identify species in noisy environments - Large volume of unlabeled data - Affected by weather and equipment degradation |
- Currently underused in Pakistan - High potential in forests, caves, and remote bat roosts - Opportunities for avian biodiversity assessments |
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