Research Gap & Motivation

There is a significant research gap regarding the prevalence, spatial hotspots, and drivers of wildlife roadkill along key public and internal park roads, as well as how vehicle traffic intensity and road characteristics influence these patterns.

Critical Context

Existing data for Uganda are limited to small stretches and specific taxa, yet new oil and gas, tourism, and other socioeconomic development projects are extending roads through critical habitats, potentially increasing wildlife mortality risk for a wide range of vertebrates and invertebrates and threatening both biodiversity and human safety.

Research Objectives

Overall Objective

To determine the extent of roadkill, hotspot areas and the impact of vehicle traffic on wildlife along selected roads inside the three national parks, to inform science-based management.

Specific Objectives

1

Quantify wildlife roadkill prevalence in each park

2

Identify roadkill hotspots

3

Measure vehicle traffic levels along the study roads

4

Assess factors associated with roadkill, including road type, traffic, environmental and spatial attributes

Study Design & Implementation

The study is a longitudinal survey being implemented in two phases, covering different seasonal and tourism patterns to capture comprehensive data on wildlife-vehicle interactions.

Research Phases
Phase 1
March - June 2025
Wet Season / Low-Tourist Season
✓ Completed
Phase 2
December 2025 - February 2026
Dry Season / High-Tourist Season
⟳ In Progress

Study Sites & Transects

In each park, two road transects (one paved, one unpaved) were selected based on known or suspected roadkill, traffic volume and accessibility:

🦁 Murchison Falls National Park

Kichumbanyobo-Tangi Paved
Paraa-Wangkwar Unpaved

🐘 Queen Elizabeth National Park

Kikorongo-Kyambura Paved
Katwe junction-Katwe Unpaved

🦍 Kibale National Park

Fort Portal-Kamwenge Paved
Fort Portal-Kampala sections Mixed

Data Collection Methods

Field teams drive or ride each transect in morning and evening, recording all carcasses and incident reports using standard forms and mobile tools (e.g. EarthRanger).

📊 Survey Protocol

Morning (7-9 am) and evening (4-6 pm) transect surveys with systematic carcass recording

🗺️ Spatial Data

GPS coordinates, road characteristics, distance to boundary, signage presence

🦎 Species Data

Species identity, age, body condition, taxonomic classification

🚗 Traffic Monitoring

Vehicle type, time of day, traffic volume patterns

🌍 Environmental Variables

Land cover, wildlife crossing points, habitat characteristics

👥 Community Input

Incident reports from community members, tour operators and park staff

Preliminary Findings (Phase 1: 40-Day Wet Season)

783 Total Roadkills Recorded
580 In MFNP Alone
96 QENP Hotspot Kills
4 Unpaved Road Kills (MFNP)

Key Observations from Phase 1

  • Murchison Falls NP: Accounted for the majority (about 580) of roadkills, especially along the busy paved Kichumbanyobo-Tangi road, while the unpaved Paraa-Wangkwar road recorded only 4 kills
  • Queen Elizabeth NP: Had lower totals overall, though the Kikorongo-Kyambura section still showed a notable concentration of 96 kills, indicating a local hotspot
  • Kibale NP: Contributed lower numbers to the overall total
  • Peak Detection Time: Most incidents were detected in the morning (7-9 am), suggesting peaks in nocturnal/crepuscular animal movement overlapping with early traffic and possibly reduced visibility or driver behaviour
  • Evening Surveys: Recorded fewer kills (4-6 pm time slot)
  • Road Type Effect: Paved roads showed dramatically higher mortality rates compared to unpaved tracks

Taxonomic Distribution of Roadkills

  • Class Insecta Dominated in MFNP & Kibale
  • Birds (Aves) High proportion in QENP
  • Mammals Consistently represented
  • Reptiles Across all parks
  • Amphibians Across all parks

This broad taxonomic representation highlights the extensive ecological impacts of road mortality across vertebrate and invertebrate classes.