Conservation Under Siege: The Intersection of Tourism and Environmental Threats in Croatian Protected Areas
Abstract
:1. Introduction
1.1. The Role of Protected Areas in Sustainable Tourism
1.2. Environmental Impacts of Tourism in Protected Areas
1.3. Nature-Based Solutions for Sustainable Tourism Development
1.4. Challenges in Protected Area Management
1.5. Research Objectives
- What are the regional patterns in the frequency and types of illegal activities across Croatian national parks and nature parks?
- How do risk-exposure levels differ among various park types in Croatia, and what specific challenges do these differences present for conservation efforts?
- What recommendations can be formulated to improve conservation efforts based on the observed patterns of illegal activities in the parks?
2. Materials and Methods
2.1. The Study Area and Design
- Coastal parks: Brijuni, Krka, Kornati, Mljet, Telašćica, Lastovo Islands
- Mountainous and forest parks: Northern Velebit, Risnjak, Velebit, Biokovo, Učka, Medvednica, Papuk
- Wetland and lowland parks: Kopački Rit, Lonjsko Polje
- Diverse landscape parks: Plitvice Lakes, Krka, Paklenica.
2.2. Data Collection
2.3. Data Analysis
- Qualitative analysis: A thematic analysis was performed on the document reviews to identify common patterns, challenges, and management strategies related to illegal activities in different park regions. This allowed for a deeper understanding of the contextual factors influencing illegal activities and their impact on conservation efforts. For qualitative analysis, additional data were drawn from records regarding the protection, maintenance, preservation, promotion, and use of the parks, as well as information on undertaken projects [35,36,37,38,39,40,41,42,43,44,45,46,47,48,49,50,51,52,53,54,55,56]. These data were crucial for scoring the risk exposure.
- Quantitative analysis: For quantitative analysis, the study utilized records on illegal activities documented in park-management reports, including frequency and type of offenses [35,36,37,38,39,40,41,42,43,44,45,46,47,48,49,50,51,52,53,54,55,56]. These data were essential in constructing a baseline for understanding the scope of illegal activities in the parks. Descriptive statistics, including means, medians, and percentages, were calculated to evaluate the contribution of each illegal activity to the overall risk exposure in each park type. To determine whether there were significant differences in risk exposure between the various park types (e.g., coastal, mountainous, wetland, and diverse landscape parks), a one-way ANOVA test was conducted. To investigate the regional patterns in the frequency and types of illegal activities across Croatian national and nature parks, as well as the differences in risk-exposure levels and their implications for conservation efforts, the following hypotheses were formulated:
- Null Hypothesis (H0): There are no statistically significant differences in the frequency and types of illegal activities across different regions and park types in Croatian national and nature parks.
- Alternative Hypothesis (H1): There are statistically significant differences in the frequency and types of illegal activities across different regions and park types in Croatian national and nature parks.
2.4. Risk Analysis
2.4.1. Risk Identification
- The Problem Tree Analysis was used to deconstruct illegal activities in Croatian protected areas into their root causes (underlying systemic issues), direct causes (immediate triggers), and consequences. This method allowed for a systematic understanding of the interconnected factors contributing to each illegal activity:
- Identifying core problems: The starting point was to identify illegal activities as the central issue affecting protected areas.
- Root causes and driving factors: The analysis mapped the underlying drivers of these activities, such as insufficient law enforcement, inadequate visitor education, and socio-economic pressures on surrounding communities. These factors were grouped under broader categories, including policy gaps, lack of infrastructure, and visitor behavior.
- Consequences: The Problem Tree illustrated the cascading effects of these activities, such as habitat destruction, biodiversity loss, and decreased ecological resilience. This visual representation clarified how illegal activities are not isolated issues but part of a larger system of challenges.
- 2.
- The Ishikawa Diagram (Fishbone Diagram) was employed to visually categorize the potential causes of illegal activities into key groups. This tool facilitated the identification of patterns and interrelations among contributing factors, offering a structured approach to addressing these issues.The Ishikawa Diagram grouped causes of illegal activities into categories such as:
- Institutional factors: Gaps in enforcement, policy inconsistencies, and lack of interagency coordination.
- Environmental factors: Geographic challenges, such as the difficulty of monitoring remote or rugged areas.
- Human factors: Visitor behaviors, local economic pressures, and lack of awareness about conservation rules.
- Technological factors: Limited use of advanced monitoring tools like drones and GIS systems.
- Comprehensive risk identification: Both methods provided complementary insights. The Problem Tree focused on causal pathways, while the Ishikawa Diagram emphasized categorizing and interrelating the factors contributing to illegal activities.
- Data-driven prioritization: Findings from these tools informed the allocation of risk-exposure (RE) scores by grounding them in a detailed understanding of the causes and challenges specific to each illegal activity.
- Improved targeting of management strategies: Combining insights from these methods enabled the identification of specific intervention points, such as enhancing enforcement mechanisms or increasing visitor education efforts in high-risk areas.
2.4.2. Qualitative and Quantitative Risk Analysis
- The nature of the ecosystem affected (e.g., wetlands with sensitive biodiversity received higher severity scores for activities like poaching and capturing protected species).
- The potential for recovery (e.g., activities causing long-term habitat damage were scored higher than those with short-term effects).
- Current monitoring capabilities in each park type (e.g., the use of surveillance tools like drones or patrolling practices).
- Visibility of activities (e.g., littering in open areas had higher detection probabilities compared to poaching in dense forests).
2.5. Ethical Considerations
2.6. Limitations and Data Availability
3. Results
3.1. Analysis of Illegal Activities in Croatian National Park and Nature Parks by Regions
3.1.1. Risk Identification in Coastal Parks
- Mooring vessels on maritime property can cause shoreline erosion and damage to coastal habitats. Coastal parks with attractive bays, such as Brijuni and Mljet, are more prone to illegal mooring, increasing the risk of habitat degradation. Shoreline change analysis using satellite imagery, vessel count surveys, and statistical analysis of mooring patterns are key tools in addressing this issue.
- Illegal fishing results in overfishing, disruption of aquatic ecosystems, and economic impacts on local fishing communities. Coastal parks attract a high density of both recreational and professional fishermen due to their proximity to rich marine ecosystems. Overfishing and illegal methods (e.g., using non-permitted nets or catching endangered species) increase the risk to marine biodiversity, which is highly sensitive to even slight changes in population balance. Marine parks like Brijuni, Mljet and Kornati are particularly vulnerable to illegal fishing due to their rich marine biodiversity. Fish stock assessments, acoustic surveys, and statistical modeling of fish populations are essential for monitoring and mitigating this risk.
- Capture of strictly protected marine animals (e.g., dolphins, sea turtles) disrupts the balance of marine ecosystems, threatens endangered species, and alters food chains. Coastal parks often harbor endemic and rare species, including marine life, coastal vegetation, and bird species, making them particularly vulnerable to illegal activities. The presence of biodiversity hotspots in these parks escalates the risk of disruption when such species are captured illegally. Wildlife population surveys, remote sensing, and statistical analysis of species abundance are critical for managing this activity.
- Illegal construction, particularly related to tourism infrastructure, can fragment habitats and erode shorelines. The attractive coastal location leads to the temptation for unauthorized development, especially illegal housing or tourist facilities, which damages fragile ecosystems like salt marshes, dune habitats, and coastal forests. Coastal erosion and habitat loss are common consequences. Coastal parks like Kornati, Mljet, and Telašćica face higher pressures from tourism-related construction, which threatens the natural aesthetic and ecological integrity. Satellite imagery analysis and land use classification can help monitor and control this activity.
3.1.2. Risk Identification in Mountainous and Forest Parks
- Causing fires and lighting fires outside designated areas increases the risk of uncontrolled wildfires, soil degradation, and human–wildlife conflicts. Forest fires are a major ecological threat in these parks, particularly in the summer. The vast forested areas combined with dry conditions make these regions highly susceptible to fires, often started by visitors who neglect fire safety rules. Fires can devastate large swathes of forests, destroy wildlife habitats, and increase soil erosion. Thermal imaging for fire detection and spatial analysis of fire patterns are effective preventive measures.
- Poaching, particularly of large mammals, disrupts predator–prey relationships and reduces game animal populations. Forest parks like Northern Velebit and Risnjak face higher pressures from poaching due to their large mammal populations. Anti-poaching patrol data, wildlife tracking, and machine learning for predictive poaching patterns are necessary tools for managing this risk.
- Illegal logging in forest parks leads to deforestation, habitat loss, and increased flood risks. Parks with valuable timber resources, like Risnjak and Velebit, are especially at risk of illegal logging. LiDAR surveys, satellite-based deforestation detection, and predictive logging models can help mitigate these impacts.
- Capture of strictly protected terrestrial animals, such as wolves or bears, poses risks of species population decline and ecosystem imbalance. Inland parks like Risnjak and Plitvice Lakes are particularly vulnerable to terrestrial animal capture. Wildlife surveys, camera traps, and statistical analysis of species population trends are vital for risk management.
- Camping and bivouacking outside designated areas can lead to vegetation trampling, increased fire risks, and human–wildlife conflicts. Remote parks like Northern Velebit, due to their isolation and scenic appeal, attract unauthorized camping. Night-time thermal imaging and spatial analysis of camping hotspots are essential for preventing these activities.
- Illegal extraction of mineral resources affects landscape integrity, causes water pollution, and destroys habitats. Mountainous areas are often rich in minerals and geological resources, leading to illegal quarrying or mining activities. Geological surveys and hyperspectral imaging are important methods for monitoring and preventing this activity.
3.1.3. Risk Identification in Wetland and Lowland Parks
- Poaching and capturing protected species: The diverse ecosystems harbor many vulnerable species, leading to high risk scores for these activities.
- Dumping of large quantities of waste near wetland areas, particularly in parks near urban zones, leads to soil and water contamination, wildlife poisoning, and aesthetic degradation. Waste quantification surveys and GIS hotspot analysis help identify and control waste dumping.
- Littering, particularly near tourist hotspots, leads to microplastic pollution, wildlife ingestion of harmful materials, and the degradation of the visitor experience. Even small amounts of pollutants can spread through the water system, affecting large areas of the ecosystem.
3.1.4. Risk Identification in Diverse Landscape Parks
3.2. The Risk-Exposure Analysis of Illegal Activities in Croatian National Parks and Nature Parks
3.2.1. Regional Patterns in the Frequency and Types of Illegal Activities Across Croatian National Parks and Nature Parks
3.2.2. Differences in Risk-Exposure Levels Among Various Park Types in Croatia and Specific Challenges These Differences Present for Conservation Efforts
- Coastal parks exhibit high RE values for maritime-related activities, such as illegal fishing and mooring vessels, reflecting the unique pressures of tourism in marine ecosystems.
- Mountainous and forest parks show elevated RE for causing fires and lighting fires outside designated areas, associated with their dry climates and large, hard-to-monitor areas.
- Wetland and lowland parks have the highest RE for poaching and capturing protected species, due to their rich biodiversity and vast floodplains.
3.3. Sensitivity Analysis of Illegal Activities in Croatian National Parks and Nature Parks
- Mooring vessels
- Swimming in prohibited areas
- Illegal fishing.
- Causing fires
- Lighting fires outside settlements and designated places
- Unauthorized construction.
- Poaching
- Capturing strictly protected plants and animals
- Illegal fishing.
- Littering outside designated areas
- Poaching
- Capturing strictly protected plants and animals.
- In coastal parks, “Mooring vessels”, “Swimming in prohibited areas”, and “Illegal fishing” have the highest impact on TRE.
- For wetland and lowland parks, “Poaching” and “Capturing strictly protected plants and animals” show the highest sensitivity, followed by “Illegal fishing”.
- In diverse landscape parks, “Littering outside designated areas” has the most significant impact, followed by “Poaching” and “Capturing strictly protected plants and animals”. This suggests that while both issues are important, fire prevention and management might be a higher priority for immediate action or resource allocation.
4. Discussion
4.1. Regional Patterns of Illegal Activities and Recommendations for Proactive Risk Management Updates
- Frequent risk monitoring updates: Existing risk registers should be updated more frequently to capture new and emerging risks [65] tied to visitor behavior. Regular reviews are essential to adjust for new trends in illegal activities.
- Adopting advanced monitoring technologies: While some technological measures may already be in place [66], strategies should incorporate more real-time data-gathering tools [67], such as advanced drone surveillance and satellite monitoring systems, to ensure that illegal activities are detected earlier and more efficiently, especially in remote areas.
- Enhancing community-based reporting systems: While community involvement exists, the development of more accessible platforms, such as mobile apps, could empower local communities and visitors to report illegal activities in real time, enabling faster intervention [68].
- Strengthening visitor education programs: As visitor numbers and illegal activities evolve, it is critical to periodically refresh educational campaigns to reflect current risks and conservation priorities [69]. New digital platforms, on-site interactive kiosks, and targeted awareness campaigns should be implemented to promote responsible behavior.
- Increasing interagency coordination: Existing collaboration between park management, law enforcement, and environmental agencies should be reinforced by formalizing more frequent joint action plans and rapid response protocols [70]. This will ensure that enforcement actions remain effective, particularly as illegal activities become more sophisticated.
- Reviewing and adjusting resource allocation: The effectiveness of enforcement and monitoring largely depends on the allocation of resources. Proactive budget planning should be incorporated into strategy updates to ensure adequate funding for necessary tools, personnel, and training in areas where risks are highest [23].
4.2. Future Directions and Policy Implications
5. Conclusions
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
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Park Name | Visitor Density (Visitors/km2) | Park Type |
---|---|---|
Brijuni | 20,991.1 | Coastal park |
Krka | 12,881.4 | Diverse landscape park |
Plitvice Lakes | 11,502.2 | Diverse landscape park |
Medvednica | 7251.0 | Mountainous and forest park |
Telašćica | 4550.4 | Coastal park |
Učka | 4413.9 | Mountainous and forest park |
Mljet | 3639.4 | Coastal park |
Paklenica | 3136.6 | Diverse landscape park |
Biokovo | 2818.1 | Mountainous and forest park |
Lastovo Islands | 2606.5 | Coastal park |
Kornati | 2439.9 | Coastal park |
Risnjak | 992.9 | Mountainous and forest park |
Northern Velebit | 839.0 | Mountainous and forest park |
Papuk | 665.2 | Mountainous and forest park |
Kopački Rit | 572.4 | Wetland and lowland park |
Lonjsko Polje | 158.9 | Wetland and lowland park |
Velebit | 62.0 | Mountainous and forest park |
Park Type | Top Five Illegal Activities | Key Impacts |
---|---|---|
Coastal parks | Mooring vessels Swimming in prohibited areas Illegal fishing Unauthorized construction Capturing protected species | Damage to marine ecosystems, and harm to protected species (e.g., Pinna nobilis). |
Mountainous and forest parks | Causing fires Lighting fires, Unauthorized construction Illegal logging Poaching | Habitat destruction, wildfire risk, overexploitation of natural resources. |
Wetland and lowland parks | Poaching Capturing protected species Illegal fishing Littering Waste disposal | Biodiversity loss, aquatic ecosystem degradation, pollution. |
Diverse landscape parks | Littering Poaching Capturing protected species Swimming in prohibited areas Lighting fires | Visitor-related environmental degradation, and wildlife disturbances. |
Illegal Activity | Coastal Parks | Mountainous and Forest Parks | Wetland and Lowland Parks | Diverse Landscape Parks |
---|---|---|---|---|
Unauthorized construction | 21.6 | 29.2 | 16.0 | 21.3 |
Illegal fishing | 22.8 | 0.2 | 32.0 | 5.9 |
Poaching | 14.3 | 23.7 | 45.0 | 31.1 |
Capturing strictly protected plants and animals | 22.2 | 23.1 | 45.0 | 31.1 |
Illegal logging | 12.3 | 22.3 | 12.0 | 12.0 |
Illegal exploitation of mineral resources | 0.0 | 23.5 | 15.8 | 7.7 |
Waste disposal outside designated areas | 15.1 | 13.3 | 18.0 | 16.0 |
Littering outside designated areas | 13.2 | 18.0 | 27.0 | 36.0 |
Causing fires | 12.0 | 37.6 | 6.0 | 22.2 |
Lighting fires outside settlements and designated places | 12.6 | 34.3 | 12.0 | 24.9 |
Driving and parking outside designated areas | 7.9 | 23.3 | 18.0 | 10.0 |
Anchoring Vessels (in inland waters) | 0.0 | 0.0 | 26.3 | 5.9 |
Mooring vessels (on maritime property) | 24.3 | 0.0 | 0.0 | 0.0 |
Camping in prohibited areas | 13.4 | 16.7 | 15.0 | 20.0 |
Swimming in prohibited areas | 23 | 3.4 | 18.8 | 29.3 |
Damaging visitor infrastructure | 7.7 | 10.3 | 9.0 | 20.0 |
Installing signs, advertisements, etc., without permission | 8.6 | 14.6 | 4.5 | 6.2 |
Source of Variation | Sum of Squares (SS) | Degrees of Freedom (df) | Mean Square (MS) | F-Value | p-Value |
---|---|---|---|---|---|
Between Groups (SSB) | 19,665.40 | 3 | 6555.13 | 47.224 | <0.0001 |
Within Groups (SSW) | 8189.69 | 59 | 138.81 | ||
Total | 27,855.09 | 62 |
Illegal Activity | Coastal Parks | Mountainous and Forest Parks | Wetland and Lowland Parks | Diverse Landscape Parks |
---|---|---|---|---|
Unauthorized construction | ±1.87% | ±1.99% | ±1.00% | ±1.42% |
Illegal fishing | ±1.97% | ±0.01% | ±2.00% | ±0.39% |
Poaching | ±1.24% | ±1.62% | ±2.81% | ±2.08% |
Capturing strictly protected plants and animals | ±1.92% | ±1.57% | ±2.81% | ±2.08% |
Illegal logging | ±1.07% | ±1.52% | ±0.75% | ±0.80% |
Illegal exploitation of mineral resources | ±0.00% | ±1.60% | ±0.99% | ±0.51% |
Waste disposal outside designated areas | ±1.31% | ±0.91% | ±1.12% | ±1.07% |
Littering outside designated areas | ±1.14% | ±1.23% | ±1.68% | ±2.40% |
Causing fires | ±1.04% | ±2.56% | ±0.37% | ±1.48% |
Lighting fires outside settlements and designated places | ±1.09% | ±2.34% | ±0.75% | ±1.66% |
Driving and parking outside designated areas | ±0.68% | ±1.59% | ±1.12% | ±0.67% |
Anchoring Vessels (in inland waters) | ±0.00% | ±0.00% | ±1.64% | ±0.39% |
Mooring vessels (on maritime property) | ±2.10% | ±0.00% | ±0.00% | ±0.00% |
Camping in prohibited areas | ±1.16% | ±1.14% | ±0.94% | ±1.33% |
Swimming in prohibited areas | ±1.99% | ±0.23% | ±1.17% | ±1.96% |
Damaging visitor infrastructure | ±0.67% | ±0.70% | ±0.56% | ±1.33% |
Installing signs, advertisements, etc., without permission | ±0.74% | ±1.00% | ±0.28% | ±0.41% |
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Mileusnić Škrtić, M.; Tišma, S.; Grgurević, D. Conservation Under Siege: The Intersection of Tourism and Environmental Threats in Croatian Protected Areas. Land 2024, 13, 2114. https://doi.org/10.3390/land13122114
Mileusnić Škrtić M, Tišma S, Grgurević D. Conservation Under Siege: The Intersection of Tourism and Environmental Threats in Croatian Protected Areas. Land. 2024; 13(12):2114. https://doi.org/10.3390/land13122114
Chicago/Turabian StyleMileusnić Škrtić, Mira, Sanja Tišma, and Davor Grgurević. 2024. "Conservation Under Siege: The Intersection of Tourism and Environmental Threats in Croatian Protected Areas" Land 13, no. 12: 2114. https://doi.org/10.3390/land13122114
APA StyleMileusnić Škrtić, M., Tišma, S., & Grgurević, D. (2024). Conservation Under Siege: The Intersection of Tourism and Environmental Threats in Croatian Protected Areas. Land, 13(12), 2114. https://doi.org/10.3390/land13122114