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Changes in the human footprint in and around Indonesia’s terrestrial national parks between 2012 and 2017

Abstract

The human footprint (HF) was developed to measure of the impact of human activities on the environment. The human footprint has been found to be closely related to the vulnerability of protected areas around the world. In Indonesia, as nature conservation is still seen as hindering economic development, it is especially important to assess the human footprint in order to comprehend the overall pressures resulting from the various human activities on Indonesia’s national parks. This study measured the change in the human footprint in and around 43 terrestrial national parks over 5 years, between 2012 and 2017. As many as 37 out of 43 NPs experienced an increase in the HF, ranging from 0.4 to 77.3%. Tanjung Puting in Kalimantan experienced the greatest increase (77.3%), while Ujung Kulon in Jawa Bali bioregion had the greatest decrease (10.5%). An increase in human population density and improved access to parks from roads, rivers and coastlines are the main drivers of increasing impacts on national parks.

Introduction

Indonesia is the largest island nation in the world with 17,504 islands covering a land area of 1.91 million km21. More than 60% has forest status, not all of which is actually forested, controlled by the state2. Of this, more than 22 million ha or 21.26% is managed as protected areas (PAs)3. This exceeds the area of PAs in most countries in Asia, Africa and Latin America4. Indonesia has already exceeded the Aichi Biodiversity Targets aim of protecting 13% to 17% of the land surface by 20205,6. However, human activities may have an impact on PAs, decreasing their effectiveness. In Indonesia, current data show that approximately 2.2 million ha of degraded lands occur in terrestrial PAs. This is approximately 10% of their total area7. Amid the current high pressures for economic and human development, forest ecosystems, wildlife populations and the various ecosystem services that they provide will likely only remain in protected areas (PAs). Protected areas have become the lead efforts of nature conservation8. A study of global PAs showed that PAs were able to protect habitats from deforestation9. Forest cover in Sumatra, Indonesia between 2000 and 2012 was more intact in and around national parks10. This was also the case for biodiversity; species richness was found to be 10.6% and abundance 14.5% higher inside than outside of PAs globally11. However, around 10% of global PAs are ‘paper parks’, protected areas with legal status that do not have management activities on the ground. More than 60% only have basic support with a significant lack of management activities12. Protected areas that lack conservation management capability tend to suffer from habitat and biodiversity loss13,14. PAs in Indonesia have not yet been proven to protect forests and biodiversity. The rate of deforestation in PAs in Sumatra is no different to that in production forest areas. Protected areas are no more effective in maintaining forest cover than areas managed for timber production15. The population of Sumatran elephants is estimated to have dropped by 35% since the 1990s16. Likewise, populations of Sulawesi's endemic species17 such as the anoa18, continue to decline. Sumatran primates10,19 and tigers20 also have not been able to maintain their populations within PAs.

This study examined pressures caused by human activities in and around terrestrial national parks in Indonesia between 2012 and 2017. In 2015, there were changes in the management of Indonesia’s PAs. Previous to 2015, PAs were managed under the Directorate General of Forest Protection and Nature Conservation (Direktorat Jenderal Perlindungan Hutan dan Konservasi Alam – PHKA), Ministry of Forestry. In 2015 this was changed to the Directorate General of Natural Resource and Ecosystems Conservation (Direktorat Jenderal Konservasi Sumber Daya Alam dan Ekosistem – KSDAE), Ministry of Environment and Forestry. The major difference is that law enforcement power used to be within the directorate general PHKA itself, whereas following this change KSDAE must work with a different directorate general within the Ministry of environment and forestry for law enforcement. Due to these changes, the number of forest guards in each park was reduced by 32% in 2017 compared to 201221. This study also includes an assessment of the impact of these changes on the degree of human pressures on national parks. Hence, for comparability reasons, this study only examined the 43 terrestrial NPs established up to and including 2012. All 43 of these NPs have their own management units. The four NPs that are not included in this study are new and do not yet have separate management units.

Pressures from human activities were calculated using Human Footprint (HF) analysis. The Human Influence Index (HII) was developed to measure anthropogenic impacts on the environment. The resultant map is called a Human Footprint map22. It can be used, among other things, for conservation planning, developing strategies for natural resource management and studies on human—environment interactions23. Previous studies have shown that the HF from economic and associated human development activities increases the vulnerability of PAs around the world24,25. In this study, we map the HII score in and around Indonesian national parks in 2012 and 2017 as the Human Footprint. The score is standardized per hectare for comparisons among NPs and bioregions. Percent changes of HII score per ha between 2012 and 2017 in each NP were also calculated to assess whether they were changing or not, and if they were, to discuss options for limiting their effects. Other HF studies in Mexico26, Ecuador27 and Tibet28 have shown that the HF has caused natural habitat degradation even inside protected areas, and even where unfavorable physical conditions such as high elevation and steep terrain hinders human activities29,30.

Indonesia currently has 54 national parks (NPs), which are a sub-set of PAs. There are 47 terrestrial NPs and 7 marine NPs. Among those, 27 have international status as World Heritage, Biosphere Reserve, ASEAN Heritage, or Ramsar Convention Sites31. In Indonesia, NPs have the most well-resourced management regimes compared to other kinds of PAs, such as Nature Reserve (NR) or Wildlife Reserve (WR). Each NP has its own management unit, while several NRs or WRs may be managed by a single management unit. Indonesia’s NPs cover approximately 16 million ha, or 60% of the total area covered by PAs in Indonesia7. They also contain 6,861,497.92 ha of primary forests, which increased by 0.07% between 2012 and 201721.

Results

Drivers of the human footprint in and around national parks

Human Footprint (HF) in Indonesia’s national parks (NPs) and their buffer areas were calculated for the years 2012 and 2017 to see if there are any significant difference across those 5 years, and if so, whether they could be related to the organizational changes in the Ministry of Environment and Forestry in 2015. Difference between 2012 and 2017 were detected but were too subtle to be shown on a map at the scale used here, so only the 2017 map is presented here. The Human Footprint 2017 map shows that Jawa Bali has the highest HF pressures both inside the parks and in the 10-km buffer areas, is followed by Nusa Tenggara. National parks in Sulawesi, Maluku, Sumatra, Kalimantan and Papua have lower HF pressures than those in Jawa Bali and Nusa Tenggara (Fig. 1). Human Footprint pressures inside the 43 terrestrial NPs and their buffer areas in 2017 varied greatly. Some bioregions had high HF while the others were relatively low, and all bioregions experienced higher HFs in the buffer areas than inside the parks (Fig. 2). This HF analysis for areas inside and around Indonesia’s terrestrial NPs is valid. The validation analysis showed that the Root Mean Square Error (RMS Error) for HF scoring was 0.14 and 0.13 for 2012 and 2017, respectively. This means there were errors around 13% and 14% in assigning HF measures and scoring pressures compared to the visual interpretation of the high resolution map. The Kappa Statistic analyses for 2012 and 2017 data were both 0.65 (P < 0.05). The Human Footprint assigned scores were a match to the visual scores if they were more than 0.5 or within 20% of one another on the 0–1 scale.

Figure 1
figure1

Human Footprint in 2017 within and around 43 terrestrial national parks (NPs) in 7 bioregions in Indonesia: (a) Sumatra, (b) Kalimantan, (c) Sulawesi, (d) Maluku and Papua, (e) Jawa and Bali, and (f) Nusa Tenggara. Activity data maps of Indonesian NPs (land cover maps, roads, river and settlements) used in the Human Footprint analysis in this study were obtained from the Indonesian Ministry of Environment and Forestry32, and Binamarga33. National Parks boundaries were obtained from The World Database on Protected Areas (https://www.protectedplanet.net/en). The Human Footprint maps were created using Esri ArcMap 10.8 (https://www.arcgis.com).

Figure 2
figure2

Each Human Footprint pressure per hectare NPs areas in 2017 in 7 bioregions in Indonesia. The numbers below each bioregion are the number of NPs in that bioregion.

In this study, HF is a summation of pressures from human population, roads, access (from roads, railways, big rivers and coastlines), settlements, and land transformation. Land transformation comprises agriculture, industrial plantation (IP), built up environment (BUE) and other land uses (OLU) such as bare lands and shrubs (Table 2 in the “Methods” section). In total, inside the parks, access delivers the highest HF, followed by human population, roads and land transformation. Outside the parks, roads provide the highest HF, followed by land transformation, access, and human population. Human Footprint also calculated the score of settlements and built up environments both inside the parks and in their buffer areas, however their scores are very low compared to the other pressures, ranging from 0 to 0.1 in each bioregion, hence are not presented (Fig. 2).

In Sumatra population is the highest pressure inside NPs, followed by access, roads, agriculture, OLU, and industrial plantation. In the 10-km buffer areas, agriculture is the highest HF driver, followed by roads, access, population, OLU, and IP. In Kalimantan, population is not the highest pressure within NPs, access is. Other land use comes next, followed by roads, agriculture and IP. Outside NPs, roads provide the highest HF, followed by population, OLU, access, agriculture, and IP. In Sulawesi, NPs are pressured by access and roads, then by population, OLU, agriculture and IP. In their buffer areas, roads and access are the two highest pressures. Agriculture follows then population, OLU and IP (Fig. 2).

Maluku also experiences access and roads as the highest provider of HF, followed by population, OLU and agriculture. In the buffer areas, roads provide the highest HF, followed by access, population, agriculture, OLU, and IP (Fig. 2).

The highest HF per ha of any NP in Indonesia occurred in Manusela NP. Approximately 75% of the area of Manusela NP is in Central Maluku District, Maluku Province. Central Maluku District is a focus for agricultural development in Maluku because it is suitable for the expansion of rice paddy fields to support Maluku’s food security program34. In addition, Maluku is currently undergoing a trans Maluku roads development program including on Seram Island where Manusela NP is located. These two factors together have had a high impact on Manusela NP and its buffer zone (Fig. 3).

Figure 3
figure3

Human Footprint and land use in Manusela National Park, Maluku in 2017. Activity data maps of Manusela NP (land cover maps, roads, river and settlements) used in the Human Footprint analysis in this study were obtained from the Indonesian Ministry of Environment and Forestry32 and Binamarga33 and NP boundary was obtained from The World Database on Protected Areas (https://www.protectedplanet.net/en). The Maps were created using Esri ArcMap 10.8 (https://www.arcgis.com).

Papua bioregion has the lowest HF inside and outside its NPs, while Nusa Tenggara has the second highest scores for HF after the Jawa Bali bioregion. NPs in Papua experience the highest HF from population, then access, roads, OLU, and agriculture. Outside the parks, it experiences the highest HF from roads then access, population, agriculture, and OLU. In Nusa Tenggara, access and roads cause the highest HF in NPs, followed by population, OLU, agriculture, and IP. In buffer areas, highest HF also comes from roads and access, followed by population, agriculture, OLU, BUE, and IP (Fig. 2).

Changes in the human footprint between 2012 and 2017

In order to plan effective protected areas management programs, it is important to see how pressures change over time, especially in a relatively short periods. This study shows that the HF has changed in and around NPs in Indonesia, even in a period of only 5 years. Between 2012 and 2017, all bioregions experienced average increases in their HFs, both inside parks as well as in the 10-km buffer areas outside the parks. The results of regression analysis show a causal significant relationship (R2 = 0.53, df = 33, P < 0.01) between the HF in NPs buffer areas and HF inside NPs. When the HF outside increases, then the HF inside also increases. Inside the parks, the highest HF increases occurred in the Kalimantan bioregion, where the average changes across eight NPs was 17.93%. The lowest increases occurred in the Nusa Tenggara bioregion, with an average change of 3.56% in five NPs. In the 10-km buffer areas, the highest increase also occurred in Kalimantan with an average of 16.61%. The lowest occurred in the Papua bioregion with an average change of 5.16% from two NPs. On average, more bioregions in Indonesia experienced higher increases of HFs inside NP compared to HFs in the 10-km buffer areas (Sumatra, Kalimantan, Sulawesi, and Papua). But HFs in the buffer areas in Nusa Tenggara, Jawa Bali and Maluku increased more than in the NPs (Fig. 4).

Figure 4
figure4

Average percent changes of the Human Footprint in the 7 bioregion of Indonesia between 2012 and 2017.

Individually, some NPs had relatively low HF changes, while others had relatively high changes. Ujung Kulon NP in the Jawa Bali bioregion, experienced a decrease of 10.5% over the 5 years between 2012 and 2017. Five other NPs, Alas Purwo, Baluran and Bali Barat also in Jawa Bali, Danau Sentarum in Kalimantan, and Komodo in Nusa Tenggara also experienced a decrease inside the parks. Those four NPs in the Jawa Bali bioregion also had a decrease within their 10-km buffer areas, while Danau Sentarum and Komodo experienced increases in their buffer areas (Table 1).

Table 1 Changes in Human Footprint (Human Influence Index scores), inside and outside 43 terrestrial national parks in Indonesia between 2012 to 2017.

All other NPs experienced an increase in the HF inside the park and in the buffer areas (Table 1). Among all NPs, Tanjung Puting in Kalimantan experienced the greatest increase inside the park (77.3%). In each bioregion, the highest increases inside parks were experienced by Way Kambas in Sumatra (24.4%), Rawa Aopa Watumohai in Sulawesi (16%), Meru Betiri in Jawa Bali (11.6%), Lorentz in Papua (10.96%), Gunung Rinjani in Nusa Tenggara (10.8%), and Manusela in Maluku (10.59%). Tanjung Puting, Rawa Aopa Watumohai, Meru Betiri, Manusela, and Lorentz also experienced the highest increase in their buffer areas, with 63.7%, 12.48%, 11.7%, 11.2%, and 10.2% respectively. Other buffer areas with high HFs are Laiwangi Wanggameti in Nusa Tenggara (16.3%) and Berbak in Sumatra (13.8%, Table 1).

Tanjung Puting NP in Kalimantan (Fig. 5) experienced the greatest HF increase, both inside and outside the park. Tanjung Puting also experienced land transformation such as secondary swamp forest (peatland) becoming degraded due to agriculture and plantation expansion, illegal logging and forest fires35.

Figure 5
figure5

Human Footprint and land use in Tanjung Puting National Park, Kalimantan in 2012 and 2017. Activity data maps of Tanjung Puting NP (land cover maps, roads, river and settlements of respected years) used in the Human Footprint analysis in this study were obtained from the Indonesian Ministry of Environment and Forestry32 and Binamarga33 and NP boundary was obtained from The World Database on Protected Areas (https://www.protectedplanet.net/en). The Maps were created using Esri ArcMap 10.8 (https://www.arcgis.com).

Jawa Bali bioregion

Jawa Bali is the most populous and well developed bioregion in Indonesia, hence it also has the highest HF compared to the other bioregions. However, in the study period between 2012 and 2017, total forest cover in NPs in Jawa Bali actually increased by 1.23%21. In those 5 years, all other bioregions experienced a decrease in forest cover in NPs, ranging from 0.24% in Maluku to 2.34% in Kalimantan21. There are 11 NPs in the Jawa Bali bioregion, four of which experienced a decrease in HF both inside and outside the parks. Jawa Bali bioregion also had higher increases in the HF outside the parks compared to the inside (Fig. 4).

Human population is the highest driver of HFs in Jawa Bali, both inside the parks and outside. Access and roads are the second biggest driver inside the parks, followed by IP, agriculture, and OLU. In the buffer areas, roads are the second highest, followed by access, agriculture, IP and OLU.

Discussion

Drivers of the human footprint in and around national parks

It has been recognized that to be able to achieve their management objectives, PAs must also be supported by appropriate management of the surrounding areas. Changes to the environment in areas directly adjacent to PAs are especially important in determining the ecological conditions for biodiversity and habitats within them36. In the past, conservation areas were managed as self-contained units, with institutional management, day to day management of species and habitats, and research all taking place within the boundaries of PAs regardless of activities outside. Protected areas were considered to be free from encroachment by economic and human development. However, PAs are embedded in landscapes and seascapes, which are complex social-ecological systems shaped by interactions between biological, ecological and physical features mediated by the actions of people37. There are clear interdependencies between a PA and the surrounding social-ecological system38,39. Forest cover, human population, road expansion, and traffic within PAs reflect what is happening in the surrounding area36. These conditions are shown clearly in most of Indonesia’s NPs, as statistical analysis here showed that increased HFs inside NPs follow what is happening in the 10 km buffer areas.

  1. a.

    Roads and access

Terrestrial NPs in Indonesia are strongly impacted by infrastructure development, especially roads. Roads are the principal driver of HFs outside the parks in most bioregions, thus causing access (from roads) to be the principal driver inside the parks. Roads are generally built to support increasing human populations and new or expanding settlements9, but road construction within or adjacent to PAs places high pressures on them because it increases the rate of forest fragmentation and the loss of habitat for wildlife36. Unfortunately, road access also helps people to encroach on NPs, although they also encroach on them using natural access via rivers and along coastlines, and facilitate agricultural and plantation development in and around NPs9. In addition, road constructions can cause erosion and landslides36.

Although they differ in the degree of pressure in each bioregion, roads and access are still the highest drivers of HFs. NPs in Jawa Bali, Nusa Tenggara, Maluku and Sulawesi have suffered the most from road development, both inside the parks and adjacent to them. Studies have shown that planned and ongoing road and rail-line developments currently occurring in Kalimantan will likely have many negative ecological impacts, including fragmenting large expanses of intact forest. If all planned projects proceed under the assumption that new road and rail projects will have only a 1-km buffer on either side, landscape connectivity across the region will decline sharply from 89 to 55%40,41. In Sumatra, a planned 2700-km pan-Sumatra Highway would affect forests in and around Kerinci Seblat and Leuser NPs. The highway would provide opportunities for encroachment into the edges of these parks42. A study in Rawa Aopa Watumohai NP in Sulawesi, documented one of the highest levels of road mortality in Asia. The survey was conducted along a 21.8-km section of paved highway that crosses the park. Forty taxa, 15% of which are endemic to the Wallacea region, were represented by animals killed on this stretch of road43.

It is believed that similar results will occur in other bioregions such as Nusa Tenggara, Maluku and Papua. In order to reduce the impact of road developments and access to NPs, it has been emphasized that prevention, or at least close supervision, of road construction within and adjacent to PAs is very important in increasing management effectiveness44. However, new Indonesian regulations on road developments seem to provide weaker protection for protected forests which are less known and less reported in the media, but contribute significantly to biodiversity conservation. These kinds of forests, less known but critical for conservation, usually are the very kinds threatened by infrastructure expansion, especially road developments42.

  1. b.

    Human population

After roads and access, human population is the main driver of HFs both inside and in the buffer areas of Indonesia’s terrestrial NPs. Human population is frequently mentioned as the main cause of declines in the quality of nature, with higher human populations leading to more adverse impacts on nature. Human population increases in areas adjacent to PAs add more pressures both inside the PAs and within the buffer areas around them24. The changes in human pressures in PAs and surrounding areas in Sundaland seemed to correspond with the increases in human population45.

This study also showed that it was the case for 43 terrestrial national parks in Indonesia. Tanjung Puting NP in Kalimantan has the highest increase in the HF and it was mostly due to a large local increase in human population. It was 21.31 people/km2 in 2010, rising to 24.7/km2 in 2015, an increase of 15.96%1. The higher the human population, the more natural resources are needed to support it. However, the impacts of the interaction between human populations and natural environment are not yet known in detail, partly because the impact will depend on the nature of the interaction as well as on the type of ecosystems, or specific natural processes22. This is also the case in Tanjung Puting NP where the very high increase in the HF in the park is due to changes in the indirect effect of increasing the human population outside the parks.

  1. c.

    Land transformation

In this HF study, land transformation comprises agriculture, industrial plantations (IP), built up environment (BUE) and other land uses (OLU) such as bare lands and shrubs. Terrestrial NPs in Indonesia experienced these land transformations both inside and outside the park areas. While land transformation inside the parks will certainly have direct impacts on forests and biodiversity, land transformations occur adjacent to park areas can also have detrimental effects. In Indonesia, land transformation around PAs due to human population changes, or regional expansion followed by infrastructure needs, mobility, mining, broad-scale plantations, as well as market demand for certain commodities, have been identified as the pressures that affect the condition of PAs2. PAs usually mirror environmental degradation that occurs in the surrounding areas. A decrease of natural habitats in the buffer areas has led to a decrease in the ability of PAs to protect their biodiversity. This has happened in Way Kambas NP, Sumatra. Between the early 1980s and 2011, the percentage of forest cover to a distance of 50 km around Way Kambas National Park in Lampung, Sumatra, fell from 80 to 33%46, while the park itself lost around 8% of its forest cover only within 5 years from 2012 to 201721.

Using production forest or industrial plantation (IP) concessions as buffers for conservation areas can increase the effectiveness of management to protect forests and biodiversity47. However, this is not always the case for Indonesia’s national parks. For example, Tesso Nilo in Sumatra has industrial timber production forest and palm oil plantations as buffers48, however its HF increased more inside the park (19.1%) than in the buffer zone (7.5%) between 2012 and 2017 (Table 1). Other land use such as bare lands and shrubs are still a big part of HF drivers in Indonesia’s NPs. There are around 2.2Mha degraded forest inside PAs in Indonesia. This is about 10% of the total areas of PAs7. Tanjung Puting NP in Kalimantan suffered the highest increase of HF between 2012 and 2017. This was partly due to land transformation in the form of natural peatlands degradation. Most peatlands in Indonesia, including in Kalimantan, have experienced decades of mis-management. Peat swamp forests have been subjected to illegal logging as well as plantation and agricultural expansion. This has led to peat being drained with a loss of biodiversity and a significant increase in fire vulnerability. In 2015, coupled with a strong El Niño event, extensive fires burned thousands of square km of peatlands, including in Tanjung Puting35.

Changes in the human footprint between 2012 and 2017

Most of the terrestrial NPs in Indonesia experienced increase of HF both inside and outside the parks between 2012 and 2017. Among 43 NPs, only 4 NPs in Jawa Bali bioregion have lower HF inside and outside the parks. Danau Sentarum in Kalimantan and Komodo in Nusa Tenggara have lower HF only inside the parks. In 2015, there were changes in the Indonesia’s Ministry of Environment and Forestry that caused the reduction of the number of forest guards on each NP in 2012 compare to 2017. Law enforcement policy plays an important role in reducing forest degradation and deforestation49,50. Although directly reduced the number of forest guards, the overall organizational changes were meant to achieve better protection and conservation outcomes not just in protected areas. However, in terms of forest cover protection, these changes have not yet seen positive impacts. Between 2012 and 2017, forest cover in most of Indonesia’s terrestrial NPs was still declining, although not significantly related to NPs forest guards’ reduction. Reduced forest cover was significantly caused by increase of HF inside the parks21.

The effectiveness of conservation areas in stopping forest encroachment, or at least reducing deforestation, hunting, and forest fires, is directly related to management activities. Basic management activities such as enforcing regulations, defining clear boundaries, and providing direct compensation to local communities around parks, have succeeded in increasing management effectiveness51. Increased investment in management infrastructure, including increased numbers of personnel, is important to maximize forests and biodiversity protection52. Partnership and collaboration with many parties can also create success stories. One example is the Bunaken Marine National Park in North Sulawesi, which collaborates with local communities, the diving tourism industry, and provincial and district level governments. Through this partnership the sustainability of revenues for national parks, community involvement and support and the achievement of conservation efforts has been increased53. Kayan Mentarang NP in Kalimantan also benefits from local communities involvement in PA management and has the lowest HF in Indonesia. This 1.4 Mha of forest is the largest forest conservation area in Kalimantan. The Human Footprint in Kayan Mentarang is low because of the difficult access due to steep terrain and wild rapid rivers54. Such areas are less suitable for agriculture or plantation expansions29. Besides that, the traditional Dayak communities living in Kayan Mentarang still value natural ecosystem highly and that helps to protect them from external influences55,56. Management by indigenous peoples or local communities can be a factor that improves the effectiveness of conservation area57. Other success stories involving communities’ collaborations also happened in Jawa Bali bioregion.

Jawa Bali bioregion

Jawa Bali bioregion is special because among the 43 terrestrial NPs in Indonesia, 6 in Jawa Bali managed to increase their forest cover despite the highest HF within and outside the parks. In a modeling study, it was suggested that in 100 years, 6 to 8 billion people on Earth will mostly be living in urban areas, with very low number still living in extreme poverty, and almost all participating in a technologically driven, interconnected market economy. They explained that the interacting effects of urban lifestyles on fertility, poverty alleviation, and ideation will shift the dynamics of the main drivers of deterioration in nature. At that stage, conservation practice will transform itself from a discipline managing declines in nature to a transformative movement of recovery58. This model is in line with another study that showed Indonesia’s deforestation rates will be declining after 2030 and will reach nil deforestation and change to afforestation in 2035–204559. This may have already started to happen in the Jawa Bali bioregion. NPs in all Indonesia’s bioregions experienced reduced forest cover from 2012 to 2017, except in the Jawa Bali bioregion21. National parks in Jawa Bali had the highest HF outside and inside the parks. However, forest cover was maintained, with some NPs even managing to gain forest cover, over the 5 year period21. The ability to regenerate forests will increase if the pressure of human activity decreases60. Most NPs in the Jawa Bali bioregion serve as the main water sources for the surrounding areas, hence are crucial to people's lives. So although the HF in the buffer zone may be high due to the expansion of agricultural land, settlements, road construction, and other human activities, the parks’ forests are still maintained for the sake of water availability61. Furthermore, the remaining forests of Jawa Bali NPs occur in the steep mountains, making it difficult to encroach. The more accessible landscapes are already degraded62.

Social and cultural customs in Jawa Bali might also be contributing to this promising phenomenon. The Balinese have a number of local policy values that govern human relations with nature. Some examples that continue to be carried out today are the tree sacred belief system and the Hindu philosophy of Tri Hita Karana. Customary laws to protect trees are not just related to certain sacred species like banyan trees63 but also to any trees in sacred areas such as waterfalls, used by Balinese Hindus to perform prayer activities, meditation and activities related to the spiritual64. Tri Hita Karana teaches that harmony between humans and nature is one of three sources of human well-being65. In Java, there is the Pranata Mangsa system which is a calendar of traditional seasonal rules that govern natural resource use. This is useful as a cultural aid in the preservation of the natural environment66. One of the uses of Pranata Mangsa today is the Brubuh practices related to forest preservation. Brubuh is a traditional seasonal logging practice. It is conducted by only cutting down trees in certain seasons according to Pranata Mangsa. Using this practice, the forest can be better protected67. Support of this kind from various sources, like in Jawa Bali bioregion, Kayan Mentarang and Bunaken, improves the effectiveness of the management of PAs57,68.

Conclusion

Human footprint analyses in this study showed that PAs, especially terrestrial national parks, in Indonesia, have experienced impacts from increased roads and access, human population as well as land transformations. Protected areas usually mirror environmental degradation that occurs in the surrounding areas. Therefore, it is very important to maintain the ecological environment around a conservation area36. A balance between conservation and sustainable development might be obtained by integrating the conservation area with the surrounding area44. Collaboration from local communities and indigenous people, especially in utilizing environment services, also proved to be beneficial to protected areas. More support for these kinds of management activities throughout Indonesia would help mitigate the increasing HFs detected in this study and perhaps begin to shift momentum towards the kind of recovery now evident in the Jawa Bali bioregion.

Methods

The Human Influence Index (HII) was measured to quantify the pressures on national parks both within the parks, and within a 10 km buffer outside the parks. The HII scores were then converted into a Human Footprint (HF) map22. We used the 43 terrestrial national parks established up to and including 2012 (Fig. 6). They are distributed across 7 bioregions: Sumatra, Kalimantan, Sulawesi, Nusa Tenggara, Maluku, Papua and Jawa Bali69.

Figure 6
figure6

Forty three (43) terrestrial national parks in Indonesia included in the analysis. National parks boundaries were obtained from The World Database on Protected Areas (https://www.protectedplanet.net/en). The Map was created using Esri ArcMap 10.8 (https://www.arcgis.com).

The steps to obtaining HII scores are shown in the diagram in Fig. 7, following a study on global HFs70. First, the different types of human activity that cause changes in forest cover were determined. Modification of the classification of pressure types from the original ones22 is shown in Table 2. Sub-pressures shown in Table 2 and scores were modified based on conditions in Indonesia and data availability as follows. In Indonesia, man-made environments such as agriculture and plantation areas usually have higher human activities due to the use of more human power compared to global averages. Thus HII scores in those areas were increased from the original scores22. In this study, roads and settlements were divided into more detailed types and given scores more closely related to each type (Table 2). Besides that, in some NPs, certain habitats are natural while in others the same habitat types occur due to human disturbances. Scrub and shrub habitats usually result from forest lost and deforestation, except in NPs with savanna-like natural habitats such as in East Jawa and north-west Bali. In order to correctly score natural habitats versus non-natural habitats, habitat conditions were assessed relative to a 1990 National Parks habitat map. The NPs studied here were established and had legal status between 13 and 37 years ago. Habitats shown on the 1990 map were deemed to be natural and therefore not much disturbed by human activities. Hence, any areas in which habitats have stayed the same since 1990 were considered to be natural and given a score of 0.

Figure 7
figure7

Flowchart showing the process of mapping the Human Footprint in 43 terrestrial national parks in Indonesia and in a 10-km buffer surrounding them. The steps detailed were slightly modified from the original70.

Table 2 Relative scores for pressures inside national parks and in 10 km buffers outside the parks used in the Human Footprint analysis.

Base maps used for each pressure data were in a 30 m × 30 m pixel format except for the human population density map25. The human population density map has a 1 km × 1 km pixel format. For this analysis, the population density map data was reduced to 30 m × 30 m using the ArcGIS bilinear sampling method70. In order to create the global Human Footprint maps, the original human population data23 were re-scaled and standardized to a maximum value of 1022. After all sub-pressures were scored, each score was summed for all pixels in each base map. All data source base maps were then overlaid and all pixel values in the overlay maps were added up. This generated a total pressure value or total HII for each national park. Total HII scores were calculated for all parks and the 10-km buffer areas outside the parks. Human Influence Index (HII) is then described as a Human Footprint (HF) map. In order to create the HF map, the total value of each overlaid pixel was then standardized to a range from 0 to 100 using the formula:

$$HF_{i} = \frac{{\left( {HII_{i} {-} \, HII_{minj} } \right) \, \times \, 100}}{{HII_{maxj} - \, HII_{minj} }}$$

where i represents the pixel and j represents the national park of which the pixel is a member24.

The global scale Human Footprint22 was revised70. That revision used a total of 3114 sample points across the globe to validate the global human footprint map. For this study, 100 sample points were taken from 43 national parks. When comparing the world land area of 51,000,000 km2 with the land area of Indonesia covering 1,905,000 km2, then 100 sample points from 43 national parks was more than sufficient for validation purposes.

The validation was conducted by repeating the relative scoring for each pressure seen at the 100 sample points. The scoring was done visually by looking at land cover across an area of 1 km × 1 km at each sample point on high-resolution satellite imagery from Google Earth. Each area of 1 km × 1 km was allocated a dominant land cover (> 50%) and given a pressure score of 0–10, according to the researchers' visual interpretation and based on the pressure scores listed in Table 2. Validation of scoring was calculated using the non-parametric statistical method Root Mean Square Error71 and Cohen kappa statistics of agreement72 commonly used in geospatial analysis, especially when calculating the validity of land cover classifications. The relative score used in the model are valid if the Kappa Statistics are > 0.5. Validation analyses were conducted for both 2012 and 2017 human footprint data. Human Footprint or HII scores were then divided by the total area of each NP and its buffer area to get HII per ha. Percent changes of this HII per ha were calculated by comparing HII in 2012 and in 2017. Finally, The relationship between the percent change of HF between 2012 and 2017 in the 10-km buffer areas outside the parks and inside the parks was tested by simple linear regression analysis performed using the R statistic packages73.

Data availability

Data available upon request.

References

  1. 1.

    BPS. Statistik Indonesia 2018 (Badan Pusat Statistik, Jakarta, 2018).

    Google Scholar 

  2. 2.

    KLHK. Pedoman penilaian efektivitas pengelolaan kawasan konservasi di Indonesia. (Direktorat Kawasan Konservasi dan Direktorat Jenderal Konservasi Sumber Daya Alam dan Ekosistem, Kementerian Lingkungan Hidup dan Kehutanan, Jakarta, 2015).

  3. 3.

    Ditjen KSDAE. Statistik Direktorat Jenderal KSDAE 2017 (Kementerian Lingkungan Hidup dan Kehutanan Direktorat Jenderal Konservasi Sumber Daya Alam dan Ekosistem, Jakarta, 2018).

  4. 4.

    Mulyana, A. et al. Kebijakan pengelolaan zona khusus. Dapatkah meretas kebuntuan dalam menata ruang Taman Nasional di Indonesia? Brief, 1 (2010).

  5. 5.

    CBD. Convention on Biological Diversity https://www.cbd.int/sp/ (2019).

  6. 6.

    Murninngtyas, E. et al. (eds) Indonesian Biodiversity Strategy and Action Plan (IBSAP) 2015–2020 (Ministry of the National Development Planning/ BAPPENAS, Jakarta, 2016).

    Google Scholar 

  7. 7.

    Wiratno. Sepuluh cara baru kelola kawasan konservasi di Indonesia: membangun “organisasi pembelajar” (Direktorat Jenderal KSDAE Kementrian Lingkungan Hidup dan Kehutanan, Jakarta, 2018).

  8. 8.

    Coad, L. et al. Measuring impact of protected area management interventions: current and future use of the Global Database of Protected Area Management Effectiveness. Philos. Trans. R. Soc. B 370, 20140281. https://doi.org/10.1098/rstb.2014.0281 (2015).

    Article  Google Scholar 

  9. 9.

    Geldmann, J. Evaluating the effectiveness of protected areas for maintaining biodiversity, securing habitats, and reducing threats. PhD thesis. (PhD School of the Faculty of Science, University of Copenhagen, 2013).

  10. 10.

    Supriatna, J., Dwiyahreni, A. A., Winarni, N., Mariati, S. & Margules, C. Deforestation of primate habitat on Sumatra and adjacent islands Indonesia. Primate Conserv. 31, 71–82 (2017).

    Google Scholar 

  11. 11.

    Gray, C. L. et al. Local biodiversity is higher inside than outside terrestrial protected areas worldwide. Nat. Commun. 7(12306), 1–7. https://doi.org/10.1038/ncomms12306 (2016).

    CAS  Article  Google Scholar 

  12. 12.

    Eklund, J. & Cabeza, M. Quality of governance and effectiveness of protected areas: crucial concepts for conservation planning. Ann. N. Y. Acad. Sci. https://doi.org/10.1111/nyas.13284 (2016).

    Article  PubMed  Google Scholar 

  13. 13.

    Jones, K. R. et al. One-third of global protected land is under intense human pressure. Science 360, 788–789. https://doi.org/10.1126/science.aap9565 (2018).

    CAS  Article  PubMed  Google Scholar 

  14. 14.

    Wiratno. Tersesat di jalan yang benar. Seribu hari mengelola Leuser (Direktorat PKPS, Jakarta, 2012).

  15. 15.

    Gaveau, D. L. A. et al. Examining protected area effectiveness in Sumatra: importance of regulations governing unprotected lands. Conserv. Lett. 5, 142–148. https://doi.org/10.1111/j.1755-263X.2011.00220.x (2012).

    Article  Google Scholar 

  16. 16.

    Azmi, W. & Gunaryadi, D. Current status of Asian elephants in Indonesia. Gajah 35, 55–61 (2011).

    Google Scholar 

  17. 17.

    O’Brien, T. G. & Kinnaird, M. F. Changing populations of birds and mammals in North Sulawesi. Oryx 30, 150–156 (1996).

    Article  Google Scholar 

  18. 18.

    Wheeler, P. & Dwiyahreni, A. Large mammal monitoring in Lambusango. Interim Progress Report January 2007 (University of Hull, UK, 2007).

  19. 19.

    Gaveau, D. L. A., Wich, S. A. & Marshall, A. J. Are protected areas conserving primate habitat in Indonesia? In An introduction to primate conservation (eds Wich, S. A. & Marshal, A. J.) 193–200 (Oxford University Press, Oxford, 2016).

    Chapter  Google Scholar 

  20. 20.

    Wibisono, H. T. & Pusparini, W. Sumatran tiger (Panthera tigris sumatrae): a review of conservation status. Integr. Zool. 5, 313–323. https://doi.org/10.1111/j.1749-4877.2010.00219.x (2010).

    Article  PubMed  Google Scholar 

  21. 21.

    Dwiyahreni, A.A. et al. Forest cover changes in Indonesia’s terrestrial national parks between 2012 and 2017. Biodiversitas, 22(3), 1235–1242. https://doi.org/10.13057/biodiv/d220320 (2021).  

  22. 22.

    Sanderson, E. W. et al. The human footprint and the last of the wild. Bioscience 52(10), 891–904. https://doi.org/10.1641/0006-3568(2002)052[0891:THFATL]2.0.CO;2 (2002).

    Article  Google Scholar 

  23. 23.

    CIESIN. United Nation's World Population Prospects (UN WPP)-Adjusted Population Density https://sedac.ciesin.columbia.edu/data/set/gpw-v4-population-density-adjusted-to-2015-unwpp-country-totals-rev11 (2018).

  24. 24.

    Wan, J. Z., Wang, C. J. & Yuc, F. H. Human footprint and climate disappearance in vulnerable ecoregions of protected areas. Global Planet. Change 170, 260–268. https://doi.org/10.1016/j.gloplacha.2018.09.002 (2018).

    ADS  Article  Google Scholar 

  25. 25.

    Leroux, S. J. et al. Global protected areas and IUCN designations: do the categories match the conditions?. Biol. Conserv. 143, 609–616. https://doi.org/10.1016/j.biocon.2009.11.018 (2010).

    Article  Google Scholar 

  26. 26.

    Ayram, C. A. C., Mendoza, M. E., Etter, A. & Salicrup, D. R. P. Anthropogenic impact on habitat connectivity: a multidimensional human footprint index evaluated in a highly biodiverse landscape of Mexico. Ecol. Ind. 72, 895–909. https://doi.org/10.1016/j.ecolind.2016.09.007 (2017).

    Article  Google Scholar 

  27. 27.

    Tapia-Armijos, M. F., Homeier, J. & Muntac, D. D. Spatio-temporal analysis of the human footprint in South Ecuador: influence of human pressure on ecosystems and effectiveness of protected areas. Appl. Geogr. 78, 22–32. https://doi.org/10.1016/j.apgeog.2016.10.007 (2017).

    Article  Google Scholar 

  28. 28.

    Li, S., Wu, J., Gong, J. & Li, S. Human footprint in Tibet: assessing the spatial layout and effectiveness of nature reserves. Sci. Total Environ. 621, 18–29. https://doi.org/10.1016/j.scitotenv.2017.11.216 (2018).

    ADS  CAS  Article  PubMed  Google Scholar 

  29. 29.

    Geldmann, J. et al. Effectiveness of terrestrial protected areas in reducing habitat loss and population declines. Biol. Conserv. 161, 230–238. https://doi.org/10.1016/j.biocon.2013.02.018 (2013).

    Article  Google Scholar 

  30. 30.

    Anderson, E. & Mammides, C. The role of protected areas in mitigating human impact in the world’s last wilderness areas. Ambio https://doi.org/10.1007/s13280-019-01213-x (2019).

    Article  PubMed  PubMed Central  Google Scholar 

  31. 31.

    Mulyana, A., Kosmaryandi, N., Hakim, N., Suryadi, S. & Suwito. Ruang adaptif: refleksi penataan zona/blok di kawasan konservasi (Direktorat Pemolaan dan Informasi Konservasi Alam dan Direktorat Jenderal Konservasi Sumberdaya Alam dan Ekosistem, Kementerian Lingkungan Hidup dan Kehutanan, Bogor, 2019).

  32. 32.

    Landuse thematic map 2012 and 2017 (Indonesian Ministry of Environment and Forestry)

  33. 33.

    Binamarga Map 2014 (Indonesian Ministry of Public Works)

  34. 34.

    Rusmin, N., Edy, S., Robby, A. & Dwi, K. R. Study of the potential expansion of new rice fields in Central Maluku District to support food security in Maluku Province. IOP Conf. Ser. Earth Environ. Sci. 334, 012067. https://doi.org/10.1088/1755-1315/334/1/012067 (2019).

    Article  Google Scholar 

  35. 35.

    Harrison, M. E., Capilla, B. R., Thornton, S. A., Cattau, M. E., & Page, S.E. Impacts of the 2015 fire season on peat-swamp forest biodiversity in Indonesian Borneo. In 15th International Peat Congress 2016, 713–717 (2016).

  36. 36.

    Laurance, W. F. et al. Averting biodiversity collapse in tropical forest protected areas. Nature 00, 1–5. https://doi.org/10.1038/nature11318 (2012).

    CAS  Article  Google Scholar 

  37. 37.

    Opdam, P. Exploring the role of science in sustainable landscape management: an introduction to the special issue. Sustainability 10, 1–6. https://doi.org/10.3390/su10020331 (2018).

    Article  Google Scholar 

  38. 38.

    Field, D. R. Symbiotic relationships between national parks and neighboring social-biological regions in National Parks and rural development. In Practice, Policy in the United States (eds Machlis, G. E. & Field, D. R.) 211–218 (Island Press, Washington, DC, 2000).

    Google Scholar 

  39. 39.

    IUCN. Protected area categories. Category II: National Park. https://www.iucn.org/theme/protected-areas/about/protected-areas-categories/category-ii-national-park (2017).

  40. 40.

    Alamgir, M. et al. High-risk infrastructure projects pose imminent threats to forests in Indonesian Borneo. Sci. Rep. https://doi.org/10.1038/s41598-018-36594-8 (2019).

    Article  PubMed  PubMed Central  Google Scholar 

  41. 41.

    Sloan, S. et al. Transnational conservation and infrastructure development in the heart of Borneo. PLoS ONE 14(9), e0221947. https://doi.org/10.1371/journal.pone.0221947 (2019).

    CAS  Article  PubMed  PubMed Central  Google Scholar 

  42. 42.

    Sloan, S., Alamgir, M., Campbell, M. J., Setyawati, T. & Laurance, W. F. Development corridors and remnant-forest conservation in Sumatra Indonesia. Trop. Conserv. Sci. 12, 1–9. https://doi.org/10.1177/1940082919889509 (2019).

    Article  Google Scholar 

  43. 43.

    Healey, R. M. et al. Road mortality threatens endemic species in a national park in Sulawesi Indonesia. Glob. Ecol. Conserv. 24, e01281. https://doi.org/10.1016/j.gecco.2020.e01281 (2020).

    Article  Google Scholar 

  44. 44.

    Du, W., Penabaz-Wiley, S. M., Njeru, A. M. & Kinoshita, I. Models and approaches for integrating protected areas with their surroundings: a review of the literature. Sustainability 7, 8151–8177. https://doi.org/10.3390/su7078151 (2015).

    Article  Google Scholar 

  45. 45.

    Verma, M. et al. Severe human pressures in the Sundaland biodiversity hotspot. Conserv. Sci. Pract. 2(e169), 2020. https://doi.org/10.1111/csp2.169 (2020).

    Article  Google Scholar 

  46. 46.

    DeFries, R., Hansen, A., Newton, A. C. & Hansen, M. C. Increasing isolation of protected areas in tropical forests over the past twenty years. Ecol. Appl. 15(1), 19–26 (2005).

    Article  Google Scholar 

  47. 47.

    Brun, C. et al. Analysis of deforestation and protected area effectiveness in Indonesia: a comparison of Bayesian spatial models. Glob. Environ. Change 31, 285–295. https://doi.org/10.1016/j.gloenvcha.2015.02.004 (2015).

    Article  Google Scholar 

  48. 48.

    Mariati, S., Kusnoputranto, H., Supriatna, J. & Koestoer, R. H. Habitat Loss of Sumatran elephants (Elephas maximus sumatranus) in Tesso Nilo Forest, Riau, Indonesia. Aust. J. Basic Appl. Sci. 8(2), 248–255 (2014).

    Google Scholar 

  49. 49.

    Busch, J. & Ferretti-Gallon, K. What drives deforestation and what stops it? A meta-analysis. Rev. Environ. Econ. Policy 11(1), 3–23. https://doi.org/10.1093/reep/rew013 (2017).

    Article  Google Scholar 

  50. 50.

    Tacconi, L., Rodriguesa, R. J. & Maryudi, A. Law enforcement and deforestation: lessons for Indonesia from Brazil. For. Policy Econ. 108, 101943. https://doi.org/10.1016/j.forpol.2019.05.029 (2019).

    Article  Google Scholar 

  51. 51.

    Bruner, A., Gullison, G., Rice, R. E., da Fonseca, R. E. & Gustavo, A. B. Effectiveness of parks in protecting tropical biodiversity. Science 291, 125–128. https://doi.org/10.1126/science.291.5501.125 (2001).

    ADS  CAS  Article  PubMed  Google Scholar 

  52. 52.

    Adams, V. M., Iacona, G. D. & Possingham, H. P. Weighing the benefits of expanding protected areas versus managing existing ones. Nat. Sustain. https://doi.org/10.1038/s41893-019-0275-5 (2019).

    Article  Google Scholar 

  53. 53.

    Bickford, D. et al. In Indonesia’s protected areas need more protection: suggestions from island examples in biodiversity and human livelihoods in protected areas: case studies from the Malay Archipelago (eds Sodhi, N. S. et al.) 53–77 (Cambridge University Press, Cambridge, 2008).

    Google Scholar 

  54. 54.

    Baier, M. The Kayan Mentarang National Park: Indonesia’s new national park in North Central Borneo bordering Northern Sarawak and Sabah. Borneo Res. Bull. 40, 297 (2009).

    Google Scholar 

  55. 55.

    Anau, N., Hakim, A., Lekson, A. S. & Setyowati, E. Local wisdom practices of Dayak indigenous people in the management of Tana’ Ulen in the Kayan Mentarang National Park of Malinau Regency, North Kalimantan Province Indonesia. RJOAS 7(91), 156–167. https://doi.org/10.18551/rjoas.2019-07.16 (2019).

    Article  Google Scholar 

  56. 56.

    Susanti, R. & Zuhud, E. A. M. Traditional ecological knowledge and biodiversity conservation: the medicinal plants of the Dayak Krayan people in Kayan Mentarang National Park Indonesia. Biodiversitas 20(9), 2764–2779. https://doi.org/10.13057/biodiv/d200943 (2019).

    Article  Google Scholar 

  57. 57.

    Blankespoor, B., Dasgupta, S. & Wheeler, D. Protected areas and deforestation: new results from high-resolution panel data. Nat. Resour. Forum 41, 55–68. https://doi.org/10.1111/1477-8947.12118 (2017).

    Article  Google Scholar 

  58. 58.

    Sanderson, E. W., Walston, J. & Robinson, J. G. From bottleneck to breakthrough: urbanization and the future of biodiversity conservation. Bioscience 20, 1–15 (2018).

    Google Scholar 

  59. 59.

    Immanuel, G. et al. Indonesia. Pathways to sustainable land-use and food systems. FABLE Report (2019).

  60. 60.

    Allan, J. R. et al. Recent increases in human pressure and forest loss threaten many natural world heritage sites. Biol. Conserv. 206, 47–55. https://doi.org/10.1016/j.biocon.2016.12.011 (2017).

    Article  Google Scholar 

  61. 61.

    Damayanti, E.K. Legality of National Parks and Involvement of Local People: Case Studies in Java, Indonesia and Kerala, India. Thesis. Ph.D. in Agricultural Science. (University of Tsukuba, Japan, 2008).

  62. 62.

    Smiet, A. C. Forest ecology on Java: human impact and vegetation of montane forest. J. Trop. Ecol. 8, 129–152 (1992).

    Article  Google Scholar 

  63. 63.

    Wijaya, I. K. M. The semiotics of banyan trees spaces in Denpasar. Bali. LivaS Int. J. Livable 4(2), 48–59. https://doi.org/10.25105/livas.v4i2.5564 (2019).

    Article  Google Scholar 

  64. 64.

    Wijaya, M. H. & Sutrisni, K. How can the existence of customary laws protect the water preservation in the Cau Belayu (Tabanan) traditional village?. Yustisia 7(3), 600–613. https://doi.org/10.20961/yustisia.v7i3.21560 (2018).

    Article  Google Scholar 

  65. 65.

    Swandi, I. W. Kearifan lokal Bali untuk pelestarian alam: kajian wacana kartun-kartun majalah “Bog-Bog”. Jurnal Kajian Bali 7(2), 229–248. https://doi.org/10.24843/JKB.2017.v07.i02.p12 (2017).

    Article  Google Scholar 

  66. 66.

    Sobirin, S. Pranata Mangsa dan budaya kearifan lingkungan. Jurnal Budaya Nusantara 2(1), 250–264. https://doi.org/10.36456/b.nusantara.vol2.no1.a1719 (2018).

    Article  Google Scholar 

  67. 67.

    Apriando, T. Brubuh, kearifan masyarakat Jawa menjaga hutan. Mongabay. https://www.mongabay.co.id/2015/02/12/brubuh-kearifan-masyarakat-jawa-menjaga-hutan/ (2015).

  68. 68.

    Sulfiantono, A., Hermawan, M. T. T. & Maluyi, A. Comparison of Effectiveness of the management of conservation areas of China and Indonesia. Int. J. Sci. 11, 73–82 (2013).

    Google Scholar 

  69. 69.

    Supriatna, J. Berwisata di Taman Nasional (Yayasan Obor, Jakarta, 2014).

    Google Scholar 

  70. 70.

    Venter, O. et al. Global terrestrial human footprint maps for 1993 and 2009. Sci. Data 3, 160067. https://doi.org/10.1038/sdata.2016.67 (2016).

    Article  PubMed  PubMed Central  Google Scholar 

  71. 71.

    Willmott, C. J. & Matsuura, K. Advantages of the mean absolute error (MAE) over the root mean square error (RMSE) in assessing average model performance. Clim. Res. 30, 79. https://doi.org/10.3354/CR030079 (2005).

    Article  Google Scholar 

  72. 72.

    Viera, A. J. & Garrett, J. M. Understanding interobserver agreement: the kappa statistic. Fam. Med. 37, 360–363 (2005).

    PubMed  Google Scholar 

  73. 73.

    R Development Core Team. R. A Language and environment for statistical computing (R Foundation for Statistical Computing, Vienna, Austria, 2014).

Download references

Acknowledgements

We acknowledge the University of Indonesia for financial support through the PITMA A research grant program, Grant ID NKB-0889/UN2.R3.1/HKP.05.00/2019. We thank Indonesian Ministry of Environment and Forestry and Ministry of Public Works for providing reference maps. We also thank the Research Center for Climate Change, University of Indonesia for administrative support of this study.

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A.A.D. and J.S.U. conceived the idea. A.A.D. and H.A.H.F. designed the project, collated the datasets and performed the analysis. A.A.D., C.M. and H.A.H.F. wrote the manuscript. J.S.U., C.M., S.M. and T.E.B.S. provided intellectual guidance at all stages. All authors reviewed the manuscript.

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Dwiyahreni, A.A., Fuad, H.A.H., Muhtar, S. et al. Changes in the human footprint in and around Indonesia’s terrestrial national parks between 2012 and 2017. Sci Rep 11, 4510 (2021). https://doi.org/10.1038/s41598-021-83586-2

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