1 Environmental Lecturer at the Medan Institute of Technology, Expert in the Field of Environmental Research and Development of North Sumatra Province
2D Biology Department of the Faculty of Mathematics and Natural Sciences, University of North Sumatra.
Abstract
Damage to coral reefs causes environmental damage and decreases in fish catches which have an impact on the welfare of coastal communities. One way to overcome the damage to coral reefs is by Marine Protected Areas (MPA). The Government of Indonesia through Law Number 32 of 2004 concerning Regional Government and Law Number 27 of 2007 concerning Management of Coastal Areas and Small Islands gives MPA authority to Regency / City Governments. However, through Law Number 23 of 2004 concerning Regional Government, conservation management authority is withdrawn from the Regency / City Government to the Provincial Government.
The study was conducted to obtain the influence of the transfer of authority on MPA management in North Sumatra. The study was carried out at 4 (four) MPAs in North Sumatra Province in 2018 and private MPAs managed by the community. Methods of data collection using observation, questionnaire and in-depth interviews.
The results of the study indicate that the Government of North Sumatra Province is not ready to accept the delegation of authority for conservation management from the districts / cities in North Sumatra. The prescribed MPA (1) MPA Sawo-Lahewa in North Nias Regency in 2017 and (2) Limited Protection Areas of Terubuk Fish in Labuhan Batu in 2016 until 2018 have not been managed. Likewise 3 MPAs in Central Tapanuli, South Nias and Serdang Bedagai have not been managed and are still in the reserve stage. The proposed MPA pending from Madina Regency, Batubara Regency and Sibolga City as well as the proposed limited Protected Area for Batak Fish, Shellfish, Turtle, Teripang from the regency / city have not yet been continued. Likewise, data collection, guidance, and community-managed private MPA assistance have not been conducted.
Keywords: 1. Conservation 2. Marine Protected Areas 3. Limited Protection Areas 4. North Sumatra
Preliminary
Indonesia has 25,000 km2 of coral reefs (10%) of 284,300 km2 of the world's coral reefs with high diversity (569 species of 82 genera, 15 tribes of a total of 845 coral species in the world, 90% of families of Fungiidae in Indonesian waters, 41 species of 43 species of coral world and 94 types of 124 types of Acropora world). This coral reef has been damaged. Data from the Oceanographic Research Center of the Indonesian Institute of Sciences (LIPI) in 2017 in 108 locations and 1,064 monitoring stations in all Indonesian waters, causing poor coral reef conditions of 35.15%, sufficient conditions of 35.06%, good condition 23.40%, and very good conditions 6.39% (Anonymous, 2017). As a result of the damage to coral reefs this causes a decrease in fish biomass, a decrease in fish catch, a decrease in income and welfare of fishermen and indirectly a decrease in national foreign exchange income and welfare of the people (Ban et al., 2015). The rate of damage to coral reefs from year to year is increasing, therefore, if the rate of damage to coral reefs is not overcome, then fish catches will run out in 2048 (Machumu et all, 2013).
Indonesia has 25,000 km2 of coral reefs (10%) of 284,300 km2 of the world's coral reefs with high diversity (569 species of 82 genera, 15 tribes of a total of 845 coral species in the world, 90% of families of Fungiidae in Indonesian waters, 41 species of 43 species of coral world and 94 types of 124 types of Acropora world). This coral reef has been damaged. Data from the Oceanographic Research Center of the Indonesian Institute of Sciences (LIPI) in 2017 in 108 locations and 1,064 monitoring stations in all Indonesian waters, causing poor coral reef conditions of 35.15%, sufficient conditions of 35.06%, good condition 23.40%, and very good conditions 6.39% (Anonymous, 2017). As a result of the damage to coral reefs this causes a decrease in fish biomass, a decrease in fish catch, a decrease in income and welfare of fishermen and indirectly a decrease in national foreign exchange income and welfare of the people (Ban et al., 2015). The rate of damage to coral reefs from year to year is increasing, therefore, if the rate of damage to coral reefs is not overcome, then fish catches will run out in 2048 (Machumu et all, 2013).
Damage to
coral reefs can be overcome by forming Marine Protected Areas (MPA) and
increasing ownership authority over marine resources (Ban et all, 2015). The
formation and management of MPA will be successful, if stakeholders have the
view that MPA benefits them. Therefore MPA management is based on agreements,
legislation, conservation education and provision of alternative income eyes.
Vice versa, the formation of the MPA will fail if stakeholders have a negative
image of conservation (Machumu et all, 2013).
Marine Protection Area
Marine Protection Area (MPA) based on Government Regulation Number 60 of 2007 concerning Fish Resource Conservation, as a protected water area, managed by a zoning system, to realize sustainable management of fish resources and their environment. The definition of fish refers to Law Number 45 of 2009 concerning Fisheries, is any type of organism that is whole or part of its life cycle in the aquatic environment.
According to the UN Union (International Union Conservation Nature-IUCN), the MPA is a clear geographical space, recognized and managed effectively, to refer to the sustainability of natural resources including cultural values in it (Briggs et all, 2018). Agbeja (2017) details protection at sea, for fauna, flora, history and cultural enhancement. MPA as an effective management model for the sustainability of marine resources (Setyawati, 2014).
The results of the MPA study show that fish marked in MPA move in and out of the MPA, so that fishermen can catch abundant fish outside the MPA (Clements et all, 2012). MPA can stop fishing and modify fishing models in other parts of the MPA (Machumu et all, 2013). Likewise, the determination of core zoning (a closed area without fish harvesting throughout the year), has been shown to be effective in increasing the amount of fish biomass (Ban et al., 2015), increasing biodiversity (Ban et all, 2015), (Charles et all, 2016), (Waltter , 2017), (Islam et all, 20127) therefore there has been an increase in the number and extent of MPAs in the last three decades (Ban et al., 2015).
The derivative impact of MPA will restore fish resources (Pascall, 2011), (Charles et all, 2016), increasing economics (Pascal, 2011), (Charles et all, 2016), (Ban et all, 2015), (Machumu et all, 2013), (Waltter, 2017), improving alternative livelihoods for local communities (Machumu et all, 2013), increasing social, cultural relations, developing ecotourism services (Pascal, 2011) and models to address habitat degradation and declining fish stocks (Machumu et all, 2013). On a macro scale MPA is useful for reducing the adverse effects of natural resource destruction (Machum et all, 2013), preserving the environment both globally, regionally, nationally and locally (Heinonen, 2013).
MPA also functions as the implementation of the Integrated Coastal Management (ICM) program for planning, management, land use, permit systems and marine zoning, natural resource conflict resolution (Briggs et all, 2018), sea and coastal management, increased productivity and fish stocks and ecosystem recovery (Islam et all, 2017), increasing resilience to over-exploitation and uncertainty, and preventing the collapse of aquatic resources (Sumaila et all, 2012). Because in its management, the government must involve the community (Waltter, 2017), by designing the active participation of coastal communities, fishermen, and other marine users in designing and implementing MPAs (Charles et all, 2016).
MPA area
Globally there are approximately 5,000 MPA, an area of 2.85 million km2 or 0.8% of 361 million km2 of the world's sea, and 2.0% of 147 million km2 of territorial sea (Agbeja, 2017). The 2015 global MPA was distributed in Chile (25.3%), Britain (21.9%), United States (15.5%), New Zealand (15.2%), Kiribati (11.9%) and Australia ( 1.9%). By the end of 2015, the Palau Government had radically set 80% of its EEZ into an MPA (Wilheml et all, 2014).
Global MPA data is comparable to the global ocean area in 2008 of 0.9% (Wilhelm et al., 2014), in 2011 MPA was 1.3% of the sea area and 3.2% of the Ecological Economic Zone (Leenhardt et all, 2014), or MPA of 1.6% (Jentoft et all, 2012). The MPA area is still small when compared to the area of land conservation area covering 11.6% of the 17.3 million km2 of the world's land (Machumu et all, 2013). Most MPAs are near shore and shallow water (Wilheml et al., 2014). The IUCN MPA target is based on the 2010 Convention on Biological Diversity of> 10% in 2020. But the MPA expansion is very slow, only 1.3% of the sea area and 3.2% in the EEZ, so based on the Sustainable Development Goal in 2015 targeting the MPA is still > 10% in 2020. The MPA target set at the 2016 IUCN World Conservation Congress is 30% in 2030 (Briggs et all, 2018). Nationally, Indonesia's sea area is 5.8 million km2, which consists of 2.95 million km2 of archipelago waters, 0.30 million km2 of territorial sea, and 2.55 million km2 of Exclusive Economic Zone and 17,504 small islands (Setyawati, 2014 ) MPA Indonesia in 2012 was 15.7 million ha (0.27%) of Indonesia's sea area. The Indonesian government sets the MPA area for 2020 to reach 20 million ha (0.34%). As a comparison, the percentage of Finnish MPA area is 46,000 km² (10%) of the national sea area (Heinonen, 2013).
North Sumatra Province has 17 coastal districts / cities from 33 city districts, 8 regencies / cities located on the East Coast and 9 regencies / cities located on the West Coast of North Sumatra. Demographically, coastal residents inhabit 85 coastal sub-districts with 539 coastal villages. The area of North Sumatra is 72,981 km2, consisting of 32,384.62 km2 of land and 40. 596.38 km2 of sea (55.63%), with a coastline of 1,299.5 km and 192 small islands (DKP-SU, 2016). The sea area has been designated as MPA North Nias Sawo-Lahewa Aquatic Park covering an area of 29,230.85 ha (0.72%) with the Decree of the Minister of Marine and Fisheries of the Republic of Indonesia Number 54 / KEPMEN-KP / 2017 dated December 22, 2017. Provincial Government Sumatra has reserved 3 (three) MPAs covering 138,483.40 Ha (3.41%) based on the Decree of the Governor of North Sumatra Number 188.44 / 629 / KPTS / 2017 dated November 21, 2017.
Transfer of Conservation Authority
Law No.23 of 2014 concerning Regional Government Article 27 and attachment to the letter "y" division of affairs in the field of maritime affairs and fisheries, revoke the authority of fisheries and marine management of the Regency / City Government and transfer them to the Provincial Government. The authority of the Provincial Government to manage natural resources in the sea includes exploration, exploitation, conservation, and management of marine assets up to 12 mills. Thus, since 2014 the Regency / City Government has no right to manage or foster MPA.
This research was conducted to get the influence of the transfer of authority on MPA management in North Sumatra, where before 2004 MPA management was carried out by the Regency / City Government and there was no MPA managed by the Provincial Government. The study was conducted at 4 (four) MPAs in Serdang Bedagai District, Tapanuli Tengah District, North Nias Regency, South Nias Regency and private MPA managed by the community. Methods of collecting data by observation, questionnaire and in-depth interviews. The results of the study are presented descriptively.
Issues of Transfer of Authority
Based on the research data, the transfer of MPA management authority from the Regency / City Government to the government of North Sumatra Province, caused the burden on the Provincial Government to increase. This transfer of authority raises issues of marine conservation management in North Sumatra Province, including:
1. There are no MPA institutions and management
The Government of Nias Regency since 2007 has established an MPA covering an area of 29,000.00 ha, for the protection of sustainable fisheries, coral reef and mangrove marine tourism. In 2008, the division of Nias Regency became Nias Regency and North Nias Regency. Most of the MPA areas that have been established are in North Nias District, so there is no longer MPA management. When the MPA management was transferred to the Province, the Government of North Sumatra Province reserved an MPA of 29,230.85 ha. Based on the Decree of the Minister of Marine Affairs and Fisheries of the Republic of Indonesia Number 54 / KEPMEN-KP / 2017 dated December 22, 2017 stipulates MPA Sawo-Lahewa, North Nias as a Aquatic Tourism Park.
The MPA function to protect, conserve, utilize the potential of fisheries and important ecosystems such as coral reefs, mangroves and seagrasses as well as important species such as turtles, dolphins, marta rays, napoleon, lola, dugong, clams, sharks, whales, sea bamboo, bahar roots , goat head, triton trumpet, sea cucumber, and hollow nautilus. MPA serves to support the development of water tourism. This MPA is managed with 5 zones, in the form of MPA-1 with an area of 2,485.34 ha, MPA-2 with an area of 12,562.50 ha, MPA-3 with an area of 7,371.09 ha, MPA-4 with an area of 3,948.80 ha and MPA -5 with an area of 2,863 12 ha.
In the decree on the decision of the MPA Sawo-Lahewa, it was stated that the management was handed over to the Government of North Sumatra Province. Although the Central Government has established it as the Sawo-Lahewa MPA since 2017, the Provincial Government has not yet established institutional, management, and budgeting activities. Thus, since the 2007 MPA determination, since 2008 until 2018, there has been no MPA management at all. The MPA area is like a no man's land, no conservation functions are carried out. Such conditions have caused a decline in coral reef cover, increased degradation of the marine environment and a decline in the economic and social community around the MPA.
2. There is
no MPA determination aru
The Central Tapanuli Regency Government since 2007 has managed MPA covering an area of 81,243.00 ha, the South Nias Regency Government has managed the MPA since 2008 covering an area of 56,000.00 ha and the Serdang Bedagai District Government has managed the MPA since 2008 covering 1,240.35 ha. Management has been stalled since 2014 because the conservation authority was taken over by the province. Administrative activities carried out by the North Sumatra Provincial Government in the form of MPA reserves covering 138,483.40 ha with the Decree of the Governor of North Sumatra Number 188.44 / 629 / KPTS / 2017 dated November 21, 2017. The North Sumatra Provincial Government, which has accepted the responsibility of managing MPA since 2014, has not been able to manage the MPA because of its absence. Therefore, there has been no management of MPA in Central Tapanuli, South Nias and Serdang Bedagai Districts since 2014. With conditions without management, open access areas, it can be ascertained that there has been a decline in coral reef cover, environmental damage and a decline in the surrounding economy and social MPA.
3. Abandoned MPA proposal
The transfer of MPA management authority from the District Government to the Provincial Government based on Law Number 23 of 2014, has led to the abandonment of the proposed establishment of the MPA in various districts / cities in North Sumatra Province. The results of research in the field, Batubara Regency, Sibolga City and Mandailing Natal District have prepared a new MPA proposal document. With this transfer of authority, the Regency / City Government does not have the authority to propose an MPA. Therefore, the North Sumatra Provincial Government should follow up on preparing MPA proposal documents. But until 2018, the district / city MPA proposal file was not followed up by the Provincial Government.
4. Abandoned the proposed Limited Protection Area
The Government of North Sumatra Province has a Limited Protection Area for Terubuk Fish (Tenualosa ilisha), in Labuhan Batu based on Decree of Kepmenkp Number 34 / KEPMEN-KP / 2016 dated August 2, 2016. Although it has been established since 2016, there is no institution yet, until 2018 management, funding and conservation activities in the field. In addition, the Regency / City Government has also compiled a proposal for a limited protection area for Batak and Shellfish for Dara in Asahan District, Turtle and Oyster Protection in Central Tapanuli Regency and others. Because the authority of the conservation proposal has been transferred from the Regency / City Government to the Provincial Government, the North Sumatra Provincial Government should continue to propose a limited area of fish protection. The results of the study show that the proposed limited protected area has not been continued by the North Sumatra Provincial Government.
5. There is no private MPA coaching
The shift in the authority of conservation management from the Regency / City Government to the Provincial Government has led to the development of private conservation institutions managed by small-scale communities such as "animals lost their mothers". The district / city government does not want to take care of it because it is not a main task and function anymore, while the Provincial Government does not have data, relations, development budgets and distance between provincial capitals and conservation locations in remote rural areas. Because of the lack of guidance and funding assistance, the private MPA has stagnated management. The conservation management community group hopes for guidance, placement of extension agents and funding assistance.
Conclusion
1. The Government of North Sumatra Province through the Department of Marine and Fisheries is not yet ready to accept the delegation of authority in the field of conservation from the Regency / City Government in accordance with Law Number 23 of 2014 concerning Regional Government. The transfer of authority does not make MPA management better, what happens is that the MPA is increasingly neglected.
2. The negative impact of the transfer of conservation authority from the Regency / City Government to North Sumatra Province, in the form of:
(1). The Government of North Sumatra Province is obliged to manage MPAs that have been determined by the Central Government: (1) North Nias MPA Sawo-Lahewa in 2017 (established 2007) and (2) Terubuk Fish Restricted Areas in 2016 in Labuhan Batu Regency. However, until 2018 it has not been managed, there are no institutions, management management models, budgets and conservation implementation in these conservation areas.
(2). The North
Sumatra Provincial Government has only reserved 3 new MPAs in 2017 but because
the Central Government has not yet established the Central Tapanuli MPA
(established 2007), South Nias (2008) and Serdang Bedagai (2008) cannot be
managed by the Government of North Sumatra Province.
(3) The Government of North Sumatra Province has not yet followed up on the proposed MPA and the proposed Limited Protection Area which was delayed due to the transfer of management authority from the Regency / City Government to the Provincial Government.
(3) The Government of North Sumatra Province has not yet followed up on the proposed MPA and the proposed Limited Protection Area which was delayed due to the transfer of management authority from the Regency / City Government to the Provincial Government.
(4). The North Sumatra
Provincial Government has not yet received a private MPA managed by the
community, as has not been done coaching, assistance and funding assistance.
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Pengaruh Pengalihan Kewenangan Konservasi Terhadap Marine Protected Areas
di Provinsi Sumatera Utara
Hamzah Lubis1 dan Mayang Sari Yeanny2
1Dosen
Lingkungan Institut Teknologi Medan, Tenaga Ahli Bidang Lingkungan Badan
Penelitian dan Pengembangan Provinsi Sumatera Utara
2Departemen
Biologi Fakultas MIPA Universitas Sumatera Utara
Abstrak
Kerusakan
terumbu karang mengakibatkan kerusakan lingkungan dan penurunan tangkapan ikan
yang berdampak bagi kesejahteraan masyarakat pesisir. Salahsatu cara untuk mengatasi kerusakan terumbu
karang dengan Marine Protected Areas (MPA). Pemerintah Indonesia melalui
Undang-undang Nomor 32 tahun 2004 Tentang Pemerintah Daerah dan Undang-Undang
Nomor 27 tahun 2007 Tentang Pengelolaan Wilayah Pesisir dan Pulau-Pulau Kecil
memberi kewenangan MPA kepada Pemerintah Kabupaten/Kota. Namun melalui Undang-Undang
Nomor 23 Tahun 2004 tentang Pemerintah Daerah, kewenangan pengelolaan
konservasi ditarik dari Pemerintah
Kabupaten/Kota ke Pemerintah Provinsi.
Penelitian
dilakukan untuk mendapatkan pengaruh pengalihan kewenangan pada pengelolaan MPA
di Sumatera Utara. Penelitian dilakukan pada 4 (empat) MPA di Provinsi Sumatera
Utara tahun 2018 dan MPA swasta yang dikelola masyarakat.Metoda pengambilan
data dengan metoda observasi, kuisoner dan wawancara mendalam.
Hasil
penelitian menunjukkan bahwa Pemerintah Provinsi Sumatera Utara belum siap
menerima pelimpahan kewenangan
pengelolaan konservasi dari kabupaten/kota di Sumatera Utara. MPA yang
telah ditetapkan (1) MPA Sawo-Lahewa di
Kabupaten Nias Utara tahun 2017 dan (2) Kawasan Perlindungan Terbatas Ikan
Terubuk di Labuhan Batu tahun 2016 sampai tahun 2018 belum dikelola. Demikian juga 3 MPA di Tapanuli
Tengah, Nias Selatan dan Serdang Bedagai belum dikelola dan masih tahap
pencadangan. Usulan MPA yang tertunda dari Kabupaten Madina, Kabupaten Batubara
dan Kota Sibolga serta usulan Kawasan Perlindungan Terbatas terunda untuk Ikan
Batak, Kerang Anak Dara, Penyu, Teripang dari kabupaten/kota belum juga dilanjutkan.
Demikian juga pendataan, pembinaan, pendampingan MPA swasta yang dikelola masyarakat belum
dilakukan.
Kata Kunci: 1.Konservasi 2. Marine Protected
Areas 3. Kawasan Perlindungan Terbatas 4.Sumatera Utara
Pendahuluan
Indonesia memiliki 25.000 km2 terumu karang
(10%) dari 284.300 km2
terumbu karang dunia dengan keanekaragam tinggi (569 jenis dari 82 marga,15
suku dari total 845 jenis karang di dunia, 90% famili Fungiidae di perairan
Indonesia, 41 jenis dari 43 jenis karang dunia dan 94 jenis dari 124 jenis Acropora dunia). Terumbu karang ini telah mengalami kerusakan. Data
Pusat Penelitian Oseanografi Lembaga Ilmu Pengetahuan Indonesia (LIPI) tahun
2017 di 108 lokasi dan 1.064 stasiun pantau di seluruh perairan Indonesia, menyebabkan
tutupan terumbu karang kondisi jelek 35,15%, kondisi cukup 35,06%, kondisi baik
23,40%, dan kondisi sangat baiki 6,39% (Anonim, 2017).
Akibat kerusakan terumbu karang ini
menyebabkan penurunan biomassa ikan, penurunan tangkapan ikan, penurunan pendapatan dan
kesejahteraan nelayan serta secara tidak
langsung penurunan penerimaan devisa negara dan kesejahateraan rakyat (Ban et
all,2015). Laju kerusakan terumbu karang
dari tahun ke tahun semakin meningkat, oleh karena itu, jika laju kerusakan
terumbu karang tidak diatasi, maka tangkapan ikan akan habis tahun 2048
(Machumu et all,2013).
Kerusakan terumbu karang dapat diatasi
dengan membentuk Marine Protected Areas (MPA) dan
meningkatkan kewenangan kepemilikan atas sumberdaya laut (Ban et all,2015). Pembentukan dan pengelolaan MPA akan berhasil, jika para pemangku kepentingan
memiliki pandangan bahwa MPA menguntungkan mereka. Oleh karena itu pengelolaan MPA berdasarkan
kesepakatan, peraturan perundang-undangan, pendidikan konservasi dan penyediaan
mata penghasilan alternatif. Demikian juga sebaliknya, pembentukan MPA akan
gagal jika pemangku kepentingan memiliki
citra negatif terhadap konservasi
(Machumu et all,2013).
Marine
Protection Area
Marine
Protection Area (MPA) berdasarkan Peraturan Pemerintah Nomor 60 tahun 2007 Tentang
Konservasi Sumberdaya Ikan, sebagai kawasan perairan yang dilindungi, dikelola
dengan sistem zonasi, untuk mewujudkan pengelolaan sumber daya ikan dan
lingkungannya secara berkelanjutan. Pengertian ikan merujuk pada Undang-Undang
Nomor 45 Tahun 2009 Tentang Perikanan, adalah segala jenis organisme yang
seluruh atau sebagian dari siklus hidupnya berada di dalam lingkungan perairan.
MPA menurut lembaga konservasi PBB (International
Union Conservation Nature-IUCN) adalah ruang
geografis yang jelas, diakui dan
dikelola secara efektif, untuk mewujutkan
keberlanjutan sumberdaya alam termasuk nilai-nilai budaya
didalamnya (Briggs et all,2018). Agbeja (2017)
mendetilkan perlindungan di laut,
untuk fauna , flora, sejarah dan
peningkalan budaya. MPA sebagai model
pengelolaan efektif untuk keberlanjutan sumber daya laut (Setyawati,2014).
Hasil penelitian MPA menunjukkan bahwa
ikan yang ditandai di MPA bergerak
keluar-masuk MPA, sehingga nelayan dapat
menangkap ikan limpahan di luar MPA (Clements et all,2012). MPA dapat menghentikan penangkapan
ikan dan memodifikasi model penangkapan
ikan di bagian lain MPA (Machumu et all,2013). Demikian juga penetapan zonasi
inti (area tertutup tanpa pengambilan ikan sepanjang tahun), terbukti efektif
menaikkan jumlah biomassa ikan (Ban et all,2015), meningkatkan keanekaragaman
hayati (Ban et all,2015), (Charles et all,2016), (Waltter,2017), (Islam et
all,20127) oleh karena itu terjadi peningkatan jumlah dan luasan MPA dalam tiga dekade terakhir (Ban et all,2015).
Dampak turunannya MPA akan memulihkan
sumberdaya ikan (Pascall,2011), (Charles et all,2016), meningkatkan ekononomi (Pascal,2011), (Charles
et all, 2016), (Ban et all,2015), (Machumu et all,2013), (Waltter,2017), meningkatkan mata pencarian alternatif bagi
masyarakat lokal (Machumu et all,2013), meningkatnya kekerabatan sosial, budaya, berkembangnya jasa ekowisata (Pascal,2011)
dan model untuk mengatasi degradasi habitat dan menurunnya stok ikan (Machumu
et all,2013). Dalam skala makro MPA bermanfaat
untuk mengurangi dampak buruk dari perusakan sumberdaya alam (Machum et all,2013),
memelihara lingkungan hidup baik global, regional, nasional dan lokal (Heinonen,2013).
MPA juga berfungsi sebagai pelaksanaan program
Integrated Coastal Management (ICM)
untuk perencanaan, manajemen, penggunaan lahan, sistem izin dan zonasi laut,
resolusi konflik sumber daya alam (Briggs et all,2018), pengelolaan laut dan pesisir , peningkatan
produktivitas dan stok ikan dan
pemulihan ekosistem (Islam et all,2017), meningkatkan ketahanan terhadap
eksploitasi berlebihan dan ketidakpastian, serta mencegah kolapsnya sumber daya
perairan (Sumaila et all,2012). Oleh karena dalam pengelolaanya, pemerintah harus
melibatkan masyarakat (Waltter,2017), dengan merancang partisipasi aktif masyarakat
pesisir, nelayan, dan pengguna laut lainnya dalam merancang dan mengimplementasikan
MPA (Charles et all, 2016).
Luasan MPA
Secara global terdapat lebih kurang 5.000 MPA, seluas 2,85 juta km2 atau 0,8% dari 361 juta km2 laut
dunia, dan 2,0% dari 147 juta km2 laut teritorial (Agbeja,2017). MPA
global tahun 2015 terdistribusi di Chili (25,3%), Inggris (21,9%), Amerika
Serikat (15,5%), Selandia Baru (15,2%), Kiribati (11,9%) dan Australia
(1,9%). Akhir tahun 2015, Pemerintah Palau
secara radikal telah menetapkan 80% ZEE-nya menjadi MPA (Wilheml et
all,2014).
Data luasan MPA global berbanding dengan
luas laut global tahun 2008 seluas 0,9% (Wilheml et all,2014), tahun 2011 MPA seluas
1,3% wilayah laut dan 3,2% Zona Ekonomi
Eklsuif (Leenhardt et all, 2014), atau MPA seluas 1,6% (Jentoft et all,2012). Luasan MPA masih kecil
bila dibanding dengan luasan kawasan
konservasi daratan seluas 11,6% dari 17,3 juta km2 daratan dunia
(Machumu et all,2013). Sebagian besar MPA
berada dekat pantai dan perairan dangkal (Wilheml et all,2014).
Target luasan MPA IUCN berdasarkan Convention on Biological
Diversity tahun 2010 sebesar >10% tahun 2020. Namun perluasan MPA
sangat lambat hanya 1,3% wilayah laut dan 3,2%
di ZEE, maka berdasarkan Sustainable Development Goal tahun 2015 menargetkan kembali MPA tetap sebesar >10% pada tahun 2020.
Target yang MPA yang ditetapkan pada IUCN World Conservation Congress 2016
sebesar 30% pada tahun 2030 (Briggs et all, 2018).
Secara nasional, luas laut Indonesia 5,8 juta km2 , yang
terdiri perairan kepulauan 2,95 juta km2 , laut teritorial 0,30 juta
km2 , dan Zona Ekonomi
Eksklusif 2,55 juta km2 dan memiliki 17.504 pulau-pulau kecil (Setyawati,2014). MPA Indonesia pada tahun 2012 seluas 15,7
juta ha (0,27%) luas laut Indonesia. Pemerintah
Indonesia menetapkan luasan MPA tahun 2020 mencapai 20 juta ha (0,34%). Sebagai perbandingan prosentase
luasan MPA Finlandia 46.000 km² (10%) dari luas laut nasional (Heinonen,2013).
Provinsi Sumatera Utara memiliki 17
kabupaten/kota pesisir dari 33 kabupaten kota, 8 kabupaten/kota berada di
Pantai Timur dan 9 kabupaten/kota berada di Pantai Barat Sumatera Utara. Secara
demografi, penduduk pesisir mendiami 85 kecamatan pesisir dengan 539 desa
pesisir. Luas Sumatera Utara 72.981 km2, terdiri dari
daratan 32.384,62 km2 dan lautan
40. 596,38 km2 (55,63 %),
dengan panjang pantai 1.299,5 km dan
memiliki 192 pulau-pulau kecil
(DKP-SU,2016). Dari luas laut tersebut telah ditetapkan menjadi MPA Taman
Wisata Perairan Sawo-Lahewa Nias Utara
seluas 29.230,85 ha (0,72%) dengan Keputusan Menteri Kelautan dan
Perikanan Republik Indonesia Nomor 54/ KEPMEN-KP/2017 tertanggal 22 Desember 2017. Pemerintah Provinsi Sumatera telah
mencadangkan 3 (tiga) MPA seluas
138.483,40 Ha (3,41%) berdasarkan Keputusan Gubernur Sumatera Utara Nomor
188.44/629/KPTS/2017 tertanggal 21 November 2017.
Pengalihan
Kewenangan Konservasi
Undang Undang No.23 tahun 2014 tentang Pemerintah Daerah Pasal
27 dan lampiran huruf “y” pembagian
urusan bidang kelautan dan perikanan, mencabut kewenangan pengelolaan perikanan dan
kelautan Pemerintah Kabupaten/Kota dan mengalihkannya ke Pemerintahan Provinsi.
Kewenangan Pemerintah Provinsi untuk mengelola sumber daya alam di laut meliputi eksplorasi,
eksploitasi, konservasi, dan pengelolaan
kekayaan laut sampai dengan 12 mill. Dengan demikian, sejak tahun 2014
Pemerintah Kabupaten/kota tidak berhak lagi mengelola atau membina MPA.
Penelitian ini dilakukan untuk mendapatkan
pengaruh pengalihan kewenangan pada pengelolaan MPA di Sumatera Utara, dimana sebelum
tahun 2004 pengelolaan MPA dilakukan oleh Pemerintah Kabupaten/Kota serta tidak
ada MPA yang dikelolola oleh Pemerintah Provinsi. Penelitian dilakukan pada 4
(empat) MPA di Kabupaten Serdang Bedagai, Kabupaten Tapanuli Tengah, Kabupaten
Nias Utara, Kabupaten Nias Selatan dan MPA swasta yang dikelola masyarakat.
Metoda pengumpulan data dengan observasi, kuisoner dan wawancara mendalam. Hasil
penelitian disajikan secara deskriptif.
Permasalaham
Pengalihan Kewenangan
Berdasarkan data hasil
penelitian, pengalihan kewenangan pengelolaan MPA dari Pemerintah
Kabupaten/Kota ke pemerintah Provinsi Sumatera Utara, menyebabkan beban
Pemerintah Provinsi bertambah. Pengalihan kewenangan ini menimbulkan
permasalahan pengelolaan konservasi laut di Provinsi Sumatera Utara, diantaranya
adalah:
1.
Belum ada kelembagaan
dan manajemen MPA
Pemerintah Kabupaten Nias sejak tahun
2007 telah menetapkan MPA seluas
29.000,00 ha, untuk perlindungan perikanan berkelanjutan, wisata bahari terumbu
karang dan mangrove. Pada tahun 2008, terjadi pemekaran Kabupaten Nias menjadi
Kabupaten Nias dan Kabupaten Nias Utara. Sebagian besar area MPA yang telah
ditetapkan berada di Kabupaten Nias Utara, sehingga tidak lagi ada pengelolaan
MPA. Ketika pengelolaan MPA dialihkan ke
Provinsi, Pemerintah Provinsi Sumatera Utara mencadangkan MPA seluas 29.230,85 ha. Berdasarkan Keputusan Menteri Kelautan dan
Perikanan Republik Indonesia Nomor 54/KEPMEN-KP/2017 tertanggal 22 Desember 2017 menetapkan MPA Sawo-Lahewa, Nias Utara sebagai
Taman Wisata Perairan.
Fungsi MPA untuk melindungi,
melestarikan, memanfaatkan potensi perikanan dan ekosistem penting seperti terumbu karang, mangrove dan
lamun serta spesies penting seperti penyu, lumba-lumba, pari marta, napoleon,
lola, dugong, kima, hiu, paus, bambu laut, akar bahar, kepala kambing, triton
terompet, teripang, dan nautilus berongga. MPA berfungsi untuk mendukung upaya pengembangan wisata
perairan. MPA ini dikelola dengan 5
zonasi, berupa MPA-1 seluas 2.485,34 ha, MPA -2 seluas 12.562,50 ha, MPA -3 seluas
7.371,09 ha, MPA -4 seluas 3.948,80 ha dan
MPA -5 seluas 2.863,12 ha.
Dalam surat keputusan penetapan MPA
Sawo-Lahewa, disebutkan bahwa pengelolaannya diserahkan kepada Pemerintah
Provinsi Sumatera Utara. Kendati Pemerintah Pusat telah menetapkan sebagai MPA Sawo-Lahewa
sejak tahun 2017, namun Pemerintah Provinsi belum menetapkan kelembagaan,
manajemen pengelolaan, dan penganggaran kegiatan. Dengan demikian, sejak penetapan MPA tahun 2007, maka sejak tahun
2008 sampai tahun 2018, tidak ada pengelolaan MPA sama sekali. Arean MPA
seperti wilayah tidak bertuan, tidak ada fungsi-fungsi konservasi yang
dilakukan. Kondisi seperti ini, menyebabkan penurunan tutupan terumbu karang,
meningkatnya degradasi lingkungan laut dan penurunan ekonomi dan sosial
masyarakat sekitar MPA.
2. Belum ada penetapan MPA aru
Pemerintah Kabupaten Tapanuli Tengah
sejak tahun 2007 telah mengelola MPA
seluas 81.243,00 ha,
Pemerintah Kabupaten Nias Selatan
telah mengelola MPA sejak tahun 2008 seluas 56.000,00 ha dan Pemerintah
Kabupaten Serdang Bedagai telah mengelola MPA sejak tahun 2008 seluas1.240,35
ha. Pengelolaan terhenti sejak tahun 2014 karena kewenangan konservasi diambil
alih provinsi. Kegiatan adiministratif yang dilakukan Pemerintah Provinsi
Sumatera Utara berupa pencadangan MPA seluas 138.483,40 ha dengan Keputusan
Gubernur Sumatera Utara Nomor 188.44/629/KPTS/2017 tertanggal 21 November 2017.
Pemerintah Provinsi Sumatera Utara yang menerima
tanggungjawab pengelolaan MPA sejak tahun 2014, belum dapat mengelola MPA
tersebut karena belum adan penetapannya. Oleh karena itu, tidak ada pengelolaan
MPA di Kabupaten Tapanuli Tengah, Nias
Selatan dan Serdang Bedagai sejak tahun 2014. Dengan kondisi tanpa pengelolaan,
wilayah open akses, maka dapat dipastikan telah terjadi penurunan tutupan
terumbu karang, kerusakan lingkungan dan penurunan ekonomi dan soial masyarakat
sekitar MPA.
3.
Terbengkalai usulan
MPA
Pengalihan
kewenangan pengelolaan MPA dari Pemerintah Kabupaten ke Pemerintah Provinsi
berdasarkan Undang-Undang Nomor 23 tahun 2014, menyebabkan terbengkalainya
usulan pendirian MPA pada berbagai kabupaten/kota di Provinsi Sumatera Utara. Hasil
penelitian di lapangan, Kabupaten Batubara, Kota Sibolga dan Kabupaten Mandailing Natal
telah menyiapkan dokumen usulan MPA baru. Dengan pengalihan kewenangan ini,
Pemerintah Kabupaten/Kota tidak berkewanangan untuk mengusulkan MPA. Oleh
karena itu, Pemerintah Provinsi Sumatera Utara semestinya menindaklanjuti
menyiapkan dokumen pengusulan MPA. Namun sampai tahun 2018, berkas usulan MPA
kabupaten/Kota tidak ada tindak lanjut dari Pemerintah Provinsi.
4.Terbengkalai
usulan Kawasan Perlindungan Terbatas
Pemerintah
Provinsi Sumatera Utara telah memiliki Kawasan Perlindungan Terbatas Ikan
Terubuk (Tenualosa ilisha), di
Labuhan Batu berdasarkan SK Kepmenkp Nomor 34/KEPMEN-KP/2016 tertanggal 2
Agustus 2016. Kendati telah ditetapkan sejak tahun 2016, namun sampai tahun 2018
belum ada kelembagaan, manajemen pengelolaan, pendanaan dan kegiatan konservasi
di lapangan. Selain itu, Pemerintah Kabupaten/Kota telah pula menyusun usulan
kawasan perlindungan terbatas untuk Ikan Batak dan Kerang Anak Dara di
Kabupaten Asahan, perlindungan Penyu dan
Tiram di Kabupaten Tapanuli Tengah dan lainnya. Karena kewenangan usulan
konservasi telah dialihkan dari Pemerintah Kabupaten/Kota ke Pemerintah
Provinsi, maka seyogianya Pemerintah Provinsi Sumatera Utara melanjutkan usulan
kawasan perlindungan terbatas jenis ikan. Hasil penelitian menunjukkan, usulan
kawasan perlindungan terbatas yang tertunda ini belum dilanjutkan Pemerintah
Provinsi Sumatera Utara.
5.
Tidak ada
pembinaan MPA swasta
Peralihan kewengan pengelolaan konservasi dari Pemerintah Kabupaten/Kota
ke Pemerintah Provinsi menyebabkan pembinaan lembaga konservasi swasta yang
dikelola masyarakat dengan luasan kecil
seperti “anak binatang kehilangan
induknya”. Pemerintah kabupaten/kota tidak mau mengurus karena tidak menjadi
tugas pokok dan fungsinya lagi sedangkan Pemerintah Provinsi belum memiliki
data, relasi, anggaran pembinaan serta jauhnya jarak antara ibu kota provinsi
dengan lokasi konservasi di pelosok pedesaan. Karena tidak adanya pembinaan dn
bantuan pendanaan maka MPA swasta mengalami stagnasi pengelolaan. Kelompok
masyarakat pengelola konservasi mengharapkan adanya pembinaan, penempatan
penyuluh dan bantuan pendanaan.
Kesimpulan
1.
Pemerintah
Provinsi Sumatera Utara melalui Dinas Kelautan dan Perikanan belum siap
menerima pelimpahan kewenangan bidang konservasi dari Pemerintah Kabupaten/kota
sesuai Undang-Undang Nomor 23 tahun 2014
tentang Pemerintahan Daerah. Peralihan kewenangan tidak membuat pengelolaan MPA
semakin baik, yang terjadi MPA semakin tidak terurus.
2.
Dampak negatif peralihan kewenangan konservasi
dari Pemerintah Kabupaten/Kota ke Provinsi Sumatera Utara, berupa:
(1). Pemerintah Provinsi Sumatera Utara
berkewajiban mengelola MPA yang telah ditetapkan Pemerintah Pusat: (1) MPA
Sawo-Lahewa Nias Utara tahun 2017 (didirikan 2007) dan (2) Kawasan Perlindungan
Terbatas Ikan Terubuk tahun 2016 di Kabupaten Labuhan Batu. Namun sampai tahun
2018 belum dikelola, belum ada kelembagaan,
model majemen pengelolaan, anggaran dan pelaksanaan konservasi pada kawasan
konservasi tersebut.
(2). Pemerintah Provinsi Sumatera Utara baru
tahun 2017 mencadangkan 3 MPA baru namun karena belum ditetapkan Pemerintah
Pusat maka MPA Tapanuli Tengah (berdiri 2007), Nias Selatan (2008) dan Serdang
Bedagai (2008) tidak dapat dikelola oleh Pemerintah Provinsi Sumatera Utara.
(3) Pemerintah
Provinsi Sumatera Utara belum menindaklanjuti
usulan MPA dan usulan Kawasan Perlindungan Terbatas yang tertunda karena
pengalihan kewenangan pengelolaan dari Pemerintah Kabupaten/Kota ke Pemerintah
Provinsi.
(4). Pemerintah Provinsi Sumatera Utara
belum mendapata MPA swasta yang dikelola masyarakat, demikian juga belum
dilakukan pembinaan, pendampingan dan bantuan pendanaan.
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*Makalah pada
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held at Grand Inna Hotel, Medan, Indonesia
on Agustus 2 nd-3nd, 2018
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