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Country review: Indonesia


Peter Flewwelling and Gilles Hosch
FAO Consultants, Fishery Policy and Planning Division, Fisheries Department
September, 2004

I. INTRODUCTION

Indonesia[172] is the fourth largest country in the world with a land mass of 1.9 million km2, archipelagic territorial sea of some 3 million km2, and an EEZ extending to approximately 3.1 million km2 around the estimated 19,000 islands and its 81,000 km of coastline. Indonesia, with its 27 provinces[173], spreads over a large area (4800 km on the base) with the South China Sea and Celebes Sea to the north, the Pacific Ocean to the northeast, the Arafura Sea to the east, and the Indian Ocean to the south and west with the Malacca Strait forming the bridge between the South China Sea and the Indian Ocean. The coastal areas are rich in seagrasses, coral reefs and mangroves.

There are two basic seasons in Indonesia, the dry season, May to October and the wet season, December to March with the transition seasons providing shifting winds and very changeable weather. Temperatures range around 25 to 33 degrees centigrade, with cooler temperatures in the mountains.

Population and the economy

The marine resources provide food to the 60 percent of the total 211.7[174] million population that live in the coastal areas. Approximately 63 million (50 percent of the total on the coast) of these coastal residents are fishers (ADB Coastal Project 1999). The value of the fishery, including mariculture, is steadily growing and was approximately US$4.2 billion (2.4 percent GDP) (Willoughby et al., 1996). It is estimated that 21 percent of the national GDP of (US$172.9 billion[175]) comes from the agricultural, coastal and marine resources.

POLICY FRAMEWORK

The fisheries sector policy statement in the National Development Plan (REPELITA VII for 2000-2005 supported by ADB) includes efficient and sustainable management of maritime resources and the rehabilitation of damaged coastal and marine ecosystems, through improved spatial planning.

Fisheries policies are set out through the new Ministry of Marine Affairs and Fisheries (MMAF established in 2000) through the legislative instruments that are used by the Government. These are discussed further under the next section, but in essence include national, presidential, ministerial, provincial, and district legal tools. For marine capture fisheries, the Directorate General for Capture Fisheries of the Ministry has the mandate to develop and issue policies for these fisheries and these are then implemented through the provinces and districts according to their respective authorities under the Autonomy Law No. 22/99[176]. Informal local policies in some areas come from traditional, unwritten laws handed down from generation to generation. These are referred to as “traditional law” or locally as sasi or adat law. Traditional conservation policies are thereby passed on to future generations.

It is to be noted that the Indonesian Institute of Science and Technology (LIPI) and Central Fisheries Research Institute (CRIFI) and three other Research Institutes (Research Institute for Marine Fisheries, Research Institute for Freshwater Fisheries and Research Institute for Coastal Aquaculture) are the official agencies that provide research assistance to the Ministry. Further, the universities often become involved in fisheries research to assist the Ministry of Fisheries in the development of capture fisheries management policies and strategies.

One of the first legislative instruments that addressed fisheries was the Ordinance on Territorial Waters and Maritime Zones, 1939 defining the zones and designating the Navy Commander as the authority for limiting or prohibiting fishing. This ordinance has evolved into a myriad of acts and regulations and other legal mechanisms that together define and provide the legal backing for the fisheries management policies at the various authority levels including those at the national, provincial and district levels.

The current national core fisheries law is the Fisheries Act No. 9 of 1985. The key objectives for fisheries management as contained in the Fisheries Act of 1985 include:

This Act is now under review for several reasons:

There is a current initiative for a Coastal and Small Islands Act under the Ministry to address fisheries management issues in the coastal areas that will also provide general consistent guidance to District Governments in the management of their coastal waters.

There are several agencies whose mandates interact and overlap with fisheries, consequently the legislation of these agencies either directly or indirectly impacts on fisheries policies, laws, and management practices. Some of these agencies include:

Compliance with fisheries laws is executed through the local provincial and district fisheries administrations, and the navy and maritime police agencies. Communities are being urged through several coastal resource development programmes to assume greater input into the management planning, policy development, and the implementation process, although this is still in its infancy. This latter task is often being undertaken through non-government organizations (NGOs).

LEGAL FRAMEWORK

Fisheries Management is defined in the legislation as the “management of all activities that are directed towards fisheries natural resources to ensure utilization in an optimal and sustainable manner”.

Fisheries management falls under the joint responsibility of the Ministry of Marine Affairs and Fisheries and the provincial and district governments. The devolution of authority for government management, including fisheries, to the provinces (0-12 nm) and district levels (0-4 nm) under Autonomy Law No. 22 is presenting new challenges for the implementation of fisheries management regimes. The establishment of the Ministry of Marine Affairs and Fisheries to coordinate this devolution exercise and provide a guide for consistent implementation according to fisheries legislation is a very positive step for fisheries management in Indonesia.

The management planning functions rest with the Directorate General for Capture Fisheries; legal and regulatory development with the Secretary General; and research with earlier noted Research Directorate. The MCS functions rest with the Directorate General for Marine Affairs Resource Controlling and Fisheries Surveillance, supplemented by assistance from the armed forces (mainly the Navy and Air Force), and the Marine Police[177].

Fisheries legislation follows a strict hierarchical structure of priority and authority levels including those shown in Figure 1.

FIGURE 1
Hierarchical structure

As noted earlier, the key fisheries legislation is the Fisheries Act No. 9 of 1985, supported directly by Government Regulations No. 15/1990 and No. 15/1994. The above system has been in place for several years and as an example, there have been one Presidential Decree, one Presidential Instruction (treated as a decree), and 24 Ministerial Decrees for fisheries since 1973 to establish various business and resource management controls. Unfortunately, implementation of these legislative instruments has generally been weak. The exception has been recent efforts (2001 to date) by the Navy against foreign fishers where they have found that financial benefits from penalties are greatest.

Indonesia has implemented a scheme of joint management and implementation authority levels in accordance with the aforementioned Autonomy Law whereby the:

Licensing of fishing vessels and reporting requirements are based on vessel size with vessels smaller than 5GT being considered artisanal and not required to report, but they must be registered at the district/provincial level. Where registration of artisanal vessel is actually carried out, it is done annually and with an automatic renewal system if there are no reported changes to the vessel, such changes seldom being reported, and the registration process being poorly maintained. Larger vessels are normally first licensed at the national office. Annual renewal licenses (depending on size) are then automatically issued at the provincial offices if there are no changes to the vessel or its equipment. All vessels over 5GT are required to be inspected for safety by the Ministry of Sea Communications and Transport prior to being licensed for fishing by the Ministry. One consequence of this safety registration is that many fishers believe this safety registration is their fisheries license and do not seek the latter from MMAF. Compliance with these requirements is still a challenge for the Ministry. Licensing has not been fully implemented as a management tool for fisheries.

Fisheries management is influenced by the autonomy law, and also, perhaps more intrusively by the Ministerial Decree from the Minister of Forestry (not fully devolved under the Autonomy Law) whereby that ministry assumes management control and authority for all marine parks. This overlap in spatial and sectoral responsibilities remains a challenge for the ministries today and is further complicated by the District authority under the Autonomy Legislation.

BOX 1
Autonomy Laws 22 & 25 of 1999 and their impact on fisheries management

The change in administrative regimes from President Suharto, President B. Josef Habibie (22 May 1998) to President Abdurrahman Wahid (Oct 1999), and then to President Megawati Sukarno-Putri (23 July 2001) in the 1998-2001 period was accompanied by considerable civil unrest and demands for greater autonomy and equitable revenue sharing from regions and provinces. This grew over the late years of President Suharto and in an attempt to placate the regional Indonesian populace, he sought assistance to devolve some of the authority of the central government to the provinces and districts. With legal support from the GTZ, the devolution exercise continued through to his successor, President Habibie and on to President Wahid when the Autonomy Laws #22 (authorities) and #25 (cost sharing) were enacted, in July 1999, and to come into effect January 2001. These laws established zones of responsibility for fisheries and the marine sector for the districts (0-4 mm), provinces (0-12 mm) and the national government (outside 12 mm). At the same time, a higher priority was given for exploitation of the marine resources. The Directorate General of Fisheries was moved out of the Ministry of Agriculture, to become a new Ministry of Marine Affairs and Fisheries (MMAF) in 2000, with the usual internal challenges for authority, that arise from such actions. The National Maritime Council was re-established; further challenges arose as the MMAF struggled with both its new organization and the devolution of national authority to the Provincial and District Leaders to become effective in January 2001. Devolution was still being resisted by centralists in Jakarta who did not wish to return to the regions.

For Presidents Suharto, Habibie and Wahid it was too little - too late, but for President Sukarno-Putri and the current and future Ministers of MMAF, the Autonomy Laws were and remain a reality.

Many believe the Autonomy Laws did not go far enough, but the Governors and District Heads are flexing their new autonomy muscles to exert their authority. The challenge for MMAF will be the change from a central, Jakarta-based directional authority, to one of coordination and facilitation of Provincial and District initiatives within the principles of sustainability and responsible fisheries.

Tourism, Port and Transport Departments under the Ministry of Sea Communications and Transport often have significant impacts on fisheries due to the spatial overlap in the coastal areas whereby, construction or other activities can clearly negatively impact fisheries health of habitat. The liaison between the Ministry of Marine Affairs and Fisheries (MMAF) and other agencies, as noted above, is facilitated through the National Maritime Council chaired by the Minister of MMAF. The effectiveness of this inter-agency arrangement has yet to be assessed, especially with the added complexities introduced by the Autonomy Law, and devolution of authority, consequently new initiatives in fisheries or coastal areas can expect to be required to clear several hurdles before approval.

Further, indirectly-related legislation that impacts on marine capture fisheries includes:

BOX 2
Non-government organizations and community groups in Indonesia

The introduction of NGOS, and community groups has been an evolving effort for several years and encountered several of the traditional stumbling blocks of many other countries:

1. Proliferation of NGO’s, many with political ties, as instruments to seek donor funding, this complicating the search for “credible” NGO’s with resulting in political outbursts of “favouritism” during tender processes.

2. The idea that “big”, or “international” is better sometimes ignores local, commitment and efforts resulting in “template” solutions that do not meet local needs.

3. Donor driven NGO selection favouring international NGO’s as opposed to local dedicated groups.

4. Direct assistance to community groups or NGO’s while ignoring the political infrastructure thereby creating two problems:

a. concern at local government level groups re: authority and participatory action; and

b. assumption of a confrontational attitude by NGO’s and community groups who perceive they have greater powers due to donor assistance and central government selection.

5. In fighting between NGO’s/community groups, or NGO’s and local government thus reducing effectiveness as a “bridge” between government and stakeholders, and the resultant preference by local government to manage without NGOs, said assistance preferred to go to local government institutional strengthening - instead of NGO/community groups that remain outside of government.

Devolution of authority can also result in a wider testing of authority by local officials. This can create tensions between local government NGO, community advocacy groups, universities and educational groups or institutions that perceive this as their role.

These have been traditional teething problems with the introduction of NGO or use of community groups in many countries, e.g., Philippines. However, in Indonesia, as credible NGO’s go through the learning curve and recognize their “bridging role” as opposed to confrontational role - the benefits of their presence is being recognized by progressive provincial and district leaders as a supportive mechanism for management.

Specific examples include:

In summary, Indonesia has a comprehensive legal framework for fisheries management that is somewhat complicated by multiple authority levels of legislation and the overlapping intra- and inter-agency jurisdictions. This framework is further complicated by the devolution of fisheries management authority to the provinces and districts, and the growing transparency and consultative, participatory approach being trailed by the national fisheries authorities.

The increasing introduction of non-government organizations and community groups to assist in bridging and providing input to management planning and implementation is a challenge for all government levels, but, despite usual introductory concerns, it is becoming accepted as the future management practice, and is supported by an appropriate legislative structure.

STATUS OF FISHERIES

The potential yield of marine fish resources of Indonesia has been estimated in 1997 to be 6.2 million tonnes/year. With Indonesia’s rapidly growing population and increased demand for fish for home consumption, currently at 20 kg/capita/year, its sustainable production capacity is already stressed. The total 1997 multi-fishery/gear fisheries marine capture landings in Indonesia was 3.6 million tonnes with an estimated value of US$4.2 billion. This equates to a contribution of some 2.4 percent to the national GDP, and 13 percent of the agricultural component. Further, fish exports in 1998 were US$1.6 billion compared to imports of US$49 million.

The former Directorate General of Fisheries in the Ministry of Agriculture grouped the fishing grounds into four key areas: (1) Eastern Indian Ocean; (2) Sunda Shelf; (3) Sulawesi; and (4) Maluku-Irian Jaya.

The Eastern Indian Ocean is divided into three sub-areas: (1) West Sumatra, covering the provinces of Aceh in North Sumatra; West Sumatra; Bengkulu; and Lampung; (2) South Java, covering the provinces of West and Central Java, Yogyakarta and East Java; and (3) Bali-Nusa Tenggara, covering the provinces of Bali, west Nusa Tenggara, east of Nusa Tenggara and East Timor. These areas have, in general, a narrow continental shelf with deep water; and fishing activities are mainly on large and small pelagic fish.

The Sunda Shelf area is divided into the Malacca Straits, the southern part of the South China Sea and the Java Sea. In these generally shallow waters, the fishery resources are mainly demersal and small pelagic fish. The stocks in the Malacca Straits are shared by Indonesia, Malaysia and Thailand. The waters around Sulawesi are generally deep with high salinity. The fisheries in these waters target large and small pelagic fish.

The waters in Maluku-Irian Jaya comprise both shallow and deep waters. The Arafura Sea is relatively shallow; and as such, it contains large fishing grounds for both demersal and small pelagic fish. Tuna and skipjack can be found over the whole area of deeper waters adjacent to the western central Pacific Ocean.[178]

Some 94.6 percent[179] of the total marine fish landings are taken by small coastal fishers using lines, traps, beach seines or lift nets, with pole and lines, trolling gear and mini-seines for tunas and small pelagics with 2/3rds coming from the western area. The industrial fishery targets the high value shrimp and tuna fisheries; hence contributes more significantly to the value of landings than the small scale coastal fisheries (Table 1).

TABLE 1
Characteristics of the major fisheries of Indonesia

Fishery

Vessels 20021

Fishers
2002

Catch & value 2002
(US$ 2002 equiv)

Catch & value
five yrs ago

Catch & value
ten yrs ago

COMMERCIAL

Longline

1,497

949,980

197,344
mt/$606,387,810

154,330 mt/
n.a.

110,035 mt/
n.a.

Purse Seiners

916

210,840

609,243 mt/
$1,872,048,440

586,241 mt/
n.a.

395,857 mt/
n.a.

BED equipped Shrimp Nets

402

5,944

103,468 mt/
$989,610,560

95,536 mt/
n.a.

18,249 mt/
n.a.

Sub-Total

2,815

1,166,764

910,055 mt/
$3,468,046,810

836,107 mt/
n.a.

524,141 mt/
n.a.

ARTISANAL2

Gillnet

(339)3

2,443,155

829,376 mt/
$4,324,138.79

708,428 mt/
n.a.

539,190 mt/
n.a.

Seine Nets

(30)

338,248

633,751 mt/
$3,304,203.74

369,686 mt/
n.a.

306,665 mt/
n.a.

Traps

(48)

129,982

226,852 mt/
$2,025,729

235,305 mt/
n.a.

192,781 mt/
n.a.

Sub-Total

(417)

2,911,385

1,689,979 mt/
9,654,071.53

1,313,419 mt/
n.a.

1,038,636 mt/
n.a.

TOTAL

(3,232)
402,104
(1997)4

4,078,149

2,600,034 mt/
$3,477,700,881

2,149,526 mt/
n.a.

1,562,777 mt/
n.a.

* It has been estimated that approximately 937 foreign fishing vessels are in joint ventures with Indonesia, and fishing in Indonesian waters (Menasveta 1997).

1 The only statistics available are for those vessels licensed at the central fisheries HQ and do not include any that may be licensed by provincial offices.

2 Artisanal fishers and fishing are classified in the Fisheries Law as those using vessels less than 5GT, or no vessel at all.

3 Written communications from MMAF Sept 2003.

4 FAO Web page, noting that this includes all artisanal fisheries, with 56.9% of the boats non-powered; 70.6% less than 5 GT and another 21.95% between 5-20 GT all making daily fishing trips.

In 1996 the estimate of total fishers was 4.7 million with 2.5 million[180] in the capture fishery and 2.2 in the aquaculture activities. This has been increasing yearly and the Government indicates that as of the latest figures in 2002, there were approximately 4.1 million capture fishers in Indonesia, 1.17 million in the commercial fisheries and the artisanal fishery taking the remainder. As in many countries the question, is raised as to whether artisanal fishers are for subsistence fishing only. In Indonesia, artisanal fishers vary from subsistence fishers in the isolated rural areas, to “small scale” commercial fishers bartering or selling their excess catch, to contracted fishers for the live reef fish trade, and also include full commercial fishers who bribe their way into the “artisanal” fishery category (<5GT) to avoid taxes, reports and restrictions. Ineffective licensing and law enforcement permits this to occur.

Fishers are categorised into full time (51 percent) and part time (49 percent). The high populations in Western Indonesia create a large demand for shallow water, reef and small pelagic fishes, while the eastern areas with the deeper waters are more suitable for the large pelagics. The South China Sea with its proliferation of charter vessels is assumed to be at, or nearing the MSY for small pelagics, however the western waters may have room for continued exploitation. The waters of the Arafura Sea and other deeper eastern waters appear to have room for expansion in the small and large pelagic, shrimp and squid fisheries.

MANAGEMENT ACTIVITY

The general fisheries development objective for Indonesia is the promotion of sustainable development in the fisheries sector through responsible fisheries with the management aim to find a balance between production, distribution and conservation of the resources and their environment. More specifically, efforts within the Ministry are targeted to:

Biologically, the management of the fisheries resources is based on fish quotas, i.e., the total allowable catch (TAC) of 4.96 million tonne/year, that is determined on the basis of up to 80 percent of the total estimated potential yield (6.2 million tonne/year). Currently the fisheries resources are classified into several groups, namely: (1) large pelagics (skipjack, tunas, billfish, oceanic sharks and small tuna); (2) small pelagics (including scads, mackerels, sardinellas, trevallies, engraulid anchovy, etc.); (3) demersal and coral reef fishes (groupers, snappers, rabbitfish, slipmouth, etc.); and (4) prawn, shrimp, and other crustaceans.

The management of the fisheries resources falls to the Ministry of Marine Affairs and Fisheries (MMAF) and through the Autonomy Law to the Provincial Governors for 0-12nm, and the District Heads (Bupati) for 0-4 nm. Fisheries law can be developed and implemented at all these levels, but it must comply in intent with the national fisheries laws and Ministerial Decrees. The Government responded to a recent FAO Questionnaire that the management process was very transparent and stakeholders were active participators into the management planning and implementation, but stakeholders have not been given full management authority for the fisheries at this time. Fishers in the commercial fisheries have formed into associations, e.g. Tuna Association.

In recent years, both the commercial and coastal fisheries management authorities have commenced consultation with stakeholders for fisheries management planning, and are working with NGOs to assist in the implementation of this process. This is becoming the norm, providing opportunities for fishers input into the process. Initial plans and strategies are still developed centrally until the devolved authorities are prepared to assume the lead in this process. The Ministry does work closely with the provincial parties, and through several coastal fisheries initiatives, with the Bupati to prepare them to assume these duties. The devolution of authority necessitates a high degree of transparency in the process to recognise the role and authority of all participants. Community and stakeholder involvement at fisheries management meetings is increasing, especially with the use of media services to announce meetings and distribute materials.

BOX 3
NGOs and community groups in Indonesia

Successful and sustainable involvement of stakeholders as a management tool in Indonesia has been dependent upon two factors:

  • continuation of donor funding; and

  • support for a “champion” for sustainable resource management, either foreigner or local, who takes the course to the community and community/local government leaders.

The risk however, is similar to that for donor funding - the commitments often exists only as long as funding and/or the “champion” remains. If either factor is removed from the initiative it often fails, e.g., WB COREMAP RIAU; USAID CRMP in Buton.

Commercial Fisheries: Approximately 1/3 - 2/3rd of the fisheries are managed from the national level, and less than 33 percent are managed at the provincial and local levels, although the number of fisheries coming under co-management has been increasing over the past ten years. At this time the three major commercial fisheries: longline for tunas (set lines and drift lines); purse seine fisheries; and by-catch exclusion device (BED) equipped shrimp nets[181] do not have formal management plans, but are regulated through legislation. The use of legislation for management, recognizing the multi-species fisheries, is more prominent (33-67 percent) in Indonesia than the use of formal management plans (less than 33 percent) with licensing and limited access, area designations, TACs, taxes, and gear (gear type, hook size, mesh size, engines and vessel sizes) restrictions being the most common for the larger commercial fisheries. Measures to address ecosystem concerns include the prohibitions regarding: setting of fish aggregating devices (FADs) during fish migration periods; and the use of poisons for fishing. Further is the requirement for the use of turtle (TEDs) or by-catch exclusion devices (BEDs) in shrimp trawls, although the enforcement of these conservation measures is weak. Education, limited area access by gear type, stock enhancement and resource allocation are also reported by MMAF as management tools used in the commercial fisheries of Indonesia.

BOX 4
Effectiveness of penalties

Enforcement includes the graduated fiscal penalties, suspension or cancellation of licenses, refusal for new licenses and full removal from the fishery as penalty options, but unfortunately the infractions appear to have been increasing over the past ten years despite the introduction of VMS, observers, dockside and landing site and at-sea inspections. This indicates the fact that the penalty scheme is not an effective deterrent, the education efforts to promote voluntary compliance are not effective, or that law enforcement monitoring efforts are increasing. Alternately, it could indicate that fishers have no respect for the laws and prosecutorial system, possibly due to the low deterrence measures in place, e.g., penalties are just a cost of doing business and do not significantly detract from illegal gains, e.g., the gains from illegal fishing exceed the penalties such as the ability to retain illegally caught fish and sell it for US$50,000, while the maximum fine is only equivalent to US$3,000.

There is reported overfishing and overcapacity in the longline and shrimp fisheries, however, aside from imposing licensing fees, reduction in capacity has not been realised.

Conflicts in the commercial fisheries are resolved through specific consultation between parties and if not resolved, through legal steps.

Artisanal/Coastal Fisheries: The three major multi-species, artisanal fisheries in terms of capacity and value are:

TABLE 2
Major artisanal fisheries in Indonesia

Fishery

Fishers (estimated)1

Area of fishery

gillnet fishery

2.4 million

in all coastal fisheries in Western Indonesia

seine net

338,000

Malacca Strait, Java Sea and North Sulawesi

trap fishery

130,000

coastal waters of East Sumatera and South Sulawesi

1 Source: Personal communications with MMAF officials Oct/03.

Management objectives are twofold, to ensure resource sustainability, and to minimise conflict. Management tools in use include licensing, gear type restrictions, limited entry, the establishment and monitoring of TACs and fish catches, and taxes on fisheries. Further, in some of the coastal fisheries recognition of traditional rules and customs are used for conservation management. Increased consultation has resulted in less conflicts between stakeholders, and efforts to merge government and stakeholder expectations, but it has not resulted in stabilisation of stocks, facilitated management decision-making nor has it provided an incentive for greater voluntary compliance and stewardship of the resources. Conflict is greater in the gill and seine net fisheries focused more on different type vessels and intrusion of fishers in other fisheries. As in the commercial fisheries the conflict resolution process includes the use of management tools to reduce these incidents including: education, stock enhancement, allocation amongst users, zoning and area restrictions with specific steps for resolution up to and including court action.

Licensing and registration mechanisms are weak and lack enforcement; data collection verification and analysis for planning is very weak; and enforcement of current laws by law enforcement agencies with appropriate penalties being handed down to violators is almost negligible for the national fleets. Lack of attention to these three key inputs to sustainable and responsible fisheries management significantly increase the challenge for the Ministry to meet its mandate, while reducing its probability for success.

In summary, the fisheries management processes rely on the legal instruments to manage the fisheries as opposed to formal management planning schemes. They include stakeholder participation, and now include devolution of management authority to the provinces and districts with greater consultation for management planning, implementation and conflict resolution. Unfortunately these measures have not yet shown an appreciable positive impact on stock recovery, stock stability, or the realisation of sustainable management in either the commercial or coastal/artisanal fisheries. The apparent lack of commitment to data collection and verifiability of such data and enforcement of the laws continues to have a negative impact on stock recovery, and hence enhanced fishers returns.

Indonesia’s recent efforts at the National level to control IUU fishing are becoming effective, but its legislation needs urgent review as non-sustainable measures have been included in past legislation to benefit foreign investors and local partners, e.g. redefinition of trawl nets to fish nets to allow their use in western Indonesia, etc. Inter-agency coordination through the National Maritime Council (DMP) has proven as ineffective as its two predecessors over the past ten years, due to lack of inter-agency cooperation, and this is expected to continue. Coastal co-management is becoming popular and growing in acceptance in donor project areas, but lack of local capacity hinder its widespread acceptance. This is further exacerbated by the continuation of centralist resistance to devolution in some agencies.

The new Ministry has potential to address the fisheries management situation in Indonesia in a responsible and sustainable manner, but it will require strong and committed leadership to change the attitudes of “laissez-faire” of the past decades, and acceptance of the principles of devolution of authority to coastal areas, consequently progress cannot be expected to be rapid. It is noted however, that key inroads and “champions” are coming to the fore to take on these challenges in both the offshore and coastal management areas.

COSTS AND REVENUES OF FISHERIES MANAGEMENT

All levels of government contribute to the cost of management with a portion of these costs assessed to fishers for their participation in the industry. Resource rents and other mechanisms are not yet being used in Indonesia. The increased involvement of stakeholders, increased monitoring and data collection, enforcement, conflict resolution requirements and modifications in management strategies have increased the cost of management of the fisheries. Although this is currently borne by the Government, officials state that they are investigating mechanisms to increase contributions from stakeholders and participants, e.g., selling user rights to coastal areas, increased licensing fees; higher penalties, etc., but these are yet to be implemented.

IMPLEMENTATION OF GLOBAL FISHERIES MANDATES AND INITIATIVES

Indonesia ratified UNCLOS 1982 on 3 February 1986 and the Agreement relating to the implementation of Part XI of the Convention on 2 June 2000. The UN Fish Stocks Agreement and the FAO Compliance Agreement have not yet been ratified.

Indonesia has taken several actions with respect to international mandates and initiatives including:

Indonesia is now measuring the capacity of its capture fisheries, said exercise to be completed prior to 2005 as urged in the IPOA. Further, Indonesia is introducing VMS, MCS, and strengthening its licensing, law enforcement and inter-agency enforcement capacity to address IUU fishing.

Increased statistical capacity is being introduced for tuna with assistance from Japan in preparation for WCPFC, but lack of budgets is hampering other data improvement initiatives.

PARTICIPATION IN REGIONAL FISHERY BODIES

Indonesia actively participates in the following regional fisheries related bodies:

Conventions to which Indonesia is a party

IOMAC

Indian Ocean Marine Affairs Cooperation

SEAFDEC

South East Asian Fisheries Development Centre


Member of Regional Organizations

BIMP-EAGA

Brunei, Indonesia, Malaysia, Philippines - East Asia Growth Area

SEAFDEC

South East Asian Fisheries Development Centre

NACA

Network of Aquaculture Centres in Asia-Pacific


Participant but not a Member

CCSBT

Commission for the Conservation of Southern Bluefin Tuna

IOTC

Indian Ocean Tuna Commission

WCPFC

Western and Central Pacific Ocean Fisheries Commission

BOBP LME

Bay of Bengal Program - Large Marine Ecosystem Project

IMT-GT

Indonesia/Malaysia/Thailand - Growth Triangle

IMS-GT

Indonesia/Malaysia/Singapore - Growth Triangle

AIDA

Inter-American Assocaiton for Environmental Defense

ICCAT

International Commission for the Conservation of Atlantic Tunas

SUMMARY AND CONCLUSIONS

Indonesia, an archipelagic state of some 19,000 islands, straddles the equator across 4,800 km forming the stepping stone island bridge between the South Pacific Ocean and the Indian Ocean. With its population of 212 million persons in 27 provinces, the greater number being in the western provinces, Indonesia has recently devolved its marine management authority (1999) to the provinces (0-12 nm) and the districts (0-4 nm) with the central government and the new Ministry of Marine Affairs and Fisheries taking responsibility for the offshore fisheries outside 12 nm. The devolution of authority is ongoing and requiring amendments to the myriad of complex legislative instruments utilized in Indonesia from the Fisheries Law and National Government Regulations to the various political authority levels for more local regulations called decrees (Presidential, Ministerial, Provincial and District decrees). The Ministry is currently reviewing its key legislation and writing a new Coastal and Small Islands (fisheries resources management) Act for the country to assist the new devolved management authorities. Indonesia has a comprehensive fisheries legislative system support its new fisheries management system. This new system is more transparent, consultative and participatory with input sought from stakeholders and efforts to establish a collaborative management regime between government and stakeholders, including the fishers down to the village levels through assistance from many donor initiatives.

The 3.6 million mt marine capture fishery, involving some 4.1 full and part time capture fishers (1.2 million being in the commercial fisheries), has an estimated total value of US$4.2 billion. Commercial fishers target the high value tunas and shrimp while the artisanal fishers target the small pelagics and reef fish, the latter group harvesting approximately 94 percent of the total volume of the fisheries most coming from the western shelf areas and the Arafura Sea area. The fisheries are harvested from an estimated half million fishing boats, 150,000 being for the open water and some 3 180 (Menasveta 1996) being used in the larger scale commercial fisheries, with the remainer for coastal areas. It has been estimated (Menasveta 1997) that approximately 937 foreign fishing vessels operate in Indonesian waters under joint venture agreements.

MMAF officials[182] state that they are now utilizing several management tools to address conservation including: limited entry licensing, zoning and area, gear restrictions, and even bycatch exclusion devices (BEDs) for the demersal by-catches in shrimp trawls. The requirement for turtle exclusion devices (TEDs) is claimed to be in place for trawls and traps, but the success of such implementation is not known by this writer.

Indonesia is in a state of evolution of its fisheries management and has based its processes on legislative instruments, with attention to more transparency, consultation and input from stakeholders and devolution of authority. Indonesia is actively participating in several regional fisheries related organizations including the new 27 country, Western Central Pacific Ocean Fisheries Commission. Further, Indonesia is actively addressing international and global conservation initiatives for:

The new Ministry for Fisheries is having difficulties in getting organized, but the efforts on the offshore fisheries through the use of the navy are starting to show the results of the FAO MCS training (FAO, multiple). Unfortunately, the National Maritime Council concept is not effective due to lack of inter-agency cooperation, but this is a mechanism that has potential for future efforts, if given the appropriate leadership and mandate to control the maritime waters. The donor projects are making inroads on management planning and implementation in their respective sites, but these efforts have not yet become ensconced in local government processes, due in part to lack of capacity, as well as central resistance to devolution of authority to provinces and districts.

REFERENCES

Dirhamsyah. 2004. Draft PhD Thesis on Fisheries Management in Indonesia. (unpublished), Wollongong University, Australia.

FAO. 1999. Report of a Regional Workshop on Fisheries Monitoring, Control and Surveillance and Supplement 1, Country Reports, Regional Reports and Case Studies. Kuala Lumpur and Kuala Terengganu, Malaysia, June/July1998, FAO, Rome.

FAO. 2000. Papers Presented at the Workshop on the Fishery and Management of Bali Sardinella (Sardinella lemuru) in Bali Strai. Denpasar, Bali, Indonesia April 1999, FAO, Rome.

FAO. 2000. Regional Introductory Workshop on MCS for Fisheries Executives of Cambodia, Indonesia, Malaysia, Philippines, Thailand and Vietnam. Songkhla, Thailand, June 2000, FAO (unpublished).

FAO. 2002/27. Building an Awareness in Aspects of Fishery Statistics, Stock Assessment and Management. Proceedings of the FAO/SEAFDEC Workshop on the Use of Statistics and Other Information for Stock Assessment. Samut Prakarn, Thailand, September 2002, FAO, Rome.

FAO. Web Pages, Ocean Law, Fisheries Country Profiles; Information on Fisheries Management in Indonesia.

Flewwelling, P. 2002. Fisheries Management and MCS in South Asia: Comparative Analysis, Rome, Italy, FAO, 2000. 56p.

Flewwelling, P. 2001. Fisheries Management and MCS in South Asia: Compendium of FAO Missions, (Not Published), Tacloban, Philippines. 258p.

Menasveta, D. 1997. Fisheries Management Frameworks of the Countries Bordering the South China Sea, FAO Regional Office for Asia and the Pacific, Bangkok, Thailand. RAP Publication 1997/33, 151p.

World Bank web pages on fisheries statistics and management issues.

APPENDIX TABLES

Current management of marine capture fisheries

Level of
Management

% Fisheries
Managed

% with Fisheries
Management
Plan

% with Published
Regulations

Trends in the number of Managed
Fisheries over ten yrs. (increasing/ decreasing/unchanged)

National

33% - 67%

33%

33% - 67%

Increasing

Regional

33%

33%

33%

Increasing

Local

33%

33%

33%

Increasing

Summary information for three largest fisheries (by volume) (Year 2002)

Category of
Fishery

Fishery

Volume
mt tons

Value*
mil USD

% of Total
Volume
Caught**

% of Total
Value
Caught**

Covered by a
Management
Plan? (Yes/No)

# of
Participants

# of
Vessels

Industrial

1 longline

197,344

606,387.81

22%

17%

No

949,980

1,497

2 purse seine

609,243

1,872,048.44

67%

54%

No

210,840

916

3 shrimp nets

103,468

989,610.56

11%

29%

No

5,944

402

Artisanal

1 gillnets

829,376

4,324,138.79

49%

45%

No

2,443,155

339

2 seine nets

633,751

3,304,203.74

38%

34%

No

338,248

30

3 trap

226,852

2,025,729

13%

21%

No

129,982

48

Recreational

1

Not available







* Value in 2002 U.S. Dollars.
** % values are based on totals for each category of fishery.

Use of fishery management tools within the three largest fisheries

Category
of Fishery

Fishery

Spatial
Restrictions

Temporal
Restrictions

Gear
Restrictions

Size
Restrictions

License/
Limited
Entry

Catch
Restrictions

Rights-based
Regulations

Taxes/
Royalties

Performance
Standards

Industrial

1

No

No

Yes

No

Yes

Yes

Yes

Yes

Yes

2

No

No

Yes

No

Yes

Yes

Yes

Yes

Yes

3

No

No

Yes

No

Yes

Yes

Yes

Yes

Yes

Artisanal

1

No

No

Yes

No

yes

Yes

No

Yes

No

2

No

No

Yes

No

Yes

Yes

No

Yes

No

3

No

No

yes

No

Yes

Yes

No

Yes

No

Costs and funding sources of fisheries management within the three largest fisheries

Category
of Fishery

Fishery

Do Management Funding Outlays Cover

Are Management Funding Sources From

R&D

Monitoring &
Enforcement

Daily
Management

License fees
in fishery

License fees from
other fisheries

Resource
rents

Industrial

1

Yes

Yes

Yes

Yes

Yes

Yes

2

Yes

Yes

Yes

Yes

Yes

Yes

3

Yes

Yes

Yes

Yes

Yes

Yes

Artisanal

1

Yes

Yes

Yes

Yes

No

No

2

Yes

Yes

Yes

Yes

No

No

3

Yes

Yes

Yes

Yes

No

No

Compliance and enforcement within the three largest fisheries

Category of
Fishery

Fishery

VMS

On-board
observers

Random dockside
inspections

Routine inspections
at landing sites

At-sea boarding
and inspections

Other
(please specify)

Industrial

1

Yes

Yes

Yes

Yes

Yes

Yes

2

Yes

Yes

Yes

Yes

Yes

Yes

3

Yes

Yes

Yes

Yes

Yes

Yes

Artisanal

1

No

No

No

No

No

No

2

No

No

No

No

No

No

3

No

No

No

No

No

No

Capacity management within the three largest fisheries

Category of
Fishery

Fishery

Does
overfishing
exist?

Is fleet capacity
measured?

Is CPUE increasing,
constant or
decreasing?

Have capacity
reduction programmes
been used?

If used, please specify
objectives of capacity
reduction programme

Industrial

1

Yes

Yes

Increasing

Yes


2

No

Yes

Decreasing

Yes


3

Yes

Yes

Increasing

Yes


Artisanal

1

No

No

No

No


2

No

No

No

No


3

No

No

No

No



[172] Note: The information for this paper was gathered from many multi-media sources, the internet, and papers, some published and some being "grey literature", but a key source was a 53 page FAO Questionnaire sent to fisheries contacts in each country to assist them in formatting their responses. Data provided in these questionnaires comes from officials and Department’s files, and shall be reported in this paper as "personal correspondence and discussions with Department officials".
[173] The country has some 300 districts, 3000 sub-districts and 60,000 villages (Directorate General of Fisheries 1997)
[174] World Bank Web Pages 2003. Indonesia at a Glance
[175] Ibid.
[176] For the purposes of this paper, "national" means the entire country; "regional" equates normally to provinces (27 in number) and "local" equates to the Districts.
[177] The structure of the new Ministry has been evolving over the past few years and MCS is now under its own Directorate while the Directorate for Capture Fisheries (formerly the entire Fisheries Department under the Ministry of Agriculture) is still under change while its former responsibilities are being revised and re-distributed leaving this Directorate with the mandate, at the time of writing, for fisheries planning, licensing and aquaculture.
[178] Menasveta, D. 1997. Fisheries Management Frameworks of the Countries bordering the South China Sea. Asia-pacific Fishery Commission, FAO, Bangkok, Thailand 1997.
[179] FAO Indonesia Information on Fisheries Management web page.
[180] The large concentrations of fishers are in north Java (22.8 percent), east Sumatra (12.3 percent), Southeast Sulawesi (9.47 percent) and North Sulawesi (8.91 percent), Ibid
[181] Longlines fishing predominantly in Banda Sea, Indian Ocean, Sulawesi Sea, and Pacific Ocean; purse seines in Java Sea, Malacca Strait, South China Sea, Sulawesi Sea and Flores Sea; and Shrimp nets in Arafura Sea (West Papua), Malacca Strait, East coast Kalimantan.
[182] Written correspondence from MMAF officials, Sept 2003.

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