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Perspective plan for sustainable eel management in Lake Poso, Central Sulawesi

Lake Poso has high eel potential and a strategic position in supporting the development of eel fisheries in Sulawesi. Lake Poso is out of 15 national priority lakes in natural resources and environmental management programs. The catch of eel from Lake Poso is reported to have been decreasing for the last twenty years. Several factors causing the decline in eel populations are fishing activities, disruption in migration routes, and other factors such as changes in habitat and environmental conditions. The sustainability of the life of the Poso eel is determined by the success of the eel migration process. The migration of adult eels to the sea and young eels from glass eels to freshwater habitats must continue. The perspective plans that can be done to manage Poso's eel resources include 1) Socializing the eco-biological characteristics of eels as catadromous fish; 2) Establishing conservation areas and regulation of eel fishing; 3) Increasing eel population through restocking 4) Integrating fisheries and aquaculture activities; 5) Developing eel culture technology through size segmentation production; 6) Developing an eel migration monitoring system; 7) Building a cross-sectoral forum and put a joint action program; 8) Proposing the Poso eel Research and Conservation Center.


Introduction
Lake Poso is located in Poso Regency, Central Sulawesi. The area of Lake Poso is 323.2 km 2 , while the area of Poso's catchment area is 1271 km 2 [1]. There are approximately 13 rivers as Lake Poso inlets. The outlet of Lake Poso is the Poso River, which flows to Tomini Bay, and the length of about 52 km [1,2]. Poso's inland waters are used as energy producers through hydroelectric power, fisheries, tourist areas, and irrigation. Lake Poso is one of 15 national priority lakes. One of the reasons is degradation in the Poso watershed area, sedimentation, and decreased water quality [3].
Lake Poso and its rivers are well known as eel habitats. There are five species of eels, namely Anguilla marmorata, Anguilla celebesensis, Anguilla bicolor pacifica, Anguilla 2 Environmental characteristics of Lake Poso Lake Poso is located in Poso Regency, Central Sulawesi Province, at a geographical position of 1 o 44'-2 o 04' S and 120 o 32'-120 o 43' E, at an altitude of ±600 m above sea level [3]. The area around Lake Poso is generally hilly and mountainous, with elevations ranging from 400 to 1200 m with a slope of 15-40%. Plain areas with slopes of less than 2% are found on the shores of the lake on the southeast, south, west, and north sides [3]. Lake Poso is the beginning of the Poso River. Characteristic of the river with rapids and strong currents flowing into Tomini Bay.
The water quality of the Poso watershed in the March and June 2021 is characterized by the pH of the waters that tends to be alkaline, especially in lake waters. The water temperature is between 27.30 -29.24 o C, the dissolved oxygen level is relatively high (> 7.0 mg/L). The transparency of the waters in Lake Poso was 8.82-11.29 m, while the water transparency in the river and estuary was lower, ranging from 0.60-0.87 m. The total suspended solids (TSS.), total nitrogen, and phosphorus content in the lake area show a lower value and increase towards the estuary (Table 1). Based on national water quality standards [13], the results of water quality measurements such as transparency, total nitrogen (TN), total phosphor (TP.), and Chlorophyll-a indicate that Lake Poso is still in an oligotrophic lake. Meanwhile, the Poso River and Poso Estuary are mesotrophic [13]. The Poso River has a length of ±68.70 km with a drainage area of 1101.87 km 2 [14]. A hydroelectric power plant (PLTA) utilizes the swift flow of the Poso River water in the Sulewana area. There is a dam located at 1° 40.165' S; 120° 39,140' E (DAM Poso 1: 120 MW) and at 1° 38,897' S; 120° 39,490' E (DAM Poso 2: 195 MW). In both dams, fishway installations have been built to provide migration routes for eels. Poso 2 fishway has been operating since 2012, and Poso 1 fishway has been operating since August 2019 [15]. The effectiveness of this fishway is still being studied whether the function of the fishway is as expected. The results of initial observations revealed that there was young eel with sizes between 10-20 cm in the fishway of the two dams ( Fig. 1.). Monitoring eel migration on the fishway is essential to identify and ensure the eel cycle continues The Poso River flows into Tomini Bay, in Poso City. Tomini Bay is the largest bay in Sulawesi and Indonesia, with a maximum of 2000 m [16]. The width of the Poso River estuary is about 120 m, with a depth of between 1.5-3 m. The water transparency at the Poso River estuary in March and June 2021 was between 0.60-0.80 m. The total suspended solids content reaches 45.8-53.5 mg/L. The surface water salinity at the Poso River estuary was 0.7-0.8 ppt. The results of water quality measurement at the Poso River estuary can be seen in Table 1. The trophic level of the Poso River estuary is based on the criteria of Regulation of Ministry of Environment and Forestry No. 28.2009 [13] belongs to mesotrophic waters.

Eel fisheries condition of Lake Poso
The Poso watershed is an eel habitat area. There are five eel species, with the dominant types of eel caught being A. marmorata and A. Celebesensis [4]. Eel has economic value and is a fishing target by the community. The capture of eel was carried out at the adult stage and juveniles during the glass eel stage. Adult eels are caught using several fishing gears such as fishing rods, traps, and trap fences. Locally, the trap fence is known as "waya masapi". This fishing gear is placed transversely at the Lake Poso outlet in the Tentena. Most of the adult eels are caught by waya masapi fish trap. The catch of adult eels has been reported to have decreased over the past 30 years. In 1990 the eel catch was recorded at 41.5 tons and decreased in 1998 to 30.5 tons in 1998. In 2009 the production of eel catches was only 6.49 tons [7]. The data collection results from the Fisheries Service of Poso Regency (unpublished data) show that the eel catch in 2017-2019 was in the range of 6.7-15.5 tons. In recent data collected, the number of eels caught in April-June 2021 in the Tentena area was only 656 eels with a total weight of 3,202 kg. The size of the eel caught was dominated by the size of 98-129 cm, with a weight between 5-9 kg/Ind. (Fig. 2.).
Compared to the research results in 2012 [12], the size of the caught eels did not show any significant changes. In 2012, the eel caught in Tentena was 60-130 cm, with individual weight varying from 330 to 5000 g. The size of an eel when migrating downstream is between 4.1 to 7.2 kg/Ind. [4]. Recently the number of eels being caught has been decreasing [7,12]. The decline in eel population in the Poso watershed is caused by the intensity of eel fishing at the Poso Lake outlet, glass eel fishing at the Poso River estuary, and disturbances in the eel migration path hydroelectric power.
The glass eel at the Poso River estuary is also a target for fishing by the local community. The catch of glass eel is used as an eel seed for aquaculture. The price of glass eel ranges from Rp. 200.000-Rp.300.000/kg [17,18]. The capture of glass eels is carried out at night during the new moon period. The fishing gear was originally used as a hand net, namely "seser". It is shaped triangular with a length of 100 cm with a mouth opening of 75 cm [19]. In the last five years, the glass eel fishing gear has become a trap net called "gorong gorong" (fyke net). This fishing gear consists of the front consisting of the wings and the mouth of the net, the middle, and the back of the catch collecting bag Based on research [20], the migration of glass eels to the waters of the Poso River estuary takes place throughout the year. The peak of glass eel migration takes place in August. There are six species of glass eel, such as A. celebesensis, A. marmorata, A. interioris, A. bicolor pacifica, and two other species that have not been identified. A. celebesensis and A. marmorata are the dominant species. The catch of glass eel in 2010-2011 is estimated at 15,000,000 Ind./year or equivalent to 2.5 tons/year [7]. The results of observations of the abundance of glass eels in April-June 2021 was 3,512-13,257 ind./night or 666-2.254 g/night. According to Mr. Irwan D.J. Lamoa (glass eel fisher), the glass eel catch during the migration season could reach 20-60 kg/month. However, the glass eel catch from this Poso estuary has not been well recorded. Hence it could be a constraint in further evaluation and management of these resources.

Perspective plan for sustainable eel management
The management of eel resources has been carried out since the early 20th century through several studies. Eel research at that time focused on research on the mysteries of the eel life cycle [21]. Other studies continue to develop research to cultivate eels through artificial spawning [22], habitat restoration, restocking, and eel fishing policies [9]. Management of eel resources in Poso waters is necessary to be done. The decline in catch production, unregulated fishing rates, obstacles in the eel migration path, and the other environmental pressures are essential points to be considered. Research Center for Limnology -LIPI through LPDP Rispro Invitasi Research Program conduct to implement the previous research and the ongoing research to maintain the sustainability of eel production in Poso Waters in 2020-2021. Perspective plans are presented in this paper to provide input to the local government of Poso Regency and business actors who are directly or indirectly involved (Fig. 4.). The recommended perspective plan in eel management is as follows:

Socialization of the eco-biological nature of eels as catadromous fish
The level of community knowledge about eel resources in Poso is still deficient. The level of knowledge of fishers and the community on the eel and the need for eel conservation was only 20% [12]. As catadromous fish, eels are not well understood by the community and fishers, especially on eel's life cycle, which must migrate to the sea to reproduce. The topics for socialization are the understanding of the eel's three life cycle phases, the ocean phase, the estuary phase, and the freshwater phase [10,23] (Fig. 5). As previously mentioned, the adult eels need to migrate to the sea. Therefore the path for migration is essential, and should be no obstacles along the migration path. Adult eels caught by waya masapi are adult eels that will migrate to spawn. The migration process of adult eels to spawn occurs throughout the year. The peak of migration occurs in January to mid-August (from the rainy season to the beginning of the dry season) [4]. The process of gonad maturation in adult eels occurs when they migrate to the sea [25]. Glass eel is a juvenile of eel that migrates through river estuary to grow and develop in freshwaters such as rivers, swamps, and lakes. As a migrating fish, the obstacles that occur due to the capture or failure of the eel to reach the ocean for downstream migration and reach fresh water in upstream migration can break the eel's life cycle.

Establishment of conservation areas and regulation on eel fishing
Conservation of fish resources is an essential part of fisheries resources (fisheries sustainability) and the community's economy (economic sustainability). An effort to protect these resources is by providing suitable locations to support the eel's life. The survival of the eel as a migratory fish is determined by the presence of a portion of the adult eel population that successfully migrated to reproduce and a portion of the glass eel or elver population to grow into adult eels. According to research [26], the sustainability of eel fishery production is highly dependent on the availability of glass eels from nature and the success of adult eels migrating to the sea to spawn. Poso Regency has established another protected area by stipulating it as a corridor area for protected species or marine biota. Poso Regency Regional Regulation No: 8 the year 2012 concerning Spatial Planning of Poso Regency for 2012-2032 stipulates that the Tomasa River area is designated for eel conservation area [27].
Nationally, the capture of eels is regulated through several regulations. The restriction on the size of eels that can be exported is 150 g/Ind. [28]. This restriction is intended for glass eel size of 0.13-0.20 g/Ind. Cultured to a specific size to provide added value to fishers before being exported. This regulation can encourage the use of eel seeds for cultivation purposes at local and national levels. Regarding the regulation of catching adult eels in 2020 [29], a ban has been issued to catch A. bicolor, A. interioris at sizes above 2 kg, and A. marmorata and A. celebesensis above 5 kg all times. The regulation also imposes a ban on catching glass eels at 27 th -28 th in the new moon phase. The regulations are intended to maintain the sustainability of eel resources. The regulation needs to be socialized in the Poso Regency community because, based on brief interviews with fishers in the Tentena and the Poso River estuary, they are not aware of the existence of this regulation.

Increasing the eel population through restocking program
The eel population in the wild can increase through restocking programs. In Europe [9], restocking is considered an effort to manage and restore eel populations. Other efforts are by increasing natural recruitment and habitat improvement or restoration. Restocking eels in Poso waters has been recommended as the result of several studies. Restocking eels can be done at sizes more than 15 cm. Eel seeds are obtained from glass eels caught in the Poso River estuary and raised first [12]. Maritime authorities and research institutes in Sweden reported that restocking and natural recruitment of eels could maintain 90% of the adult eel population (silver eel) [30].
Eel restocking must be done regularly so that the impact of its success can be felt. The essential things in restocking eels are the size of the eel stock, stocking location, and stocking time. The initial stages in the restocking process can be started from glass eel enlargement to elver. The results culture of the glass eel is then adapted to the lake. The adaptation process in the lake can be done using a pen culture system or a floating net cage system. The length of the elver adaptation process in the lake is adjusted to the size of the stocking target. The mechanism of the eel restocking program in Lake Poso can be seen in Fig. 6.  Fig. 6. The mechanism of the eel restocking program in Lake Poso.

Integration fishing activities and aquaculture
Capture fisheries and aquaculture can be integrated to provide value for business actors (fishermen). The number of fish capture households in Poso Regency in 2018 was 509 households. The number of aquaculture households was 1091 households [31]. Fishers who catch glass eels can combine their activities into aquaculture. Catching glass eels in estuaries generally lasts a short 5-7 days per month. Glass eel storage time before being sold to collectors or cultivators is also limited to 2-3 days. Many glass eel catches cannot be sold in certain conditions where there is less demand for eel seeds. The glass eel eventually died and was sold at a low price. In such conditions, some glass eels can be raised by fishermen to a particular stage so that their utilization can be more optimal. The integration of capture fisheries activities into aquaculture can be a solution in utilizing the captured glass eel to be maintained at a particular stage to be ready for further cultivation.
The Department of Maritime Affairs and Fisheries of Poso Regency already has an eel village development program. In this program, the cultivation for eel enlargement is started in designated villages. This program includes glass eel fishers to provide the need for eel seeds for cultivation on time. If there is a failure in the cultivation process, the activity can be carried out again because the fisher can still provide glass eels as seeds for cultivation. The estimation of eel production from aquaculture can reach up to 1,000 tons/year if it raises 20% of the glass eels that enter Poso waters [7]. Eel conservation, eel cultivators who utilize glass eel from the Poso River estuary must release some of their cultivated into Poso waters. Meanwhile, adult eel fishers must buy glass eels to be released into nature. As recommended by research [7], if a fisher catches 5 kg of adult eel, he must buy and then release 1 kg of glass eel into the lake or river.

Developing eel culture technology through the segmentation production
The eel cultivation in the world began to be carried out around the beginning of the 20th century, namely in Japan, China, Korea, and Italy [32]. In Indonesia, eel cultivation activities began in the early 1990s. Currently, eel cultivation has emerged in several aquaculture companies in Sukabumi, Karawang, Bogor, Bandung, Jogjakarta, Cirebon, and Banyuwangi. The need for glass eel tends to increase along with the development of eel cultivation technology in the community and is related to the high demand for eel commodities globally.
Cultivation of eels in the small and medium-scaled business community is still constrained by the high price of glass eels, the length of culture, availability of the feed, and maintenance of the facilities. These obstacles can be overcome if the production segmentation is created to have a mutually supportive cultivation chain. In fish culture, there are two business segments, namely the hatchery and the enlargement. This segmentation model is commonly found in gourami (Osphroenomus gouramy), tilapia (Oreochromis niloticus), and carp (Cyprinus carpio). In eel culture, aquaculture segmentation can be done in enlargement segmentation. The segmentation can be separated into a) from glass eel (0.13-0.2 g) to elver 1 (1-3 g), b) elver 1 to elver 2 (3-5 g), c) elver 2 to fingerling (10-20 g), and d) fingerling to consumption size (200-300 g). The production time from glass eel to consumption size can reach 1-1.5 years. This eel culture segmentation creates market opportunities for business actors in a not too long time. The crucial period in the segmentation of eel production is in the first segmentation, namely from glass eel to elver. In this period, good facilities and expertise are needed in rearing glass eels to elvers.

Developing an eel migration monitoring system
The success of eel migration is significant in determining its survival. The migration is divided into the downstream migration of adult eels and the upstream migration of larvae and young eels. Monitoring of migration process is essential to ensure the sustainability of its population in nature. The information on eel migration is obtained from the fish catch recorded by an institution or data collected by researchers [4,7,19,20]. However, the actual number of eels that migrate cannot be known with certainty. During the upstream migration process in the estuary, the number of glass eels can still be calculated manually from the recruitment rate.
Data on eel migration in 2001 showed that the number of migrated adult eels from Lake Poso to the sea ranged from 0-323 eels/month or an average of 138 eels/month [4]. The number of migrated glass eels entering the Poso River during new moons ranged from 187,200-769,920 glass eels/night [19]. Compared to the study in 2011-2012, the number of glass eels migrating from the Poso river estuary reached 35,000,000 ind./year, while the adult eel migrating to the sea was 1000 eels/year [7]. However, these eel migration numbers come from estimation and calculations using various approaches; hence, the eel migration information results may have many interpretations.
The development of an eel migration monitoring system is a way to determine the number of migrating eels. The monitoring system can be developed by utilizing hydroacoustic technology. The hydroacoustic method is widely used to estimate stock abundance, geographic map distribution, and ecological information [33]. However, this technology has never yet been used to estimate the abundance of eels in nature. This method can be an alternative to estimate the abundance of eels during migration and monitor their behavior. According to [34], acoustic surveys using quantitative echo sounders have been commonly used to estimate fish abundance and biomass to provide data and information for fisheries resource management. Hydroacoustic technology can be carried out in the lake or river waters, which are usually turbid, so video or visual observations are minimal. This method can be tried in monitoring eel migration and becomes a challenge in future eel migration research.

Building cross-sectoral forums and making joint action programs
Collaborative management between different sectors is now an approach in managing the environment and biota resources. This collaboration involves several components: the government, community, business actors, universities, and research institutes. In the management of Lake Poso, guidelines have been prepared for the action program to save Lake Poso, namely "Germadan Danau Poso" [3]. In this Germadan, programs such as (1) application of science and technology, (2) institutional development, and (3) increasing community participation in lake management and conservation are planned.
At present, the management of the environment and its resources is still carried out on a sector and regional basis. Therefore, management activities often are based on the interests of each sector. Management on eel fishery should include the migration processes from upstream to downstream and vise versa involving the government, private sector, research institutions, educational institutions, and the community. As for Poso eel resources management, the actors that should be involved are the Government (Marine and Fisheries Service, the Environment Service); Private Sector (PT. Poso Energy); Research Institutes: (LIPI, BRSKP; Educational Institutions: Local universities); Community (N.G.O.s: Institut Mosintuwu, WWF Indonesia) and Indigenous institutions. In implementing activities, it is necessary to make an integrated action plan that involves all parties. The research program of "LPDP Rispro Invitasi" 2020-2021, conducted by the Research Center for Limnology-LIPI, tries to involve all components in Poso Regency to collaborate in the sustainable management of eels. The joint programs carried out include: 1) Data collection of migrating eels from Poso Lake and Poso River estuary.
2) Monitoring of eel migration on the fishway in the Poso hydropower plant area.
3) Development of eel culture through production segmentation that can be applied to the community. 4) Restocking program to increase eel population and production

Proposing the Poso eel research and conservation center
The Lake Poso ecosystem has unique characteristics. Lake Poso is one of two lakes in Indonesia known as ancient lakes [2]. Various types of biota were found living in this lake, namely fish, bivalves, gastropods, crustaceans, plankton, reptiles and birds, and higher plants. Ten endemic fish species live in Lake Poso and five species of eel [4]. Eels are of economic value, and as catadromous fish, eels have unique ecological properties and attracted many national and world researchers in conducting research. As a fishery commodity, the eel has a high nutritional content, so that the need for eel as food is essential. The sustainability of eel production is the hope of many people in Poso and perhaps in the world.
Poso Regency is a regency with the authority to manage Lake Poso and the biota that live in it. Poso Regency has received recognition for intellectual property as the area of origin of the A. marmorata eel from the Ministry of Law and Human Rights by granting a geographical indication certificate in 2019. The Poso Regency Government has determined eels to be one of the leading commodities stated in the Regional Medium-Term Development Plan (RPJMD) 2016-2021. The Poso River estuary is the largest glass eel-producing area in Indonesia. The glass eel from this estuary has been the source for eel culture not only in the area but also outside Poso Regency.
Decreases in eel catch in Poso have been reported in several studies [7,12]. Intensive fishing activities on adult eels and glass eels, barriers to migration pathways, and the influence of other environmental pressures are thought to cause the decline in the Poso eel population. Several points above encourage the existence of special units in conducting research and conservation of Poso eel. This institution can become a center for research studies collaborating with other research institutions nationally or within the region. The research conducted covers aspects of biology, environment, population dynamics, and exploitation. LRPT also conducts research collaborations with other agencies. It is also hoped that a similar institution can be established in Poso.

Conclusions
The sustainability of the Poso eel is determined by the success of the eel migration process. The migration of adult eels to the sea and young eels to freshwater habitats must continue. The planning perspectives that can be proposed in conserving the Poso eel resources are 1) Promoting an understanding of the biological and ecological characteristics of eels as catadromous fish; 2) Determining the existence of conservation areas and regulation on eel fishing; 3) Recovering and increasing eel population through restocking 4) Synergizing fisheries and aquaculture activities to provide added value to the community; 5) Developing eel cultivation technology through size segmentation system; 6) Developing eel migration monitoring system; 7) Establishing a cross-sector communication forum and create a joint action program in the eel resources management; 8) Establishing a Poso eel research and conservation institute.