Expansion of global sea cucumber fisheries buoys exports
Chantal Conand 1,2
1. Université de La Réunion, ENTROPIE, 97715 Saint Denis messag, La Réunion; conand@univ-reunion.fr
2. Muséum National Histoire Naturelle Paris, rue Cuvier, 75005 Paris, France
Recibido 07-VII-2016. Corregido 25-ii-2017. Aceptado 23-VI-2017.
Abstract: The sea cucumber fisheries have expanded during the past two decades, at a faster rate than the management capacity. The exploitation is now qualified as ‘serial’ and ‘contagious’. I present the most recent trends from the last six years of the FAO capture data. Hong Kong remains the most important market for the imports and re-exports of the processed products, mainly the dry “trepang” (or bêche-de-mer), but also other product forms, which raised difficulties for the analysis. The catches still increase. with new countries developing export fisheries, species targeted change and new products are traded. Rev. Biol. Trop. 65(Suppl. 1): S1-S10. Epub 2017 November 01.
Key words: holothurian; trepang; bêche-de-mer; statistics; trade; globalization; management.
Several sea cucumbers species (Echinodermata: Holothuroidea) are consumed traditionally, mostly by asiatic populations and their fisheries have been presented in detail (Conand, 1990, 1998, 2004, 2006; Conand & Byrne, 1993). For the Chinese consumption the holothurians are mostly processed in a dry product called Hai Shen, trepang or bêche-de-mer, depending on the region where they are fished. Foreign fisheries have been limited to the Indo-Pacific for a long time.
Given the development of China, an increase of demand for trepang occured during the 20th century, making the exploitation very valuable. It remained small scale fisheries (SSF) in most tropical countries, with fishers collecting the commercial species in shallow waters. The processing, traditionally artisanal, comprises several steps (Conand, 1990; Purcell, 2014a) to get a dry product of good quality; it is essential to get a good grade and therefore a good value. The dried products are then shipped to the main markets of Hong Kong, mainland China, Singapore, Taiwan (Conand, 1990; Conand & Byrne, 1993) and ‘China Towns’ in the large cities worldwide (Conand, 2015). The product now fetches high prices; for example, in Hong Kong the maximum price per kg exceeded 1 000 US$ (Purcell, 2014b).
The fisheries have expanded rapidly during the last decades (Conand, 2004; Anderson Flemming, Watson & Lotze, 2011; Purcell et al., 2013; Eriksson, Conand, Lovatelli, Muthiga, Purcell, 2015a; Fabinyi, 2016) from tropical Indo-Pacific countries where they are multispecific to worldwide tropical regions, as shown in the Latino-America where Isostichopus fuscus is the most valuable species, then to the temperate coastal regions and the overexploitation has become apparent.
Much attention is presently being paid to the fisheries management with an abundant recent literature (for example Friedmann, Purcell, Bell & Hair, 2008; FAO, 2010; Purcell, 2010; Purcell, et al., 2013, 2014; Eriksson, et al., 2015a; Conand, 2016). The management had first been questioned by FAO at the world scale, with publications and several international meetings, where regional syntheses were prepared (Conand, 1990; Lovatelli, et al. 2004; Toral-Granda, Lovatelli & Vasconcellos, 2008; FAO, 2010; Purcell, 2010). A first version of a book on commercially important sea cucumbers provides detailed informations on taxonomy, biology and distribution of 58 species (Purcell, Samyn & Conand, 2012a).
The question of CITES listing has first been deeply debated during an international meeting on holothuroids in Malaysia (Conand, 2004; Bruckner, 2006). It is still up-to-date, as shown by the results of the last CITES meeting in South Africa (2016) where the proposed holothuroids were not adopted for listing and the need for more discussions and agreements is still necessary, before adding species. Presently only Isostichopus fuscus from Ecuador is listed in Annex III. A good step forward would be to propose the teatfish group (Holothuria (Microthele) for listing, as the four species H. nobilis, H. whitmaei, H. fuscogilva, H. sp. ‘pentard’, presented in Purcell, et al. (2012a), are commercially very valuable large species, easy to recognize, alive as well as processed, a very important point for checking the trade and are largely overfished.
The IUCN listing has followed an international meeting in Colombia (Conand, et al., 2014a; Purcell, et al., 2014). It is effective for sixteen holothurian species with seven endangered and nine vulnerable (see http://www.iucnredlist.org/documents/RedListGuidelines.pdf). For Latin America only one species Isostichopus fuscus is listed as Endangered.
Given the differences in exploited species and in policies the regional scale has appeared the best to facilitate management. The Secretariat of Pacific Community (SPC) has been active on the topic with meetings and a specific journal, the SPC Bêche-de-mer Bulletin published yearly since 1990, giving the main findings and informations on the subject (see http://www.spc.int/coastfish/en/publications/bulletins/beche-de-mer.html).
Regional meetings (Sea Cucumber Ecosystem Approach Management, SCEAM) have been organized by FAO and other organizations in the tropical Pacific (FAO, 2012) and Indian Ocean (FAO, 2013). Other important regional projects and initiatives have come from the Australian Centre for International Agricultural Research (ACIAR), the Western Indian Ocean Marine Science Association (WIOMSA), with many publications and syntheses (Conand & Muthiga, 2007; Friedmann, et al, 2008; Muthiga & Conand, 2014; Eriksson, et al., 2015b).
Recent fisheries have also developed rapidly in the temperate and tropical parts of the Atlantic (Toral-Granda, Hamel and Mercier in Toral-Granda et al., 2008); several meetings were then organized in Cuba (2014), Mexico (2015) and regionally (Flores et al., 2016). Finally, the fisheries are developing in the Mediterranean sea (González-Wangüemert, Aydin & Conand,2014; González-Wangüemert, Valente, Henriques, Domínguez-Godino & Serrão 2016). Noteworthy is the present development of the interest for the biochemical use of the saponines and other components from holothurians (Honey-Escandon, Arreguín-Espinosa, Solís-Marín & Samyn, 2015; Gomes, Freitas, Duarte & Rocha-Santos, 2016).
It is therefore necessary to follow the most recent trends in captures and markets, at the different scales, international, regional and in the main producing countries. This will help enabling better decisions and management practices.
MATERIALS AND METHODS
The FAO capture data of holothurians, by country, for the last six years (FAO, 2009 to 2014) have been analyzed to be able calculate the mean tonnage (t p.a.) over this period for the main fishing areas (FAO zones). The data have been separated into two categories:
1. the traditional dry products bêche-de-mer (or trepang) whose processing results in a product weighing only 5 to 8% of the fresh weight.
2. the other products, frozen and in brine, whose weights do not differ too much from the fresh one. The data for the regions where they appear mostly as other products, are transformed into comparable dry weight, by taking 8% of the values which is a mean reduction coefficient during processing, despite it varies between the species (Conand, 1979, 1990; Purcell, et al., 2009, 2014a, 2016; Purcell, Hair & Mills, 2012b; Prescott, Zhou & Prasetyo, 2015). They are then compared with previous results.
Hong Kong statistics for holothurians comprise several categories (Table 1), with overall quantities in kg, for imports and re-exports under the following codes:
• 1190, fresh product for local consumption,
• 1910, frozen product from fresh or processed,
• 1990, dry or in brine.
The tonnages from the different categories cannot be summed, as the weights they represent, in comparison with the live animal weights, are different.
The category 1990 (dry or in brine) is then used here, in more details, to follow the countries of origin then ranked by percent of the total for the years 2013 and 2014.
These data (2013 and 2014) are presented and analyzed here. The results are then compared with previous results on this market (Conand, 1990; Conand & Byrne, 1993; Anderson, et al., 2011; To & Shea, 2012; Conand Shea & To, 2014b; Eriksson, et al., 2015b).
RESULTS
World holothurian fisheries: The world catches are presented by FAO regions, from the mean, calculated for the six years period 2009 to 2014, for the two main categories already defined in previous section (Table 2).
The most important fishing areas are clearly the Western Central Pacific (FAO zone 71) with 6 675 t p.a and the Western Indian Ocean (51) with 4 179 t p.a.
The main countries by FAO zone for the dry product category (1) are: for the Western Central Pacific (71): Indonesia followed by the Philippines, the Eastern Indian Ocean (57) again Indonesia, the Western Indian Ocean (51) Madagascar, the Pacific Eastern Central (Mexico). Using the transformed weights for the category (2), the main countries are: for the Pacific Northwest (61): Japan, the Atlantic Northwest (21): Canada, the Atlantic Northeast (27): Iceland.
Some important changes over time appear when comparing these results with previous publications (Conand & Byrne, 1993; Conand, 2004, 2006, 2008; Purcell, et al., 2013).
1. The catches have increased globally, despite overexploitation is mentioned by many observers. It is also possible that they are now better reported than previously.
2. The catches have much increased in temperate regions where the activity is more recent that the traditional tropical fisheries (Hamel & Mercier in Toral-Granda, et al., 2008; Purcell, et al., 2012b).
3. New countries presently exploit the holothurians in the temperate Atlantic and the Mediterranean (González-Wangüemert, et al., 2014, 2016).
Main sea cucumber markets: Several earlier studies have been published on the main markets: Hong Kong, Singapore, and Taiwan (Conand, 1989, 2001, 2004; Conand & Byrne 1993; Lovatelli, et al., 2004). The reciprocal exchanges between these markets have also been noted, showing that some products can arrive to an intermediate market, before going to the final one (Jaquemet & Conand 1999). The importance of Hong Kong market for sea cucumber is detailed elsewhere (To & Shea 2012; Conand, et al., 2014).
Recent publications have analysed Hong Kong statistics, attracting much interest and showing the ‘serial exploitation’ and spatial extension of the fisheries for holothurians from 1950 to 2006 (Anderson, et al., 2011) and more recently the ‘contagious exploitation’ showing, from data 1996 to 2011, the ‘fast moving system resembling an epidemic disease, where long-distance transport expedites large-scale expansion followed by diffusive local spread into neighbouring areas’ (Eriksson, et al., 2015b).
From the most recent data (2013 and 2014) presented here for Hong Kong, it appears that:
1. the imports have globally declined, but the weight units in the different categories are questionable;
2. the imports of live, fresh, chilled (code1190), intended for local consumption (as there are nearly no re-exports) have slightly increased;
3. the imports of frozen, fresh or smoked (code 1910) are very important, with more than 3 000 t each year, with a small, probably not significant, decrease in 2014; they are mostly re-exported;
4. the dried, salted in brine (code 1990) are even more important than the previous category, with more than 4 000 t each year; they are also mostly re-exported.
For this category (code 1990), the details by country, taking into account the countries contributing to at least 1% of the total, are presented in Table 3, with the ranks for the most important countries, which helps to observe the short term changes:
a. the number of countries still increases, from 29 countries in 2013 to 33 in 2014 ; this is in agreement with previous studies on this essential market.
b. Japan and Indonesia respectively keep the first and second rank.
c. some changes are noted between 2013 and 2014: the Philippines declined, while Mexico and China increased. The Solomons do not appear in 2014.
d. a new category concerns the prepared foodstuff (Table 1), which was not included in previous data, but the product is probably re-exported; more details are needed on this category.
DISCUSSION
These recent statistics on captures have not been examined in detail before this study; previous publications had used FAO data, results from regional meetings, or direct enquires to the fishing countries (Conand, 2004, 2008; Anderson, et al., 2011; FAO, 2013; Purcell, et al., 2013). From this analysis, it appears that the catches still increase in some regions, sometimes appear to stabilize, but this is often a bias due to the changes in species captured from high to lower value categories, or diminished in highly overexploited countries.
The sea cucumber resource has now attracted much attention, but it is still mostly not well managed. It appears that the statistics quality must be much improved, at the different levels. There are still much confusion between the live weights and the weights obtained from the various forms of processing. Another difficulty arises from countries having fisheries in two oceans (Atlantic and Pacific, for example for the latinoamerican region) and the data are not differentiated. As the fisheries are generally multispecific, the specific conversion values have to be evaluated for the species not previously captured; they have then to be adopted and used in international, regional and national instances.
The main markets statistics data are important to follow recent changes Hong Kong the main market is detailed here, but attention has to be paid to the others markets and their reciprocal exchanges, The most recent data for Hong Kong (2013-2014) are useful to show trends as the increase in number of exporting countries, but also need improvement in the categories changes and delimitation.
These sea cucumber resources need much better management practices, taking into account the socio-economic situations and the various actors (Purcell, et al., 2013). Some international and regional advances have appeared during the last decade, at the FAO initiative, in collaboration with other agencies and organizations. But during the same period the illegal fisheries have bloomed, their characteristics have been discussed to find the best ways to fight them (Conand, et al., 2015). As already presented by Eriksson, et al., (2015b) ‘multi-level and multi-scale decision making is urgently needed to control and mitigate the effects of contagious exploitation’.
Mariculture had long been used in China and Japan for the temperate species Apostichopus japonicus (Lovatelli, et al. 2004; Yang, Hamel, Mercier, 2015). Mariculture then developed on the tropical sandfish Holothuria scabra in Madagascar and other countries in the Indo-Pacific and the interest is raising on several species (Purcell et al, 2012b; Brown & Eddy, 2015). Several countries from the latinoamerican region (Ecuador, Nicaragua, Colombia) are presently conducting experiments on Isostichopus fuscus (see Lovatelli et al., 2004 and SPC Bêche de mer Bulletins). Mariculture is very important to the future conservation of the resources.
As large and abundant species in the benthic communities, the exploited holothurians play very important ecological roles in the bioturbation of the sediments where they live, in recycling nutrients by their nutrition, in being preyed (mostly as juveniles) thus transferring organic matter to higher trophic levels, and finally in enhancing biodiversity through the very large variety of symbionts and parasites they host (Eeckhaut, Parmentier, Becker, Gomez da Silva & Jangoux, 2004; Purcell, et al., 2016).
ACKNOWLEDGMENTS
I thank FAO for the recent capture data and Stan Shea (Bloom/Hong Kong) for the Hong Kong market statistics. Institut Français d’Amérique Centrale and the organizers of 3rd Congreso Latinoamericano de Equinodermos (Costa Rica) are warmly thanked for invitation and financial support. The comments of S. Purcell, I. Eeckhaut and J.J. Alvarado have been very valuable to improve the manuscript.
Resumen
Expansión de la pesca global de pepino de mar. Las pesquerías de pepino de mar se han expandido durante las últimas dos décadas, a un ritmo más rápido que la capacidad de gestión. La explotación ahora se califica como “en serie” y “contagiosa”. Aquí presento las tendencias más recientes, según los últimos seis años de los datos de captura de la FAO. Hong Kong sigue siendo el mercado más importante para las importaciones y re-exportaciones de los productos transformados, principalmente el “trepang” seco (o bêche-de-mer), así como otros productos, lo que plantea dificultades para el análisis. Las capturas siguen aumentando, nuevos países desarrollan pesquerías de exportación, las especies clave cambiar y se comercializan nuevos productos.
Palabras clave: holoturio; trepang; bêche-de-mer; estadísticas; comercio; globalización; gestión.
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Table 1
Hong Kong categories of sea cucumber products and recent statistics
Cuadro 1
Categorías de Hong Kong de productos de pepino de mar y estadísticas recientes
HK categories |
codes |
IMPORTS kg |
RE-EXPORTS kg |
||
2013 |
2014 |
2013 |
2014 |
||
Live, fresh, chilled |
0308 1190 |
89 996 |
108 404 |
9 240 |
|
Frozen, fresh or smoked |
0308 1910 |
3 963 866 |
3 261 949 |
3 261 011 |
3 138 295 |
Dried, salted, in brine |
0308 1990 |
4 941 709 |
4 427 520 |
4 563 166 |
4 761 700 |
Total |
8 995 571 |
7 797 873 |
7 833 417 |
7 899 995 |
|
Prepared foodstuff |
1605 6100 |
47 284 |
24 451 |
- |
20484 |
Table 2
Sea cucumber captures annual tonnage (t) mean for the period 2009 to 2014, by country and FAO fishing areas.
The means are presented from FAO yearly statistics (1) and corrected in equivalent dry weights (2) when the data
are in fresh weight (*), using 8% of fresh weight, as correction for weight loss during processing
Cuadro 2
Tonelaje de captura anual de pepino de mar (t) para el período 2009-2014, por país y por las zonas de pesca
de la FAO. Las medias se presentan a partir de las estadísticas anuales de la FAO (1) y se corrigen en pesos secos equivalentes (2) cuando los datos están en peso fresco (*), utilizando el 8% del peso fresco como corrección
para la pérdida de peso durante el procesamiento
TABLE 2 (Continued) |
|||
FISHING AREA Country |
code |
(1) t mean p.a |
(2) t dry p.a |
FISHING AREA Country |
code |
(1) t mean p.a |
(2) t dry p.a |
PACIFIC NORTH WEST |
61 |
12 590* |
1008 |
Japan |
10 073 |
||
Korea, Republic of |
2 517 |
||
ATLANTIC NORTH WEST |
21 |
5859* |
472 |
Canada |
5 006 |
||
United States of America |
854 |
||
ATLANTIC NORTH EAST |
27 |
1 624* |
128 |
Iceland |
1624 |
||
Spain |
|||
ATLANTIC CENTRAL WEST |
31 |
2 669* |
216 |
Bahamas |
9 |
||
Belize |
202 |
||
Haiti |
13 |
||
Honduras |
686 |
||
Mexico |
1144 |
||
Nicaragua |
613 |
||
United States of America |
1 |
||
Mauritania Atlantic Eastern Central |
34 |
18 |
|
Spain Mediterranean |
37 |
2 |
|
INDIAN OCEAN WEST |
51 |
1 555 |
1 555 |
Egypt |
3 |
||
Kenya |
31 |
||
Madagascar |
1336 |
||
Maldives |
131 |
||
Mauritius |
33 |
||
Mozambique |
0 |
||
Tanzania, United Rep. of |
0 |
||
Yemen |
20 |
||
INDIAN OCEAN EAST |
57 |
4 179 |
4 179 |
Indonesia |
484 |
||
Malaysia |
- |
||
Sri Lanka |
3695 |
||
PACIFIC NORTH-EAST |
67 |
1 632* |
128 |
Canada |
910 |
||
United States of America |
722 |
||
PACIFIC CENTRAL WEST |
71 |
6 675 |
6 675 |
Cambodia |
0 |
||
Fiji, Republic of |
75 |
||
Indonesia |
5003 |
||
Kiribati |
75 |
||
Malaysia |
0 |
||
New Caledonia |
368 |
||
Palau |
0 |
||
Papua New Guinea |
96 |
||
Philippines |
844 |
||
Solomon Islands |
199 |
||
Vanuatu |
1 |
||
Wallis and Futuna Is. |
16 |
||
PACIFIC CENTRAL EAST |
77 |
935 |
935 |
French Polynesia |
178 |
||
Mexico |
306 |
||
Nicaragua |
85 |
||
Tonga |
127 |
||
United States of America |
238 |
||
New Zealand Pacific Southwest |
81 |
17 |
|
PACIFIC SOUTH EAST |
87 |
182 |
182 |
Chile |
182 |
||
Ecuador |
- |
Table 3
Hong Kong main imports for 2013 and 2014
for sea cucumbers in category 1990, by countries
with percentage and rank
Cuadro 3
Principales importaciones de Hong Kong para 2013
y 2014 para los pepinos de mar de la categoría 1990,
por países con porcentaje y rango
Countries |
2013 |
2014 |
||
Total 4941 t |
Total 4427 t |
|||
% |
rank |
% |
rank |
|
US |
6 |
6 |
6 |
5 |
Aust & Oceanian Nes |
1 |
1 |
||
Australia |
2 |
2 |
||
Canada |
2 |
2 |
||
Colombia |
- |
1 |
||
Egypt |
1 |
- |
||
Fiji |
7 |
4 |
6 |
5 |
Greece |
1 |
3 |
||
Honduras |
1 |
|||
Indonesia |
10 |
2 |
10 |
2 |
Japan |
12 |
1 |
11 |
1 |
S. Korea |
1 |
1 |
||
Madagascar |
6 |
6 |
6 |
5 |
Malaysia |
1 |
1 |
||
Maldives |
1 |
1 |
||
Mauritania |
1 |
1 |
||
Mexico |
6 |
6 |
7 |
3 |
MicronFS-Palau |
1 |
|||
Mozambique |
- |
1 |
||
New Zealand |
- |
1 |
||
Nicaragua |
- |
2 |
||
Peru |
2 |
4 |
||
Philippines |
8 |
3 |
5 |
8 |
Russian |
2 |
1 |
||
Seychelles |
1 |
2 |
||
Singapore |
2 |
1 |
||
Solomon Island |
7 |
4 |
- |
|
Sri Lanka |
4 |
2 |
||
Taiwan |
3 |
3 |
||
Tanzania |
1 |
1 |
||
Thailand |
1 |
1 |
||
The Mainland China |
1 |
7 |
3 |
|
Tonga |
2 |
1 |
||
Turkey |
1 |
1 |
||
Yemen |
4 |
3 |
||
> 28 |
>32 |