Rotational culture of the sea cucumber Holothuria scabra with the shrimp Litopenaeus stylirostris: trade-off between growth performance and bioremediation,

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Rotational culture of the sea cucumber Holothuria scabra with the shrimp Litopenaeus stylirostris: trade-off between growth performance and bioremediation, comparison with shrimp monoculture. Hochard S.1, Lemonnier H.2, Letourneur Y.3, Lorrain A.4, Royer F.2, Hubert M.2 1 ADECAL Technopôle, 1 bis rue berthelot, BP 2384, 98846 Nouméa cedex, NEW CALEDONIA 2 IFREMER, LEAD NC, Station de Saint Vincent – 98812 Boulouparis, NEW CALEDONIA 3 Université de la Nouvelle-Calédonie, Laboratoire LIVE, BP R4, 98851 Nouméa cedex, NEW CALEDONIA 4 IRD LEMAR, Centre IRD Nouméa, BP A5, 98848 Nouméa cedex, NEW CALEDONIA

Intensive fishing=> massive reduction of naturals stocks. General context Sea cucumber fisheries represent 17 000 T.y-1 in dry weight (56 à 130 millions of US$.) Intensive fishing=> massive reduction of naturals stocks. Attractive aquaculture perspectives In china the sea cucumber aquaculture production reach 3 200 T.y-1 (dry weight) for the temperate species Apostichopus japonicus. The aquaculture of the tropical species Holothuria scabra is still at its beginning. Purcell et al. 2013

+ No cost for structures. - Expose to natural alas. Different aquaculture methods Sea ranching: + No cost for structures. - Expose to natural alas. Necessity of an important maritime concession. Farming in pens + low cost of production, apart the pens. - Expose to natural alas. Limited by the carrying capacity of the environment. Farming in ponds + Semi-controlled system. + Higher productivity. - Cost link to the structures, energy and the feed.

Bioremediation H. scabra = Benthic detrivorous species. Agudo H. scabra = Benthic detrivorous species. Its farming could be articulate with a principal species, here shrimp, with a double benefit: H. scabra farming could benefit from the organic matter produced/ accumulated by the culture of the principal species, sustaining its growth. Detritus assimilation by H. scabra could have a beneficial effect on the system quality and improving the environmental condition for the rearing of the principal species. Former studies showed that direct co culture may not be viable (Bell et al., 2007).

Cascade culture between the shrimp L. stylirostris and H. scabra. Rotational culture The HOBICAL program: How to insert the farming of H.scabra in the New-Caledonian aquaculture based on shrimp farming? Cascade culture between the shrimp L. stylirostris and H. scabra. Rotational culture between the shrimp L. stylirostris and H. scabra.

Cascade culture between the shrimp L. stylirostris and H. scabra. Rotational culture The HOBICAL program: How to insert the farming of H.scabra in the New-Caledonian aquaculture based on shrimp farming? Cascade culture between the shrimp L. stylirostris and H. scabra. Rotational culture between the shrimp L. stylirostris and H. scabra. Two goals : Maximize the production performances of H. scabra. Bioremediate the pond in order to enhance the production performances of the shrimp L. stylirostris.

Material and methods Two step experiment in mesocosms: Step 1: H. Scabra farming Study of different culture protocol on the growth performances and on the environment evolution. Step 2: Shrimp farming Comparison of the performances of rotational culture with shrimp monoculture Experimental structures: 16 mesocosms of 1,75 m2 (1600L)

Semi-intensive shrimp pond Material and methods 2013 2014 2015 Semester 2 Semester 1 Semester 2 Semester 1 Holothuria non fed Shrimp Holothuria Shrimp Rotational culture Holothuria fed Shrimp Holothuria Shrimp Classic dry-out Shrimp Shrimp Shrimp Shrimp monoculture Long dry-out Shrimp Shrimp New sediment Shrimp Step 1 Semi-intensive shrimp pond Step 2

Food supply (corn waste) Material and methods Step 1: Study of different culture protocol on the growth performances and on the environment evolution. No food supply Food supply (corn waste) Nutrition protocol High density (6 ind.m-2) Non fed fed Control (no animals) Low density (3 ind.m-2) Low density

Production performances Feeding led to a better growth at the beginning of the experiment. After 100 days, lower growth in spite of more favorable temperatures.

Production performances Lower density led to constant growth, with higher mean weight.

Production performances Lower density led to constant growth, with higher mean weight. Survivals were above 80% for all the treatments. The carrying capacity of the system was equivalent for all the treatments at the end of the experiment. =>Feeding might allow faster growth but cannot outcome the carrying capacity of the system.

Bioremediation performances The non feed treatment is equivalent to the control. Feeding led to an enrichement of the sediment. Bioremediation appeared to depend of the rearing strategy.

Conclusions of step 1 Lowest production performances Best “bioremediation” Best production performances Lowest “bioremediation” Holothuria non fed Holothuria fed

Impact on the next shrimp rearing Step 2: Comparison of the performances of rotational culture with shrimp monoculture. Holothuria non fed All the mesocosmes received post larvae with a density of 20 shrimp .m-2 . The experiment last for 120 days, from March to June Holothuria fed Classic dry-out Long dry-out New sediment

Environmental characteristics of the sediment at the beginning of the experiment New sediment Long dry-out Holothuria non fed Holothuria fed Classic dry-out pH 6,87 7,15 7,33 7,21 6,84 Redox (mV) 68,1 18,3 19,0 24,1 41,9 Chl a (mg/m²) 16,6 66,8 119,7 120,5 147,2 OM (%) 1,7 1,6 2,0 2,2 2,3 NH4 (µM) 125 283 65 144 1437 GPP (µM/h) 6999 11943 5577 7264 8268 R (µM/h) -2639 -3594 -4550 -4764 -4513

New sediment Long dry-out Holothuria non fed Holothuria fed Classic dry-out pH 6,87 7,15 7,33 7,21 6,84 Redox (mV) 68,1 18,3 19,0 24,1 41,9 Chl a (mg/m²) 16,6 66,8 119,7 120,5 147,2 OM (%) 1,7 1,6 2,0 2,2 2,3 NH4 (µM) 125 283 65 144 1437 GPP (µM/h) 6999 11943 5577 7264 8268 R (µM/h) -2639 -3594 -4550 -4764 -4513

New sediment Long dry-out Holothuria non fed Holothuria fed Classic dry-out pH 6,87 7,15 7,33 7,21 6,84 Redox (mV) 68,1 18,3 19,0 24,1 41,9 Chl a (mg/m²) 16,6 66,8 119,7 120,5 147,2 OM (%) 1,7 1,6 2,0 2,2 2,3 NH4 (µM) 125 283 65 144 1437 GPP (µM/h) 6999 11943 5577 7264 8268 R (µM/h) -2639 -3594 -4550 -4764 -4513

New sediment Long dry-out Holothuria non fed Holothuria fed Classic dry-out pH 6,87 7,15 7,33 7,21 6,84 Redox (mV) 68,1 18,3 19,0 24,1 41,9 Chl a (mg/m²) 16,6 66,8 119,7 120,5 147,2 OM (%) 1,7 1,6 2,0 2,2 2,3 NH4 (µM) 125 283 65 144 1437 GPP (µM/h) 6999 11943 5577 7264 8268 R (µM/h) -2639 -3594 -4550 -4764 -4513

Very similar zootechnical performances between the treatments

Conclusion: Holothuria farming: Shrimp farming: Production performances: Feeding might ameliorate growth rate but did not allow to outcome the system carrying capacity. Lower density permitted much better zootechnical performances. Bioremediation: Feeding led to an enrichment of the system. No clear differences between the control and the non fed treatment. Shrimp farming: The sediment characteristics were mainly influence by the dry out time. For similar dry out time, rotational culture presented cleaner sediments. Zootechnical performances were comparable between the treatments.

Perspectives: We are analyzing Isotopes and fatty acid data Identify the food sources of H. scabra during the experiment. Find a more adapted aliment. “Bioremediation?” Make medium scale zootechnical experiment of H.scabra farming. Co culture with other species (fish…) appear as the most attractive scenario.

Thank you. FAMB