The spider crab Maja squinado is restricted to the Mediterranean Sea, and as captures of this species became very rare in the last decades, it is a protected species. To improve spider crab production in experimental or commercial hatcheries and allow the future success of restocking programmes, knowledge of larval growth and biochemical characteristics is mandatory. In the present study, larvae from 4 different batches were studied. Larvae were examined to determine the larval instar and moulting stages. In each moulting stage for all larval instars, carapace length, dry weight, ash and proximal composition (protein, carbohydrates and lipids) were measured. Metamorphosis began at 14 d posthatching (dph), with metamorphosis to the first juvenile crabs completed in about 90% of the specimens at 17 dph. Survival dropped from 59. 25 ± 19.53% to 33.49 ± 19.53% between the zoea II and megalopa stages, and only 7.74 ± 1.94% of newly hatched larvae (NHL) reached the first juvenile crab stage. NHL weighed 120.40 ± 18.95 µg, increasing their dry weight and ash content 6-fold after metamorphosis. Dry weight also increased through the moulting cycle in each larval instar, while ash content was higher in early premoult stages. Proximal composition increased between 8-and 6-fold from NHL to megalopa in the premoult stage and then decreased 2-fold during metamorphosis. Lipid and protein content varied among moulting stages from the postmoult to the premoult stages, with more significant alterations seen during the megalopa instar stage.KEY WORDS: Decapoda · Majoidea · Larval instars · Moult stages · Size · Biomass · Protein · Lipids
Resale or republication not permitted without written consent of the publisherAquat Biol 20: [13][14][15][16][17][18][19][20][21] 2014 species included in the Action Plan for the Mediterranean (UNEP 1996). The Bern Convention on the conservation of wildlife and natural habitats, opened for signature on 19 September 1979 and ratified by the EU in Strasbourg in 1997, established M. squinado as a species of protected wildlife in the Mediterranean (Anonymous 1999) and its exploitation in Spain is regulated by general courts (Anonymous 1998).Re-stocking is one of the options for allowing depleted stocks to recover. The restocking programmes include plans for evaluating the stock after releasing cultured individuals of the target species, and when recovery is sufficient, limited fisheries can be established in the area (Bell et al. 2008, Lorenzen et al. 2012. Overall, the focus has been on developing methods for mass-producing environmentally fit juveniles and releasing them in ways in which they survive without affecting the ecosystem or genetic diversity of wild stocks. Trial release programmes for enhancing or improving stocks of several severely depleted crab species have been implemented in Asia and North America, using aquaculture techniques as a tool for producing juveniles. Examples are the swimming crab Portunus trituberculatus (Okamoto 2004), the blue crab Callinectes sapidus (Zo...