Habitats Other target species Non target species

Moody Marine Ltd Page 16 • P. pelagicusmegalopae usually are found in settling areas not far from the coastline and do not need a mechanism for long-distance transportation such as attachment to jellyfish as is the case in Cancer magister. • Fast larval development of P. pelagicus means that there is no need for long distance transport. • P. pelagicuszoeae larvae are positive phototactic and negative geotactic, older megalopae are positive geotactic • Spatial distribution of P. pelagicus larvae is determined by 3 main factors: i small-scale patchiness as a result of schooling behaviour, ii local currents systems and iii behaviour, particularly attaching behaviour, in older megalopae, explaining their relative abundance in seagrass beds and coral reefs. • Megalopae swim to maintain themselves in the water column, not to purposely move actively in a horizontal manner • Local currents including wind induced surface currents can have an important impact on the recruitment of P. pelagicus populations, e.g. by transporting larvae to deep areas where settling is not possible, contributing the very high mortality during larval stages. Larvae can be transported by wind-induced currents for over two weeks at 6-7 km per day. • Salinity tolerance of zoea of P. pelagicus ranges from 16.2-35 ppt. Diurnal tidal pattern salinity fluctuations in river mouths and irregular amounts of rainfall can cause very strong salinity fluctuations within a very short time, which may render certain areas inhospitable for zoeae even when average salinity levels are within their tolerance range. • Megalopae are believed to be more tolerant to low salinity levels. • Temperature range for normal development of P. pelagicus lies between 18 and 35 ˚C. Megalopae of P. pelagicus, another Indo-Pacific portunid, have also been observed to be photopositive and more active when illuminated in offshore water Webley Connolly 2007 Juvenile recruitment success is dependent on factors such as i favourable ocean currents that transport eggs and larvae, and ii the availability of food and nursery habitats i.e. seagrass or other suitable marine vegetation for juveniles N. 2006. The settling postlarvae of P. pelagicus, as distinct from benthic juveniles, were defined as those with a carapace width CW of 20 mm or less. This definition was based on Potter et al. 1983 finding that 25 mm CW was the modal width for new recruits of P. pelagicus caught in the entrance channel of the Peel-Harvey inlet in Western Australia. They found few individuals less than 30 mm CW in the estuary itself. Settlement of the postlarvae of P. pelagicus on seagrass habitat ensures that they select a habitat with shelter and food. They have a preference for structured nursery habitats and recruit to suitable habitats adjacent to established nursery habitat, a pattern similar to that of some other crustaceans. Crabs mate in coastal and estuarine waters. Estuary-based females then migrate to sea to spawn. Blue Swimmer Crabs are short-lived, with a maximum age of about three years and maximum carapace width of 200 mm. Maturity is reached at about one year, and recruitment to lower fisheries occurs at an age of about 18 months. Due to this life cycle, crab stocks have relatively fast rates of replacement and can recover quickly from depletion. Despite the drift and movement of eggs and larvae of P. pelagicus, there is no general pattern of source-sink relations. Local current patterns and overall conditions determine the distribution and settlement of the young crabs and their chances of survival. This is not to say that larval drift cannot be an issue as part of management of a crab fishery Ingles Braum 1989.

4.5 Habitats

Although P. pelagicus is frequently confined to coastal marine waters and particularly embayments Moody Marine Ltd Page 17 Ingles Braum 1989, it also often enters estuaries early in life and remains there for many months, during which period it increases markedly in size Smith 1982. Potter de Lestang 2000.Salinity, and in temperate regions water temperature, determine the distribution of P. pelagicus. They live in a wide range of inshore and continental shelf areas, including sandy, muddy or algal and seagrass habitats from the intertidal zone to at least 50 metres in depth. They move to deeper water as they age and in response to changes in water temperature and inshore salinity. 5 STOCK ASSESSMENT There is no fisheries research programme covering P. pelagicus in Vietnam. The work has been extracted from other work activities. The most specific to the location Philippines is from Ingles Braum 1989. 6 ENVIRONMENTAL INTERACTIONS

5.1 Other target species

Blue swimming crabs are the only target species.

5.2 Non target species

Other species caught comprise slipper lobster, gastropods, shark Nebrius ferrugineus and other shark species, rays `and soles. None of the by-catch species is individually more than 5 of the total. Little is known about predation on this species, but marine turtles, sharks, rays and large fish are likely predators on blue swimming crab, with crabs being most vulnerable to predation immediately after moulting Kailolaet al., 1993. One of the shark species identified was a Tawny shark Nebrius ferrugineus. These are n octurnal animals. Tawny nurse sharks tend to spend the day resting in piles of two dozen or more individuals inside caves or under ledges. They are active-swimming predators at night. They are not listed as vulnerable species in the Vietnamese “Red Book’ 5 . However, because of their low fecundity, the quantities caught are sufficiently worrying to suggest a problem.

5.3 Benthos impact