Potential implications of harvesting ornamental sabellids from coral reefs

download Potential implications of harvesting ornamental sabellids from coral reefs

of 1

Transcript of Potential implications of harvesting ornamental sabellids from coral reefs

  • 8/13/2019 Potential implications of harvesting ornamental sabellids from coral reefs

    1/1

    Potential implications of harvesting ornamental sabellids

    from coral reefsMurray J. M. 1,2and Bonner, A. J. 3.

    1. Cefas, Pakefield Road, Lowestoft, Suffolk, NR33 0HT. [email protected]

    2. C3 Philippines, Barangay Salvacion, Busuanga, Palawan, Philippines [email protected]

    3. Flint Cottage, Norton Subcourse, Norfolk, NR14 6RS .

    Results

    Collection and implication Conclusions

    References

    MotivationCollection of live invertebrates from coral reefs has increased dramatically in response to the

    growing marine aquarium industry and currently, more than 500 species (excluding corals) aretraded. Sessile and conspicuous species have been highlighted as a riskgroupdue to the potentialimpacts of over-collection. Ornamental fan worms such as sabellids are routinely traded and at

    present, all specimens are collected from wild sources. Sabellids build their own mucoid-sediment

    tubes which attaches to the surrounding reef framework. Very little is known about their population

    ecology and therefore an assessment of the likely impact of their removal to the surrounding coralreef community is difficult. The Philippines is one of the biggest exporters of the marine aquarium

    trade and was used as a case study to investigate the population ecology of ornamental sabellids.

    [1] Hill & Wilkinson, 2004. Methods For Ecological Monitoring Of Coral Reefs : A Resource For Managers.Version 1. Australian Institute of Marine Science ( AIMS), Townsville, Australia. 117 p.[2] MurrayJ, Watson G, Bentley M, Giangrande A (2012) Managing the marine aquarium trade: revealingthe data gaps using ornamental polychaetes. PLoS One, 7 (1). e29543. ISSN 1932-6203

    10.1371/journal.pone.0029543.[3] MurrayJ.M, Watson GJ, Bentley MG, Giangrande A (2013) Regeneration as a novel method to culturemarine ornamental sabellids. Aquaculture,410-411, 129-137.

    Sabellid distribution and density

    Associated habitat type

    Methods

    Sabellid population dynamics

    Population densities of sabellids were quantified

    at each site using five 25m long invertebrate belt

    transects with a 2m cross line [1]. Swimming

    observers spent at least 25 minutes search timealong each belt transect and recorded: a count;

    genus-level identification; position in meters along

    the transect; a measurement of each specimens

    branchial crown in cm; and a description of thehabitat/coral species with which the specimen

    was associated.

    Study area and site selection

    Fig 1. Location mapof Busuanga Island and survey locations.

    Figure 2a, b, c, d. Species from

    the genus Sabellastarte . Figure

    2e, f, g. Bispira sp Figure 2h,

    Megalomma sp. Figure 2i.

    Sabellasp.

    Two hundred and ninety nine individuals wereassessed across the 6 sites during this survey,

    62% of which were recorded the Concpcion non-MPA site.

    As the identification of sabellids is notoriously

    problematic, worms were grouped based on

    genus or possible genus (Fig. 2). The mostcommonly observed group was Sabellstarte

    (Fig 2a, b, c, d), and is notably the most popular

    ornamental group in the trade [2].

    Crown diameter ranged from 150mm on thesmallest individuals but up to 600mm in the

    largest. A mean crown diameter of 380mm was

    calculated, a smaller diameter than the average

    size which is recorded in worms imported by themarine aquarium trade [3].

    The municipality of Busuanga is part of the Calamaines Group of Islands located in thenorthernmost part of the province of Palawan in the Philippines (Fig 1). Six coral reef sites

    located were selected; Conception MPA, Conception non-MPA, Black Island, Lajo, Maglalambay,and New Busuanga.

    Sabellids were found to embedded within coral,

    on coral rubble or buried within sandy substrate.

    The majority, 49% of individuals, were

    embedded within Mil lepora sp. (Fig 3a,b).Pori tes sp. also played host to sabellids with

    37% of worms associated with this slow growing

    coral (Fig 3c,d) and 18% were found attached to

    other coral species including; Goniastrea sp.(Fig 3e,f) and Montipora sp. (Fig 3g,h). Only

    14% or worms were on coral rubble(Fig 3i) and

    6% in sand(Fig 3j).

    a

    e

    Fig2.

    dc

    ba

    ih

    gf

    dc

    b

    h

    f

    i

    g

    e

    jFig3.

    The majority of sabellids (88%) surveyed inBusuanga were found in close association with

    species of coral.

    Tubes were embedded within the coral with only

    the branchial crown visible.Interviews with aquarium collectors established

    that tube removal was achieved by inserting a

    metal rod into the coral structure to release the

    mucus attachment of the worm tube to the coral.

    Preliminary analysis shows worms are attached to

    slow growing and delicate coral species (eg. Porites

    sp.).

    Removal is a delicate procedure with both worms

    and coral easily damaged.

    mailto:[email protected]:[email protected]://www.google.co.uk/url?sa=i&source=images&cd=&cad=rja&docid=toSrhrLNuDIW_M&tbnid=B39FcmcBYQ5FAM:&ved=0CAgQjRwwAA&url=http://www-users.york.ac.uk/~csww500/&ei=jEXmUbaCKrON7AaUpIH4Bw&psig=AFQjCNHQVqBw_c9XOF-s7lJ001f-x5wGmg&ust=1374131980805451mailto:[email protected]:[email protected]:[email protected]:[email protected]