The potential for translocation of marine species via small-scale disruptions to antifouling surfaces

Vessel hull fouling is a major vector for the translocation of nonindigenous species (NIS). Antifouling (AF) paints are the primary method for preventing the establishment and translocation of fouling species. However, factors such as paint age, condition and method of application can all reduce the effectiveness of these coatings. Areas of hull that escape AF treatment (through limited application or damage) constitute key areas that may be expected to receive high levels of fouling. The investigation focused on whether small-scale (mm2 to cm2) areas of unprotected surface or experimental ‘scrapes’ provided sufficient area for the formation of fouling assemblages within otherwise undamaged AF surfaces. Recruitment of fouling taxa such as algae, spirorbids and hydroids was recorded on scrapes as narrow as 0.5 cm wide. The abundance and species richness of fouling assemblages developing on scrapes ≥1 cm often equalled or surpassed levels observed in reference assemblages totally unprotected by AF coatings. Experiments were conducted at three sites within the highly protected and isolated marine park surrounding Lady Elliott Island at the southernmost tip of the Great Barrier Reef, Australia. Several NIS were recorded on scrapes of AF coated surfaces at this location, with 1-cm scrapes showing the greatest species richness and abundance of NIS relative to all other treatments (including controls) at two of the three sites investigated. Slight disruptions to newly antifouled surfaces may be all that is necessary for the establishment of fouling organisms and the translocation of a wide range of invasive taxa to otherwise highly protected marine areas.

[1]  E. Johnston,et al.  Differential effects of tributyltin and copper antifoulants on recruitment of non-indigenous species , 2008, Biofouling.

[2]  Mark P. Johnson,et al.  Hull fouling on commercial ships as a vector of macroalgal introduction , 2007 .

[3]  G. Swain,et al.  Managing the Use of Copper-Based Antifouling Paints , 2007, Environmental management.

[4]  J. Pettengill,et al.  Biofouling likely serves as a major mode of dispersal for the polychaete tubeworm Hydroides elegans as inferred from microsatellite loci , 2007, Biofouling.

[5]  H. Kawai,et al.  Occurrence and diversity of barnacles on international ships visiting Osaka Bay, Japan, and the risk of their introduction , 2007, Biofouling.

[6]  E. Johnston,et al.  Differential resistance to extended copper exposure in four introduced bryozoans , 2006 .

[7]  E. Johnston,et al.  Differential tolerance to metals among populations of the introduced bryozoan Bugula neritina , 2006 .

[8]  S. Kiil,et al.  Presence and effects of marine microbial biofilms on biocide-based antifouling paints , 2006, Biofouling.

[9]  Oliver Floerl,et al.  Starting the invasion pathway: the interaction between source populations and human transport vectors , 2005, Biological Invasions.

[10]  Oliver Floerl,et al.  A Risk-Based Predictive Tool to Prevent Accidental Introductions of Nonindigenous Marine Species , 2005, Environmental management.

[11]  T. Ward,et al.  Marine introductions in the Shark Bay World Heritage Property, Western Australia: a preliminary assessment , 2005 .

[12]  Oliver Floerl,et al.  POSITIVE INTERACTIONS BETWEEN NONINDIGENOUS SPECIES FACILITATE TRANSPORT BY HUMAN VECTORS , 2004 .

[13]  Michael D. Taylor,et al.  A preliminary investigation of biosecurity risks associated with biofouling on merchant vessels in New Zealand , 2004 .

[14]  M. Keough,et al.  Competition modifies the response of organisms to toxic disturbance , 2003 .

[15]  Oliver Floerl,et al.  Boat harbour design can exacerbate hull fouling , 2003 .

[16]  L. Godwin,et al.  Hull Fouling of Maritime Vessels as a Pathway for Marine Species Invasions to the Hawaiian Islands , 2003, Biofouling.

[17]  Stephan Gollasch,et al.  Fouling and Ships' Hulls: How Changing Circumstances and Spawning Events may Result in the Spread of Exotic Species , 2003, Biofouling.

[18]  G. Quinn,et al.  Experimental Design and Data Analysis for Biologists , 2002 .

[19]  C. Hewitt Distribution and Biodiversity of Australian Tropical Marine Bioinvasions , 2002 .

[20]  S. Gollasch,et al.  The Importance of Ship Hull Fouling as a Vector of Species Introductions into the North Sea , 2002 .

[21]  K. Wasson,et al.  Biological invasions of estuaries without international shipping: the importance of intraregional transport , 2001 .

[22]  M. Keough,et al.  Field assessment of effects of timing and frequency of copper pulses on settlement of sessile marine invertebrates , 2000 .

[23]  Rita R. Colwell,et al.  Global spread of microorganisms by ships , 2000, Nature.

[24]  James T. Carlton,et al.  Biological Invasions and Cryptogenic Species , 1996 .

[25]  J. Geller,et al.  Ecological Roulette: The Global Transport of Nonindigenous Marine Organisms , 1993, Science.

[26]  Michael J. Keough,et al.  Introduced and cryptogenic species in Port Phillip Bay, Victoria, Australia , 2004 .

[27]  R. Thresher,et al.  Introduced and cryptogenic species in Port Phillip , 2004 .

[28]  D. Gordon,et al.  Atlas of marine-fouling bryozoa of New Zealand ports and harbours , 1992 .