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Biological Invasions by Marine Jellyfish 249<br />

14.7 Transport of Invasive Marine Jellyfish<br />

The primary vector for the introduction of non-indigenous species into<br />

marine ecosystems is widely perceived to be shipping traffic, which enables<br />

organisms to cross natural oceanic barriers (Carlton and Geller 1993; Holland<br />

2000; Chap. 4). Over the past 20–30 years, increases in the speed, size, and volume<br />

of shipping traffic on a global scale, along with stricter regulation of the<br />

use of anti-fouling paints, have resulted in concomitantly accelerating rates of<br />

non-indigenous species introductions into marine ecosystems (Ruiz et al.<br />

1997, and references therein). In addition, oil and gas drilling platforms are<br />

routinely moved over large distances, sometimes between ocean basins, as<br />

new fields or markets emerge for exploration. In terms of the total number of<br />

fixed platforms in the sea, individual drill platform movements are extremely<br />

small. Still, the relocation of even a single platform via ocean towing will<br />

transport not only individuals, but perhaps entire exotic populations or<br />

mature communities.<br />

Both ballast water and hull fouling are plausible mechanisms of jellyfish<br />

introductions. While ships carry large volumes of ballast water containing an<br />

enormous variety of potentially invasive organisms (Carlton and Geller<br />

1993), only the holoplanktonic ctenophores appear suited to ballast watermediated<br />

introduction. By contrast, hull fouling transport, either by ships or<br />

on drill platforms, is more likely for the hydrozoans and scyphozoans, owing<br />

to their bipartite life-histories that include a sessile polypoid stage. Despite<br />

the early observations described by Galil et al. (1990) of C. andromeda<br />

medusae swimming into the Mediterranean through the Suez Canal, it is more<br />

likely that translocation occurs not by the medusa stage, but rather by the sessile<br />

polyps, a counterintuitive argument supported by recent molecular<br />

genetic research (Dawson et al. 2005).<br />

The aquarium trade has also received extensive attention as an important<br />

mode of marine introductions of ornamental fish and invertebrates. Recently,<br />

Bolton and Graham (2006) reported on incipient introductions resulting from<br />

the transport of ‘live rock’ materials associated with the aquarium trade.‘Live<br />

rock’, either naturally collected or artificially cultured, refers to rock coated<br />

with algae, invertebrates, and microorganisms that is used for the purpose of<br />

increasing the aesthetics of home aquaria. Live rock became apparent as a<br />

potential vector of invasive organisms when material collected in the Indo-<br />

Pacific (likely Indonesia or Fiji) was imported to a local pet store in Florida<br />

(USA). Several weeks after purchase, a home aquarium enthusiast reported<br />

the appearance of numerous small jellyfish that ultimately were identified as<br />

‘upside-down’ jellyfish Cassiopea spp., a recognized globally invasive genus<br />

(Sect. 14.3.2). The fact that the live rock trade in the United States receives little<br />

attention, much less appropriate quarantine measures, makes it a concern<br />

for aquatic invasive research (Bolton and Graham 2006).

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