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Proceedings of the International Cyanide Detection Testing Workshop

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<strong>the</strong> high-value fi sh species such as emperor angel-fi sh (Pomacanthus imperator), blue surgeon-fi sh<br />

(Paracanthurus sp.), and blue ring angelfi sh (Pomacanthus annularis) (Fahrudin, 2003). The marine<br />

aquarium industry worldwide is worth an estimated $200 to $330 million annually (USCRTF,<br />

2000. Wabnitz et al., 2003. FAO, 1996-2005). When examined by weight, aquarium fi sh are<br />

valued at $500 per kilogram or more, which is considerably higher than a similar weight <strong>of</strong><br />

food fi sh (Cato and Brown, 2003. Wabnitz et al., 2003).<br />

Environmental concerns about cyanide fi shing<br />

Although illegal in most countries, <strong>the</strong> use <strong>of</strong> cyanide to capture live reef fi sh remains pervasive,<br />

propelled by <strong>the</strong> lucrative growing and largely unregulated international trade in live reef food<br />

fi sh and <strong>the</strong> marine aquarium industry. The United States is <strong>the</strong> number-one importer <strong>of</strong> coral<br />

reef fi sh for <strong>the</strong> aquarium trade, and <strong>the</strong> demand for <strong>the</strong>se species may be one factor driving <strong>the</strong><br />

continued use <strong>of</strong> cyanide. <strong>Cyanide</strong> is toxic to fi sh because it interferes with oxygen metabolism<br />

by blocking <strong>the</strong> key enzyme system, cytochrome oxidase (Metzler, 2001), and blocks enzymatic<br />

pathways in <strong>the</strong> liver (Solomonson, 1981). Once inside <strong>the</strong> fi sh tissue, cyanide reacts with<br />

thiosulfate to produce <strong>the</strong> comparatively nontoxic thiocyanate which is excreted in <strong>the</strong> urine.<br />

Rapid detoxifi cation enables animals such as fi sh to ingest high, sub-lethal doses <strong>of</strong> cyanide<br />

(Eisler, 1991), although some <strong>of</strong> <strong>the</strong> effects are irreversible and may lead to <strong>the</strong> death <strong>of</strong> <strong>the</strong><br />

fi sh (Way et al., 1988).<br />

Several studies have also demonstrated negative impacts <strong>of</strong> cyanide on non-target coral reef<br />

species including corals (Cervino et al., 2003. Jones et al., 1998). Exposure <strong>of</strong> corals to cyanide<br />

causes rapid signs <strong>of</strong> stress and bleaching, and at high concentrations, progressive tissue<br />

sloughing that can lead to colony mortality. Fishermen spray cyanide into crevices and coral<br />

thickets where fi sh <strong>of</strong>ten hide, and <strong>the</strong>n break apart <strong>the</strong> corals to access <strong>the</strong> stunned fi shes,<br />

leading to substantial damage to <strong>the</strong> habitat. Large percentages <strong>of</strong> <strong>the</strong> target fi sh captured<br />

with cyanide die during collection or in transit due to <strong>the</strong>ir weakened state, which requires<br />

fi shermen to capture signifi cantly higher numbers <strong>of</strong> fi shes than would o<strong>the</strong>rwise be needed.<br />

In fact, some studies indicate that as many as 75% <strong>of</strong> fi sh collected with cyanide die within<br />

hours <strong>of</strong> collection, and ano<strong>the</strong>r 30% die prior to export. In addition, more than half may<br />

die shortly after arrival in <strong>the</strong> United States from a combination <strong>of</strong> <strong>the</strong> poisons used in <strong>the</strong><br />

capture and stress associated with handling and transport. <strong>Cyanide</strong> fi shing is also risky for <strong>the</strong><br />

divers, who <strong>of</strong>ten go to considerable depths for extended periods without following proper<br />

dive procedures.<br />

Conservation approaches to address cyanide fi shing<br />

Although cyanide fi shing is illegal in most countries, poor law enforcement capabilities and<br />

high levels <strong>of</strong> corruption have allowed <strong>the</strong> use <strong>of</strong> cyanide to continue. In 1989, <strong>the</strong> Haribon<br />

Foundation and Ocean Voice initiated a program to train fi shermen in <strong>the</strong> use <strong>of</strong> nets as an<br />

alternative to cyanide. A second, more aggressive program was implemented in <strong>the</strong> Philippines<br />

in <strong>the</strong> early 1990s by <strong>the</strong> <strong>International</strong> Marinelife Alliance (IMA), in partnership with <strong>the</strong><br />

Philippine government’s Bureau <strong>of</strong> Fisheries and Aquatic Resources. Through a combination<br />

<strong>of</strong> <strong>the</strong> right policies and laws, improved enforcement, enhanced public awareness, training <strong>of</strong><br />

cyanide fi shers in cyanide-free fi sh capture techniques, development <strong>of</strong> livelihood alternatives,<br />

community-based resource management programs, and cyanide testing <strong>of</strong> live fi sh exports<br />

10

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