Invertebrate · Molluscs · Clams

Giant Clam

Tridacna maxima (Röding, 1798)
syn. Tridachnes maxima, Tridacna (Chametrachea) maxima, Tridacna acuticostata, Tridacna compressa, Tridacna detruncata, Tridacna elongata +7 more
up to 35 cm0-20 mCITES IILeast Concern
1543

Tridacna gigas is the largest living bivalve mollusk, reaching up to 120 cm (47 in) across and over 200 kg (440 lb), with an average wild lifespan exceeding 100 years. Its shell has four or five distinct vertical folds, differentiating it from Tridacna derasa's six or seven. Adults cannot fully close their shells; small gaps always remain, revealing the retracted brownish-yellow mantle tissue. Its mantle is fleshy, extending beyond shell edges and densely packed with symbiotic zooxanthellae. Hundreds of eyespots, each about 0.5 mm in diameter, dot the mantle border, containing a pupil-like aperture and over a hundred photoreceptors.

It inhabits shallow coral reefs, found in flat coral sand or broken coral at depths of up to 20 m (66 ft). Though a filter-feeder, 65-70% of its nutrition comes from symbiotic unicellular algae (zooxanthellae) cultivated within a specialized circulatory system. During the day, the clam extends its mantle to expose these algae to sunlight for photosynthesis. Its eyespots enable rapid mantle retraction and partial shell closure in response to sudden light dimming, a defense against potential predators. It also reacts to object movement before a shadow is cast and adjusts mantle orientation with changes in light direction. Tridacna gigas is an endangered species, with populations experiencing rapid declines across its range.

Tridacna gigas is a hermaphrodite, producing both eggs and sperm, though self-fertilization does not occur. Reproduction involves broadcast spawning, releasing up to 500 million eggs (100 micrometres/0.0039 in diameter) and sperm. A Spawning Induced Substance (SIS), detected by chemoreceptors near the incurrent syphon, synchronizes this release, triggering mantle swelling, adductor muscle contraction, and vigorous shell contractions to expel gametes. Spawning coincides with incoming tides, typically near the second, third, and fourth quarters of the moon phase, with intense periods (30 minutes to 2.5 hours) at 2-3 minute intervals. Fertilized eggs float for about 12 hours before hatching into trochophore larvae; these measure 160 micrometres (0.0063 in) after two days and soon develop a foot for locomotion. Larvae are planktonic, consuming plankton and capturing free-floating zooxanthellae. Settlement occurs at about one week of age, though juveniles may relocate frequently. They are considered juvenile once 20 cm (8 in) long, with laboratory-reared clams showing growth rates of 12 cm (4.7 in) per year.

How to recognise it
  • highly corrugated shell
  • brightly coloured mantle with iridescent spots

Why it's threatened

Biological resource use
Intentional use: (subsistence/small scale) [harvest] · Unintentional effects: (subsistence/small scale) [harvest]
Climate change & severe weather
Habitat shifting & alteration

The extent of fishing of T. maxima can vary depending on the local coastal communities. For instance, T. maxima (and other large clam species) is opportunistically taken during fishing trips targeting other marine resources such as fish and lobsters (Purcell et al. 2020). In the Republic of Kiribati, all giant clams (including T. maxima) are heavily exploited for subsistence purposes (Eurich et al. 2023). On the other hand, it is relatively untargeted by fishers in areas where larger species occur, and high densities of the species are still observed on some isolated and enclosed reefs of the Central Pacific (Van Wynsberge et al. 2016). As this species is highly popular in the aquarium trade, numerous South Pacific nations (such as Fiji, Solomon Islands, Vanuatu, and the Federated States of Micronesia) were extracting their wild T. maxima for live exports in the early 1990s and 2000s, which appears to have impacted populations (Neo et al. 2017).

Climate change could threaten this species. Massive mortalities due to climate variability (i.e., high water temperatures) have been reported from the isolated populations of this species in the atolls of French Polynesia (Andréfouët et al. 2013, Van Wynsberge and Andréfouët 2017) and Lakshadweep Reefs (Apte et al. 2019). In addition, thermal stress alone can cause the degradation and death of Symbiodiniaceae cells (Dubousquet et al. 2016) and reduce fertilisation success in this species (Armstrong et al. 2020). Experimental studies combining the effects of elevated temperatures and _p_CO2 levels found that elevated temperatures exert a stronger impact on this species’ physiology than acidification (Armstrong et al. 2020, Brahmi et al. 2021). These collectively suggest that variability in thermal conditions could be detrimental to this species in the future.

Threat classification from the IUCN Red List.

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Last Update: August 11, 2026