Giant clams of the subfamily Tridacninae are conspicuous members of Pacific coral reef communities that play such important ecological roles that some authors have considered them as keystone species (Guibert et al., 2020; Mamat et al., 2021). All species of Tridacninae are of widespread conservation concern and are listed on both the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) and the International Union for Conservation of Nature (IUCN). However, giant clams are notoriously difficult to identify, and recent molecular work has revealed that morphological misidentification of giant clams have confounded current population assessments and extinction risk (Neo et al., 2017; Tisdell, 1989; Wells, 1997). As a case in point, Tridacna noae that was first described by C. Röding in 1798 became synonymized to T. maxima as it appeared to be a variant of the latter species based on shell morphology (Rosewater, 1965). Only recently has T. noae been resurrected as a valid species distinct from its congener T. maxima based on both morphological and molecular data (Su, 2014).
Neo et al. (2017) present the most comprehensive survey of giant clam species distributions and status, but no samples from the Samoan archipelago were included in that study. In previous studies by Fauvelot et al., 2019, a team sampled Upolu, Independent Sāmoa finding individuals belonging to T. noae. However, the most recent published studies conducted on tridacnine clams in the territory of American Sāmoa were published nearly 20 years ago (Green & Craig, 1999). This study was conducted prior to recent genetic recognition of T. noae (Su et al., 2014), so the authors assumed all visually similar samples were T. maxima (A. Green, pers. obs.), which would confound population density estimates if T. noae were also present in American Sāmoa. As genetic techniques are more commonly used to confirm species, more cases of T. noae are being identified, as seen in Militz et al. (2015).
Previously, American Sāmoa hosted two species of giant clams in the territorial waters: Tridacna squamosa and T. maxima. Fossilized shells indicate a third species, Hippopus hippopus, used to occur in Sāmoa, but is now locally extinct (Nagaoka, 1993; Newman & Gomez, 2000). Additionally, an aquaculture program was started for juvenile H. hippopus T. gigas, and T. derasa, but stocks were harvested prior to reproduction and appear to be functionally extirpated. Here, we use next generation sequencing to confirm identification of giant clams and expand the species range of T. noae to include American Sāmoa. Additionally, this discovery highlights the need to revisit historical population assessments to determine the distribution and abundance of each T. noae and T. maxima across the Samoan Archipelago.
Tissue biopsies were collected from four clams, two putative T. noae and two putative T. maxima, found during surveys on Tutuila, American Sāmoa, with in situ photos taken of each individual sampled, seen in figure 1. Clams were sampled from depths between 27-37 ft and ranged from 12 to 20 cm in antero-posterior shell length. Clams were identified morphologically as either T. noae or T. maxima (following Militz et al. 2015; Fatherree 2016) and then sequenced using reduced representation genomic sequencing (ezRAD, Toonen et al., 2013). Reads were mapped to reference mitogenomes from Tan et al. (2022) using Minimap2 (Li, 2018) in Geneious Prime v2021.1.1 (www.geneious.com).
The two individuals identified morphologically as T. noae (Figure 1) were confirmed genetically with nearly complete mitogenomes 15,240 ± 4 base pairs in length (86.5 ± 1.2%), and with high coverage depth (106.2 ± 75X), that matched the Tan et al. (2022) reference sequence provided by Danwei Huang at 99.7 ± 0.05% pairwise identity.  Another individual identified morphologically as T. maxima was also confirmed genetically with a nearly complete mitogenome of 14,978 base pairs (80.7%), with relatively high coverage depth (53.5X), matching at 99.6% pairwise identity to the T. maxima reference sequence (E. Y. Tan et al., 2022).  Given this clear distinction among the morphologically identified samples, the final T. maxima sample was not sequenced here.
 
There is considerable morphological variation within American Samoan T. maxima (Figure 1B and C) and T. noae. The morphological characteristics that are typically used for identification (such as the size of byssal orifice, number of radial folds in the rib interstices, elaborate vs. simple incurrent siphon tentacles, size of scutes) are variable within the species which can lead to confusion or misidentification between T. maxima and T. noae. Additionally, the mantle can vary dramatically in color, pattern and texture, and are unreliable as proxies for species identification (Su et al., 2014). As with the many phenotypic morphs of Tridacna maxima, T. noae can exhibit two color morphs, brown and blue (Militz et al. 2015).
Many of these characteristics also fluctuate based on individual health (Mies, 2019). However, certain morphologic characteristics can aid in distinguishing between T. maxima and T. noae. Examples of features more commonly observed in T. noae are “tear-drop” oval patterns on the mantle edge and less pronounced hyaline organs (Su et al., 2014).
Based on these findings, we can update the catalog of extant species in American Sāmoa to include: Tridacna maxima, Tridacna squamosa, and now Tridacna noae. By confirming the identification of these two sometimes difficult to distinguish clam species genetically along with photo-documentation to highlight morphological distinctions, we hope to improve the efficacy and accuracy of identification of T. noae and T. maxima during future field surveys. Tridacnid clams are listed as a priority species under the territory’s Local Action Strategy, and accurately identifying species is critical to understanding the distribution and abundance of each and can help ensure the appropriate and most effective management of these long-lived species.