Hostname: page-component-745bb68f8f-cphqk Total loading time: 0 Render date: 2025-02-11T20:19:51.014Z Has data issue: false hasContentIssue false

Geometric morphometric analysis discriminates native and non-native species of Caprellidae in western North America

Published online by Cambridge University Press:  19 September 2008

Eva I. Riedlecker
Affiliation:
Smithsonian Environmental Research Center, 647 Contees Wharf Road, Edgewater, MD 21037, US Department of Theoretical Biology and Morphology, University of Vienna, Althanstraße 14, A-1090, Vienna, Austria
Gail V. Ashton*
Affiliation:
Smithsonian Environmental Research Center, 647 Contees Wharf Road, Edgewater, MD 21037, US
Gregory M. Ruiz
Affiliation:
Smithsonian Environmental Research Center, 647 Contees Wharf Road, Edgewater, MD 21037, US
*
Correspondence should be addressed to: Gail V. Ashton, Smithsonian Environmental Research Center, 647 Contees Wharf Road, Edgewater, MD 21037, US email: ashtong@si.edu
Rights & Permissions [Opens in a new window]

Abstract

Characteristics of the second gnathopod are traditionally used to distinguish between species of caprellid amphipods. However, these distinctions are often subjective and can be variable within a species. Geometric morphometrics were used to quantitatively assess shape variation of the second gnathopod propodus of three species of caprellids in North America, including the non-native Caprella mutica. Gnathopod shapes of C. mutica specimens from different latitudes revealed distinct morphologies; the factors responsible for the shape variations are unknown. Allometric change of propodus shape was observed in C. mutica. Larger individuals showed a wide array of possible propodus morphologies. Despite this variability, there were clear differences between large specimens of C. mutica and two species native to North America: C. alaskana and C. kennerlyi. The use of geometric morphometrics and the thin-plate spline method can serve to both complement descriptions using traditional keys and aid in identification of non-native species in novel geographical regions.

Type
Research Article
Copyright
Copyright © Marine Biological Association of the United Kingdom 2008

INTRODUCTION

Crustacea are typically identified taxonomically using morphological distinctions in the exoskeleton. Within the amphipod genus Caprella, these characters include the presence, size, shape and position of pereonite projections, relative size of the antennae, and the size and shape of the second gnathopod (e.g. Laubitz, Reference Laubitz1970; Smith & Carlton, Reference Smith and Carlton1975; Arimoto, Reference Arimoto1976; Hayward & Ryland, Reference Hayward and Ryland2000). However, these distinctions are often described subjectively (e.g. a little shorter, very small, quite large, sparse and many) and can be variable within a species, especially since morphology can change due to ontogenetic development or environmental influences (Vermeij, Reference Vermeij1978; Caine, Reference Caine1989). Confusion and incorrect identifications can occur when morphological descriptions are based on a few individuals, sizes, or geographical locations. As a result, newly introduced species can be difficult to distinguish from native congeners (Wasson et al., Reference Wasson, Von Holle, Toft and Ruiz2000).

Caprella mutica Schurin, 1935 (Figure 1), has the potential to create considerable taxonomic confusion, as it has been widely introduced throughout the world (Ashton, Reference Ashton2006). Its native range includes coastlines of Japan and Eastern Russia, whilst the known introduced range now spans across all temperate coastlines in the northern hemisphere (Ashton et al., Reference Ashton, Willis, Cook and Burrows2007) and New Zealand in the southern hemisphere (Inglis et al., Reference Inglis, Gust, Fitridge, Floerl, Woods, Hayden and Fenwick2006). In the native range, C. mutica inhabits algal beds, particularly in association with algiculture. Where introduced, individuals are most commonly found associated with fouling communities on man-made structures, including submerged areas of buoys, fish farms and marina or pontoon structures (Ashton, Reference Ashton2006). The identification of C. mutica has already been problematic on a number of occasions in northern Europe. For example, in The Netherlands, Platvoet et al. (Reference Platvoet, de Bruyne and Gmelig Meyling1995) described specimens of C. mutica as C. macho sp. nov. (Wolff, Reference Wolff2005). In Scotland, Caprella specimens collected in 1999 were initially unrecognized and later described as C. mutica upon closer scrutiny (O'Reilly, Reference O'Reilly2006).

Fig. 1. Adult male individuals of Caprella mutica (left), Caprella alaskana (middle) and Caprella kennerlyi (right). Scale bars 2 mm.

In western North America, C. mutica co-occurs with several other congeners and may be mistaken for native species, especially if significant geographical variation exists in morphological characteristics. For example, in a guide to the seashore life of the northern Pacific coast of America, Kozloff (Reference Kozloff1993, Figure 91, p. 114) showed an illustration that was described as the native C. californica Stimpson, 1856. The illustrated specimen is clearly setose on pereonites 1 and 2 and gnathopod II, and has dorsal spines on pereonites 3–5; it seems likely that this was C. mutica, which was described from the area in 1977 (USGS, 2005). This interpretation is consistent with a recently updated guide to the intertidal organisms of California (Carlton, Reference Carlton2007), where C. mutica was described as having several to many sharp spines on pereonites 3, 4 and 5. This contrasts with the description of two of the native caprellids: (a) C. alaskana Mayer, Reference Mayer1903 (Figure 1), with one or two small blunt spines on pereonites 5–7, although spines may extend as far as the cephalon (Laubitz, Reference Laubitz1970); and (b) C. kennerlyi Stimpson, 1864 (=Metacaprella kennerlyi) (Figure 1) that is distinguished by the presence of a pair of head spines (Laubitz, Reference Laubitz1970). The head spination is the only characteristic described to reliably define between these two native species (Laubitz, Reference Laubitz1970). However, it is noteworthy that species of caprellid amphipods are often discriminated on the basis of the second gnathopods, which are morphologically similar for C. mutica, C. alaskana and C. kennerlyi (Table 1). Moreover, the extent of morphological variation has not been quantitatively assessed for these species. The terms tubercle, spine and projection have been used in the description of caprellids. It is the authors' impression that a spine is typically longer and more pointed than a tubercle, which would be shorter and blunter. The term projection would describe both the aforementioned and setae. However, these terms are subject to personal interpretation and for the purposes of this paper the term spine has been used to describe all spine- and tubercle-like features.

Table 1. Descriptions of the second gnathopods of the three caprellid species found on the northern Pacific coast of America.

Geometric morphometric techniques are being increasingly used to quantify organisms' shapes. Traditional morphometrics include size and shape variables and also include qualitative variables. Descriptions are often accompanied by an illustration drawn from a single specimen. Like traditional morphometrics, geometric morphometric methods allow statistical inference, but importantly, they preserve information about the geometry of the object. The use of landmarks yields variables of significance and the technique is independent of measurements which must be chosen prior to the analysis (Zelditch et al., Reference Zelditch, Swiderski, Sheets and Fink2004). They often enable the quantification of features that are difficult to measure with traditional measurements, and are therefore usually described qualitatively. For example, semi-landmarks provide the opportunity to describe curvature. Consequently, geometric morphometrics generates large amounts of useful shape information which previously were unattainable. Finally, they allow morphological differences to be visualized using interactive computer graphics. Therefore, a hypothetical mean ‘shape reference’ of a species derived from several specimens could be used during identification as opposed to traditional drawings, which originate from only one specimen. Variation among the specimens can also be described visually using deformation grids. This ability to visualize morphological differences is invaluable to help identify and validate simple morphological measurements that can be used in future studies and identification keys (Rohlf & Marcus, Reference Rohlf and Marcus1993). With their hard exoskeletons, crustaceans should be excellent candidates for such analyses (Rufino et al., Reference Rufino, Abello and Yule2006). The method used in this study has been applied to quantify claw-shape differences in members of the genus Uca (Rosenberg, Reference Rosenberg2002) and to discriminate fishery stocks of the American lobster Homarus americanus Milne-Edwards 1837 (Cadrin, Reference Cadrin1995).

The current study demonstrates the use of geometric morphometrics to contribute increased clarity in species descriptions, serving to both substantiate and quantify taxonomic differences and to help identify introduced species. The objectives were to use shape differences in the gnathopod II propodus: (1) to measure latitudinal variation in C. mutica; (2) to assess allometric growth of C. mutica; and (3) to determine and quantify morphological differences between C. mutica and two North American caprellids with similar gnathopod shapes: C. alaskana and C. kennerlyi. In order to investigate the influence of size on the ability to differentiate the species, small and large individuals were treated independently for the final objective.

MATERIALS AND METHODS

Sample collection and specimen classification

Male caprellid specimens were collected from the Pacific coast of North America during summer periods between 2001 and 2003. Several keys to the Caprellidae were used to identify the species (Mayer, Reference Mayer1903; Laubitz, Reference Laubitz1970; Arimoto, Reference Arimoto1976). Distinguishing characteristics were used as follows: Caprella mutica have setation on pereonites 1 and 2 and gnathopod II, and multiple dorsal and lateral spines on pereonites 3–7, including more than 3 pairs of dorsal spines on pereonite 5; Caprella alaskana do not have body setation, have fewer dorsal spines (3 pairs on pereonite 5) and no lateral spines; Caprella kennerlyi can be distinguished by paired head spines. Several C. mutica from non-native populations in Scotland were also included in the analyses. The individuals from Scotland did not form an outlying group in the analyses and were therefore not treated independently. Two hundred and twelve individual caprellids were isolated, including 29 C. alaskana, 25 C. kennerlyi and 153 C. mutica. Male individuals greater than 15 mm total length were considered adults. Caprellids were used in different combinations according to the objectives (see below).

DATA ACQUISITION

Only the outer surface of the right gnathopod II propodus was used in this study. Images were acquired using a binocular microscope equipped with an Olympus 750 camera connected to a computer. All images were saved as TIF files using Scion Image software (Scion, Frederick, MD). Coordinates of landmarks and semi-landmarks (Figure 2) were digitized and recorded using tpsDig2 (Rohlf, Reference Rohlf2006). Landmarks 1 through to 7 captured shape information on all three spines: the comparatively large distal triangle (landmark 2; Figure 2), the medial (landmark 4; Figure 2) and proximal spines (landmark 7; Figure 2). Landmarks 8 and 9 marked the points where the propodus and carpus meet. Landmark 16 represents the end of the upper margin of the propodus where the dactyl is connected. Landmarks 10 through to 15 were semi-landmarks, used due to a lack of homologous points along the upper margin of the propodus. Semi-landmarks can be used in such cases, as tpsRelw (Rohlf, Reference Rohlf2005b) includes a command allowing semi-landmarks to slide along a tangent to the traced curve in order to remove tangential variation but retain information on contour (Bookstein, Reference Bookstein1997). Semi-landmarks will hereafter be referred to as landmarks.

Fig. 2. Digital image of second gnathopod of Caprella mutica with landmarks 1 through to 9 and 16 and semi-landmarks 10 through to 15. Scale bar 1 mm.

Shape variables were constructed from the landmarks through the following steps in tpsRelw. Landmark configurations were superimposed using the generalized least squares Procrustes superimposition (GLS). Scaling, translation and rotation was employed to minimize the Procrustes distance, the sum of squared distances between corresponding landmarks. In short, the object was centred at the origin by subtracting the coordinates of its centroid from the coordinates of each landmark. Then each object was scaled to unit centroid size by dividing each coordinate of each landmark by its centroid size. One configuration was used as a reference and all others were rotated to minimize partial Procrustes distance. The average shape was then calculated and became the new reference to which all objects were rotated again. This step was repeated until rotation ceased to occur.

The thin-plate spline procedure was used to describe the observed morphologies. This method generates deformation grids by dividing shape change into uniform and non-uniform shape components (Bookstein, Reference Bookstein1991; Rohlf & Marcus, Reference Rohlf and Marcus1993). Uniform shape change occurs when parallel lines remain parallel in a deformation grid and alterations occur equally across the entire grid. Non-uniform aspects lead to varying shape changes throughout the grid. Deformation grids depict shape change over the entire object by interpolating between landmarks. The metaphor upon which the thin-plate spline method is based and which intuitively explains a deformation grid is an extremely thin metal plate which can be rotated or bent to conform to shape variation. The plate is bent so as to minimize the energy expended to achieve the shape change and therefore also minimizes highly localized shape variation. Not only is a thin-plate spline an effective visualization tool but its coefficients (partial warps scores) can be used in descriptive and inferential statistical tests as well (Rohlf, Reference Rohlf1999). This method provides variables with the correct number of degrees of freedom (2k–4 where k is the number of landmarks) and employs the Procrustes distance as a metric. The partial warps scores represent the non-uniform shape variation between the specimens and the consensus.

In tpsRelw a principal components analysis (PCA) of the partial warps matrix, including the uniform components as a pair of partial warps, was carried out to describe major trends in morphological variation. Principal components of the partial warps scores are referred to as relative warps. The total variability described by each principal component axis was noted and included in PCA figures. Statistical analyses were performed, including the testing of assumptions (normality and homogeneity of variance), using both uniform and non-uniform components in Statistica 6.0. (StatSoft, Inc., 2001). A fully detailed description of the mathematics underlying these geometric morphometric methods is beyond the scope of this paper. For further information see the works by Bookstein (Reference Bookstein1991), Rohlf & Marcus (Reference Rohlf and Marcus1993) and Slice (Reference Slice2005).

ANALYSIS

Latitudinal variation

To investigate intraspecific shape variation in C. mutica at different latitudes, three regions on the west coast of North America were chosen: San Francisco Bay (California (CA), 37.7°N; N = 18), Puget Sound (Washington (WA), 47.4°N; N = 24) and Dutch Harbor (Alaska (AK), 53.9°N; N = 18). Adult male specimens from these regions were used to gather landmark data used in a relative warps analysis (Rohlf & Marcus, Reference Rohlf and Marcus1993). tpsRelw yielded a PCA to observe regional clustering and deformation grids based on the average individual from each location to describe morphology. Shape variation was assessed using multivariate analysis of variance (MANOVA) on both uniform and non-uniform components.

Allometry

A PCA of the partial warps scores of 142 C. mutica individuals was carried out, using tpsRelw, to examine trends in morphological change throughout growth. Specimens were categorized into 4 size-classes according to total body length: (1) greater than 20 mm; (2) 15–20 mm; (3) 10–15 mm; and (4) less than 10 mm. This included individuals from the Pacific coast of North America and the west coast of Scotland. In addition, a multivariate regression analysis of shape against total length (mm) was carried out using principal component scores 1 through to 3 to determine which shape change best described allometry. tpsRegr (Rohlf, Reference Rohlf2005a) provided a visualization window allowing to monitor how shape changes with size. Shape variation was assessed using MANOVA on both uniform and non-uniform components.

Species

The GLS method and thin-plate spline procedures (tpsRelw) were used to discern significant variations in propodus shape between C. alaskana, C. kennerlyi and C. mutica. Specimens from the small and large sizes were treated separately. Small individuals were those less than 10 mm length: 15, 13 and 17 individuals of C. alaskana, C. kennerlyi and C. mutica, respectively, from Alaska. Large individuals were greater than 15 mm length: 14 C. alaskana from Ketchikan (N = 12), Kodiak (N = 2); 12 C. kennerlyi from Prince William Sound (AK, N = 5), Kodiak (AK, N = 2) and Kachemak Bay (AK, N = 5); 47 C. mutica from Dutch Harbor (N = 7), Humboldt (CA, N = 1), Ketchikan (N = 6), Puget Sound (N = 9), San Francisco Bay (N = 7), Sitka (AK, N = 9) and the west coast of Scotland (N = 8). Shape variation was assessed using MANOVA on both uniform and non-uniform components.

RESULTS

Latitudinal variation

Principal components analysis shows clustering of adult male Caprella mutica according to source region (Figure 3). There was some overlap in propodus morphology, but the differences between populations were significant (MANOVA, Wilks' lambda = 0.046, F 28,60 = 3.94, P < 0.001). The gradation of shape change did not follow a linear latitudinal trend. Thin-plate splines illustrate that the main area of shape variation was located around the median spine (Figure 3). The size of the spine changed from being most massive in individuals from Dutch Harbor to a much reduced size in individuals from Puget Sound. Another area of variation was the relative build of the propodus, with those from Dutch Harbor typically broad and short, those from Puget Sound long and thin. Individuals from San Francisco Bay were intermediate in propodus shape.

Fig. 3. Scores on the first two principal components of Procrustes shape coordinates for Caprella mutica males, >15 mm, from 3 geographical locations. (A) Thin-plate spline deformation grids show the deviation from the total mean individual to mean individuals from (B) Dutch Harbor, (C) San Francisco and (D) Puget Sound.

ALLOMETRY

Propodus shape and variability changed with the size-class of the individual (Figure 4). Larger individuals (>15 mm) showed more shape variation than smaller ones, with variation in both the propodus curvature and relative size of the median spine between large individuals with extreme morphologies (D and E; Figure 4). Shape variation between the size-classes was significant (MANOVA, Wilks' lambda = 0.08, F 28,142 = 5.1, P < 0.001). Eighty per cent of the shape variation was described in principal components 1 through to 3, all of which correlated significantly with individual size (PC1 Rsq = 0.165, P < 0.001; PC2 Rsq = 0.379, P < 0.001; PC3 Rsq = 0.087, P < 0.001). The strongest relationship was with principal component 2 (Figure 5), which describes a continuous elongation and thinning of the propodus and extension of the median spine as body size increases (Figure 4).

Fig. 4. Scores on the first two principal components of Procrustes shape coordinates for Caprella mutica individuals of 4 size-classes. (A) Thin-plate spline deformation grids show the deviation from the total mean individual to (B) mean small (<10 mm) (C) mean medium (10–15 mm) (D) and (E) two extreme shapes of large (>15 mm) individuals as indicated in (a).

Fig. 5. Regression of principal component 2 of Procrustes shape coordinates against size for 142 Caprella mutica individuals (Rsq = 0.379; P < 0.001).

SPECIES

Propodus shape is clearly distinct in large individuals of the 3 caprellid species (Figure 6) (MANOVA, Wilks' lambda = 0.00, F 28,73 = 24.05, P < 0.001). No overlap of the species was observed. The outer surface of the propodus of Caprella alaskana was more rounded than the other species, the median spine being small. Caprella kennerlyi was less rounded, but maintains the small median spine. Propodus shape was most variable in individuals of C. mutica. The mean C. mutica gnathopod was much less curved and had a massive median spine relative to the other species.

Fig. 6. (A) Scores on the first two principal components of Procrustes shape coordinates for large Caprella alaskana, Caprella kennerlyi and Caprella mutica individuals (>15 mm). Thin-plate spline deformation grids show the deviation from the total mean individual to (B) C. alaskana (C) C. kennerlyi and (D) C. mutica mean individuals.

Small individuals of the three species often overlapped in the PCA, although shape variation was statistically significant (MANOVA, Wilks' lambda = 0.00, F 28,45 = 15.97, P < 0.001). Characteristics for differentiating between species could not be deciphered from the deformation grids (Figure 7).

Fig. 7. Scores on the first two principal components of Procrustes shape coordinates for small Caprella alaskana, Caprella kennerlyi and Caprella mutica individuals (<15 mm). (A) Thin-plate spline deformation grids show the deviation from the total mean individual to (B) C. alaskana (C) C. kennerlyi and (D) C. mutica mean individuals.

DISCUSSION

Morphology of the second propodus of Caprella mutica was much more variable than expected, showing significant geographical variation among populations in western North America. However, there was no direct relationship between latitude and shape variation which would enable morphology to be predicted according to latitude. The results suggest that external or biological influences, which do not co-vary with latitude, are driving the observed morphologies. Environmental factors such as temperature, salinity and chlorophyll-a concentrations are known to have an impact on body size and various life history traits in crustaceans (Frank, Reference Frank1975; Dugan et al., Reference Dugan, Hubbard and Wenner1994; Contreras & Jaramillo, Reference Contreras and Jaramillo2003). Turbulence has also been described to affect the ‘robustness’ or ratio between segment depth and length at the widest portion, of several caprellid species (Bynum, Reference Bynum1980; Caine, Reference Caine1989). Individuals were found to become more robust with increasing wave exposure. Caine (Reference Caine1989) described a process by which changes in the musculature of an appendage should be reflected by changes in the dimensions of that appendage. In addition, changes in the appendage may affect the musculature (and thus dimensions) of the pereonite which supports the appendage. In the decapod Munida rugosa, an arched chelate morphology was able to generate greater force than a straight chela (e.g. Smith, Reference Smith2004; Claverie & Smith, Reference Claverie and Smith2007). Claverie & Smith (Reference Claverie and Smith2007) suggest that the arched morphology has evolved as a result of sexual selection by improving the use of the chela as a weapon in addition to its function during feeding. Thus, sexual selection may also influence shape variation in crustacea. The caprellid gnathopod II is employed in numerous activities (e.g. grasping the substrate, movement, feeding and agonistic interactions), whereby differences in the organism's local environment and behaviour could also explain shape variation. For example filter feeders may be expected to have a more robust gnathopod II for grasping the substrate while filter feeding with the antennae; compared to active predators which develop robust posterior appendages to grasp the substrate while anterior appendages capture prey (Caine, Reference Caine1989). With decreasing wave exposure, predatory caprellids may be expected to have a more robust gnathopod II, as filter feeders would not develop the increased musculature associated with grasping. Aggressive species are expected to have an enlarged gnathopod II in which the basis is long (Caine, Reference Caine1974, Reference Caine1977). The large amount of variability found in gnathopod shape of adult, male C. mutica individuals implies aggressive behaviour and an increased level of adaptability to unused trophic niches. This morphological suitability could serve this species in establishing populations outside its native range.

Alternative explanations include population genetic differences and reproductive isolation as a result of geographical barriers (Contreras & Jaramillo, Reference Contreras and Jaramillo2003; Rufino et al., Reference Rufino, Abello and Yule2006). The genetic source(s) of the respective C. mutica populations examined in this study are presently unknown. This is further complicated by the fact that some morphological traits evolve rapidly (often predictably) in invasive species (Huey et al., Reference Huey, Gilchrist, Hendry, Sax, Stachowicz and Gaines2005).

As a species that is now widespread, invading many regions of the world, the functional significance of the large range of propodus shape in C. mutica is of particular interest. Whether the result of phenotypic plasticity or evolutionary change, the observed shape variation may allow this species to successfully exploit a wider range of resources (e.g. habitat types, environmental conditions and food sources) than other congeners and increase success in establishing self-sustaining populations. Although an intriguing possibility, this remains to be tested.

The results indicate a change of allometry in the second propodus of C. mutica. The propodus of large individuals becomes more extended, and the median spine can take on a large range of sizes relative to the rest of the propodus, compared to smaller individuals. Inconsistency in median spine size causes more shape variation and less condensed clustering among larger individuals. This indicates that both origin and size of the individual must be considered when using the second gnathopod as a taxonomic feature for identification.

At a large size (>15 mm), geometric morphometric analysis clearly distinguishes between the three species of caprellid. Exploratory analyses, using fewer C. mutica individuals originating only from Alaska, indicated that this variation was not biased by the larger sample size or number of source locations included in the analysis (again, individuals from Scotland were not outliers). Figure 6 includes deformation grids depicting the changes responsible for the distinctions between species: position and size of the median spine, build and curvature of propodus. Large males of these morphologically similar species could still be distinguished even though propodus shape in C. mutica was highly variable. A study using traditional morphometric techniques also described considerable gnathopod II shape variation in C. mutica (Faasse, Reference Faasse2005). The advantage of using geometric morphometrics is that it enables simple quantitative analysis of the characters described by Faasse (Reference Faasse2005) from multiple specimens. In addition, sampling images enables the researcher to avoid sacrificing endangered or expensive specimens and any further measurements would no longer require revisiting the individual, which will not be possible if it has been used for genetic analysis (Cadrin, Reference Cadrin2000). Using geometric morphometrics, the digital image is saved and can be revisited and any shapes which had not been previously considered important can be included in the analysis.

Smaller individuals of C. mutica often have very similar propodus morphology. Therefore when these species co-occur it can be difficult or impossible to identify juveniles to the species level. This must be taken into account when including small individuals in analyses (e.g. of abundance). Further investigation using geometric morphometrics may reveal characteristics which ascertain identification to the species level of the three species. The authors would suggest experimenting with the inclusion of other appendages or pereonites. In studying juveniles, care must be taken to ensure that the identity of the juvenile is known, e.g. by selecting them from a single species community.

In the future, it may be possible to hold digital images and coordinate data in a database to allow insertion of extra landmarks or identify an unknown species. However, geometric mophometrics can be sensitive to inconsistencies in image quality (Rufino et al., Reference Rufino, Abello and Yule2006). For this reason all images for the current study were taken by a single person using the same equipment and settings. In order to begin a morphological database, care must also be taken to assure the quality of digital images, including size, profile and correct labelling of the images, similar to restrictions implemented on genetic databases. The positioning of landmarks is also critical to the geometric morphometric analysis and a detailed description of the exact position of landmarks would be necessary for any such database. Finally, Saila & Martin (Reference Saila, Martin, Kumpf, Vaught, Grimes, Johnson and Nakamura1987) suggest that N (total individuals) should be roughly three times the number of variables (2* number of landmarks – 4). Therefore as the number of landmarks increase, a considerable increase in sample size is required. This is not always possible due to various reasons, e.g. endangered species, and small number of available specimens. In this study, the number of available specimens was limited and this rule of thumb could not always be followed. The authors attempted to find the optimal number of landmarks for shape description.

Overall, this study demonstrates how geometric morphometrics and the thin-plate spline method can contribute to descriptions using traditional keys. In invasion biology, misidentification can lead to errors in the history of patterns and baseline data, especially among closely related natives and non-natives (Müller et al., Reference Müller, Schramm and Seitz2002). In such cases of uncertainty, quantification of morphological characters using geometric morphometrics provides an important tool in taxonomic analysis. This reduces the likelihood of errors that may result from a more qualitative approach to identification.

ACKNOWLEDGEMENTS

The authors are grateful to staff at the Smithsonian Environmental Research Center involved in specimen collection and Michael Stachowitsch for comments on the manuscript. This research was supported by the National Sea Grant Program, Prince William Sound Regional Citizens' Advisory Council, and Smithsonian Institution.

References

REFERENCES

Arimoto, I. (1976) Taxonomic studies of caprellids (Crustacea, Amphipoda, Caprellidae) found in the Japanese adjacent waters. Special Publications from the Seto Marine Biological Laboratory Series III. Osaka, Japan: Nippon Printing & Publishing Co., Ltd. 111.Google Scholar
Ashton, G.V. (2006) Distribution and dispersal of the non-native caprellid amphipod, Caprella mutica Schurin 1935. PhD thesis. Scottish Association for Marine Science, Oban, Scotland.Google Scholar
Ashton, G.V., Willis, K.J., Cook, E.J. and Burrows, M.T. (2007) Distribution of the introduced amphipod, Caprella mutica Schurin on the west coast of Scotland and a review of its global distribution. Hydrobiologia 590, 3141.Google Scholar
Bookstein, F.L. (1991) Morphometric tools for landmark data. Cambridge: Cambridge University Press.Google Scholar
Bookstein, F.L. (1997) Landmark methods for forms without landmarks: morphometrics of group differences in outline shape. Medical Image Analysis 1, 225243.CrossRefGoogle ScholarPubMed
Bynum, K.H. (1980) Multivariate assessment of morphological variation in Caprella penantis Leach, 1814 (Amphipoda: Caprellidae). Estuarine, Coastal and Marine Science 10, 225237.Google Scholar
Cadrin, S.X. (1995) Discrimination of the American lobster (Homarus americanus) stocks off southern New England on the basis of secondary sexual character allometry. Canadian Journal of Fisheries and Aquatic Science 52, 27122723.CrossRefGoogle Scholar
Cadrin, S.X. (2000) Advances in morphometric identification of fishery stocks. Reviews in Fish Biology and Fisheries 10, 91112.CrossRefGoogle Scholar
Caine, E.A. (1974) A comparative functional morphology of feeding in three species of caprellids (Crustacea, Amphipioda) from the northwestern Florida Gulf coast. Journal of Experimental Marine Biology and Ecology 15, 8196.Google Scholar
Caine, E.A. (1977) Feeding mechanisms and possible resource partitioning of the Caprellidae (Crustacea: Amphipoda) from Puget Sound, USA. Marine Biology 42, 331336.CrossRefGoogle Scholar
Caine, E.A. (1989) Relationship between wave activity and robustness of caprellid amphipods. Journal of Crustacean Biology 9, 425431.CrossRefGoogle Scholar
Carlton, J.T. (ed.) (2007) The Light and Smith manual: intertidal invertebrates from central California to Oregon, 4th edition. Berkeley, CA: University of California Press.CrossRefGoogle Scholar
Claverie, T. and Smith, I.P. (2007) Functional significance of an unusual chela dimorphism in a marine decapod: specialization as a weapon? Proceedings of the Royal Society of London B 274, 30333038.Google Scholar
Contreras, H. and Jaramillo, E. (2003) Geographical variation in natural history of the sandy beach isopod Excirolana hirsuticauda Menzies (Cirolanidae) on the Chilean coast. Estuarine, Coastal and Marine Science 58S, 117126.CrossRefGoogle Scholar
Dugan, J.E., Hubbard, D.M. and Wenner, A.M. (1994) Geographic variation in life history of the sand crab Emerita analoga (Stimpson) on the California coast: relationships to environmental variables. Journal of Experimental Marine Biology and Ecology 181, 255278.CrossRefGoogle Scholar
Faasse, M. (2005) Notes on diagnostic characters and morphological variability of Caprella mutica Schurin, 1935 in The Netherlands (Crustacea: Amphipoda: Caprellidea). Het Zeepaard 65, 2228.Google Scholar
Frank, P.W. (1975) Latitudinal variation in the life history features of the black turban snail Tegula funebralis (Prosobranchia: Trochiddae). Marine Biology 31, 181192.CrossRefGoogle Scholar
Hayward, P.J. and Ryland, J.S. (eds) (2000) Handbook of the marine fauna of north-west Europe. Oxford: Oxford University Press.Google Scholar
Huey, R.B., Gilchrist, G.W. and Hendry, A.P. (2005) Using invasive species to study evolution: case studies with Drosophila and salmon. In Sax, D.F., Stachowicz, J.J. and Gaines, G.S. (eds) Species invasions: insights into ecology, evolution, and biogeography. Sunderland, MA: Sinauer Associates, pp. 139164.Google Scholar
Inglis, G., Gust, M., Fitridge, I., Floerl, O., Woods, C., Hayden, B. and Fenwick, G. (2006) Port of Timaru: baseline survey for non-indigenous species. Biosecurity New Zealand Technical Paper No. 2005/06. ISBN No: 0-478-07902-8.Google Scholar
Kozloff, E.N. (1993) Seashore life of the northern pacific coast. Seattle: University of Washington Press.Google Scholar
Laubitz, D.R. (1970) Studies on the Caprellidae (Crustacea, Amphipoda) of the American North Pacific. National Museum of Canada.Google Scholar
Mayer, P. (1903) Die Caprellidae der Siboga-Expedition. Siboga-Expeditie, Monographie 34, 1160.Google Scholar
Müller, J.C., Schramm, S. and Seitz, A. (2002) Genetic and morphological differentiation of Dikerogammarus invaders and their invasion history in Central Europe. Freshwater Biology 47, 20392048.Google Scholar
O'Reilly, M. (2006) The Japanese macho skeleton shrimp (Caprella mutica) in the Clyde Estuary. The Glasgow Naturalist 24, 156157.Google Scholar
Platvoet, D., de Bruyne, R.H. and Gmelig Meyling, A.W. (1995) Description of a new Caprella-species from the Netherlands: Caprella macho nov. spec. (Crustacea, Amphipoda, Caprellidae). Bulletin of the Zoological Museum, University of Amsterdam 15, 14.Google Scholar
Rohlf, F.J. (1999) Shape statistics: Procrustes superimpositions and tangent spaces. Journal of Classification 16, 197223.CrossRefGoogle Scholar
Rohlf, F.J. (2005a) tpsRegr, thin-plate spline regression, version 1.31. Stony Brook, NY: Department of Ecology and Evolution, State University of New York.Google Scholar
Rohlf, F.J. (2005b) tpsRelw, relative warps analysis, version 1.44. Department of Ecology and Evolution, State University of New York at Stony Brook.Google Scholar
Rohlf, F.J. (2006) tpsDig2, digitize landmarks and outlines, version 2.10. Department of Ecology and Evolution, State University of New York at Stony Brook.Google Scholar
Rohlf, F.J. and Marcus, L.F. (1993) A revolution morphometrics. Trends in Ecology and Evolution 8, 129132.Google Scholar
Rosenberg, M.S. (2002) Fiddler crab claw shape variation: a geometric morphometric analysis across the genus Uca (Crustacea: Brachyura: Ocypodidae). Biological Journal of the Linnaean Society 75, 147162.Google Scholar
Rufino, M.M., Abello, P. and Yule, A.B. (2006) Geographic and gender shape differences in the carapace of Liocarcinus depurator (Brachyura: Portunidae) using geometric morphometrics and the influence of a digitizing method. Journal of Zoology 269, 458465.Google Scholar
Saila, S.B. and Martin, B.K. (1987) A brief review and guide to some multivariate methods for stock identification. In Kumpf, H.E., Vaught, R.N., Grimes, C.B., Johnson, A.G. and Nakamura, E.L. (eds) Proceedings of the Stock Identification Workshop. NOAA Technical Memorandum NMFS–SEFC 199, 149175.Google Scholar
Slice, D.E. (2005) Modern morphometrics in physical anthropology. New York: Kluwer.CrossRefGoogle Scholar
Smith, L.D. (2004) Biogeographic differences in claw size and performance in an introduced crab predator Carcinus maenas. Marine Ecology Progress Series 276, 209222.CrossRefGoogle Scholar
Smith, R.I. and Carlton, J.T. (eds) (1975) Light's manual: intertidal invertebrates of the central California coast. Berkeley, CA: University of California Press.Google Scholar
StatSoft Inc (2001) STATISTICA for Windows (data analysis software system), version 6 (http://www.statsoft.com).Google Scholar
USGS (2005) Nonindigenous aquatic species database. Gainesville, FL. http://nas.er.usgs.gov.Google Scholar
Vermeij, G.J. (1978) Biogeography and adaptation: patterns of marine life. Cambridge, MA: Harvard University Press.Google Scholar
Wasson, K., Von Holle, B., Toft, J. and Ruiz, G. (2000) Detecting invasions of marine organisms: kamptozoan case histories. Biological Invasions 2, 5974.Google Scholar
Willis, K.J., Cook, E.J., Lozano-Fernandez, M. and Takeuchi, I. (2004) First record of the alien caprellid amphipod, Caprella mutica, for the UK. Journal of the Marine Biological Association of the United Kingdom 84, 10271028.CrossRefGoogle Scholar
Wolff, W.J. (2005) Non-indigenous marine and estuarine species in The Netherlands. Zoologische Mededelingen 79, 1116.Google Scholar
Zelditch, M., Swiderski, D., Sheets, D.H. and Fink, W. (2004) Geometric morphometrics for biologists: a primer. London: Elsevier Academic Press.Google Scholar
Figure 0

Fig. 1. Adult male individuals of Caprella mutica (left), Caprella alaskana (middle) and Caprella kennerlyi (right). Scale bars 2 mm.

Figure 1

Table 1. Descriptions of the second gnathopods of the three caprellid species found on the northern Pacific coast of America.

Figure 2

Fig. 2. Digital image of second gnathopod of Caprella mutica with landmarks 1 through to 9 and 16 and semi-landmarks 10 through to 15. Scale bar 1 mm.

Figure 3

Fig. 3. Scores on the first two principal components of Procrustes shape coordinates for Caprella mutica males, >15 mm, from 3 geographical locations. (A) Thin-plate spline deformation grids show the deviation from the total mean individual to mean individuals from (B) Dutch Harbor, (C) San Francisco and (D) Puget Sound.

Figure 4

Fig. 4. Scores on the first two principal components of Procrustes shape coordinates for Caprella mutica individuals of 4 size-classes. (A) Thin-plate spline deformation grids show the deviation from the total mean individual to (B) mean small (<10 mm) (C) mean medium (10–15 mm) (D) and (E) two extreme shapes of large (>15 mm) individuals as indicated in (a).

Figure 5

Fig. 5. Regression of principal component 2 of Procrustes shape coordinates against size for 142 Caprella mutica individuals (Rsq = 0.379; P < 0.001).

Figure 6

Fig. 6. (A) Scores on the first two principal components of Procrustes shape coordinates for large Caprella alaskana, Caprella kennerlyi and Caprella mutica individuals (>15 mm). Thin-plate spline deformation grids show the deviation from the total mean individual to (B) C. alaskana (C) C. kennerlyi and (D) C. mutica mean individuals.

Figure 7

Fig. 7. Scores on the first two principal components of Procrustes shape coordinates for small Caprella alaskana, Caprella kennerlyi and Caprella mutica individuals (<15 mm). (A) Thin-plate spline deformation grids show the deviation from the total mean individual to (B) C. alaskana (C) C. kennerlyi and (D) C. mutica mean individuals.