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al. 2004), molecular and morphological methods were combined to establish a more robust taxonomic subdivision of Ammonia worldwide. Thirteen phylotypes (T1–T13) could be distinguished and discrimi- nated on the basis of morphometric analyses (Figs. 1, 2). The distinction of phylotypes is based on phylogenetic analysis of 267 partial LSU rDNA sequences, obtained from 202 living Ammonia specimens sampled at 30 localities from the Pacific Ocean, the Atlantic Ocean, Mediterranean Sea, Red Sea, Caribbean Sea and North Sea (Table 2, Fig. 2). The morphology of 127 sequenced specimens was recorded by SEM prior to DNA extraction and the images were utilized for morphometric analysis. Measurements or assessments of 37 external test characters were used to perform different types of analysis, suggesting that each phylotype can also be distinguished morphologically. At least 8 of the 13 phylotypes can be equated to described species. Morphometric analysis can therefore be successfully used to distinguish species in highly variable taxa if a sufficient number of specimens and morphological characters are taken into consideration. Each phylotype (T1–T13) is monophyletic and separated by elevated genetic distances from other types. Furthermore, as no intermediate types have been observed, the different phylotypes can be regarded as distinct species (Hayward et al. 2004). This is in contrast to the popular taxonomic concept on the genus Ammonia that only recognizes a limited number of species with many ecophenotypes (Poag 1978; Walton and Sloan 1990). The recognition that Ammonia represents only a single or very few species worldwide should therefore be abandoned as a theory lacking a genetic basis. Analysis of the biogeographical patterns shows that most Ammonia phylotypes are characterized by a restricted distribution 86 W. Foissner et al. (eds) (Fig. 1, Table 2). Only one phylotype (T1) features a cosmopolitan distribution. Several other types are dispersed only in the northern or southern hemisphere (T2, T3, T5), some of them showing a transoceanic distribution (T2, T5). Many phylotypes are regionally restricted (T4, T7, T8, T9, T10, T11, T12, T13) while one phylotype (T6) shows a disjunct area. While transoceanic dispersal (T2, T5) could be aided by surface currents and/or transport via seabirds (Hayward and Hollis 1994), this would be difficult to accept with the disjunct distribution of T6. Human-assisted dispersal is the most likely explanation in the latter case. The genotype T6 is distributed around the coasts of China and Japan (Fig. 1) which is congruent with the habitat of Eriocheir sinensis, a decapod that has been intro- duced in the Wadden Sea at the end of the 19th century by shipping (Nehring and Leuchs 2000). Some of the ballast tank water that included E. sinensis could also have contained Ammonia individuals of the genotype T6 which since then spread out in the Wadden Sea and the adjacent Baltic Sea. Human-induced introduction of foraminifera is not an unknown phenomenon and has also played a role in the agglutinated foraminifer Trochammina hadai from Japan that has invaded the bay of San Francisco in the mid 1980s, most likely from ballast waters and sediments discharged from ships (Mc Gann and Sloan 1996). The results of our studies provide just a sampling on the global diversity of the genus Ammonia. There are extended geographical regions that have not yet been investigated (Indian and South Atlantic Oceans, tropical and east Pacific, Southeast Asia and the East Indies). It is highly likely that the number of genetically distinct species could approach the number of formally named species (about 40; Ellis and Messina 1940 and supplements), most of which will be also distinguishable by a combination of subtle morphological characters. Cryptic diversity in monothalamous foraminifera In contrast to Ammonia, monothalamous foraminifera are a poorly known group, widely ignored by micropaleontologists. They are characterized by single-chambered organic-walled Fig. 1 Global distribution of the 13 Ammonia phylotypes (T1–T13) genetically identified and morpho- logically analysed Protist Diversity and Geographical Distribution 87 or agglutinated tests that are rarely preserved in the fossil record. The fact that this group is particularly abundant in widely undersampled deep-sea and high latitude waters (Gooday et al. 2004) is also contributing to our lack of knowledge concerning its diversity. Mono- thalamous foraminifera are traditionally classified in the orders Allogromiida and Astrorhizida (Debenay et al. 1996). Morphological distinction of the latter orders is based on wall structure but is not confirmed by molecular studies (Pawlowski et al. 2003). SSU rDNA sequences have been used to resolve higher-level phylogenetic relationships (Paw- lowski et al. 2002a, b; Pawlowski and Holzmann 2002), yet relations at lower taxonomic level remain unexplored. Fig. 2 Phylogenetic analysis of 267 partial LSU rDNA sequences using the Neighbour Joining method. The numbers are bootstrap percent values based on 500 resamplings. The scale bar corresponds to the number of substitutions per site. The names of sampling localities and number of sequences (in brackets) are indicated for each molecular type 88 W. Foissner et al. (eds) T a b le 2 C o ll ec ti o n lo ca li ti es , d is tr ib u ti o n an d h ab it at o f in v es ti g at ed A m m o ni a sp ec im en s P h y lo ty p e N u m b er o f in v es ti g at ed sp ec im en s N u m b er o f p ar ti al L S U rD N A se q u en ce s D is tr ib u ti o n C o ll ec ti o n lo ca li ti es H ab it at T 1 5 2 6 5 C o sm o p o li ti an F ra n ce : C am ar g u e, B re ta g n e, V en d e´e ; It al y : L ag o o n o f V en ic e, T ri es t T h e N et h er la n d s: M o o k B ai ; G B R : D o v ey E st u ar y ; S w ed en : T ja er n o U S A : C ap e C o d , L o n g Is la n d ; N ew C al ed o n ia : T ie ti B ea ch ; C u b a: P la y a B ai le´ n ; C h il e: L a L ig u a; N ew Z ea la n d : W ai te m at a H ar b o u r M ic ro ti d al m ar sh es B ra ck is h w at er es tu ar y T 2 4 0 6 1 E u ro p ea n co as ts N o rt h er n A tl an ti c co as t, U S A F ra n ce : C am ar g u e, B re ta g n e, V en d e´e ; It al y : L ag o o n o f V en ic e, T ri es t G B R : D o v ey E st u ar y ; S w ed en : T ja er n o ; U S A : C ap e C o d M ic ro ti d al m ar sh es T 3 1 1 1 8 E u ro p ea n co as ts F ra n ce : B an y u ls -s u r- m er , V en d e´e ; S w ed en : T ja er n o O p en m ar in e h ab it at s, ro ck y sh o re s T 4 3 6 Ja p an es e co as t Ja p an : H am an a L ak e B ra ck is h w at er la k e T 5 4 5 4 7 C h il ea n co as t, N ew Z ea la n d , A u st ra li a C h il e: L a L ig u a; N ew Z ea la n d : A k ar o a, P o ll en Is la n d , G o v em o rs B ay A u st ra li a: U ll ad u ll a- B u rr il L ak e, P o rt H ac k in g -G ra y s P o in t M ic ro ti d al m ar sh es T 6 2 9 3 6 W ad d en S ea , B al ti c S ea N E C h in a, Ja p an es e co as t T h e N et h er la n d s: M o o k B ai ; G er m an y : W il h el m sh av an ; Ja p an : L ak e S ar o m a, H am an a L ak e; C h in a: Y al u Ji an g M es o /m ac ro ti d al fl at s M ic ro ti d al m ar sh es , ro ck y sh o re s T 7 6 1 2 N o rt h er n A tl an ti c co as t, U S A U S A : G eo rg ia -S ap el o Is la n d , B ea u fo rt -N o rt h C ar o li n a M ic ro ti d al m ar sh es T 8 2 2 R ed S ea Is ra el : T ab a O p en m ar in e h ab it at s T 9 2 3 N o rt h er n A tl an ti c co as t, U S A U S A : L o n g Is la n d M ic ro ti d al