ATOLL RESEARCH BULLETIN NO* 271 CAY SAL BANK
Transcription
ATOLL RESEARCH BULLETIN NO* 271 CAY SAL BANK
A T O L L RESEARCH B U L L E T I N NO* 271 CAY S A L BANK, BAHAMAS: A B I O L O G I C A L L Y I M P O V E R I S H E D , P H Y S I C A L L Y T R O L L E D ENVIRONMENT SEPTEMBER 198 3 CAY S A L BANK, BAHAMAS: A B I O L O G I C A L L Y IMPOVERISHED P H Y S I C A L L Y CONTROLLED ENVIRONMENT 1 by Walter M. Goldberg ABSTRACT Cay Sal Bank is a shallow water, oceanic platform whose lagoonal surface is 9-16m below sea level. Benthic communities on the bank are divided into four major zones based upon biotic composition and substrate. These are (1) rubble- Lobophora 12) Sargassm-gorgonian-sponge (3) Halodule and associates aKd ( ) a patchy Thalassia zone. Sediment is largely restricted to the western portion of the lagoon, especially in zone 3. Although occasional patch reefs are noted, the bank lagoon is virtually devoid of coral reefs and coral communities, The submerged, leeward bases of islands and cays represent the principal substrate for the development of scleractinian corals, but these do not appear to form a reef framework, Scleractinian development on the windward sides of the islands is negligible, Patch reefs and spur and groove systems are usually poorly developed on the outer bank slope to depths approaching 30m, The best developed coral communities occur below this depth with the exception of the southwestern sector where reefs are smothered in sediment, The biological structure of the bank lagoon is interpreted as being controlled largely by wind and periodic storm forces that result in frequent resuspension and eventual offbank transport of sediment, especially to the southwest, Gay SaX is not a drowned bank; it is a submerged platform on which biological impoverishment appears to be maintained through disturbance phenomena engendered by an open and poorly developed rim. These stresses prevent establishment of more complex coral reefs or coral communities, and promote domination by fleshy algae and other more tolerant organisms. l ~ e ~ a r t m e nof t Biological Sciences, Florida International University, Miami, Florida 33199, U.S.A. (Manuscript received March 1983 - Eds.) INTRODUCTION Cay S a l Bank i s a s h a l l o w , d e t a c h e d c a r b o n a t e bank l y i n g r o u g h l y 1 0 0 km s o u t h o f t h e F l o r i d a Keys, 54 km n o r t h o f Cuba a n d 50 km w e s t o f t h e G r e a t Bahama Bank ( F i g . 1 ) . I t i s 1 0 5 km by 6 6 km i n i t s g r e a t e s t d i m e n s i n s , and c o n s t i t u t e s a n o v e r a l l a r e a o f n e a r l y 4000 km The r i m i s l i n e d w i t h a s c a t t e r i n g o f i s l a n d s and r o c k s e s p e c i a l l y a l o n g t h e n o r t h e r n and e a s t e r n margins. Over 9 9 p e r c e n t o f t h e bank i n c l u d i n g t h e s o u t h e r n f l a n k a n d t h e e n t i r e c e n t e r a r e c o m p l e t e l y submerged, p r i m a r i l y i n d e p t h s r a n g i n g from 9-16m. 9. Few s t u d i e s h a v e b e e n made o f t h i s r e g i o n i n s p i t e of i t s s i z e and p r o x i m i t y t o U,S, c o a s t a l w a t e r s . Agassiz ( 1 8 9 4 ) v i s i t e d t h e b a n k , b r i e f l y d e s c r i b i n g some o f i t s geomorphic f e a t u r e s ; a d e s c r i p t i o n o f t h e bathymetry o f t h e bank s l o p e ( M a l l o y ti H u r l e y , 1 9 7 0 ) a n d s t r a t i g r a p h i c s t u d i e s from a w e l l d r i l l e d t o 5766111 by S t a n d a r d O i l Company (Myerhoff & H a t t e n , 1 9 7 4 ) h a v e made more r e c e n t c o n t r i b u t i o n s t o o u r knowledge o f t h e a r e a , However, d e s c r i p t i o n s o f t h e m a r i n e c o m m u n i t i e s of Cay S a l Bank h a v e a p p a r e n t l y n o t been p u b l i s h e d , T h i s paper d e s c r i b e s t h e n a t u r e and d i s t r i b u t i o n of t h e s h a l l o w - w a t e r c o m m u n i t i e s o f Cay SaP Bank by a e r i a l a n d s a t e l l i t e photographk., c o u p l e d w i t h s h i p - b a s e d b o t t o m Physical t r u t h i n g by SCUBA o b s e r v a t i o n a n d d r e d g e s a m p l i n g . f a c t o r s i n c l u d i n g s t o r m t r a c k s and f r e q u e n c y , wind a n d wave d a t a and s e d i m e n t d e p t h s on t h e bank l a g o o n a r e a n a l y z e d a n d r e l a t e d t o community s t r u c t u r e . M a t e r i a l s a n d Methods A t o t a l o f 1 8 d a y s w e r e s p e n t on Gay S a l Ban Biologics d u r i n g t h e sumxer months o f 1980-1982, t i o n s w e r e made a t 9 7 s t a t i o n s s c a t t e r e d a c r o s s t h e s h a l l o w These Lagoon a n d o u t e r m a r g i n t o a d e p t h of 6 0 m ( F i g , 2 ) . c o n s i s t e d of simple v i s u a l surveys t o confirm composition o f the b e n t h o s , c o l l e c t i o n s assisted minute Gapeto redge tows, Samples o m a t e r i a l s hav e n d e p o s i t e d i n the FIU e x c e p t a s n o t e d ere i d e n t i f i e d by t h e a u t h o r . S e d i m e n t d e p t h s were r e c o r d e d a t 27 s t a t i o n s (1982 o n l y ) using a steel probe, Where s e d i m e n t s e x c e e d e d a d e p t h o f o n e m e t e r , a 2 1/2 HP w a t e r pump was employed t o f o r c e s e a Sediment w a t e r t h r o u g h a 5 meter l e n g t h o f PVC p i p e . f l u i d i z e d i n t h i s manner e n a b l e d t h e p i p e t o q u i c k l y p e n e t r a t e t o bedrock. The names o f emergent i s l a n d s u s e d i n t h i s p a p e r correspond t o t h o s e given i n B r i t i s h Admiralty Chart No. 1217 ( F i g . 2 ) . C o o r d i n a t e l o c a t i o n s have been m o d i f i e d a c c o r d i n g t o more r e c e n t d a t a (see a p p e n d i x ) . RESULTS a. The Lagoonal Environment The l a g o o n a l s u r f a c e o f t h e bank c a n b e d i v i d e d i n t o f o u r major b i o t i c zones ( F i g . 3 ) . The n o r t h w e s t e r n s e c t o r w i t h i t s i n c l u d e d s a n d r i d g e s i s c h a r a c t e r i z e d by a s p a r s e b u t c o n s i s t e n t c o v e r o f s e a g r a s s e s and a l g a e i n c l u d i n g H a l o d u l e w r i g h t i i , C a u l e r p a s p p . , Syringodiurn f i l i f o r m e and v a r i o u s s p e c i e s o f c a l c a r e o u s c h l o r o p h y t e s ( F i g . 4 A ) . Members o f t h i s community ( h e r e a f t e r r e f e r r e d t o a s t h e Halodule community) a r e summarized i n T a b l e 1. A d e n s e r H a l o d u l e community a p p e a r s t o be r e s p o n s i b l e f o r s e v e r a l o f t h e l a r g e d a r k p a t c h e s n o t e d i n s a t e l l i t e imagery of t h i s zone, The s e d i m e n t c o v e r o f t h i s q u a d r a n t r a n g e s from 2 c m t o 1 m. The d e e p e r s a n d a c c u m u l a t i o n s o c c u r b e h i n d and s o u t h o f Double Headed S h o t Cays, ( h e r e a f t e r r e f e r r e d t o a s DHS Cays) p a r t i c u l a r l y i n a s s o c i a t i o n w i t h t h e i n t e r s e c t i n g s e t s o f bedforrns prominent i n t h e w e s t e r n p a r t o f t h e z o n e , and t h o s e t r e n d i n g NE t o SW 20 km t o t h e e a s t , The H a l o d u l e zone g r a d e s i n t o a s e d i m e n t - b a r e , r u b b l e bottom e a s t o f Muertos Cays. T h i s n o r t h e a s t e r n s e c t o r i s c o v e r e d by a mixed Sargassum-gorgonian-sponge community. The r u b b l e c h a r a c t e r i s t i c o f t h e n o r t h e a s t bank l a g o o n continues throughout t h e southeast s e c t o r b u t without a s much v e g e t a t i o n , The bottom i s c o v e r e d p r i m a r i l y by a s c a t t e r i n g o f t h e brown a l g a Lobophora v a r i e g a t a , w i t h an o c c a s i o n a l c l u s t e r of sponges and g o r g o n i a n s as above, Along t h e s o u t h e r n and e a s t e r n b o r d e r s o f t h i s zone t h e r u b b l e i s i n t e r s p e r s e d w i t h a g g r e g a t i o n s of c o r a l s , e s p e c i a l l y D i p l o r i a s p p , , A g a r i c i a a g a r i c i t e s and M o n t a s t r e a a n n u l a r i s , t o g e t h e r w i t h s p o n g e s and g o r g o n i a a s ( F i g , For t h e most p a r t t h e s e do n o t form p a t c h r e e f s f i . no a p p r e c i r e l i e f above b o t t o m ) , However, two r e e f a r e a s a r e e n c o u n t e r e d a l o n g t h e w e s t e r n edge o f t h i s zone a s n o t e d i n f i g u r e 3. One o f t h e s e n e a r 23'34' and 7 9 ° 4 8 ~ o n s i s t so f numerous b u t s m a l l (1-2mZ) D i p l o r i a , P o r i t e s and M o n t a s t r e a p a t c h e s r i s i n g l m above t h e bottom ( d e p t h = 7-8m). The most s i g n i f i c a n t p a t c h r e e f a r e a , s e v e r a l km2 i n e x t e n t , i s l o c a t e d 10 krn s o u t h w e s t o f Damas Cays. T h i s subzone was c h a r a c t e r i z e d by t h i c k e t s o f Acro o r a c e r v i c o r n i s r i s i n g t o a d e p t h o f 6m from a 10m b 0 t t . h 4 C ) . Scattered c o l o n i e s o f M o n t a s t r e a a n n u l a r i s- , ~ g a r i c i aa g a r i c i t e s and I t may b e C o l p o p h y l l i a n a t a n s c o n t r i b u t e t o t h e framework, s i g n i f i c a n t t h a t much o f t h e r u b b l e s u b s t r a t e i n t h i s zone consists of what appears to be recent Acropora cervicornis. There is little evidence of recolonization. The last zone consists of a sigmoidally shaped area extending across the bank from Cay Sal to the Damas Cays. This area is characterized by patches of Thalassia testudinum which become somewhat more extensive toward the southwestern (leeward) side. Turtle grass becomes particularly well developed in the lee of larger islands on the bank, especially the Double-Headed Shot Cays and the Anguilla Cays (Fig. 4E). Farther behind the latter group, Thalassia grades into a Halodule-calcareous green algae subzone (Fig. 3). At the edges of this area Thalassia intermingles with other communities. This is particularly notable west of Damas Cays where zonation overlap is extensive (Fig. 3)The Damas Cays area is also notable for the existence of several "blue holes" (Capt, Bob Mbein, pers, corn,). One of these located at 23O49@8% and 70°47'28, 2. the islands, was briefly investigated. It measures approximately lOOm across and lO0m deep, beginning on the bank at a depth of 10-b3m (surface to bottom = 110-ll3m). The surrounding area is a Thalassia-gorgonian-sponge bottom, grading into colonies of Montastrea cavernosa and Agaricia agaricites at the edge of the blue hole, The variegata to a vertical walls are covered wit depth of l8m, below which Halimeda goreauii dominates, Submersible observations at the bottom reveal numerous Strornbus qigas shells apparently the result of the animal becoming entrapped while migrating through the surrounding turtle grass ( E , Shinn, pers, comm.). A wider and slightly deeper blue hole is located a few km farther west (Fig* 4F), The sediment cover of the Thalassia zone is highly variable, Through most of this region the range is 2-5cm, increasing to 20-60cm under Thalassia itself, Just north of Gay Sad Island in an area covered by a mixed community of scattered angiosperms and cabcareous green algae, a sand body 4-4-5 meters deep was encountered (Pig, 4@), The area covered by this accumulation was not several sediment stations taken around the periphery of Cay Sal indicates that it is highly localized, b. The Bank Rim and Slope The only areas characterized by substantial coral development are the bank slope below 30m and the submerged portions of the islands. Most of the larger cays have been examined and appear to be uniform with regard to their flora and fauna from the littoral zone to the base of the island (Table 1). The sublittoral portions are characterized by an intertidal bench cemented with an unidentified encrusting coralline alga. Immediately below this surge zone, dropping vertically to a depth of 7-8 m, is a coral community consisting of yellow and purple sea fans (Gorgonia ventalina and G. flabellurn) plus a variety of other gorgonians, corals-and hydrocorals, especially Millepora complanata (Fig. 5A). In general the amount of scleractinian development is greater along the northern border of islands, but only along the lagoonal side where Montastrea annularis, Diploria spp. Siderastrea siderea, Agaricia agaricites and Porites porites become especially numerous (Table 1, Fig. 5B). However, the coral communities appear to be insufficiently developed under the best of circumstances to prevent erosion of the underlying substrate. Large blocks of island material are usually found adjacent to the cays and these serve as substratum for additional albeit superficial coral development (Fig. 5C ,D), Shallow water coral development along the oceanic side of the islands is not appreciable, Acropora palmata, for example, is found only in isolated pockets (e.g. between Water Cays and some of the Damas Cays, There is no "palrnata zon@ (cf, Geister, 1977) characteristic of any of the islands. Along the eastern bank there is little difference between exposed and sheltered sides of the islands with regard to coral development. The same species of coral as noted above form spurs <lm in height in 10m depth directly in front of many islands along the Santaren Channel. However, even this limited amount of coral growth does not occur on the ocean side of the DHS Cays where the bottom at lorn is composed of rock colonized by Sargassum spp., Dictyosphaeria cavernosa and Microdictyon sp., along with occasional gorgonia and sponges (Fig. 5 E ) . Coral communities are not developed on either the exposed nor the sheltered sides of south guilla Cay or Cay Sal due to accumulation of sand, In depths of 15 to 2 5 m along the eastern bank, spurs 3m high are covered by cervicornis, iderastrea siderea, Hontastrea ann onq with Jarq quantities gorgonians, ~ a l i r n e d a s ~ _ of south Anauilla Cav (in the ~icholasCZ groove deveiopment is somewhat greater (Fig. 6 ~ but ) simil in composition and in coral density to those at Dog Rocks. There appear to be no comparable coral communities in thes depths along the DHS Cays or near Cay Sal. 4 . Outer reef slopes have been investigated briefly on several sides of the bank in depths ranging from 25-60m. At 25m the angle of slope begins to increase, allowing a relatively dense algae-sponge-gorgonian community. Some scleractinian coral development is also in evidence but is not strongly represented (Fig. 6B). The outer reef escarpment ("dropoff") begins at 44-46m on the eastern side of the bank and at 38-40m on the western and northwestern sides. There is a substantial difference in the structure of the deep reefs developed on these slopes. Off south Anguilla, for example, the dominant organisms are Lobophora variegata and Halimeda spp. interspersed by sponges, some coral (primarily Montastrea spp.), whip-like gorgonians (Ellisella and Eunicea spp.) and antipatharians (Cirrhipathes luetkeni). The diversity of deep reef organisms here is relatively low; the face of the escarpment is smooth, without appreciable development of ledges, caves and overhangs. The same description applies to the deep reefs off southern Dog Rocks, however diversity of organisms and relief in the slope is somewhat greater off the northern Dog Rocks group, Scleractinian coral development at depths below 25m is greatest off the northwestern and western border of the bank, along the edge of the Straits of Florida, Off Elbow Cay, for example, an appreciable development of Montastrea spp. Porites astreoides and Wgaricia agaricites begins at 25m (Fig. QC), The latter species forms an extensive cover that continues over the escarpment to depths of at least 50m, The central portion of the western bank margin drops precipitously into the Straits of Florida. The outer reef slope here is as well developed as I have seen it in this area. The escarpment beginning at 38m is characterized by spurs extending seaward nore than lorn from the wall. From the amount of coral cover these appear to be the result of recent growth although no cores have been taken. Flat, platey forms of Montastrea spp. and Agaricia lamarcki, along with large colonies'of Colpophyllia natans dominate these structures along with numerous sponges, gorgonians and antipatharians (Fig. QE), In direct contrast, the outer slope around Cay Sal island has no reef development at all; off the northern end in particular, the outer reef slope is totally inundated with sediment (Figs, 6D,7). DISCUSSION Unlike the larger Bahamian banks, Cay Sal has a largely submerged, poorly developed rim. Agassiz (1894) and Davis (1928) refer to the bank as a drowned atoll emphasizing the apparent inability of coral growth to keep pace with subsidence or rise in sea level. The process of drowning may be initiated by a variety of factors (reviewed by Schlager, 1981) which commonly result in bank or platform surfaces 50m or more below present sea level (Davis, 1928). In such cases the use of the term "drowning" may be justified because processes operating in the past have placed reefassociated organisms out of their effective depth range for photosynthesis. Cay Sal Bank lagoon, on the other hand is only 9-16 m deep, submerged, but well within the range of appreciable carbonate production (Schlager, 1981) and reef growth (Macintyre, 1967; Porter, 1973; Goreau & Land, 1974; ~iitzler& Macintyre, 1982). As noted above, reef growth is occurring on at least some of Cay Salts deeper margins. Therefore the notion of reef drowning as means of accounting for this bank's present biotic composition is untenable. The antithesis of platform drowning is physical control by shallow water processes. Shallow water is subject to a wide variety of environmental alterations inimical to reef development. These may include exposure and thermal et al,, 1982) chemical disturbances (Glynn, 1968; Roberts et al., 1959; Voss c Voss, 1960; alterations (Newell Milliman, 1 9 7 3 ) and floods of fresh or turbid water (Goodbody, 1961; Lighty et aE., l 7 8 ) , Although none these processes is likely operati e on Cay Sax Bank to such stresses may have served to reduce early olocene reef growth enough to account for its poorly developed rim, The hack of a protective rim, in turn, may have promoted conditions which account for the sparsely colonized, bow diversity, ahermatypic environment typical of the bank shallows. Although the mechanisms and trends of the sequential replacement of communities through time are controversial (Connell & Slayter, 1977; Sousa, 1980; Greene & Schoener, l982), the process of succession is generally understood to culminate in one or more communities called chimaxes, Such communities are widzspread in a given ciimatic regime and are typically characterized y an equilibrium between production and respiration, a re a t i v e k y high diversity of species, a well-developed spacial structure and a complex food web lodurn, 1969) , In the coral reef enviro normal successional process redicts eventual st of soft bottom communities by Thalassia ( G i n s b u r g & Lowenstam, 1 58; Patriq~in,1975) or coral communities (Jones, 1977)- However, it is generally recognized that local conditions may often prevent the succession to climax, In these cases, terms such as edaphic climax, cyclic climax, disclimax or subclimax have been applied ( O d m , 1971) Species diversity as one of the more readily measurable ecological parameters, is often employed as a standard by which the degree of community complexity can be gauged, High diversity is maintained by some measure of disturbance or non-equilibrium conditions that prevents monopolization of resources by superior competitors (Connell, 1978; Pearson, 1981; Sheppard, 1982). However, frequent and/or s e v e r e d i s t u r b a n c e c a n r e t u r n t h e community t o an immature ( e a r l y successional) s t a g e o r perhaps i n h i b i t succession entirely. F o r example D o l l a r (1982) found t h a t wave and s t o r m stress c a u s e d f r e q u e n t mass m o r t a l i t i e s on a n Hawaiian r e e f , r e s u l t i n g i n a low d i v e r s i t y , r e l a t i v e l y s i m p l e c o r a l r e e f community. F r e q u e n t l y a f t e r d i s t u r b a n c e by s t o r m s o r o t h e r s t r e s s e s , damaged r e e f s w i l l be c o l o n i z e d by f l e s h y a l g a e ; t h e i r c o n t i n u e d dominance i s l i m i t e d by t h e t i m e r e q u i r e d f o r r e c o v e r y o f t h e c o r a l community ( P e a r s o n , 1 9 8 1 and c o n t a i n e d r e f e r e n c e s ) . Thus a l g a l dominated r e e f s may b e viewed a s an i n d i c a t i o n o f d i s t u r b a n c e t o a d e g r e e t h a t does n o t a l l o w t h e normal p r o c e s s o f s u c c e s s i o n o r r e c o v e r y t o o c c u r . L i g h t y (1981) h a s d e s c r i b e d s u c h an environment i n t h e n o r t h e r n Bahamas (which h e u n f o r t u n a t e l y r e f e r s t o a s a " c l i m a x community") and c o r r e l a t e s t h i s c o n d i t i o n w i t h h i g h e n e r g y stress. A someet a l , (1977) what s i m i l a r s i t u a t i o n i s d e s c r i b e d by Adey i n t h e Lesser A n t i l l e s . The f o l l o w i n g e v i d e n c e s u g g e s t s t h a t Cay S a l B a n k ' s low c o r a l d i v e r s i t y ( T a b l e 1) and dominance by f l e s h y a l g a e a s w e l l a s o t h e r f l o r a , i s a l s o a f u n c t i o n of e n v i r o n m e n t a l stress. The l a g o o n o f Gay S a l i s dominated by t h e s e a g r a s s Malodule w r i g h t i i and a s s o c i a t e s , H a l o d u l e i s an o p p o r t u n i s t species t h a t colonizes areas e i t h e r unsuitable for Thalassia o r a r e a s where T h a l a s s i a h a s become d i s t u r b e d bv * storms o r o t h e r f a c t o r s (den H a r t o g , 1 9 7 7 ) . A s a p i o n e e r , H a l o d u l e i s a poor c o m p e t i t o r and u n d e r normal c o n d i t i o n s i s r e p l a c e d by s p e c i e s wikh more e x t e n s i v e , s t a b i l i z i n g b l a d e and rhizome s y s t e m s ( S c o f f i n , 1970; B u r r e l l and S c h u b e l , 1 9 7 7 ) . T h i s s u c c e s s i o n i s n o t e v i d e n t a t Cay S a l where T h a l a s s i a i s s t r o n g l y developed only i n t h e l e e of l a r g e r i s l a n d s . The d i s t r i b u t i o n of s e d i m e n t on t h e bank (Fig. 3 ) s roughly with t h e g e n e r a l d e s c r i p t i o n g i One o f t h e more s t r i k i n g a s p e c t s o f t d i s t r i b u t i o n i s t h e m o u n t s f ank s u r f a c e s e d i m e n t . More t h a n h a l f of t h e lagoon i s e s p e c i a l l y t h e e a s t e r n s i d e , The s e d i m e n t is concentrated largely i n i n c r e a s e s toward t o f s a n d waves b e h i n d D H S Cays, and i n a r e l a t i v e l y ) s a n d body r e s t r i c t e d t o t h e n o r t h s i d e of Cay S a l I s l a n d . The v i r t u a l a b s e n c e o f s e d i m e n t on t h e e a s t e r n margin and i t s a c c u m u l a t i o n toward t h e s o u t h w e s t s u g g e s t s a c t i v e t r a n s p o r t , Moreover, t h e s m o t h e r i n g o f t h e o u t e r r e e f s l o p e c o r a l communities around Cay S a l I s l a n d p r o v i d e s e v i d e n c e t h a t t h i s t r a n s p o r t is o f f b a n k , a s c o n f i r m e d r e c e n t l y by seismic p r o f i l e s ( H i n e , p e r s o n a l communication). Wind and s t o r m g e n e r a t e d f l o w s a r e l i k e l y a g e n t s o f et a l . , 1981; Hubbard et al,, o f f b a n k s e d i m e n t t r a n s p o r t (Hine 1 9 8 1 ) . Two c a t e g o r i e s o f s t o r m s t o c o n s i d e r a r e a c u t e , p e r i o d i c t r o p i c a l s t o r m s o c c u r r i n g i n summer and t h e more regular, chronic disturbances associated with t h e passage of w i n t e r f r o n t a l systems. A c h a r t d e p i c t i n g t h e approximate p a t h o f t r o p i c a l s t o r m and h u r r i c a n e s y s t e m s p a s s i n g w i t h i n L O O km o f Cay S a l Bank i s p r e s e n t e d i n F i g u r e 8 , Although n o d a t a a r e g i v e n on s t o r m i n t e n s i t i e s , 32 c y c l o n i c s t o r m s have been n o t e d s i n c e 1871, p l u s an a d d i t i o n a l 4 t r o p i c a l depressions. Nine s t o r m s o r h u r r i c a n e s h a v e c r o s s e d t h e s o u t h e a s t e r n bank i n t h e v i c i n i t y o f t h e A n g u i l l a Cays, 9 more h a v e c r o s s e d ( o r p a s s e d p a r a l l e l ) i n an e a s t - w e s t d i r e c t i o n , w h i l e a n o t h e r 7 c r o s s e d t h e bank n e a r Cay S a l e Given t h e o p e n n e s s o f t h e b a n k , s e v e r e s t o r m s and h u r r i c a n e s a r e c e r t a i n t o e f f e c t damage, e v e n on d e e p e r r e e f s ( c f . Woodley, 1 9 8 0 ) . However, t h e o v e r a l l i m p o r t a n c e o f t r o p i c a l With a n a v e r a g e s t o r m s on Cay S a l i s d i f f i c u l t t o a s s e s s . o f 3 s t o r m s p e r d e c a d e , Cay S a l i s l e s s f r e q u e n t l y a f f e c t e d by s u c h s y s t e m s t h a n t h e F l o r i d a Keys o r L i t t l e Bahama Bank where an a v e r a g e o f 7-8 s t o r m s p e r d e c a d e o c c u r s et a l . , 1977; Wine, 1 9 7 7 ) . D u r i n g t h e l a s t d e c a d e (Neumann o n l y one h u r r i c a n e h a s p a s s e d n e a r t h i s a r e a ( 1 9 8 1 ) ; moreo v e r , t h e p a t t e r n of storm c r o s s i n g s does n o t correspond w i t h e i t h e r t h e d e g r e e o f community development o r t h e p a t t e r n of o b s e r v e d s e d i m e n t a c c u m u l a t i o n , The s m a l l amount o f hydrographic/meteorological i n f o r m a t i o n a v a i l a b l e f o r t h e a r e a i s summarized i n F i g u r e 9. Winds a r e p r i n c i p a l l y from t h e e a s t d u r i n g most o f t h e y e a r b u t d i s p l a y a p r o m i n e n t s h i f t t o t h e n o r t h and n o r t h e a s t d u r i n g t h e winter. T h i s change c o r r e s p o n d s w i t h t h e i n c r e a s e i n The p a s s a g e o f p e r c e n t o f s e a and s w e l l n e a r t h e bank, f r o n t a l s y s t e m s from t h e n o r t h and n o r t h e a s t i s a r e l i a b l e and p e r s i s t e n t w i n t e r phenomenon i n t h i s r e g i o n (U.S. Naval Weather S e r v i c e Cornand, 1 9 7 5 ) and may a c c o u n t f o r t h e following observations, 1) Wcropora c e r v i c o r n i s r u b b l e i s common i n t h e s o u t h e a s t e r n s e c t o r o f t h e bank w h i l e l i v i n g c o l o n i e s a r e r e l a t i v e l y uncommon, S t o m f o r c e s may p r o v i d e r u b b l e s u b s t r a t u m t h r o u g h r e c u r r e n t c y c l e s o f Acropora g r o w t h and r e c o v e r y H a l l , 1 9 7 6 ; T u n n i c l i f f e , 1 9 8 1 ) f o l l o w e d by s t o r m destruction. The dominance o f a n u n s t a b l e r u b b l e s u b s t r a t e i n t u r n r e d u c e s t h e chance of c o r a l s u r v i v a l and r e c o l o n i z a t i o n ( G o r e a u , 1 9 5 9 ; S t o d d a r t , 1974; P e a r s o n , 1 9 8 1 ) . 2 ) The b e s t d e v e l o p e d s h a l l o w c o r a l communities a r e on t h e p r o t e c t e d l a g o o n s i d e o f t h e n o r t h e r n c a y s ; t h e The p o o r e s t development i s on t h e u n p r o t e c t e d o c e a n s i d e . r e a s o n f o r t h i s c o n t r a s t may b e t h e a b r u p t t r a n s i t i o n between s h a l l o w and d e e p w a t e r t h a t a l l o w s l a r g e waves t o pound t h e o u t s i d e of t h e s e cays. For e x a m p l e , a 50 km h r - 1 wind from t h e n o r t h o r n o r t h e a s t w i l l p r o d u c e waves a t l e a s t 3.2 m h i g h (U.S. Army CERC, 1 9 7 3 ) . Such wind/wave c o n d i t i o n s a r e p r o b a b l y common n e a r Cay S a l (see b e l o w ) . 3 ) A T h a l a s s i a zone f i r s t n o t e d i n 8m d e p t h b e h i n d n o r t h e r n Dog Rocks d u r i n g J u l y , 1 9 8 1 , was r e p l a c e d by r u b b l e t w e l v e months l a t e r . A e r i a l p h o t o g r a p h s t a k e n d u r i n g May, 1982 r e v e a l e d c r e s c e n t i c "blowout'' s t r u c t u r e s i n T h a l a s s i a b e d s b e h i n d Water Cays i n 8-9m d e p t h ( F i g s . 6 D , E ) , a n d n o r t h o f Cay S a l i n s i m i l a r d e p t h s ( F i g . 4C). T h e s e a r e known t o r e s u l t from s t o r m damage a n d i n d i c a t e t h e d i r e c t i o n o f e n e r g y p r o p a g a t i o n ( P a t r i q u i n , 1 9 7 5 ) . The b l o w o u t s on Cay S a l Bank are concave from t h e n o r t h . Storm-induced b o t t o m c u r r e n t s and wave a c t i v i t y , a r e c a p a b l e o f c o n s i d e r a b l e s e d i m e n t r e s u s p e n s i o n and t r a n s p o r t e t a l . , 1981; Murray et a l . , 1 9 7 7 ) known t o b e (Mine -d e t r i m e n t a l t o c o r a l d e v e l o p m e n t (Dodge et a l . , 1 9 7 4 ; Loya, l 9 7 6 ) , The amount o f t r a n s p o r t c a n b e e s t i m a t e d u s i n g e s t a b l i s h e d r e l a t i o n s h i p s ( F i g s . 3-15, 3 - 2 9 , 4-20 and 4-21 i n U,S. Army CERC, 1 9 7 7 ) b e t w e e n wind stress and maximum i n d u c e d m o t i o n on t h e s e a f l o o r (Urnax(-dl, N o r t h e a s t and e a s t e r l y w i n d s n e a r Cay S a l r e a c h s p e e d s 0-25% of t h e t i m e d u r i n g October-April. o f 50 krn h s - 1 , Winds d u r i n g t h s t h e r months a p p r o a c h t h i s s p e e d o n l y 6-12% o f t h e t i m e ( U , S . Naval Weather S e r v i c e Command, l 9 7 5 ) , Winds o f 50 krn h r - I from t h e e a s t i n % I m w a t e r d e p t h ( a v e r a g e l a g o o n d e p t h ) w i l l g e n e r a t e waves 1,4m h i g h , w i t h p e r i o d s o f 4.7 s e c and w i l l p r o d u c e Urnax(-d) o f 25 c m sec-l on t h e l a g o o n f l o o r . T h i s i s w i t h i n t h e g e n e r a l l y a c c e p t e d r a n g e o f 1 5 - 30 c m sec-l r e q u i r e d f o r f i n e t o m o d e r a t e s i z e d s a n d g r a i n m o t i o n ( U . S . A m y CERC, 1 9 7 7 ; see a l s o d i s e u s s i o n i n Mine et a l . , 1 9 8 1 ) . The p r i n e i p a l l i m i t a t i o n t o b o t t o m c u r r e n t g e n e r a t i o n w i t h e a s t e r l y w i n d s on Cay S a l i s t h e l i m i t e d f e t c h ( 6 5 km), However, w i t h w i n d s from t h e Thus a 50 km h r - I northeast, fetch increases 2 l/2 fold. wind w i l l p r o d u c e waves 1 - 5 m h i g h , w i t h p e r i o d s o f 5 , 2 sec and w i l l p r o d u c e urnax(-df o f 7 cm sec-a, This f i g u r e is o v e c r i t i c a l v e l o c i t y and may a c c o u n t for a c c u m u l a t i o n of sediment toward t h e southwest, a s w e l l a s d i s t u r b a n c e t o the l a g o o n and SW bank s l o p e c o m u n i t i e s , Thus t h e p h y s i c a l e n v i r o n m e n t of Cay S a l Bank a p p e a r s t o b e s u f f i c i e n t l y v i g o r o u s t o p r o d u c e d i r e c t wave stress as w e l l a s current-induced sediment stress, These c o n d i t i o n s , w h i l e by n o means u n i q u e , combine w i t h t h e h i s t o r i c a l l y d e r i v e d l a c k o f a p r o t e c t i v e r i m t o produce high energy c h a n n e l s i n t o t h e bank i n t e r i o r . The r e s u l t i s t h e m a i n t e nance of a v i r t u a l l y r e e f l e s s environment. Table 1. Marine plants and invertebrates characteristic of Cay Sal Bank Lagoon. Zones: 1 = Halodule, 2 = Thalassia, 3 = Rubble-Lobophora, 4 = Sargassumgorgonian-sponge, 5 = Island-littoral Angiosperms Zone Halodule wrightii Ascherson Thalassia testudinum Koenig Syringodium filiforme Kutzing Algae Avrainvillea nigricans Becaisne Caulerpa prolifera Lamoroux Caulerpa cupressoides Agardh Cladophora sp. Dasycladus vermicularis Krasser Dictyopteris justii Lamoroux Dictyosphaeria cavernosa Boergesen Dictyota dentata Lamoroux Galaxaura squakida Kjellrnan HaLirneda incrassata Lamoroux Malimeda lacrirnosa Mowe Malirneda opuntia (Lamoroux) Laurencia papillosa (Forsskal) Lobophora variegata Womersley Microdictyon sp. Padina sanctae-crucis Boergesen Penicillus capitatus Lamarck Penicillus dumetosus (Lamoroux) Penicillus pyriformis Gepp .Rhipocephalus phoenix Kutzing Sargassum cymosum Agardh Sargassum hystrix Agardb Sargasswrn polyceratium Taylor Sargassum vulgare Agasdh Stypopodium zonale Papenfuss Turbinaria turbinata Muntae Udotea spinulosa Bowe Sponges Anthosigmella varians var. incrustans (D&M) Spheciospongia vesparium (Lamarck) Goraonians Eunicea spp. Gorgonia flabellurn Linn. Gorgonia ventalina Linn. Muricea muricata (Pallas) Muriceopsis f3avida (Lamarck) 5 lP2,3t4 Plexaura flexuosa Lamoroux Plexaura homomalla (Esper) Plexaurella spp. Pseudopterogorgia americana (Gmelin) Pterogorgia anceps (Pallas) Scleractinians Acropora cervicornis (Lamarck) Agaricia agaricites (Linn.) Diploria labyrinthiformis (Linn.) Diploria strigosa (Dana) Montastrea annularis (E&S) Porites astreoides Lamarck Porites porites Lamarck Siderastrea siderea (E&S) ' Molluscs Wcanthopleura granulata Gmelin Acmea antillarum Sowerby Antigonia listeri Gray Chione paphia Linn, Chiton squamosus Linn, Echininus nodulosus Pfeiffer Glycymeris undata Gmelin Laevicardium kaevigatum (%inn,) Littorina zic-zac Gmelin Livona pica Gray Nerita peloronta Linn, Nerita versicolor Gmelin Purpura patula Linn. Strombus costatus Gmelin Stsonbus gigas Linn, Tais rustica Lmarck Teetarius murieatus &inn, Arthropods G r a p s u s grapsus IEinn,) Metapenaeopsis cf. goodei (Smith) Portunus bahamensis Rathbun Portunus ordwayi (Stimpson) Portunus spinimanus Latreille Tetraclita sp. Echinoderms Astichopus multifidus (Sluiter) Astropecten duplicatus Gray Oreaster reticulatus (Linn.) REFERENCES Adey, W., Adey, P., Burke, R. and Kaufman, L. 1977. Holocene reef systems of eastern Martinique. Atoll Res. Bull. 218:l-40. Agassiz, A. 1894. 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F u n d a m e n t a l s o f E c o l o g y , 2nd Ed. W.B. S a u n d e r s , P h i l a d e l p h i a , 574 p p . P a t r i q u i n , D.G. 1975. "Migration" of blowouts i n seagrass beds a t Barbados and Capriacou, W e s t I n d i e s and i t s e c o l o g i c a l and g e o l o g i c a l i m p l i c a t i o n s . A q u a t i c BOt. 1 2 1 6 3 1 8 9 . P e a r s o n , R.G. 1 9 8 1 , R e c o v e r y a n d r e c o l o n i z a t i o n o f c o r a l reefs. Mar. E c o l . P r o g . S e r . 4:105-122. P o r t e r , J . W . 1973. Ecology and composition o f deep r e e f c o m m u n i t i e s o f t h e t o n g u e o f t h e o c e a n , Bahama I s l a n d s , D i s c o v e r y 9:3-12. R o b e r t s , . t i . H . , R o u s e , L . J . , J r , , i d a l k e r , N , D , , a n d HudS'Qn, J,M. 1 9 8 2 , c o l d w a t e r stress i n F l o r i d a Bay a n d n o r t h e r n Bahamas: a p r o d u c t o f w i n t e r c o l d - a i r o u t b r e a k s . 52~145-155, J o u r n . Sed. P e t r o l . ~ i i t z l e r ,K,, M a c i n t y r e , I , G , 1 9 8 2 , T h e h a b i t a t d i s t r i b u t i o n a n d community s t r u c t u r e o f t h e b a r r i e r r e e f complex In: RGtzler, M e , a t C a r r i e Bow C a y , B e l i z e . M a c i n t y r e , I . G . , ( e d s ) The A t l a n t i c b a r r i e r r e e f I. S t r u c t u r e and e c o s y s t e m a t C a r r i e Bow C a y , B e l i z e . c o m m u n i t i e s , S m i t h s o n i a n C o n t r . Mar. S c i . 1 2 . p p . 9-45. . S c h l a g e r , W. 1 9 8 1 . The p a r a d o x o f drowned r e e f s a n d carbonate platforms. Geol. Soc. America. B u l l , 92 :L97-211, S c o f f i n , T , P , 1 9 7 0 , The t r a p p i n g a n d b i n d i n g o f s u b t i d a l c a r b o n a t e s e d i m e n t s by m a r i n e v e g e t a t i o n i n B i m i n i L a g o o n , Bahamas. J o u r , Sed, P e t r o b , - Sheppard, C.R,C, 1982, C o r a l p o p u l a t i o n s on r e e f s l o p e s a n d t h e i r major c o n t r o l s , Mar, E c o l , P r o g , S e r e 7 : 83-115. S o u s a , W.P. 1 9 8 0 . The r e s p o n s e s o f a community t o d i s t u r b a n c e : The i m p o r t a n c e o f s u c c e s s i o n a l a g e a n d 45~72-81, speciess l i f e histories. Oecologia S t o d d a r t , D.R. 1 9 7 4 . P o s t - h u r r i c a n e c h a n g e s o n t h e B r i t i s h Honduras r e e f s : r e - s u r v e y o f 1972. I n : C a m e r o n , A.M. e t a l . ( e d s ) P r o c . S e c o n d I n t l . Symp. Coral Reefs. -Great B a r r i e r Reef Comrn, B r i s b a n e 2:473-483. T u n n i c l i f f e , V. 1981. Breakage and p r o p a g a t i o n o f t h e s t o n y c o r a l Acropora c e r v i c o r n i s . Proc. N a t l . Acad. S c i . 78:2427-2431. U.S. Army C o a s t a l E n g i n e e r i n g Research C e n t e r . 1977. S h o r e p r o t e c t i o n manual V . 1 . U.S. Govt. P r i n t i n g O f f i c e , Washington, D.C. pp. 1-180. U n i t e d S t a t e s Naval Weather S e r v i c e Command. 1975. Summary o f s y n o p t i c m e t e r o l o g i c a l o b s e r v a t i o n s , North American C o a s t a l m a r i n e a r e a s , Vol. 4 . N a t i o n a l C l i m a t i c C e n t e r , A s h e v i l l e , N C . , USA. gp. 80-146. Voss, G . L . , Voss, N . A . 1960. An e c o l o g i c a l s u r v e y o f t h e marine i n v e r t e b r a t e s of B i m i n i , Bahamas, w i t h a c o n s i d e r a t i o n of t h e i r z o o g e o g r a p h i c a l r e l a t i o n s h i p s . 10~96-116. B u l l , Mar. S c i . Gulf and C a r i b . W i l s o n , P , 1909. R e p o r t on t h e b o t a n i c a l e x p l o r a t i o n of J o u r . NY. B o t , t h e i s l a n d s of S a l t Key Bank, dahamas. Garden, 10 :173-176. Woodley, J . D . 1980. H u r r i c a n e A l l e n d e s t r o y s Jamaican c o r a l 287~387. reefs. Nature. West I n d i e s P i l o t , 1957, Hydrographic Dept. B r i t i s h A d m i r a l t y , London, 5 t h e d . v. 3. S t r a t i f i c a t i o n and c i r c u l a t i o n i n t h e Wust, G. 1 9 6 4 . Antillean-Caribbean basins. Columbia U n i v e r s i t y P r e s s , New York, pp. 1-201. ACKNOWLEDGMENTS T h i s s t u d y was made p o s s i b l e t h r o u g h s h i p t i m e g r a n t s T am s u p p o r t e d by t h e F l o r i d a I n s t i t u t e f o r Oceanography, g r a t e f u l t o C a p t a i n R. M i l l e n d e r , J r . , t h e crew of R/V Bellows and t h e s t a f f of FIO f o r t h e i r c o o p e r a t i o n and 1 thank a s s i s t a n c e i n making a s u c c e s s o f t h e s e c r u i s e s , t h e Government of t h e Bahamas, M i n i s t r y of F i s h e r i e s f o r t h e i r c o o p e r a t i o n and c o u r t e s y i n g r a n t i n g p e r m i s s i o n t o c o n d u c t r e s e a r c h i n Bahamian w a t e r s , Funding f o r a e r i a l photography was p r o v i d e d by a g r a n t t o t h e a u t h o r from I t h a n k K e i t h Wylde f o r Florida International University, h i s e x p e r t p i l o t i n g ; M. McLean and M. U p r i g h t t o o k t h e a e r i a l photographs. P. McLaughlin and R. L e m a i t r e i d e n t i f i e d t h e c r u s t a c e a n s and A. Labonte p r o v i d e d t h e equipment u s e d I t h a n k my c o l l e a g u e i n sediment depth d e t e r m i n a t i o n s . J . C . Makemson f o r d r a f t i n g t h e pen and i n k d r a w i n g s and l a b e l s accompanying t h e f i g u r e s i n t h i s p a p e r , and C a p t . Bob K l e i n f o r p r o v i d i n g t h e a e r i a l photograph o f t h e Damas Cay b l u e h o l e ( F i g . 4 F ) . F i n a l l y I t h a n k A . E . Hine f o r comments t h a t c o n s i d e r a b l y improved t h e m a n u s c r i p t . FIGURE LEGENDS Figure 1. Geographic position of Cay Sal Bank from ERTS/ LANDSAT imagery. Scale bar = 10 km. Figure 2. British Admiraly Map No. 1217 (Rev. 1977). Station positions on Cay Sal Bank. Figure 3 . ERTS/LANDSAT composite depicting the biological zones and subzones of Cay Sal Bank, Encircled numbers indicate thickness of sediment in cm. Sand waves in northwest lagoon are covered with Halodule as are NE-SW oriented sand waves to the east. Dark region between these structures is result of denser accumulations of Halodule and calcareous green algae. Note sand accumulation near Cay Sal on the southwest corner. Double Headed Shot Cays, Dog Rocks, Damas Cays and Anguilla Cays are also visible along the bank margin. Figure 4, Communities of Cay Sal Bank Lagoon: (A) Halod-ule-Caulerpa-calcareous green algae community typical of the central lagoon. Note numerous volcano-like burrows, possibly of callianassid shrimp; Sea star Oreaster reticulatus lies next to scale bar, = QOcm; depth = 13m at 23O50'N and 80°20W 13 km SE of ~ l b o wCay. (B) Rubble dominated bottom along southeast bank is occasionally colonized by coral clusters composed of gorgonians, especially ~seudopterogorgia spp., and scleractinians Montastrea annularis, Agaricia agaricites and Porites porites (vertical view, Depth: 13m), (C) Acropora patch reef southwest of Bamas Cays in 7-8m depth at 23O34'N and 79O48'W(D) Aerial view of Thalassia development, eastern Water Cay; scale bar = Sm, Note crescentic blowouts indicating bankward storm direction from the north, (E) Und-erwater detail of above; crescent is l o r n in diameter; depth = 8-9m. (F) Blue hole 5-6km west of Damas Cays; note coral patches developed on edge under boat; scale bar = loom, ( G ) Sand body 4.0-4.5m deep in 8m of water, 2km north of Cay Sal. Divers are measuring sand depth by inserting 5m length of PVC pipe. Note oriented megaripples indicating sand motion, and sparse colonization of sediment by Halodule and calcareous green algae. Inset: Figure 5. Communities of the Bank Rim: (A) Intertidal' bench with typical wave resistant Gorgonia spp. from lagoon side of Bellows Cay (see appendix map). (B) coral development below the surge zone with extensive cover of Agaricia agaricites and large (-lm3) colony of Montastrea annularis : lagoon side Crenula Cay, 0-6m (see appendix map). Scale bar = 60cm. (C) Eolianite blocks broken from lagoon side of northernmost Dog Rocks; scale bar = 2m. (D) Colonization of above by Millepora -- complanata and small colonies of Diploria strigosa and Montastrea annularis: scale bar = 60 cm. (E) Ocean side Elbow Cay showing lack of coral development on island base. ~ o t espur and groovelike system and scour holes; scale bar = 60 cm, depth = 3-10m. Figure 6 , Communities of the Outer Reef Slope: (A) Deep spur systems in Nicholas Channel south of Anguilla Cays, 23'22'N and 79O34'WS Note profusion of gorgonians and sponges, Scleractinian development is occasionally moderate but generally poor. Spur height = 3-4m; Depth = 20-25m. (B) Edge of escarpment at above location. TJote gorgonians and sponges but poor scleractinian development; Depth = 35m. (C) Development of Agaricia agaricites and porites astreoides on the edge of the escarpment off Elbow Cay; flabellate gorgonian is Iciligoria schrammi, Depth = 30m, (D) Escarpment off north Cay Salblanketed in fine sediment of undetermined thickness. Coral at center is mud-dwelling sclearactinian, Meandrina danae l2.cm Long, Note conch trails (~trombus gigas) above; Depth = 30m. ( E ) Deep spurs on the escarpment north of Rompidas Ledge composed largely of platey growths of Montastrea annularis, - Figure '7, Comparison of fathometer profiles from Gay SaL Island northward at 15 to 30m depth. Arrow indicates increased inflection of outer reef slope at 20m. Distances north of Cay Sal: 1 = 3km, 2 = 4km, 3 = 5.5km, 4 = 6,5km, 5 = 8km. Note smooth surfaces indicative of sediment drowning near Cay Sal and increased reef development toward Rompidas. Figure 8. Tropical storm and hurricane track passing within 100 km of Cay Sal Bank, i871 through 1981. Year of each track indicates direction of continued motion. Data from Neumann et -al. (1978) with additions from NOAA Mariner's Weather Log (1977-1982). Figure 9. Climatic and hydrographic conditions near Cay Sal Bank. Data compiled from West Indies Pilot (1957), WBst (l964), NOAA (1973) and U.S. Naval Weather Service Command (1975) . Figure 1 Sea and Swell Conditions >2m month sea s m observations O/O May 18 8 4,448 August 15 6 6,4 17 November 25 15 5,338 February 20 12 4,667 APPENDIX The l a c k o f b a s i c i n f o r m a t i o n on Cay S a l Bank i s p e r h a p s n o b e t t e r r e f l e c t e d t h a n b y c o n s i d e r a b l e errors i n i t s c h a r t e d p o s i t i o n ( B r i t i s h Admiraly 1217; Defense Mapping Agency 1 1 4 5 1 ; NOAA 1 1 0 1 3 ) . The p u r p o s e o f t h i s n o t e i s t o c o r r e c t mapping e r r o r s by e m p l o y i n g a e r i a l a n d s a t e l l i t e photography coupled w i t h ship-based n a v i g a t i o n a l t e c h n i q u e s and bottom s o u n d i n g s . Additional information is p r e s e n t e d o n t h e b i o t i c c o m p o s i t i o n a n d morphology o f m a j o r islands. D a t a on t h e bank were o b t a i n e d d u r i n g t h r e e c r u i s e s o f t h e R/V B e l l o w s i n t h e summers o f 1 9 8 0 t h r o u g h 1 9 8 2 . P o s i t i o n f i x i n g a b o a r d t h e v e s s e l employed b y s i m u l t a n e o u s u s e o f a 7100 M i c r o m a r i n e LORAN C N a v i g a t o r c o m p u t e r , p l u s An I T T a M i c r o l o g i c ML-320 LORAN-C N a v i g a t o r a s a b a c k u p . Decca M a r i n e 8 0 1 s a t e l l i t e n a v i g a t i o n c o m p u t e r a n d a Decca RM 5314 r a d a r u n i t ( 7 7 km r a n g e ) w e r e u s e d t o c o n f i r m LO data. B a t h y m e t r y i n f o r m a t i o n was o b t a i n e d u s i n g a R a y t h e o n E x p l o r e r I11 r e c o r d i n g f a t h o m e t e r ( t o 7 5 f a t h o m s ) a n d a R a y t h e o n DE-731 r e c o r d i n g f a t h o m e t e r t o ( 4 1 0 f a t h o m s ) 811 i s l a n d s and r o c k s w e r e s u r v e y e d b y o b l i q u e a e r i a l p h o t o g r a p h y f r o m a n a l t i t u d e o f 600 meters. These w e r e s u p p l e m e n t e d by a e r i a l p h o t o g r a p h s o f t h e A n g u i l l a C a y s made a v a i l a b l e by t h e U.S. D e f e n s e I n t e l l i g e n c e Agency, The low a l t i t u d e p h o t o g r a p h s w e r e employed i n c o n j u n c t i o n w i t h ERTS/LANDSAT i m a g e r y a n d s h i p b o a r d p o s i t i o n f i x i n g i n t h e c o n s t r u c t i o n o f a map o f t h e b a n k , a c c u r a t e t o w i t h i n +- 300 meters. R e s u l t s o f t h e mapping o f Cay S a l Bank a r e d e p i c t e d i n F i g u r e 1. Comparison w i t h t h e 1890 B r i t i s h AZamirality C h a r t ( F i g * 2 ) shows an e r r o r b e t w e e n 1 a n d 5 km i n t h e p o s i t i o n o f t h e i s l a n d s , t h e magnitude o f which i s g r e a t e s t i n t h e s o u t h e a s t e r n p o r t i o n of t h e bank, The s h a p e o f l a r g e r i s l a n d s h a s b e e n more a c c u r a t e l y d e p i c t e d and s o m e h a v e b e e n named ( @ r e n u l a C a y , N o r t h a n d S o u t h D a n g e r o u s Rocks a n d B e l l o w s C a y ) , The b a t h y m e t r y of t h e bank a s o r i g i n a l l y presented appears t o be e s s e n t i a l l y c o r r e c t f o r t h e r e l a t i v e p o s i t i o n o f t h e 5 fathom c u r v e . Only m i n o r c o r r e c t i o n s have been i n s e r t e d , The p o s i t i o n o f t h e 25 f a t h o m ( = l o 0 F ) c u r v e h a s b e e n f i t t e d u s i n g s a t e l l i t e imagery ( t e x t f i g . 3) . Some o f t h e s h o a l w a t e r a r e a s d e p i c t e d on t h e B r i t i s h c h a r t ( a n d c o p i e d on a l l o t h e r c h a r t s ) c o u l d n o t b e l o c a t e d d e s p i t e numerous a t t e m p t s . Most n o t a b l y , a r e a s s u c h a s L a v a n d e r a s R o c k s , e a s t o f Cay S a l a n d " D a n g e r o u s S h o a l " d e p i c t e d on t h e c e n t r a l e a s t e r n b o r d e r ( F i g . 2 ) a r e n o . s h a l l o w e r t h a n 3.5 t o 4 fathoms. This i s a l s o t r u e f o r t h e s h o a l a r e a s n e a r t h e c e n t e r o f t h e bank. Repeated c r o s s i n g s have i n d i c a t e d t h a t t h e lagoon i s g e n e r a l l y no s h a l l o w e r t h a n 3.5 fathoms (6.4m) a t MSL. The exception to t h i s r u l e i s a s m a l l ( s l k r n 2 ) a r e a on t h e w e s t e r n bank r e f e r r e d t o a s Rompidas Ledge, where t h e b o t t o m s h o a l s t o less t h a n two f a t h o m s , and l a r g e s c a t t e r e d h e a d s o f Montastrea a n n u l a r i s p r o j e c t c l o s e t o t h e surface. N a v i g a t i o n a l maps p l a c e Rompidas o v e r 5km from i t s a c t u a l position. However, t h e s i t e i s now marked by a c a r g o s h i p , M/V Cork t h a t r a n aground on Rompidas i n 1983. The l o c a t i o n o f t h i s submerged s h o a l c a n now b e s e e n c l e a r l y from a d i s t a n c e o f o v e r 15km. APPENDIX F I G U R E LEGENDS F i g u r e 1. C h a r t o f Cay S a l Bank w i t h r e v i s e d c o o r d i n a t e s a c c o r d i n g t o LORAN a n d r a d a r p o s i t i o n i n g ; t w e n t y f i v e f a t h o m (=100F) c u r v e f i t t e d f r o m s a t e l l i t e imagery. F i g u r e 2. Comparison o f new c h a r t ( s o l i d l i n e s ) w i t h B r i t i s h A d m i r a l i t y C h a r t No. 1 2 1 7 ( d a s h e d l i n e s ) showing 25 fathom c u r v e and p o s i t i o n o f m a j o r i s l a n d s , When t h e 24' a n d 80' c o o r d i n a t e s o f t h e two maps are o v e r l a p p e d e r r o r s o f u p t o 5km are shown a l o n g t h e s o u t h e a s t e r n s e c t o r o f t h e U . S . D e f e n s e Mapping Agency No. 1 1 4 6 1 i s bank, v i r t u a l l y i d e n t i c a l w i t h t h e B r i t i s h map. F i g u r e 3. I s l a n d s o f Cay S a l Bank, ( A ) U,S, A i r F o r c e p h o t o g r a p h o f s o u t h A n g u i l l a Cay; s c a l e b a r = 500m. N o t e embayed m a r g i n s and s a n d s h o a l s . S a l i n i t y of s a l i n e l a k e i n Lake J u n e , 1 9 8 2 was 37. Gy,, by c o n d u c t i v i t y . marqins a r e covered with e y a n o b a c t e r i a l mats ( ~ s c i l l a t o r i as p , ) a l o n g w i t h t h o s e of a n A u n i d e n t i f i e d red photosynthetic bacterium, s i m i l a r l a k e on n b r t h g l n g u i l i a Cay r e t a i n e d a s a l i n i t y o f 45C/,0. ( B ) S u r f a c e o f s o u t h A n g u i 1 l a Cay from e a s t w a r d Development o f f a c i n g dune c r e s t b o o k i n g n o r t h : p a l m s ( C o c c o t h r i n a x a r g e n t a t a Brown) and s c r u b vegetation. E a s t e r n dune f a c e i s s t e e p l y s l o p i n g and e r o d e d . P o o r l y cemented e o l i a n s a n d g r a i n s a r e t y p i c a l o f t h e windward s i d e . ( C ) Lagoon ( w e s t e r n ) s i d e o f s o u t h A n g u i l l a Cay: bedded s t r u c t u r e o f w e l l - c e m e n t e d e o l i a n i t e c l i f f s . (D) Cay S a l from 600m l o o k i n g t o w a r d s o u t h e r n F l o r i d a S t r a i t s , Unpaved a i r s t r i p a t n o r t h e r n t i p of i s l a n d ends a t edge of h y p e r s a l i n e lagoon, H i g h e s t p o r t i o n of i s h a n d i s 10m r i d g e a t t h e e a s t e r n t i p ( l o w e r l e f t ) , Note s a n d y s h o a l s a r o u n d i s l a n d and w e a k l y d e v e l o p e d b l o w o u t s t r u c t u r e s a t l o w e r right corner, S c a l e b a r = l50m. ( E ) Elbow Cay i s t y p i c a l o f m o s t i s l a n d s o n Cay S a l Bank, c o n s i s t i n g o f k a r s t i f i e d e o h i a n i t e a n d c o r a l r u b b l e c o l o n i z e d by m a r i t i m e v e g e t a t i o n , p r i m a r i l y Sesuvium p o r t u l a c a s t r u m L i n n . a n d T o u r n e f o r t i a g n a p h a l o d e s Brown. See Wilson (1909) a n d G i l l i s ( 1 9 7 6 ) f o r a d d i t i o n a l n o t e s on Cay S a l Bank t e r r e s t r i a l f l o r a . T h i s and o t h e r rocky i s l a n d s o f t h e bank s e r v e a s n e s t i n g s i t e s f o r enormous numbers o f s o o t y and brown noddy t e r n s d u r i n g t h e summer m o n t h s . S e e Buden and S c h w a r t z (1968) f o r a review o f h e r p e t o - and a v i f a u n a o f Cay S a l . A p p e n d i x Fig. 1 Appendix F i g , 2