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A comparison of insular seaweed floras from Penobscot bay, Maine, and other northwest Atlantic islands PDF

50 Pages·1997·21.4 MB·English
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Preview A comparison of insular seaweed floras from Penobscot bay, Maine, and other northwest Atlantic islands

RHODORA, Vol. 98, No. 896, pp. 369-418, 1996 FROM A COMPARISON OF INSULAR SEAWEED FLORAS PENOBSCOT AND OTHER NORTHWEST MAINE, BAY, ATLANTIC ISLANDS Arthur Mathieson, Edward Hehre, Hambrook, Julie C. J. Gerweck AND James Department of Plant Biology and Jackson Estuarine Laboratory, NH New University of Hampshire, Durham, 03824 ABSTRACT. Ninety-seven taxa of seaweeds were collected from nine is- lands within the Penobscot Bay area of central Maine, including 25 Chloro- phyceae, 34 Phaeophyceae, and 38 Rhodophyceae. The patterns of species richness and longevity (#annuals/#perennials) per island are highly variable, Wooden with species richness ranging from only 4 taxa on Allen to 65 on I. = Ball (mean 30,8 ± 23.0 taxa) and longevity ratios varying from 0.33- I. A ± of 48 annuals and 49 perennials recorded 1.0 (0.64 28.1). total is throughout the Bay, giving a longevity ratio of 0.98. This value lower than is An many that found at open coastal habitats within the Gulf of Maine. ex- E amination of historical collections by Hooper and S. Collins from the J. 1800s revealed three unusual coastal records {Stilophora rhizoides, Gracilaria tikvahiae, and Cladophora ruchingeri) and sixteen additional seaweeds that were not encountered our study. Based upon these historical and present in well extensive sampling from more than 70 nearshore collections, as as sites, a total of 139 seaweed taxa is known from the Penobscot Bay area, including 40 Chlorophyceae, 47 Phaeophyceae and 52 Rhodophyceae. In a comparison New of seaweed floras from fourteen individual islands, from South Wolf I., Brunswick, Penikese Massachusetts (including a "composite" of Pe- to I., nobscot Bay Islands), 216 seaweed taxa arc documented, including 52 Chlo- The numbers rophyceae, 63 Phaeophyceae, and 101 Rhodophyceae. highest of taxa occur Smuttynose Maine and Penikese Massachusetts at I., (136), I., Wooden Maine Monhegan Maine (131), and the lowest on Ball (65), I., I., New and Kent Brunswick of individual (64), (63). Floristic affinities is- I., lands tend mimic patterns of species richness, with Smuttynose having the to = Wooden ± highest number of shared taxa (mean 92.4 20.2) and Kent and = ± ± Ball Islands the lowest numbers (mean 50.8 5.2 and 53.9 6.2, re- spectively). The seaweed diversity of Penikese Island and nearby environs (187 taxa) comparable io the entire Gulf of Maine. is New Key Words: seaweeds, Penobscot Bay, Maine, Bruns- coastal islands, New wick, Hampshire, Massachusetts, Gulf of Maine As noted by Hill (1923), and Pike and Hodgdon (1963), com- parative investigations of islands have been grossly ne- floristic many North America, even though have been glected within there fine studies of individual islands. Although their statement applies 369 370 Rhodora [Vol. 98 Table Dates and 1. locations of insular collections within the Penobscot X Bay = ^ area of mid-coastal Maine, Symbols: X* inteilidal; subtidal; = X** and intertidal subtidal. Islands 1985 6/2 6/6 6/9 6/11 6/12 Allen I. X X Hurricane I. Long I. X Marshall I. X McGlathery ** I. Monhegan I. Pond I. Two X Bush I. X Wooden Ball I. to terrestrial vegetation, equally true for marine (Bow- is floras it Wood Doty ers 1942; Collins 1900; 1948; Koetzner and 1972; Wil M two thousand Simpson islands (Piatt 1996; 1987), but atten- little been tion has paid to their marine algal Johnson and floras. Skutch (1928a, b) conducted an early ecological study of inter- Mount Maine ecology. one of most It is still the significant studies of kind its Maine sular within the Gulf of Maine was conducted sites at the Isles New of Shoals southern Maine and Hampshire in (Mathieson and We Penniman 1986b). are aware of only one other comparative study of insular marine North America, namely floras in the Channel Islands in Southern California (Murray and Littler 1981; Muiray et 1980). al. we In the present study, evaluate the composition and floristic seaweed affinities of populations from nine islands within the Penobscot Bay area of mid-coastal Maine, including contiguous Bay nearshore Jericho and offshore habitats (Table Appendix). 1; We compare these records with previous documentations of spe- cies composition from thirteen other islands, from the Bay of Fundy southern Massachusetts to (Figures 1-3; Table Data 2, 3). from 20 of 22 these islands represent our collections (Hehre et 1970; Mathieson and Penniman 1986b; Stone al. et 1970), al. — Mathieson Seaweed Floras 371 Insular 1996] et al. Table Extended. 1. 1994 1986 5/29 5/30 6/1 6/2 6/5 6/6 6/7 6/8 6/9 6/12 7/15 7/16 7/17 7/18 XXX X X XX * X XXX ^*+ ^** ^*D{C J^** X X X** made and accordance with a uniform protocol for collecting in identifying seaweeds, including the establishment of extensive two voucher collections (Druehl 1981). Information for the other New Mas- (Kent Brunswick, and Penikese Island, islands Island, upon work (Bowers Doty based of others 1942; sachusetts) the is Wood 1948; Koetzner and 1972; Lewis 1924). In summary, the were objectives of our study four- fold as follows: to assess (1) the numbers and types of species from nine islands within the Bay Maine Penobscot area of mid-coastal (Appendix); to eval- (2) uate the longevity pattern of seaweed populations from the Pe- nobscot Bay compare the patterns of species richness area; to (3) Bay among from Penobscot 22 individual islands, including nine from Bay Fundy, Canada, Buz- and thirteen other the of to sites, compare zards Bay, Massachusetts; and to a ''composite" of (4) Penobscot Bay taxa from nine islands with thirteen other North- west Atlantic islands. AND METHODS MATERIALS seaweeds were Collections of intertidal and shallow subtidal Bay made nine islands within the Penobscot area (Figure at 2, The selection of islands was based upon a variety of fac- 3a, b). by degree of including accessibility boat, variation in size, tors, wave exposure, and proximity other insular and nearshore en- to Penobscot vironments. Four of the nine islands are located within Two Wooden Bay McGlathery, Bush, and proper (Hurricane, 372 Rhodora [Vol. 98 1^ 71 46 MAINE \ \ \ \ \ \ \ \ \ CAPE SABLE \ \ 44 \ PORTION D GULF OF MAINE KITTERY BOON I. OF ISLES SHOALS N.H 42 COD CAPE km MASSACHUSETTS 20 t \ MARTHA'S VINEYARD \ o£) CONN. PENIKESE I. The Figure northeastern coast of North America, from South Wolf 1. New Island, Biunswick, Canada, Buzzards Bay, to Massachusetts, including the mid-coastal Penobscot Bay area of Maine. Ball); three others (Long, Marshall, and Pond) occur within the contiguous Bay Jericho to the east (Figure 3b), and two (Allen W and Monhegan) He just of Penobscot Bay proper (Figure 2, As Conkhng noted by 3a). seaward boundary (1996), the for Pe- Bay nobscot somewhat vague is but approximated by 50 the is it — Mathieson Seaweed 1996] et Insular Floras 373 al. PENCeSCOT RIVER 44°10"N PENOBSCOT BAY MATINICUS I. WOODEN BALL I. RAGGED (CRIEHAVEN) AS^SO'N BANTAM LEDGE L A MATINICUS ROCK MONHEGANI. it 68'50'W 69°10'W 1 I Figure 2. The mid-coastal Penobscot Bay area of Maine, showing the Monhegan, Two Wooden location of Hurricane, Bush, and Ball Islands. 374 Rhodora 98 [Vol. a 43-57 - :9G d MOSQUITO HOOPER I. I. TTHOMPSON I, ^^ '^ GEORGES ISLANDS t o cP 43''54' - 4<? - 0. / V km BURNT 3.0 I 4 L J I u L _I I DESERT Ml, X? ^<. <?• O. ?^ \ 44''15' - /'V \ DEER \ ISLE i- ^ POND I, BASS hlARBOR Q GREAT GOTT i km 5.0 .^ b!^°^<?: ^ - "* ^ . MARSHALL \. c::> O McGLATHERY I, c- S MERCHAf^S ROW o LONG I 68''25' 1 1 I Figure West 3. Penobscot Bay, showing Allen Island that is located south of Port Clyde; b) Bay Eastern-most Penobscot showing McGlathery area, the locations of Is- land near Deer Island Thorofare and three islands within contiguous Jericho Bay (Pond, Long, and Marshall). W fathom As Monhegan near Matinicus Rock. line of lies just we Matinicus Rock, have chosen to include within our study. it Similarly, the other three islands (Long, Marshall, and Pond) are Bay east of Penobscot proper (Figure 3a, b). — Mathieson Seaweed Floras 375 1996] et al. ^Insular Most made of our Penobscot were insular collections during summers when the of 1985 and 1986, one of us (JH) was working on The Hurricane Island (Table notable exceptions are the 1). made on Monhegan summer collections Island during the of 1994. Intertidal samples were collected on foot during low tides; SCUBA made were by subtidal collections diving approxi- to 10-12m mean mately below low water (M.L.W.). Although an attempt was made sample conspicuous seaweeds on each to all island, limitations of boat time and diving personnel did not allow detailed subtidal sampling of nine Therefore, islands. all floristic documentations for individual islands should be considered pre- Bay liminary; the ''composite" for the Penobscot area probably more representative of the geography as a whole. The most is made detailed collections were on Hurricane Island with six sam- Wooden pling dates (Table Appendix), followed by Ball 1; (4), Monhegan Long Pond and Islands single collections (4), (3), (3); made Two were on Allen, Marshall, McGlathery, and Bush Is- lands. Seaweed samples either were pressed immediately or preserved 2% in formalin in seawater and stored in the dark. Several ref- erences were (Adey and Adey utilized for these identifications 1973; Bird and McLachlan 1992; Blair 1983; Bhding 1963, 1968; Burrows 1991; Dixon and Irvine 1977; Diiwel and Wegeberg Hoek Farlow 1996; 1881; Fletcher 1987; 1963, 1982; Irvine Maggs 1983; Irvine and Chamberlain 1994; Kingsbury 1969; and Hommersand 1993; Schneider and Searles 1991; Taylor 1957; Webber Villalard-Bohnsack 1995; and Wilce 1971; Woelkerling Wynne 1973; and Heine 1992). Nomenclature primarily follows South and Tittley (1986), except for several recent changes noted above and Villalard-Bohnsack Approximately 600 in (1995). Hodgdon voucher specimens are deposited in the Albion R. Her- New barium the University of Hampshire (nha) documenting at Penobscot Bay's insular flora. Bay we In addition to our insular Penobscot collections, have made extensive collections over 70 nearshore (Mathieson at sites and Hehre, The which were made unpubl. data). latter collections, during 1993 to 1996, are utilized to characterize Penobscot Bay's E total flora, in concert with several historical collections by S. W. and Hooper Collins, G. Farlow, during the century. last J. Many of Collins' and Farlow's specimens are deposited either at New the York Botanical Garden (ny) or the Farlow Herbarium U) ^ Seaweed Table 2. taxa from fourteen individual islands from the Bay of Fundy, Canada, to Buzzards Bay, Massachusetts, plus ^ % a ''composite" of nine islands from the Penobscot Bay area of mid-coastal Maine. Key to symbols; X = a taxon's presence; = — percent occurrence at 13 individual islands and the ^'composite" value for nine Penobscot Bay islands excluding Wooden — i.e., Ball as an individual. The values in indicate the 14 individual islands including Wooden Ball and excluding Penobscot I. ) i.e., ( I. = " Bay's "composite" value; '' stage in the hfe history of another seaweed but recognizable as a distinct entity. Key to abbre- SW = Wolf New CA = New = New = viations: South L, Brunswick; Campobello Brunswick; KI Kent Brunswick; PB —I., I., "composite" of nine islands from the Penobscot Bay area of Maine Allen, Hurricane, Long, Marshall, McGlathery, Mon- i.e., WB began. Pond, Two Bush, and Wooden = Wooden ME; BO = Boon ME; AP = Ball Islands; Ball L, Penobscot Bay, T, ME ME CE - DU - ME LU Appledore I., (Isles of Shoals); Cedar I., (Isles of Shoals); Duck (Isles of Shoals); = Lunging L, I., MA NH ME = SM - ME = NH (Isles of Shoals); Malaga I., (Isles of Shoals); Smuttynose L, (Isles of Shoals); ST Star (Isles I., WH NH = White of Shoals); -= (Isles of Shoals); PI Penikese Buzzards Bay, Mass. I., I., SW WB MA WH CA PB BO AP CE DU LU SM % KI ST PI Chlorophvta O X X X Acrochaete vindis (Reinke) R. Nielsen 21.4 O^ (14.3) X Acrochaete wittrockii (Wille) R. Nielsen XXXXXXXXXXX R 7.1 XXX XX minima Blidin^ia (Nageli ex KUtzing) X X Kylin 100 X Bry apsis plwnosa (Hudsonj C. Agardh 28.6 XX Capsosiphon fidvescens (C. Agardh) X Gardner Setchell et 14.3 Capsosiphon groenkmdician Agardh) XXXXXXXXX (J. X X XX Vinogradova 14.3 X Chaetotnorpha aerea (Dillwyn) Kutzing 78.6 Chae brachxgona Harvey X X to/no f'pha XXXXXXXXX 14.3 Chaetomorpha Union (O. Miiller) F. X Ktitzing XXXXXXXXXXX 71.4(64.3) XX < Chaetomorpha melagonium (Weber el o X Mohr) Kutzing X 100 Chaetomorpha minima X Hervey Collins et 7.1 )0 00 Table Continued. 2. SW CA PB WB BO AP CE DU LU MA SM ST WH % KI PI c Chaetomorpha picquotlana Montagne ex X X X X X X X X X Kutzing 57.1 X X Chlorochytrium cohnii Wright 7.1 X X X X X X X Cladophora albida (Nees) Kutzing 50.0 Cladophora Agardh) ruchingeri (J. X Kutzing 7.1 O X X X X X X X X Cladophora rupcsths Kutzing 57.1 (L,) X X X X X X X X X X X X X X Cladophora sericea (Hudson) Kutzing 92.9 X X X X X X X X X X ''Codiolum grcgarium A. Braun" 71.4 X X X X X X X X X X X CO Kuckuck" ''Codiolum pctrocelidis 78.6 (71.4) X X X X X X X X X "Codiolum pus ilium (Lyngbye) Kjellman' 64.3 Codium fragile (Suringar) Har. ssp. 3 X X X X X X tomentosoides (Goor) C. Silva 42.9 P. X X X X X Derbesia marina (Lyngbye) Solier 35.7 X X X X X X X X X Enteromorpha clathrata (Roth) Greville 64.3 X X X X X X X X X X Enteromorpha compressa Nees 71.4 (L.) CD Enteromorpha JiexHosa (Wulfen ex Roth) Agardh paradoxa (Dillwyn) ssp. J. X X X X X X Eliding 42.9 (35.7) X X X X X X X X X X X X X X X Enteromorpha Nees 100 intestinalis (L.) X X X X X X X X X X X X X X X Enteromorpha Agardh 100 linza (L.) J. Enteromorpha prolifera (O. F. X X X X X X X X X X X X X Agardh 85.7 Miiller) J. X X X Epicladia Reinke 21.4 flustrae ''Gomontia polyrhiza (Lagerheim) Bornet X X Flahault" 14.3 et Kornmannia leptoderma (Kjellman) X X Bhding 14.3 Table Continued. 2. -J oc SW CA WB MA WH PB AP CE DU LU SM % KI PI Monostroma grevlllei (Thuret) Wittrock X X X X X X X X X X X X 78.6 Monostroma oxyspei-mufu Kiitzing X 7.1 Ochlochaete hystrix Thwaites ex Harvey X 7.1 X Percursaria percursa Agardh) Bory X X X (C. 28.6 Prasiola stipitata Suhr in lessen X X X X X X X X X X X 78.6 Pringshcimiella scutata (Reinke) Hoehnel ex Marchewianka X 7.1 Protomonostroma widulatum (Wittrock) Vinogr pulchrum (Farlow) M. Wynne X X X X X X X X X X X X X f. 85.7 Pseiidendoclonium submarinum X X X X X Wille X 35.7 Rhizoclouium ripariuni (Roth) Kiitzing ex X X Harvey X X X X X X X X X X X X 92.9 Rhizoclouium tortuosuni fDillwyn) Kiitzing X X X X X X X X X X X X X X o 92.9 Spongomorpha aeruginosa Hoek X o (L.j 7.1 Spongomorplia arcta (Diilwyn) Kiitzing X X X X X X X X X X X X X X 92.9 &2 Spongomoj-pha X X X X X X X X X X X X X X spinescefjs Kiitzing 92.9 Slichococciis marinus (Wille) Hazen X X 14.3 Tellamia contoria Batters X 7.1 Ulothrix fhicca (Diilwyn) Thuret in Le X X X X X X X X X X X X X Jolis 85.7 Ulothrix speciosa (Carmichael ex Harvey Hooker) X X X X X in Kiitzing 35.7 Ulva lacluca L. X X X X X X X X X X X X X X X 100 Ulvaria obscura (Kiitzing) Gayral X X X X X X X X X X X X X 85.7 Urospora penicilliformis (Roth) Areschoug X X X X X X X X X X X X X X 92.9 Urospora wormskjoldii (Mertens in < Hornemann) Rosenxinee X X X X X X X X O 57.1 = Chlorophyta Total taxa 52 23 30 17 25 21 20 30 27 33 34 25 34 29 28 27 00

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