<str<strong>on</strong>g>Proceedings</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> <str<strong>on</strong>g>Third</str<strong>on</strong>g> <str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g> <str<strong>on</strong>g>C<strong>on</strong>ference</str<strong>on</strong>g> <strong>on</strong> <strong>Invasive</strong> SpartinaChapter 2: Spartina Distributi<strong>on</strong> and SpreadWILL SPARTINA ANGLICA INVADE NORTHWARDS WITH CHANGING CLIMATE?A.J. GRAY 1,2 AND R.J. MOGG 11 Centre for Ecology and Hydrology, CEH Dorset, Winfrith Technology Centre, Dorchester, Dorset, DT2 8ZD, UK2 email: ajg@ceh.ac.ukSpartina anglica’s successful invasi<strong>on</strong> has depended <strong>on</strong> its ability to occupy mudflats atlower elevati<strong>on</strong>s than existing saltmarsh vegetati<strong>on</strong> but has slowed, with dieback in <str<strong>on</strong>g>the</str<strong>on</strong>g>south and successi<strong>on</strong>al replacement in <str<strong>on</strong>g>the</str<strong>on</strong>g> north. The elevati<strong>on</strong>al niche <str<strong>on</strong>g>of</str<strong>on</strong>g> S. anglica in <str<strong>on</strong>g>the</str<strong>on</strong>g>UK was shown to extend below that <str<strong>on</strong>g>of</str<strong>on</strong>g> its main competitor Puccinellia maritima by 68centimeters (cms). The niche <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> two species overlapped by 20 cms and within thisz<strong>on</strong>e <str<strong>on</strong>g>the</str<strong>on</strong>g>ir distributi<strong>on</strong> depends <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> outcome <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g>ir competitive interacti<strong>on</strong>. Thisinteracti<strong>on</strong> was investigated in <str<strong>on</strong>g>the</str<strong>on</strong>g> light <str<strong>on</strong>g>of</str<strong>on</strong>g> projected climate changes and <str<strong>on</strong>g>the</str<strong>on</strong>g> fact that <str<strong>on</strong>g>the</str<strong>on</strong>g>two species utilize different photosyn<str<strong>on</strong>g>the</str<strong>on</strong>g>tic pathways. A competiti<strong>on</strong> experiment underelevated levels <str<strong>on</strong>g>of</str<strong>on</strong>g> temperature and carb<strong>on</strong> dioxide is described and its implicati<strong>on</strong>s for <str<strong>on</strong>g>the</str<strong>on</strong>g>future development <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina-dominated marshes is discussed.Keywords: Spartina anglica, elevati<strong>on</strong>al niche, Puccinellia maritima, climate change,competiti<strong>on</strong>, C3 and C4 grassesTHE ORIGIN AND SPREAD OF S. ANGLICASpartina anglica CE Hubbard is arguably <str<strong>on</strong>g>the</str<strong>on</strong>g> bestknown example worldwide <str<strong>on</strong>g>of</str<strong>on</strong>g> an invasive allopolyploidspecies. It originated <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> south coast <str<strong>on</strong>g>of</str<strong>on</strong>g> England sometime between 1870, when <str<strong>on</strong>g>the</str<strong>on</strong>g> sterile F1 hybrid S. townsendiiwas first noticed, and 1892 when <str<strong>on</strong>g>the</str<strong>on</strong>g> first fertile specimenwas collected. The allopolyploid was subsequently named asSpartina anglica and its spread both naturally and bydeliberate planting, has been extremely well documented —Gray et al. (1991) provide a summary. The parental species,S. maritima, a native <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> old world, and S. alterniflora,accidentally introduced from North America intoSouthampt<strong>on</strong> Water, probably in ships’ ballast, were inc<strong>on</strong>tact for a relatively short period (30-40 years?).Never<str<strong>on</strong>g>the</str<strong>on</strong>g>less <str<strong>on</strong>g>the</str<strong>on</strong>g> patterns <str<strong>on</strong>g>of</str<strong>on</strong>g> isoenzyme variati<strong>on</strong> haveunambiguously established <str<strong>on</strong>g>the</str<strong>on</strong>g> hybrid origin <str<strong>on</strong>g>of</str<strong>on</strong>g> S. anglica(Raybould et al. 1991a), and analysis <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> DNA sequence<str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> chloroplast leucine tRNA gene intr<strong>on</strong> has shown thatS. alterniflora was <str<strong>on</strong>g>the</str<strong>on</strong>g> female parent in <str<strong>on</strong>g>the</str<strong>on</strong>g> original cross(cpDNA is maternally inherited in most grass species)(Ferris et al. 1997). This is not surprising in view <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g>relative frequency <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> two species in <str<strong>on</strong>g>the</str<strong>on</strong>g> area <str<strong>on</strong>g>of</str<strong>on</strong>g>hybridizati<strong>on</strong> during <str<strong>on</strong>g>the</str<strong>on</strong>g> middle <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> last century.Following hybridizati<strong>on</strong> and chromosome doubling(nei<str<strong>on</strong>g>the</str<strong>on</strong>g>r <str<strong>on</strong>g>of</str<strong>on</strong>g> which events have been repeated experimentally)<str<strong>on</strong>g>the</str<strong>on</strong>g> hybrids and <str<strong>on</strong>g>the</str<strong>on</strong>g>ir parents appear to have been quiterapidly isolated both genetically and ecologically. Spartinamaritima is found in <str<strong>on</strong>g>the</str<strong>on</strong>g> mid-level and high marsh z<strong>on</strong>es <str<strong>on</strong>g>of</str<strong>on</strong>g>well established salt marshes and is today largely c<strong>on</strong>fined to<str<strong>on</strong>g>the</str<strong>on</strong>g> east coast <str<strong>on</strong>g>of</str<strong>on</strong>g> England in <str<strong>on</strong>g>the</str<strong>on</strong>g> counties <str<strong>on</strong>g>of</str<strong>on</strong>g> Essex andSuffolk (Raybould et al. 1991b). The nearest extantpopulati<strong>on</strong> to <str<strong>on</strong>g>the</str<strong>on</strong>g> site <str<strong>on</strong>g>of</str<strong>on</strong>g> origin is <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> Isle <str<strong>on</strong>g>of</str<strong>on</strong>g> Wight, about10 miles away. Spartina alterniflora has been reduced to asingle cl<strong>on</strong>al populati<strong>on</strong> in Southampt<strong>on</strong> Water and israpidly being lost as <str<strong>on</strong>g>the</str<strong>on</strong>g> lower z<strong>on</strong>es <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> salt marshes areeroded al<strong>on</strong>g this coast. (There are a small number <str<strong>on</strong>g>of</str<strong>on</strong>g> o<str<strong>on</strong>g>the</str<strong>on</strong>g>rcl<strong>on</strong>es <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> species elsewhere but <str<strong>on</strong>g>the</str<strong>on</strong>g>se have beendeliberately introduced from known sources since <str<strong>on</strong>g>the</str<strong>on</strong>g> date <str<strong>on</strong>g>of</str<strong>on</strong>g><str<strong>on</strong>g>the</str<strong>on</strong>g> original hybridizati<strong>on</strong>.) Thus, somewhat ir<strong>on</strong>ically inview <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> main <str<strong>on</strong>g>the</str<strong>on</strong>g>me <str<strong>on</strong>g>of</str<strong>on</strong>g> this c<strong>on</strong>ference, S. alterniflora in<str<strong>on</strong>g>the</str<strong>on</strong>g> UK is regarded as a rare and threatened species <str<strong>on</strong>g>of</str<strong>on</strong>g>c<strong>on</strong>servati<strong>on</strong> interest, and its presence was recentlyinstrumental in <str<strong>on</strong>g>the</str<strong>on</strong>g> refusal for permissi<strong>on</strong> to extend anddevelop <str<strong>on</strong>g>the</str<strong>on</strong>g> nearby port. The sterile hybrid S. townsendii isalso largely c<strong>on</strong>fined to <str<strong>on</strong>g>the</str<strong>on</strong>g> original hybridizati<strong>on</strong> site,although its distributi<strong>on</strong> is uncertain because it wasintroduced to many estuaries al<strong>on</strong>g with <str<strong>on</strong>g>the</str<strong>on</strong>g> fertile form.By c<strong>on</strong>trast S. anglica has col<strong>on</strong>ized, or been planted in,almost all English and Welsh estuaries, is found in Scotland,and occurs in suitable habitats around <str<strong>on</strong>g>the</str<strong>on</strong>g> coast <str<strong>on</strong>g>of</str<strong>on</strong>g> Europefrom 48 to 57.5° N. It has famously been introduced to manyo<str<strong>on</strong>g>the</str<strong>on</strong>g>r parts <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> world and in several areas has become aserious invader <str<strong>on</strong>g>of</str<strong>on</strong>g> native biotopes. As detailed below, S.anglica mostly occurs in <str<strong>on</strong>g>the</str<strong>on</strong>g> lowest z<strong>on</strong>es <str<strong>on</strong>g>of</str<strong>on</strong>g> salt marshes,and at its peak occupied almost 25% <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> total saltmarsharea in Britain (10,000 hectares (ha) <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> 44,000 hasurveyed by Charman (1990)).The initial rapid genetic isolati<strong>on</strong>, and current ecologicalisolati<strong>on</strong>, <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> species involved in <str<strong>on</strong>g>the</str<strong>on</strong>g> evoluti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> S.anglica makes a fascinating c<strong>on</strong>trast to <str<strong>on</strong>g>the</str<strong>on</strong>g> situati<strong>on</strong> in SanFrancisco Bay, where hybridizati<strong>on</strong> between <str<strong>on</strong>g>the</str<strong>on</strong>g> native plantS. foliosa, and its ecological replacement, are a feature <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g>invasi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> n<strong>on</strong>-native S. alterniflora.- 103 -
Chapter 2: Spartina Distributi<strong>on</strong> and Spread<str<strong>on</strong>g>Proceedings</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> <str<strong>on</strong>g>Third</str<strong>on</strong>g> <str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g> <str<strong>on</strong>g>C<strong>on</strong>ference</str<strong>on</strong>g> <strong>on</strong> <strong>Invasive</strong> SpartinaTHE CURRENT STATUS OF S. ANGLICA IN EUROPEInvasi<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> European mudflats by S. anglica (hereafterrefered to simply as ‘Spartina’) has been characterised by adifferent sequence <str<strong>on</strong>g>of</str<strong>on</strong>g> events at different latitudes. In <str<strong>on</strong>g>the</str<strong>on</strong>g>south <str<strong>on</strong>g>of</str<strong>on</strong>g> England, and from <str<strong>on</strong>g>the</str<strong>on</strong>g> southwest Ne<str<strong>on</strong>g>the</str<strong>on</strong>g>rlandssouthwards, large m<strong>on</strong>ospecific stands developed rapidlyfollowing initial introducti<strong>on</strong> and have in many places beenfollowed in <str<strong>on</strong>g>the</str<strong>on</strong>g> early years <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> last century by ‘dieback,’<str<strong>on</strong>g>the</str<strong>on</strong>g> swards breaking up and retreating in area. By c<strong>on</strong>trast innor<str<strong>on</strong>g>the</str<strong>on</strong>g>rn England north <str<strong>on</strong>g>of</str<strong>on</strong>g> about 54° N and in <str<strong>on</strong>g>the</str<strong>on</strong>g> Dutch andGerman Waddensea, invading Spartina is replacedsuccessi<strong>on</strong>ally by o<str<strong>on</strong>g>the</str<strong>on</strong>g>r species, most comm<strong>on</strong>ly <str<strong>on</strong>g>the</str<strong>on</strong>g> grassPuccinellia maritima (hereafter ‘Puccinellia’). For examplein Morecambe Bay a 100-ha marsh formerly dominated bySpartina is now a Puccinellia-dominated sward from whichSpartina has almost disappeared (Gray and Raybould 1997).Although c<strong>on</strong>founded in some cases by latitudinal variati<strong>on</strong>in sediment type (<str<strong>on</strong>g>the</str<strong>on</strong>g> nor<str<strong>on</strong>g>the</str<strong>on</strong>g>rn marshes tend to be moresandy) this c<strong>on</strong>trast between nor<str<strong>on</strong>g>the</str<strong>on</strong>g>rn and sou<str<strong>on</strong>g>the</str<strong>on</strong>g>rn marshesmay be related to <str<strong>on</strong>g>the</str<strong>on</strong>g> effects <str<strong>on</strong>g>of</str<strong>on</strong>g> differences in climate anddaylength <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> two species (see below).Although <str<strong>on</strong>g>the</str<strong>on</strong>g> Spartina invasi<strong>on</strong> has not completelyhalted it has certainly slowed, and with dieback widespreadin <str<strong>on</strong>g>the</str<strong>on</strong>g> south and a slow rate <str<strong>on</strong>g>of</str<strong>on</strong>g> col<strong>on</strong>izati<strong>on</strong> in <str<strong>on</strong>g>the</str<strong>on</strong>g> north,<str<strong>on</strong>g>the</str<strong>on</strong>g>re is probably a net loss <str<strong>on</strong>g>of</str<strong>on</strong>g> area <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina marsh at <str<strong>on</strong>g>the</str<strong>on</strong>g>present day. Small isolated foci <str<strong>on</strong>g>of</str<strong>on</strong>g> recol<strong>on</strong>izati<strong>on</strong> may befound in <str<strong>on</strong>g>the</str<strong>on</strong>g> south where, in resp<strong>on</strong>se to rising relative sealevels, sea defences have been removed to create newmudflats and salt marsh, a process termed ‘managedrealignment’. Active invasi<strong>on</strong> by Spartina <str<strong>on</strong>g>of</str<strong>on</strong>g> such newlycreated intertidal mudflats can be observed at Tollesbury inEssex, a county which has lost more than 25% <str<strong>on</strong>g>of</str<strong>on</strong>g> its saltmarsh in <str<strong>on</strong>g>the</str<strong>on</strong>g> last thirty years. For <str<strong>on</strong>g>the</str<strong>on</strong>g> moment it seems <str<strong>on</strong>g>the</str<strong>on</strong>g>Spartina invasi<strong>on</strong> is ‘<strong>on</strong> hold.’INTERACTIONS BETWEEN SPARTINA AND PUCCINELLIAThe most parsim<strong>on</strong>ious explanati<strong>on</strong> for Spartina’ssuccess as an invader is that it has been able to grow <strong>on</strong>intertidal mudflats at lower elevati<strong>on</strong>s than <str<strong>on</strong>g>the</str<strong>on</strong>g> existingperennial saltmarsh vegetati<strong>on</strong>. This is undoubtedly due to arange <str<strong>on</strong>g>of</str<strong>on</strong>g> adaptive morphological and physiological features<str<strong>on</strong>g>the</str<strong>on</strong>g> net effect <str<strong>on</strong>g>of</str<strong>on</strong>g> which enable Spartina to withstand higherfrequencies <str<strong>on</strong>g>of</str<strong>on</strong>g> tidal submergence. The ‘elevati<strong>on</strong>al niche’ <str<strong>on</strong>g>of</str<strong>on</strong>g>Spartina in Britain has been measured by surveyingtransects across salt marshes and recording <str<strong>on</strong>g>the</str<strong>on</strong>g> highest andlowest levels <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> sward (in meters above <str<strong>on</strong>g>the</str<strong>on</strong>g> standard UKdatum height) and relating this to tidal c<strong>on</strong>stants (Gray et al.1991, 1995). Comparis<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> this niche with that <str<strong>on</strong>g>of</str<strong>on</strong>g> o<str<strong>on</strong>g>the</str<strong>on</strong>g>rsaltmarsh species c<strong>on</strong>firms that Spartina extends <strong>on</strong> average68 centimeters (cm) below Puccinellia, <str<strong>on</strong>g>the</str<strong>on</strong>g> species with <str<strong>on</strong>g>the</str<strong>on</strong>g>next lowest elevati<strong>on</strong>al limit. There is also a niche overlapbetween <str<strong>on</strong>g>the</str<strong>on</strong>g> two species by 20 cm. Within this overlap z<strong>on</strong>e<str<strong>on</strong>g>the</str<strong>on</strong>g> distributi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> two species is likely to be principallydetermined by interspecific competiti<strong>on</strong>, and Scholten andRozema (1990) provide clear evidence <str<strong>on</strong>g>of</str<strong>on</strong>g> this using anelegant removal experiment. The outcome <str<strong>on</strong>g>of</str<strong>on</strong>g> interspecificcompetiti<strong>on</strong> was shown to be critically dependent <strong>on</strong>variati<strong>on</strong> in local marsh elevati<strong>on</strong>.Measurement <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina’s elevati<strong>on</strong>al niche alsoindicated that its upper limit varies with latitude. Theregressi<strong>on</strong> equati<strong>on</strong> describing this limit (Gray et al. 1991)was:Upper Limit = 4.74 + 0.483(R) + 0.068(F) – 0.099(L)where R = spring tide range (m), F = fetch in <str<strong>on</strong>g>the</str<strong>on</strong>g> directi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g><str<strong>on</strong>g>the</str<strong>on</strong>g> transect (kilometers) and L = latitude (decimal degreesN). This equati<strong>on</strong>, which accounted for 90.2% <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g>variati<strong>on</strong> in <str<strong>on</strong>g>the</str<strong>on</strong>g> species’ upper limit, shows that Spartinadoes not extend so far upshore in more nor<str<strong>on</strong>g>the</str<strong>on</strong>g>rly latitudes. Apossible explanati<strong>on</strong> for this is that <str<strong>on</strong>g>the</str<strong>on</strong>g> competitiveinteracti<strong>on</strong> between Spartina and Puccinellia increasinglyfavours <str<strong>on</strong>g>the</str<strong>on</strong>g> latter as <strong>on</strong>e goes northwards, enabling it toinvade <str<strong>on</strong>g>the</str<strong>on</strong>g> Spartina z<strong>on</strong>e at lower elevati<strong>on</strong>s.The increasing competitive advantage <str<strong>on</strong>g>of</str<strong>on</strong>g> Puccinellia athigher latitudes may be linked to <str<strong>on</strong>g>the</str<strong>on</strong>g> different effects <str<strong>on</strong>g>of</str<strong>on</strong>g>temperature <strong>on</strong> Spartina and Puccinellia, which are revealedby differences in <str<strong>on</strong>g>the</str<strong>on</strong>g>ir seas<strong>on</strong>al growth patterns. Fieldmeasurements <strong>on</strong> a salt marsh at 52° N showed thatPuccinellia shoot weight increased in March when airtemperatures rose above 5° C, with growth peaking in Juneand July, whereas Spartina did not begin to grow until May,when temperatures reached 9° C, and reached maximumgrowth in October (Dunn et al. 1981). This laterdevelopment and growth <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina can be related to <str<strong>on</strong>g>the</str<strong>on</strong>g>species’ utilizati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> C4 photosyn<str<strong>on</strong>g>the</str<strong>on</strong>g>tic pathway. One<str<strong>on</strong>g>of</str<strong>on</strong>g> <strong>on</strong>ly eight C4 species in <str<strong>on</strong>g>the</str<strong>on</strong>g> UK flora, Spartina is <strong>on</strong>lypartially adapted to cooler climates (C4 photosyn<str<strong>on</strong>g>the</str<strong>on</strong>g>sis, inwhich <str<strong>on</strong>g>the</str<strong>on</strong>g> first product <str<strong>on</strong>g>of</str<strong>on</strong>g> carb<strong>on</strong> dioxide fixati<strong>on</strong> isoxaloacetate instead <str<strong>on</strong>g>of</str<strong>on</strong>g> phosphoglycerate as in C3 species, ismost comm<strong>on</strong> in semi-arid tropical and subtropical regi<strong>on</strong>s)(L<strong>on</strong>g 1983,1990).THE EFFECTS OF CLIMATE CHANGEThe studies outlined above suggest that <str<strong>on</strong>g>the</str<strong>on</strong>g> northwardinvasi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina is being prevented, or slowed, by <str<strong>on</strong>g>the</str<strong>on</strong>g>species inability to grow at low temperatures, and that, at itsnor<str<strong>on</strong>g>the</str<strong>on</strong>g>rn limits it is replaced by Puccinellia (a C3 specieswith a circumpolar distributi<strong>on</strong> from 70° N southwards).These two pi<strong>on</strong>eer saltmarsh species bioengineer vast tracts<str<strong>on</strong>g>of</str<strong>on</strong>g> intertidal mudflats and must be regarded as keyst<strong>on</strong>especies in saltmarsh development. The obvious andintriguing questi<strong>on</strong> is: will increases in air temperaturespredicted under various climate change scenarios enableSpartina to invade northwards into marshes currentlydominated by Puccinellia? Higher temperatures will bothincrease growth rate and extend <str<strong>on</strong>g>the</str<strong>on</strong>g> period <str<strong>on</strong>g>of</str<strong>on</strong>g> growth during<str<strong>on</strong>g>the</str<strong>on</strong>g> early m<strong>on</strong>ths <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> year. Spartina is unlikely to beaffected by increased atmospheric carb<strong>on</strong> dioxide as, where- 104 -
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FORWARD & ACKNOWLEDGEMENTSThe <stro
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TABLE OF CONTENTSForward & Acknowle
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Community Spartina Education and St
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included the docum
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CHAPTER ONESpartina Biology
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Chapter 1: Spartina Biology
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Chapter 1: Spartina Biology
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Chapter 1: Spartina Biology
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Chapter 1: Spartina Biology
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Chapter 1: Spartina Biology
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Chapter 1: Spartina Biology
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- Page 140: CHAPTER THREEEcosystem Effects <str
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Chapter 4: Spartina Control and Man
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Chapter 4: Spartina Control and Man
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Chapter 4: Spartina Control and Man
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Chapter 4: Spartina Control and Man
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Chapter 4: Spartina Control and Man
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Chapter 4: Spartina Control and Man
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Chapter 4: Spartina Control and Man
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Chapter 4: Spartina Control and Man
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Chapter 4: Spartina Control and Man
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Chapter 4: Spartina Control and Man
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