<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 1: Spartina BiologyMECHANISMS OF SULFIDE AND AOXIA TOLERANCE IN SALT MARSH GRASSESIN RELATION TO ELEVATIONAL ZONATIONB.R. MARICLE 1,2 AND R.W. LEE 11 School <str<strong>on</strong>g>of</str<strong>on</strong>g> Biological Sciences, Washingt<strong>on</strong> State University, Pullman, WA 99164-42362 Present address: Department <str<strong>on</strong>g>of</str<strong>on</strong>g> Biological Sciences, Fort Hays State University, Hays, KS 67601-4099; brmaricle@fhsu.eduSharply-defined ecot<strong>on</strong>es comm<strong>on</strong>ly separate species living in high intertidal and low intertidalestuarine z<strong>on</strong>es. Low intertidal regi<strong>on</strong>s are characterized by anoxic sediments and toxic levels <str<strong>on</strong>g>of</str<strong>on</strong>g>hydrogen sulfide. These c<strong>on</strong>diti<strong>on</strong>s exclude high marsh species. In c<strong>on</strong>trast, low marsh species arebelieved to possess physiological adaptati<strong>on</strong>s to resist <str<strong>on</strong>g>the</str<strong>on</strong>g> anoxia and sulfide. However, <str<strong>on</strong>g>the</str<strong>on</strong>g>seadaptati<strong>on</strong>s are poorly understood. One <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> most important characteristics <str<strong>on</strong>g>of</str<strong>on</strong>g> waterloggedsediments is <str<strong>on</strong>g>the</str<strong>on</strong>g> lack <str<strong>on</strong>g>of</str<strong>on</strong>g> oxygen. Many wetland plants have been shown to transport atmosphericoxygen internally to support respirati<strong>on</strong> in submerged tissues. This ability may allow plant survivalin low intertidal marsh areas and is <str<strong>on</strong>g>of</str<strong>on</strong>g>ten implicated as a factor in determining species z<strong>on</strong>ati<strong>on</strong> inestuaries. In this study, oxygen transport and metabolic characteristics related to anoxia toleranceand rhizosphere oxidati<strong>on</strong> were investigated in <str<strong>on</strong>g>the</str<strong>on</strong>g> emergent estuarine species Spartina alterniflora,S. anglica, S. densiflora, S. patens, and Distichlis spicata (Poaceae). Plants were grown ingreenhouse experiments under simulated estuarine c<strong>on</strong>diti<strong>on</strong>s. All species showed a str<strong>on</strong>g ability torespire anaerobically. The high intertidal marsh species S. densiflora, S. patens, and D. spicata werefound to have high aerobic respirati<strong>on</strong> rates, low oxygen transport rates, and an apparent highsensitivity to sulfide. The low intertidal marsh species S. alterniflora and S. anglica had loweraerobic respirati<strong>on</strong> rates, moderate to high oxygen transport rates, and a lower sensitivity to sulfide.Spartina anglica appeared to have <str<strong>on</strong>g>the</str<strong>on</strong>g> greatest ability to transport oxygen and was more resistant tomudflat-related stressors compared to <str<strong>on</strong>g>the</str<strong>on</strong>g> o<str<strong>on</strong>g>the</str<strong>on</strong>g>r plants in this study. Evidence is presented thataerobic respirati<strong>on</strong> rates and sulfide sensitivity may be important factors for differences in estuarinez<strong>on</strong>ati<strong>on</strong> between species.Keywords: Distichlis spicata, hypoxia, oxygen transport, respirati<strong>on</strong>, sediment, Spartina, sulfideINTRODUCTIONThe introducti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> four species <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina grasses(Poaceae) into Washingt<strong>on</strong> estuaries has led to manydevastating ecological and ec<strong>on</strong>omic impacts. Nearly 8,100hectares (ha) <str<strong>on</strong>g>of</str<strong>on</strong>g> intertidal mudflat in Willapa Bay,Washingt<strong>on</strong>, USA, has been affected by introduced S.alterniflora (Hedge et al. 2003). Similarly, S. anglica wasintroduced in nor<str<strong>on</strong>g>the</str<strong>on</strong>g>rn Puget Sound, Washingt<strong>on</strong> in 1961 topresvent shoreline erosi<strong>on</strong>, but quickly spread via tidalcurrents and now affects over 3,300 ha in <str<strong>on</strong>g>the</str<strong>on</strong>g> Puget Soundarea (Hacker et al. 2001). O<str<strong>on</strong>g>the</str<strong>on</strong>g>r Spartina introducti<strong>on</strong>s intoWashingt<strong>on</strong> estuaries include Spartina densiflora Br<strong>on</strong>g.(WSDA news release 11 Jan 2002) and S. patens (Ait<strong>on</strong>)Muhl. (Frenkel 1987). These populati<strong>on</strong>s remain small andare closely m<strong>on</strong>itored to prevent spread.Introduced Spartina flourishes in West Coast estuariesbecause it can occupy an open niche: low intertidal mudflatsand tidal channels characterized by highly reducingc<strong>on</strong>diti<strong>on</strong>s (an oxidati<strong>on</strong> reducti<strong>on</strong> potential less than -300millivolts [Eh
Chapter 1: Spartina Biology<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> Spartinain <str<strong>on</strong>g>the</str<strong>on</strong>g>se envir<strong>on</strong>ments is thought to be oxygen transport to<str<strong>on</strong>g>the</str<strong>on</strong>g> roots and rhizosphere, facilitated by a system <str<strong>on</strong>g>of</str<strong>on</strong>g> gasspaces (aerenchyma) c<strong>on</strong>necting leaves to root tissues (Tealand Kanwisher 1966, Hwang and Morris 1991, Arenovskiand Howes 1992, Howes and Teal 1994). The presence andfuncti<strong>on</strong>ing <str<strong>on</strong>g>of</str<strong>on</strong>g> aerenchyma is well documented in plantstolerant <str<strong>on</strong>g>of</str<strong>on</strong>g> flooded c<strong>on</strong>diti<strong>on</strong>s, and generally results in asupply <str<strong>on</strong>g>of</str<strong>on</strong>g> oxygen for aerobic respirati<strong>on</strong> as well as radialoxygen loss to <str<strong>on</strong>g>the</str<strong>on</strong>g> envir<strong>on</strong>ment (reviewed by Jacks<strong>on</strong> andArmstr<strong>on</strong>g 1999).Once oxygen has reached submerged tissues inemergent plants like Spartina, it has at least three possiblefates (Fig. 1). Oxygen can be released into <str<strong>on</strong>g>the</str<strong>on</strong>g> rhizosphere,support mitoch<strong>on</strong>drial respirati<strong>on</strong>, or be used in sulfideoxidati<strong>on</strong> processes. The strength <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g>se competing oxygensinks can be important in <str<strong>on</strong>g>the</str<strong>on</strong>g> ecophysiology <str<strong>on</strong>g>of</str<strong>on</strong>g> wetlandplants since it influences how oxygen is budgeted insubmerged tissues (Sorrell 1999).Anoxic estuarine sediments represent a str<strong>on</strong>g externaloxygen sink and <str<strong>on</strong>g>the</str<strong>on</strong>g>y can overwhelm plant oxygen transportprocesses. Therefore, Spartina grasses also must exhibit astr<strong>on</strong>g capability for anaerobic respirati<strong>on</strong> to sustainmetabolism when oxygen supplies are low. The enzymealcohol dehydrogenase (ADH) catalyzes <str<strong>on</strong>g>the</str<strong>on</strong>g> final reacti<strong>on</strong> infermentative ethanol syn<str<strong>on</strong>g>the</str<strong>on</strong>g>sis. The ability to respire underhypoxic c<strong>on</strong>diti<strong>on</strong>s is important for life in waterlogged soils,so ADH activity in <str<strong>on</strong>g>the</str<strong>on</strong>g>se plants appears to be an adaptati<strong>on</strong>for anoxia tolerance (Crawford 1967).To understand <str<strong>on</strong>g>the</str<strong>on</strong>g> mechanisms c<strong>on</strong>ferring success inlow intertidal z<strong>on</strong>es, aspects <str<strong>on</strong>g>of</str<strong>on</strong>g> oxygen transport andmetabolic characteristics related to anoxia tolerance andrhizosphere oxidati<strong>on</strong> were investigated in greenhouseSpartina plants. The four Spartina species introduced intoFig. 1. Atmospheric oxygen can be transported through wetland plants tosubmerged tissues. Once oxygen reaches <str<strong>on</strong>g>the</str<strong>on</strong>g> roots (inset), it has severalpossible fates. Measurements <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> indicated processes and enzymeactivities may indicate how oxygen is allocated in <str<strong>on</strong>g>the</str<strong>on</strong>g> roots <str<strong>on</strong>g>of</str<strong>on</strong>g> flood-tolerantplants.Washingt<strong>on</strong> estuaries provide a good system for studyingestuarine z<strong>on</strong>ati<strong>on</strong> since <str<strong>on</strong>g>the</str<strong>on</strong>g>y represent a range from highmarsh to low marsh species. The low marsh species Spartinaalterniflora and S. anglica were studied and compared to <str<strong>on</strong>g>the</str<strong>on</strong>g>high marsh species S. densiflora, S. patens, and <str<strong>on</strong>g>the</str<strong>on</strong>g> nativeDistichlis spicata.Plants are aerobes. Therefore, survival in waterloggedsoils requires a supply <str<strong>on</strong>g>of</str<strong>on</strong>g> oxygen to support tissuessubmerged in anoxic sediments (Crawford 1982). However,many additi<strong>on</strong>al physiological processes can be affected by<str<strong>on</strong>g>the</str<strong>on</strong>g> supply <str<strong>on</strong>g>of</str<strong>on</strong>g> oxygen to submerged tissues in wetland plants.Measures <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> mechanisms shown in Fig. 1 may allow <strong>on</strong>eto estimate how much oxygen is used in aerobic respirati<strong>on</strong>and how str<strong>on</strong>g external oxygen sinks may be. In <str<strong>on</strong>g>the</str<strong>on</strong>g> presentstudy, rates <str<strong>on</strong>g>of</str<strong>on</strong>g> oxygen transport were measured andcompared to rates <str<strong>on</strong>g>of</str<strong>on</strong>g> aerobic respirati<strong>on</strong>. Highly reducingmudflat c<strong>on</strong>diti<strong>on</strong>s may inhibit aerobic respirati<strong>on</strong> processesand induce alternative anaerobic respirati<strong>on</strong> pathways.Therefore, rates <str<strong>on</strong>g>of</str<strong>on</strong>g> aerobic respirati<strong>on</strong> were measured as wellas activities <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> aerobic respirati<strong>on</strong> enzyme cytochrome coxidase and <str<strong>on</strong>g>the</str<strong>on</strong>g> anaerobic respirati<strong>on</strong> enzyme alcoholdehydrogenase. Tolerance <str<strong>on</strong>g>of</str<strong>on</strong>g> estuarine mudflat c<strong>on</strong>diti<strong>on</strong>smay also require mechanisms to detoxify hydrogen sulfide, aphytotoxin produced under anaerobic c<strong>on</strong>diti<strong>on</strong>s.C<strong>on</strong>sequently, rates <str<strong>on</strong>g>of</str<strong>on</strong>g> sulfide oxidati<strong>on</strong> processes were alsomeasured in root tissues. The results <str<strong>on</strong>g>of</str<strong>on</strong>g> this study areexpected to provide a physiological explanati<strong>on</strong> to helpdefine differences between high marsh and low marshfuncti<strong>on</strong>al types and <str<strong>on</strong>g>the</str<strong>on</strong>g>ir relati<strong>on</strong>ship to estuarine z<strong>on</strong>ati<strong>on</strong>.MATERIALS AND METHODSSpartina plants were collected from field sites andsubsequently maintained under greenhouse c<strong>on</strong>diti<strong>on</strong>s.Spartina alterniflora plants were collected in Willapa Bay,Washingt<strong>on</strong> and S. anglica was collected from nor<str<strong>on</strong>g>the</str<strong>on</strong>g>rnPuget Sound, Washingt<strong>on</strong>. Additi<strong>on</strong>ally, S. patens plantswere obtained from <str<strong>on</strong>g>the</str<strong>on</strong>g> Gulf Coast <str<strong>on</strong>g>of</str<strong>on</strong>g> northwest Florida andS. densiflora plants were obtained from <str<strong>on</strong>g>the</str<strong>on</strong>g> Odiel SaltMarshes, southwest Spain. The native Distichlis spicata wascollected in nor<str<strong>on</strong>g>the</str<strong>on</strong>g>rn Puget Sound, Washingt<strong>on</strong>.Greenhouse temperatures were 26°C during <str<strong>on</strong>g>the</str<strong>on</strong>g> day and18°C at night. Natural lighting provided a photosyn<str<strong>on</strong>g>the</str<strong>on</strong>g>ticphot<strong>on</strong> flux density (PPFD) averaging 200 micromolesquanta per square meter per sec<strong>on</strong>d (200 μmol quanta m -2sec -1 ) during daylight hours with peaks around 1,100 μmolquanta m -2 sec -1 <strong>on</strong> sunny days. Daughter tillers from fieldcollectedplants were potted individually in a 50/50(vol./vol.) sand/potting soil mixture and were watered tosaturati<strong>on</strong> twice weekly with modified Hoagland nutrientsoluti<strong>on</strong> (Epstein 1972). Freshly potted plants were selectedfor uniformity in size and randomized between flooded anddrained treatments. At least four replicate plants were grownin each treatment. Plants were allowed 60-80 days in <str<strong>on</strong>g>the</str<strong>on</strong>g>ir-48-
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