Supplementary material 1 from: Grewell BJ, Gallego-Tévar B, Castillo JM, Futrell CJ, Drenovsky RE, Harms NE, Pratt PD (2025) Functional trait responses of emergent and free-floating Alternanthera philoxeroides to increasing salinity with sea level rise: stress tolerance, avoidance, and escape strategies. In: Anastácio P, Ribeiro F, Chainho P (Eds) Invasions in Aquatic Systems. NeoBiota 102: 9-36. https://doi.org/10.3897/neobiota.102.150325
Abstract
Supplemental tables and figures supporting functional trait responses of Alternanthera philoxeroides to increasing salinity in tidal wetlands
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Supplementary Material 1 Supplemental tables and figures supporting Functional trait responses of Alternanthera philoxeroides to increasing salinity in tidal wetlands Brenda J. Grewell, Blanca Gallego-Tévar, Jesús M. Castillo, Caryn J. Futrell, Rebecca E. Drenovsky, Nathan E. Harms, Paul D. Pratt Table S1. F-statistic and P-values from General Linear Models with salinity (0.5, 12, 24, 36 ppt) as fixed factor for traits of emergent and free-floating invasive Alternanthera philoxeroides plants. Significant differences are marked in bold. Abbreviation: TNC, total nonstructural carbohydrates. Plant traits Salinity F3,16 P Experiment A: Emergent Growth Form Biomass, morphology and allocation Total biomass (g) 341.530 <0.0001 Specific leaf area (m2 kg-1) 59.509 <0.0001 Leaf mass ratio 1.103 0.377 Adventitious root mass ratio 22.159 <0.0001 Below-ground mass ratio 22.538 <0.0001 Branch intensity index 10.068 <0.0001 Gas exchange and pigments Net photosynthetic rate (µmol CO2 m-2 s-1) 46.228 <0.0001 Water use efficiency (mmol CO2 mol H2O) 44.413 <0.0001 Chlorophyll a (mg g-1) 12.307 <0.0001 Chlorophyll b (mg g-1) 32.885 <0.0001 Carotenoids (mg g-1) 8.722 0.001 Plant tissue bio chemistry Leaf nitrogen (mg g-1) 9.955 <0.0001 Leaf sodium (mg g-1) 64.683 <0.0001 Leaf proline (µmol g-1) 14.471 <0.0001 Leaf glycinebetaine (µmol g-1) 49.189 <0.0001 Leaf total phenolics (mg g-1) 7.156 0.003 Leaf lignin (mg g-1) 8.624 0.001 Stem lignin (mg g-1) 7.466 0.002 Stem node nitrogen (mg g-1) 21.734 <0.0001
Stem node TNC (mg g-1) 0.576 0.639 Soil root TNC (mg g-1) 1.690 0.209 Soil root nitrogen (mg g-1) 9.198 <0.001 Experiment B: Free-floating Growth Form Biomass, morphology and allocation Total biomass (g) 588.930 <0.0001 Specific leaf area (m2 kg-1) 57.292 <0.0001 Leaf mass ratio 150.470 <0.0001 Adventitious root mass ratio 26.206 <0.0001 Stem pith cavity diameter (mm) 40.667 <0.0001 Plant tissue bio chemistry Chlorophyll a (mg g-1) 69.138 <0.0001 Chlorophyll b (mg g-1) 10.462 <0.0001 Leaf nitrogen (mg g-1) 12.692 <0.0001 Leaf proline (µmol g-1) 16.631 <0.0001 Leaf glycinebetaine (µmol g-1) 149.160 <0.0001 Leaf total phenolics (mg g-1) 20.557 <0.0001 Stem node nitrogen (mg g-1) 19.412 <0.0001 Stem node TNC (mg g-1) 8.019 0.001
Figure S1. A priori structural equation model illustrating the hypothesized direct or indirect effects of salinity on three groups of response variables measured in different growth forms of Alternanthera philoxeroides: (1) biomass allocation and morphology, (2) leaf gas exchange and photosynthetic pigments, and (3) plant tissue chemistry.
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Figure S2. Trait responses to salinity by the emergent growth form of Alternanthera philoxeroides (Experiment A). Different letters above columns indicate significant differences among salinity treatments based on Tukey’s post-hoc tests. Figure S3. Trait responses to salinity by the free-floating growth form of Alternanthera philoxeroides (Experiment B). Different letters above columns indicate significant differences among salinity treatments based on Tukey’s post-hoc tests.
Figure S4. Trait responses to salinity by the free-floating growth form of Alternanthera philoxeroides following a freshwater recovery period after exposure to three increasing salinity levels (Experiment C). Different letters above columns indicate significant differences among salinity treatments based on Tukey’s post-hoc tests.
Figure S5. Images of Alternanthera philoxeroides (alligator weed; ALPH) invasion in fringing wetlands along oligohaline to mesohaline tidal reaches in Suisun Marsh, San Francisco Bay-Delta Estuary: A) Displacing open water, and native Schoenoplectus actus and Typha domingensis at Wings Landing, Suisun Slough (2023); B) Invading native Schoenoplectus americanus, S. acutus, Euthamia occidentalis, Juncus balticus, and Typha community at Nurse Slough (2024); C) With Schoenoplectus californicus at Grizzly Island, Montezuma Slough (2020); D) Overgrowing T. domingensis – S. acutus along Montezuma Slough (2023); E) Over-growing S. acutus at Chipps Island (2019); F) Displacing Schoenoplectus americanus, Erythranthe guttata, Juncus balticus and Typha sp. at mid-elevation tidal elevation at Montezuma Slough (2024). A B C D E F