Linking physiological traits and species abundance to invasion resistance Jeremy James Framework • Plant community composition influences ecosystem properties • Much emphasis on effects of functional group diversity on ecosystem properties • Invasive plant management can be improved by managing plant communities based on functional traits as opposed to functional groups Outline • An example of how functional traits influence ecosystem properties (N capture and invasion) – Traits related to N capture – Trait effects on ecosystems are moderated by species abundance • What traits might be important to consider when revegetating areas prone to weed invasion? – At the seedling stage traits affecting initial growth rate important • Conclusions and future directions Functional group diversity, nitrogen capture and invasion resistance Study site Group Annual Annual Bunchgrass Bunchgrass Bunchgrass Forb Forb Code BRTE TACA PSSP ELEL POSE LOTR CRIN Common Name cheatgrass medusahead bluebunch wheatgrass bottlebrush squirreltail Sandberg’s bluegrass nineleaf biscuitroot grey hawksbeard Scientific Name Bromus tectorum L. Taeniatherum caput-medusae (L.) Nevski Pseudoroegneria spicata (Pursh) A. Löve Elymus elymoides (Raf.) Swezey Poa secunda J. Presl Lomatium triternatum (Pursh) Coult. & Rose Crepis intermedia Gray Experimental design • 15N was injected into soils around 7 study species • Injections were made: – 3 times during the growing season (April, May June) – At 2 soil depth (2-7 cm, 17-22 cm) – Using 2 forms of N (NH4+, NO3-) • Removal plots – Medusahead establishment in plots where different functional groups removed April May 60 40 20 15 N capture (% of each species total) N partitioning through time Annuals Bunchgrasses Sandberg Forbs 100 2-7 cm 17-22 cm 80 60 40 20 15 N capture (% of each species total) N partitioning by soil depth Annuals Bunchgrasses Sandberg Forbs Integrating N uptake patterns and species abundance Influence on ecosystem = trait × abundance Portion of community biomass Nitrogen uptake × annuals bunchgrasses Sandberg forbs Total N capture April May June 2.0 1.5 1.0 3.0 2-7 cm 17-22 cm 2.0 1.0 15 -2 N capture (mg m ) 0.5 NH4 2.0 NO3 1.5 1.0 0.5 0.0 + Annuals Bunchgrasses Sandberg Forbs - - T. caput-medusae (plants m 2) Removal plots b 300 200 a a a 100 Nothing removed Annual forbs removed Perennial forbs removed Bunchgrasses removed A trait based approach for managing invasives • Conventional groupings encompass a wide range of trait differences • Different traits likely influence different ecosystem properties • Effective invasive plant management requires an understanding of traits allowing invaders to outperform natives Trait variation of desirable species • Do you want to: – maximize trait variation – maximize a trait A B D C What traits should be considered? • Relative growth rate (RGR) is a key trait to consider Native grass • Invasives often have a higher RGR • Seed → seedling stage – Plant size – Resource capture • Influences competitive interactions and survival Invasive grass Components of RGR • RGR (mg g-1 d-1) has two components – Leaf area ratio (LAR, m2 kg-1), the amount of leaf area per unit total plant mass – Net assimilation rate (NAR, g m-2 d-1), the rate of dry mass gain per unit leaf area RGR (mg g-1 d-1) = LAR (m2 kg-1) x NAR (g m-2 d-1) Decomposition of LAR Leaf area ratio (LAR, m2 kg-1), the amount of leaf area per unit total plant mass, can increase by: 1. Adding more leaf biomass • Leaf mass ratio (LMR) amount of leaf mass per unit plant mass 2. Making more leaf area per unit biomass • Specific leaf area (SLA) amount of leaf area per unit leaf mass LAR = SLA x LMR Decomposition of NAR • NAR (g m2 d-1) rate of dry mass gain per unit leaf area • Is the net balance of: – Photosynthetic carbon gain per unit leaf area minus carbon loss through respiration – Influenced by how efficiently plants use nitrogen (leaf N productivity) and how much N is allocated to leaves. Traits driving RGR variation SLA (m2 kg-1) LAR (m2 kg-1) LMR RGR (g g-1) (mg g-1 d-1) NAR (g m-2 d-1) Leaf N productivity (g leaf g N-1 d-1) Leaf N concentration (g N m-2) Approach • Use model to examine RGR traits in 3 invasive annual grasses, 3 perennial bunchgrasses, 6 invasive forbs, 6 desirable forbs -1 0.12 cre st e d blu eb un ch sq uir rel tai l ch ea tgr as me s du sa he ad ve nte na ta -1 0.14 RGR (g g d ) RGR variation among grasses 0.20 0.18 0.16 0.10 0.08 0.06 0.04 0.02 0.00 sp ot kn ske apw e let on ed we toa ed d wh flax ite top sc t otc ease ht his l tle Ro woo ya ck y m ly su rrow t. p nflo en wer ste Mu m L nro ew on glo is f la be ma x llow -1 -1 RGR (g g d ) RGR variation among forbs 0.15 0.10 0.05 Traits driving RGR variation Invasive Invasive vs. desirable vs. desirable forbsgrasses SLA (m2 kg-1) LAR (m2 kg-1) LMR RGR (g g-1) (mg g-1 d-1) NAR (g m-2 d-1) Leaf N productivity (g leaf g N-1 d-1) Leaf N concentration (g N m-2) Toward trait-based management of invasives • This involves identifying: 1. The specific ecosystem property or processes that we want to manage/ traits of the invader 2. The traits likely to have the largest impact on the property or processes 3. Trait variation and abundance in your desirable species pool • May only need to consider a handful of traits to maximize invasion resistance Traits to consider in desirable species pool 1. Get biomass established and get it fast – Target species with high RGR • High SLA and high nitrogen productivity 2. Select species that differ in phenology 3. Select species that differ in root distribution Questions and comments