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Plant recruitment Control of recruitment Models of recruitment Seed flow Site and seedlimita7on Historical background Desert plants Ben-Gurion University of the Negev 1 Vegeta7on Ecology Course 2015/16 Bertrand Boeken

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Plant  recruitment  • Control  of  recruitment  • Models  of  recruitment  

• Seed  flow  • Site-­‐  and  seed-­‐limita7on  

• Historical  background  • Desert  plants  

Ben-Gurion University of the Negev"

1  

Vegeta7on  Ecology  Course  2015/16  Bertrand  Boeken  

Plant  recruitment  

End  of  a  chain  of  processes  

1.  Seed  produc4on,  primary  and  secondary  dispersal,  arrival,  reten4on  

2.  Seed  imbibi4on  (water  uptake)  and  germina4on  (radicle  protrusion)  

3.  Seedling  emergence  and  establishment  

www.tutorvista.com    

Seeds on mother plant

Seeds in target location

Germinating seeds

Emerging seedlings

Established seedlings

Photo:  Piccolo  Namek  

Recruitment  =  addi4on  of  individuals  to  a  popula4on  

 Usually  of  seedlings  from  sexual  reproduc4on  (seeds),    

some4mes  ramets  from  vegeta4ve  propaga4on  (clonal  

growth)  

Agur  Sands,  Negev  

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Controllers  of  recruitment  

Seeds on mother plant

Seeds in location

Germinating seeds

Pre-­‐dispersal  preda4on  

Secondary  dispersal  vector  

Primary  dispersal  vector  

Post-­‐dispersal  preda4on  

Condi4ons  

Other  plants  

Animal  preda4on  

Microbial  decay  

Resources,  Condi4ons  

Other  plants  

Animal  preda4on  

Microbial  decay  

Emerging seedlings

Resources,  Condi4ons  

Other  plants   Disturbance  

Established seedlings

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Preda4on  during  dispersal    

Models  of  recruitment  

Plant  recruitment  from  seeds  in  a  loca4on  (from  4me  t1  to  t2)  

   NPlants,t2  =  rt1,2  NSeeds,t1        (NPlants,t2  ≤  M  =  NSites,t2)  

•  Density  dependence  

“Site  limita4on”    Recruitment  depends  on  availability  of  microsites  M  

for  which  r>0      

Condi4ons:  sufficient  seeds  present  (large  NSeeds,t1)  e.  g.  ample  seed  rain  or  long-­‐term  dormant  seed  bank  

•  Density  independence  “Seed  limita4on”  (Eriksson  and  Ehrlén  1992)    Recruitment  depends  on  both    

   seed  availability                  NSeeds,t1  

 and  recruitment  rate        rt1,2      rt1,2  =  f  (condi4ons,  resources,  interac4ons,  

 species  traits)  from  4me  t1  to  t2  (site  quality  rel.  to  species  requirements)    Assump4on:  r  includes  low  juvenile  mortality  

in  annual  plants  

NSeeds,t1   NPlants,t2    rt1,2   Pla

nt d

ensi

ty

NP

lant

s,t2

Seed availability NSeeds,t1

rt2

Mt2

P(r

ecru

itmen

t)

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Seed  availability  •  Seed  availability    Depends  on  seed  produc4on  at  the  source(s)  at  

4me  t0  and    

arrival  (a)  at  the  target  un4l  4me  t1:  

NSeeds,t1  =  a  Nseeds  in  sources,t0    

 

 

 

For  species  i,  seed  sources  j:  

   NSeeds,t1  i  =  Σ  aij  Ni,j,t0    

 

Arrival  rates  aij  =  f  (dispersal  I  &  II,  post-­‐release  

preda4on,  accessibility,  pathogens,  

disrup4on);    

aij  also  depends  on  species  traits,  vectors,  

landscape  structure,  patch  proper4es.  

•  Seed  limita4on    if  seed  availability  is  restricted  (<  M)  due  to  

–  No  [input  from]  dormant  seed  bank  

–  Reduced  produc4on  at  the  sources  

–  Low  probability  to  arrive  

•  Improbable  dispersal  from  source  

•  High  post-­‐release  preda4on  •  Low  dispersal  into  target  (import)  

Seed import Local seed production

aj  

Seeds

Sites

r    M  

Dormant seeds

Plants

Nseeds  in  sources,t0   Nseeds,t1    a  Seed flow model

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Site  and  seed  limita7on  •  Is  recruitment  either  seed-­‐  or  site-­‐limited?  

–  At  similar  intermediate  values,  at  low  density  (N/area)?  –  Even  if  seed-­‐limited,  sites  mager.  

•  If  recruitment  is  seed-­‐limited,  is  this  due  to    –  Limited  produc4on  –  Dispersal  limita4on,    –  Seed  removal/decay,  or  

•  Is  this  fixed  per  species,  or  does  it  vary?  –  Is  recruitment  limita4on  a  specific  trait  under  selec4on?  –  Or  is  recruitment  limita4on  an  emergent  demographic  property?  

(due  to  popula4on  responses  to  environmental  varia4on)  

•  Are  sites  either  suitable  (or  safe)  for  recruitment  or  not,    or  somewhere  along  a  site  quality  con7nuum?  

–  Few  high-­‐quality  sites  and  many  low-­‐quality  sites  undis4nguishable  –  Many  quan4ta4ve  and  qualita4ve  factors  determine  suitability  

•  Is  recruitment  an  on/off  process,  or  gradual,  depending  on  variable  site  quality?  –  Variable  germina4on,  seedling  emergence,  growth  and  establishment  rates  –  Each  responding  differently  to  combina4ons  of  factors,  at  different  4mes  

•  Do  only  a  few  seeds  find  a  suitable  site  by  chance,    or  do  seeds  keep  moving  un7l  they  do?  

–  Repeated  dispersal  (e.g.  wind,  runoff)  –  Agractors  –  diggings,  shrub  patches  

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Site  limita7on  in  vegeta7on  science  •  Migra7on  (arrival  of  propagules)  and  ecesis  (establishment  and  persistence)    

(Clements  1904,  1905,  1916)  –  Seed  dispersal  (migra4on)  recognized,  but  arrival  assumed  to  be  unimpeded  

(esp.  in  climax  communi4es)  

–  “Eventually,  all  sites  will  be  occupied  by  suitable  species”  –  Focus  on  the  match  between  species  traits  and  the  biophysical  environment,    

and  reac4on  (facilita4on  by  environmental  modifica4on)  

–  ‘Supra-­‐organismal’  view  of  plant  associa4ons    

•  Assump7on  of  ever-­‐present,  randomly  mixed  seed  rain    (Beijerinck  1913,  Baas  Becking  1934  in  Dutch)  

–  "Everything  is  everywhere,  and  the  environment  selects"    

–  Based  on  cosmopolitan  bacteria  and  ruderal  plants  

–  Communi4es  are  determined  by  climate  and  soil  (Braun-­‐Blanquet  1932,  Oos4ng  1953)  

–  Classifica4on,  syntaxonomy,  mapping  7  

Site  limita7on  in  popula7on  ecology  

•  Stochas7city  of  migra7on  (Gleason  1926)  

–  Communi4es  are  “too  noisy”  to  study  because  of  random  migra4on  

–  Associa4ons  are  coincidental  –  “Only  popula4on-­‐based  focus  will  reveal  rules”    

 

•  Recruitment  site  concept:  safe  sites  (Harper  1965),  regenera7on  niche  

(Grubb  1977)  

–  Plants  establish  in  suitable  sites    •  Interac4ons  (preda4on,  compe44on),  abio4c  condi4ons,  resource  availability  

–  “Plant  popula4ons  are  governed  by  local  processes”  

–  Individual,  not  area-­‐based  

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Seed  limita7on  in  ecological  theory  

•  Seed  limita7on  of  abundance    –  Seed  shadows  (radial  gradients  from  mother  plant)  (Janzen  1971)    

–  Implied  in  metapopula4on  theory  (Hanski  and  Gilpin  1991)  

–  First  men4oned  in  plant  ecology  textbook  by  Crawley  (1990)  (ca.  100  words)  

–  New  empirical  and  theore4cal  studies  (Eriksson  and  Ehrlén  1992,  Turnbull  2000,  Muller-­‐Landau  et  al.  2002)  

–  Experimental  test  by  seed  addi4on  (Turnbull  2000)  and  removal  (Boeken,  in  prep.)   9  

•  Vegeta7on  dynamics  (Pickeg  and  McDonnell  1989)    –  Site  availability,  species  availability,  and  species  performance  

–  Mul4ple  factors,  responses,  scales,  and  levels  of  complexity  

–  No  equilibrium  assump4ons  (satura4on,  DD-­‐density  dependence)  

–  Includes  disturbance,  landscape  heterogeneity  and  human  impacts  

–  Species  availability  implies  a  switch  in  observa4on  

•  from  the  source  (individual  mother  plant)    

•  to  the  target  (a  community  in  a  heterogeneous  landscape)  

Seed  dormancy  in  deserts  •  Seed  banks  (Went  1947,  1948)  

–  Desert  annuals  have  large  dormant  seed  banks  –  Respond  strongly  to  seasonal  rainfall  –  Rainfall  threshold  –  Therefore  site-­‐limited  

•  Predic7ve  and  delayed  germina7on  (e.g.  Koller  1956,  Negbi  and  Evenari  1962,  Evenari  and    Gugerman  1966,  Venable  1989)  –  Highly  selec4ve:  germina4on  if  condi4ons  very  good  –  Prolonged  dormancy  of  a  large  frac4on  of  the  seed  bank  –  Maximiza4on  of  reproduc4ve  value  (Cohen  1966,  1967)  –  Germina4on  upon  rain  dispersal  (Gugerman  1993)  

 

•  High  germina7on  rate  with  no  secondary  dormancy  –  If  dispersal  is  good  (MacArthur  1972,  Venable  and  Lawlor  1980)?  –  Maximiza4on  of  fitness  by  coloniza4on  ability  in  spa4ally  heterogeneous  

and  temporally  variable  landscapes  (“alterna4ve  deserts”)?  –  Such  species  may  experience  seed-­‐limita4on  

Seed  dispersal  in  deserts  s4ll  debated:  strongly  scale-­‐dependent,    probably  short  distance  (1-­‐100  cm)  during  flow  events  

Many  seeds  without  appendages  –  ground  dispersal  (Boeken  and  Shachak  1994)  –  But  non-­‐selec4ve  germina4on  may  have  advantages  –  During  drought,  ayer  ample  seed  crop  in  previous  year  (B.  Boeken  in  prep.)  

www.desertusa.com    

Aizoon  hispanicum  

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Importance  of  seed  limita7on  When  is  seed  limita7on  of  recruitment  important?  

–  During  or  ayer  drought  

•  Annuals  without  dormant  seeds  should  be    

seed-­‐limited  ayer  poor  years  (Boeken,  in  prep.)  

–  Herbivory  and  granivory  –  Landscape  fragmenta4on  –  Regional  ex4nc4on  

Spa4al  context  and  scale      

When  is  it  unimportant?  –  Seed  satura4on  (seed  rain,  seed  bank)  –  Accessible  loca4ons  –  Highly  selec4ve  species  (predic4ve  germina4on)  –  For  species  with  high  DD  juvenile  mortality  

 e.g.  self-­‐thinning  perennials    

Local  condi4ons    (i.e.,  site  availability  and  limita4on)  

Erucaria  pinnata,  Park  Shaked  2004  

Messor  ebeninus,  Park  Shaked  2004  

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