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RIVER NETWORKS
AS ECOLOGICAL CORRIDORS
FOR SPECIES
POPULATIONS AND WATER-BORNE
DISEASE
Andrea Rinaldo

!
!

Laboratory of Ecohydrology ENAC/IIE/ECHO Ecole Polytechnique Fédérale Lausanne (EPFL) CH
Dipartimento ICEA Università di Padova
PLAN
tools: reactive transport on networks
nodes (reactions) + branches (transport)
metacommunity & individual-based models

!

!
modeling migration fronts &
human range expansions
!
spreading of water-borne disease
hydrologic controls on cholera epidemics
!
invasion of vegetation or
freshwater fish species
along fluvial corridors
!
hydrochory & biodiversity
questions of scientific & societal relevance
(population migrations, loss of biodiversity, hydrologic
controls on the spreading of Cholera, meta-history)

explore two critical characteristics (directional dispersal
& network structure as environmental matrix)
for spreading of organisms, species & water-borne disease
Muneepeerakul et al., JTB, 2007
Rodriguet-Iturbe et al., PNAS, 2012
Carrara et al., PNAS, 2012
Carrara et al., PNAS, 2012
Carrara et al., Am. Nat., 2014
TOOLS - about the progress (recently) made on
how to decode the mathematical language
of the geometry of Nature
DTM - GRID
(Planar view)

DTM – GRID format
(Perspective – North towards bottom)
remarkable capabilities
to remotely acquire
& objectively
manipulate
accurate descriptions
of natural landforms
over several orders
of magnitude

if I remove the
scale bar …consilience…

Rodriguez-Iturbe & Rinaldo, Fractal River Basins: Chance and Self-Organization, Cambridge
Univ, Press, 2007
TOOLS
from O(1) m scales…
the MMRS
random-walk
drainage basin network
(Leopold &
Langbein, 1962)
& the resistible
ascent of the
random paradigm
!
Eden growth & self-avoiding random walks
Rigon et al., WRR, 1998

!
Scheidegger’s construction
is exactly solved for
key geometric & topologic features

Huber, J Stat Phys, 1991; Takayasu et al., 1991
optimal channel networks

Rodriguez-Iturbe et al., WRR, 1992 a,b; Rinaldo et al. WRR, 1992
Rigon et al., WRR, 1997
Rinaldo et al., PNAS, in press
Peano – exact results & subtleties
(multifractality
binomial multiplicative process & width functions)

Marani et al., WRR, 1991; Colaiori et al., PRE, 2003
TOOLS 1 - comb-like structures, diffusion processes &
CTRW framework
in terms of density
of particles ρ(x,t)
l

A

B
from traditional
unbiased random-walks to general cases

!

heterogeneous distributions
of spacing, Δx
& length of the comb leg, l
tools - 2
A

B

A

B

delay ~ reactions, lifetime distributions
network → oriented
graph made by nodes
& edges

models of reactive transport

COUPLED MODELS
NODAL REACTIONS

TRANSPORT
MODELS BETWEEN
NODES

individuals, species, populations (metacommunities)
TOOLS 2 - reactive continuous time random walk
Φ(t)

Ψ ( x, t ) pdf of jump &

waiting time

x

diffusion

f (ρ ) reaction
ρ (x,0) ?

∞

+∞

t

−∞

φ (t ) = ∫ dt ' ∫ dx Ψ ( x, t ' )
transport + possibly reactions or interactions
a master equation – if we consider many realizations
of independent processes (large number of
noninteracting propagules) ρ(i,t) is proportional
to the number of propagules in i at time t
hydrochory
!
!
human-range expansion, population migration
quantitative model of US colonization 19th century
& transport on fractal networks
Campos et al., Theor. Pop. Biol., 2006




!
!
the idea that landscape heterogeneities & need for
water forced settling about fluvial courses
!
!
Ammerman & Cavalli Sforza, The Neolithic transition and the
Genetics of population in Europe, Princeton Univ. Press 1984

exact reaction-diffusion model
(logistic with rate parameter a for population growth)

!
!
!
!
a little background on Fisher’s fronts
phase plane → the sign of the eigenvalues of an
appropriate Jacobian matrix
determines the nature of the equilibria
!
(e.g. Murray, 1993)
a few further mathematical details
the Hamilton-Jacobi formalism

the network slows the front!
you waste time trapped in the pockets
Peano’s network

initial cond
r=1

f
a

reaction
logistic growth at every node

transport

f ( ρ ) = aρ (1 − ρ )

0

at every timestep each
particle moves towards a
nearest neighbour
w.p. p= 1 / # nn

1

ρ
SIMULAZIONI
P+=0.5

a=0.5
v speed of front [L/T]

Campos et al., Theor. Pop. Biol., 2006; Bertuzzo et al., WRR, 2007

isotropic migration – Fisher’s model
v = 2√aD

Murray, 1988

Peano (exact)

Peano (numerical)

a (logistic growth)
Relative frequency (%)

geometric constraints imposed by the network
(topology & geometry) impose strong corrections
to the speed of propagation of migratory fronts

Campos et al., Theor. Pop. Biol., 2006; Bertuzzo et al., WRR, 2007
what is a node?
strong hydrologic controls

!
!
!
Giometto et al., PNAS, 2013
Fisher-­‐Kolmogorov	
  Equation

$ ρ'
∂ρ
∂2 ρ
= D 2 + rρ & 1− )
∂t
∂x
% K(

What	
  about	
  variability?
$ ρ'
∂ρ
∂2 ρ
= D 2 + rρ & 1− ) +σ ρ η
∂t
∂x
% K(

η	
  is	
  a	
  δ-­‐correlated	
  gaussian	
  white	
  noise	
  
Itô	
  stochastic	
  calculus

ML	
  estimates	
  for	
  r,K,	
  σ

$ ρ'
∂ρ
= rρ & 1− ) +σ ρ η
∂t
% K(
Transitional	
  probability	
  densities	
  are	
  
computed	
  by	
  numerical	
  integration	
  of	
  the	
  
related	
  Fokker-­‐Planck	
  equation.
Demographic	
  stochasticity

$ ρ'
∂ρ
∂2 ρ
= D 2 + rρ & 1− ) +σ ρ η
∂t
∂x
% K(

η	
  is	
  a	
  δ-­‐correlated	
  gaussian	
  white	
  noise	
  
Itô	
  stochastic	
  calculus

ML	
  estimates	
  for	
  r,K,	
  σ

$ ρ'
∂ρ
= rρ & 1− ) +σ ρ η
∂t
% K(
Transitional	
  probability	
  densities	
  are	
  
computed	
  by	
  numerical	
  integration	
  of	
  the	
  
related	
  Fokker-­‐Planck	
  equation.
Front	
  variability

Giometto et al., PNAS, 2013
Take-­‐home	
  message
• Fisher-­‐Kolmogorov	
  equation	
  
correctly	
  predicts	
  the	
  mean	
  
features	
  of	
  dispersal	
  
!
• The	
  observed	
  variability	
  is	
  
explained	
  by	
  demographic	
  
stochasticity

Link	
  between	
  scales

Giometto et al., PNAS, 2013
Zebra Mussel
Dreissena polymorpha

larval stages
transported along the
fluvial network

1988
1989
1990
1991
data: Nonindigenous Aquatic
species program USGS 1992

1993
1994
1995
Mari et al., in review, 2007

local age-growth model
(4 stages)
!
larval production
!
larval transport
(network)

Zebra Mussel
Zebra Mussel
Mari et al., WRR, 2011; Mari et al., Ecol. Lett., 2014
river biogeography
!
spatial distribution of
biodiversity within a biota
!
riparian vegetation
fluvial fauna
freshwater fish
neutral metacommunity model
metacommunity model
every link is a community of
organisms & internal implicit
spatial dynamics
Explicit spatial dynamics
among different communities

the neutral assumption
all species are equivalent (equal
fertility, mortality, dispersion
Kernel)
the probability with which a
propagule colonizes a site
depends only on its relative
abundance
patterns of biodiversity emerge
because of ecological drift
Hubbel, 2001
neutral metacommunity model
the model
at each timestep an
organism is randonly chosen &
killed
w.p. ν it is substituted by a
species non existing (prob
of speciation/immigration)

w.p. 1-ν the site is colonized
by an organism present in the
system

Pij = (1 − v)

K ij H j
N

∑K

ik

Hk

k =1

H j :habitat capacity link i
K ij :dispersal kernel
run up to steady state
river biogeography
global
properties
γ-diversity: total # of species
patterns of abundance

# of species

preston plot

20 21 22 23 24 25 26 27 28 29 210 211 212

abundance
river biogeography
LOCAL PROPERTIES

α-diversity
number of
species at local
scale
river biogeography

a)

β-diversity
b)

Jaccard similarity index
S ab
S ab # common species
J ab ( x) =
x distance measured along the
α a + α b − S ab
4
J ab ( x) =
= 0.57
6+5−4

network
river biogeography

geographic range

geographic range

area occupied
by a species

ranked species
Mississippi-Missouri freshwater fauna

database
presence(absence) of 429 species freshwater fish in 421 subbasins

α-diversity, β-diversity, γ-diversity, geographic range
fonti

USGS, hydrologic data, NatureServe, Bill Fagan’s ecological data
Mississippi-Missouri freshwater fish

α-diversity

strong correlation
habitat capacity ~
runoff

runoff
distance to outlet

Muneeperakul, Bertuzzo, Fagan, Rinaldo, Rodriguez-Iturbe, Nature, 2008
Muneeperakul et al., Nature, May 8 2008
constant
habitat
capacity
per DTA

hydrologic controls
model

weak interspecific interactions & weak/strong
formulations of the neutral model
patterns -- weak or strong impliations of neutrality?

comparison between geographic ranges of individual
species: a) data b) results from the neutral
metacommunity model (after matching procedure)
Bertuzzo et al., submitted, 2008

equiprobability map – ratio between the number of
common species and the number of species in
the central DTA
environmental resistance R50 for data & the model
is topology reflected in the spatial
organization of the species?

!
species range & maximum drainage
area – the max area experienced
by a species is that in blue color, range
is cross-hatched red
!
containment effect favors colonization
!
Corridors for pathogens of waterborne disease

!
!

Of cholera epidemics & hydrology
Haiti (2010-2011)
Piarroux et al., Emerging Infectious Diseases, 2011
no elementary correlation between population
and cholera cases
Mari et al., J Roy Soc Interface, 2011
Codeco, JID, 2001; Pascual et al, PLOS, 2002; Chao et al, PNAS, 2011

continuous SIR model
αI

µI
infected I

γI

persons

p
I
W

β

B
S
K+B

vibrios

vibrios/m3 B
recovered R

µB B

µR
H: total human population at disease free
equilibrium
µ: natality and mortality rate (day-1)
β: rate of exposure to contaminated water
(day-1)
K: concentration of V. cholerae in water
that yields 50% chance of catching
cholera (cells/m3)

susceptibles S

µS

µH

α: mortality rate due to cholera(day-1)

γ : rate at which people recover from
cholera (day-1)
µB:death rate of V. cholerae in the aquatic
environment (day-1)
p : infected rate of production of V.
cholerae (cells day-1 person-1)
W: volume of water reservoir (m3)
Chao et al., PNAS, 2011
the class of SIB models

Capasso et al, 1979; Codeco, JID, 2001
person

!
SIR model for the temporal &
spatial evolution of water-transmitted
disease revisited → network
susceptibles
I(t)
infected
!
S(t)
a few assumptions
!
!
0
50
100
150
200
total population of humans is
t [days]
unaffected by the disease
!
diffusion of infective humans is small
w.r. to that of bacteria thus set to zero
!
density-dependent reaction terms depend on
local susceptibles
!
!
Capasso et al, 1979; Codeco, JID, 2001; Pascual et al, PLOS, 2002; Hartley et al, PNAS, 2006
person

susceptibles
infected

0

50

100

t [days]

150

200
nodes are human communities with population H
in which the disease can diffuse & grow
Hydrologic Networks

Human-Mobility Network

i

Pij

i
Qij

Rij
j

Qij

j
Mari et al., J Roy Soc Interface, 2011
uniform population
600

500

I(t)
infected

400

300

200

100

0
0

50

100

150

200

time [days]

250

t

300

350
Zipf distribution of population size & self-organization
Zipf’s distribution of population &
secondary peaks of infection
1400

1200

I(t)

infected

1000

800

600

400

200

0
0

50

100

150

200

time [days]

250

t

300

350
spatio-temporal dynamics

initial
conditions

refelecting boundary
condition at all the leaves
and at the outlet

the higher the transport rate, the better the system is approximated by a well-mixed
reactor (spatially implicit scheme)
Bertuzzo et al., J Roy Soc Interface, 2010
10

20

Weekly Cases [103]

25

calibration

20

Cumulative Cases [103]

Rainfall [mm/day]

0

500

300

100

prediction

Nov 10

Sep 11

prediction

15

10

5

0

Nov 10

Jan 11

Mar 11

May 11

Jul 11

Sep 11

Bertuzzo et al. GRL 2011
Bertuzzo et et al., GRL, 2011
θ
m
σ
l
∝B
φ
D
ρ
β
γ
∝

α
−60%

−40%

−20%

0

20%

40%

60%
Rainfall [mm/day]

0

10

20

Weekly Cases [103]

25

calibration

hindcast

20

15

10

5

0
Nov 10

Jan 11

Mar 11

May 11

Jul 11

Sep 11

Rinaldo et al., PNAS, in press
5

Sud−Est

0

Sud

0

5

Nord−Est

5

Nippes

0

0

Weekly Cases [103]

5

5

Nord

0

5

Grande Anse

0

5

Nord−Ouest

5

Centre

0

0
15

Artibonite

15

10

10

5

Ouest

5

0

Jan 11

May 11

Sep 11

0

Jan 11

May 11

Sep 11
25

Weekly Cases [103]

20

15

10

5

0

Nov 10

Jan 11

Mar 11

May 11

Jul 11

Sep 11
effects of rates of loss of acquired immunity (1-5 years)

Weekly Cases [103]

40

30

20

10

0

Jan 11

Jul 11

Jan 12

Jul 12

Jan 13

Jul 13

Jan 14

Rinaldo et al., PNAS, in press
Rainfall [mm/day]

0
5
10
15

Weekly Cases [103]

20
30
20
10
0

Jan 11

Jul 11

Jan 12

Jul 12

Jan 13

Jul 13

Jan 14

Rinaldo et al., PNAS, in press
recorded cholera
cases in Haiti
(2010-2013)
(normalized)

normalized maximum
eigenvector

Gatto et al, PNAS, 2012; Gatto et al, Am Nat, 2014
river networks & biodiversity
!
tradeoff versus neutral models of
the ecology of riparian vegetation

Muneepeerakul et al., JTB, 2007 --> Mari et al., Ecol Lett., 2014
Mari et al., Ecol. Lett., 2014
Muneepeerakul, Weitz, Levin, Rinaldo, Rodriguez-Iturbe, JTB, 2007

links are essentially patches within a landscape
cointaining sites that are occupied by individual plants
the containment effect: the network structure
significantly hinders the dispersal of propagules
across subbasins – less sharing of species
!
fragmentation increases species richness (both neutral
& trade-off communities) (diameters ~ species’
link-scale abundance
power laws matter alot - hotspots & geomorphology
!
indeed a frontier of ecological research

Muneepeerakul et al., WRR, 2007
remote sensing & (much) hydrologic research
→

CONCLUSIONS
!
rivers as ecological corridors →
containment effects (hydrochory
migrations & spreading of epidemics)
!
network structure
provides strong controls & susceptibility
!
e.g. secondary peaks of ‘infections’ or
biodiversity hotspots ~ geometric
constraints rather than dynamics
!
river networks are possibly
templates of biodiversity
impacts of climate change scenarios on local
and regional biodiversity
!
CONCLUSIONS -- 2
!
ecohydrological footprints
from rivers as ecological corridors
& human mobility
for the spreading of epidemic cholera
!
network structure(s)
provides controls & susceptibility
!
from secondary peaks of infections to
rainfall prediction ~ it’s all in the water
!
rainfall drivers –
seasonality, endemicity &
impacts of climate change scenarios,
water management, sanitation
!
collaborations

IGNACIO RODRIGUEZ-ITURBE
MARINO GATTO AMOS MARITAN
RICCARDO RIGON
the ECHO/IIE/ENAC/EPFL Laboratory
ENRICO BERTUZZO, LORENZO MARI, SAMIR SUWEIS
LORENZO RIGHETTO, FRANCESCO CARRARA
SERENA CEOLA, ANDREA GIOMETTO
PIERRE QUELOZ, CARA TOBIN, BETTINA SCHAEFLI

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RIVER NETWORKS AS ECOLOGICAL CORRIDORS FOR SPECIES POPULATIONS AND WATER-BORNE DISEASE