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Interactions between drought and forest pests and diseases
3 approaches
Epidemiological approach: field surveys
Experimental, quantitative approach: metaanalysis of available evidence
Analysis of underlying mechanisms in experimental conditions
Field surveys
Field surveys by operational services: spatial and temporal patterns of occurrence and damagefor different (important) species
Qualitative information (expert judgement) availabe quickly: massive bark beetle attack in 2003 (increase after a decrease in 2002 in the areas damaged by the 1999 storms, and in other regions), etc.
Quantitative information on occurrence / damage is delayed (with a few exceptions) due to validation procedure, not homogeneous over the borders, and generally poor quality.
Field surveys and their interpretation
Relating intensity of damage to intensity of water stress / heat is sofar almost impossible outside experimental conditions
Few scientists have tried to explore the (large-scale) spatial-temporal patterns of pests and diseases versus climate stress
Analysis of published information on the response of pests and diseases to
water stressSee Jactel et al.
Numerous experiments, few well documented!
Damage proportional to pests and diseases
But : response of pests and diseases to stress is non linear (confirms that the intensity of water stress must be known)
Working group
Marie-Laure Desprez-Loustau, Dominique Piou, Andrea Vannini, Louis-Michel Nageleisen and Benoît Marçais
Interactive effects of drought and pathogens in forest tress
THE DISEASE TRIANGLE
PATHOGEN HOST
DISEASE
ENVIRONMENT natural and anthropic effects ; local and global change
(drought, heat, sylviculture, …)
DIRECT or INDIRECT EFFECTS OF DROUGHT ON PATHOGENS?
Foliar polycyclic diseases : often less common and less severe during drought episodes:
rain/moisture needed for dissemination, germination and penetration)
E
DISEASE
HP
Relative importance of external / internal infection processes:
Stem and root diseases : indirect effects through host physiology : water stress is determinant
1. Effects of drought on host –pathogen interaction :
increased susceptibility to pathogens:PREDISPOSITION
• generally, development of disease during or following stress
• some types of pathogens: mainly necrotrophs, facultative parasites
E
HP
E
HP
2. Effects of disease on the plant response to drought stress :
decreased tolerance to MULTIPLE STRESSES
•disease developed before stress
•all types of pathogens (including biotrophs)
1. Predisposition of trees to disease by drought (heat) stress
« Drought-enhanced diseases » : favoured by drought but caused by « true parasites »
mainly cankers (necrotroph pathogens)Example : Sphaeropsis sapinea
Sensu lato: Increased « disease proneness » resulting from external causes (does not imply that infection always occurs after stress)
« Drought-induced diseases »: caused by opportunistic, facultative or conditional parasites
mainly endophytic speciesExample : Biscognauxia mediterranea
Mechanisms of predisposition
Decrease in photosynthetic activity and altered protein synthesis in dehydrated plants resulting in :
Metabolic changes : improved substrate for pathogen (nitrogen)
Decreased defensive compounds (phytoalexins, enzymes, etc…)
Slowed defenses limiting compartmentalization
Experimental evidence of predisposition mechanisms: Effects of water stress on the rate of formation of
physical defenses (after wounding) in Abies grandis* (Puritch & Mulklick 1975)
0
10
20
30
40
50
60
70
0 1 2 3 4
Stress level (-MPa)
Nb
Day
s to
fo
rm N
IT
exp1exp2exp3exp4
* NIT = non-suberized impervious tissue, involved in necrophylactic periderm formation
Sphaeropsis sapinea : an endemic pathogen in Europe with recent outbreaks in pine forests
associated with predisposing stresses
1991-4 D
1996 D
1990-94 D t°>
1980's
1984 t°>
1986 D t°> t°<
2002
1982-5 D N
1990
1999 H
1990-2 D
2001-2 t°>
1988
2000-1
1986-90
1994 D
1992
1998
1986
1994 D t°>
1994 H1986-9 D
2001 D
1992-3 D
1991
1994
1996-97 D t°>
P. pinasterP. halepensis
P. radiataP. nigraP. pinea
P. sylvestris
1991-4 D
1996 D
1990-94 D t°>
1980's
1984 t°>
1986 D t°> t°<
2002
1982-5 D N
1990
1999 H
1990-2 D
2001-2 t°>
1988
2000-1
1986-90
1994 D
1992
1998
1986
1994 D t°>
1994 H1986-9 D
2001 D
1992-3 D
1991
1994
1996-97 D t°>
P. pinasterP. halepensis
P. radiataP. nigraP. pinea
P. sylvestris
P. pinasterP. pinasterP. halepensisP. halepensis
P. radiataP. radiataP. nigraP. nigraP. pineaP. pinea
P. sylvestrisP. sylvestris
Stress factors : N = nitrogen pollutψantsD = drought t°> = hight temperaturesH = Hail t°< = low temperatures
Main symptoms associated with drought * S. sapinea
Bark necrosisCanker (uncommon in Europe)
Crown or branch dieback
Affected stands are always plantation forests(P. pinaster not affected in Europe but heavily damaged in S Africa
Biscogniauxia (Hypoxylon) mediterraneum :an endophyte turning to parasite with drought stress
Q. cerris
Q. pubescens
5101520253035
-4,0 -3,5 -3,0 -2,5 -2,0 -1,5 -1,0
MWP (MPa)
Iso
lati
on
%B. mediterraneum is morereadily isolated in stressed
trees (Quercus cerris) (Lucero 2000)
The development of symptoms is linked to water status
(Vannini et al. 1996)
1. Predisposition2. Combination of biotic and abiotic stresses : effects of multiples stresses
Both infection and drought act as stresses on the plant
In general, this results in additive or synergistic deleterious effects
3.Collapse or exhaustion
Combined effects of infection and drought stresses1. Root pathogen (affecting directly water relations)
Ex : Collybia fusipes, root pathogen on oak (Marçais)
Not a predisposition effect : oaks growing in high sand content are not more susceptible to Collybia) > likely explained by a reduced water uptake due to root loss
0123456789
Sand content (%)0 20 40 60
Rel
ativ
e ris
k of
dec
line
asso
ciat
ed w
ith in
fect
ion
0123456789
Sand content (%)0 20 40 60
Rel
ativ
e ris
k of
dec
line
asso
ciat
ed w
ith in
fect
ion
0123456789
0123456789
Sand content (%)0 20 40 60
Rel
ativ
e ris
k of
dec
line
asso
ciat
ed w
ith in
fect
ion risk of decline in
infected trees (compared to healthy ones) increases sign. with sand content (decreasing water availability)
2. Foliar pathogen (Groundsel rust, Ayres 1991)
5
9
13
17
21
9 11 13 15
Days after inoculation
Pn (m
g CO
2 pl
ant-1
h-1
)
HEALTHY
INF
DROUGHT
INF +DROUGHT
-0.2 MPa
-1.6 MPa
-1.1 MPa
-0.8 MPa
(affecting the photosynthesis)
drought prevents the growth of new, uninfected leaves
The decline concept (Manion 1991)
Some documented oak declines in FranceTronçais Harth Mediterr.
regionHaguenau Lure
SpeciesMortality period
Q. robur
1978-82
Q.spp
1991-94
Q.suber
1991-94
Q.robur, Q.petraea1995-97
Q.robur
1995-97PredisposingSite, AgeRoot pathogens (Collybia, Phytophthora)
+
+
+
(+)
+
+
+ +
(+)
IncitingWater stressDefoliatorsPowdery mildew
+(76)??
+(89-92)(+)
+(89-92)(+)
?+(93-94)+(93-94)
+(89-91)
ContributoryFungi (Armillaria)Insects(borers)
+
? +
+
+ + +
MECHANISMS : Plants stress responses
STRESSStress recognition
Signal transduction
Gene expression
Altered cell metabolism
Physiological and developmental response
Effects of stresses in plant populations and communities
Drought and infection can have additive effects in increasing both inter- and intra- specific competitive fitness
Competition for resources
DROUGHTDISEASE
Fitness
Competitive fitness affected by disease and droughtgroundsel rust: an experimental demonstration of
(Ayres 1991)
Dry
wei
ght
Shoot potential
Well-watered
Water-stressed
Monoculture H or I (no competition)
Mixture H + I (competition)
�Healthy
Infected Reallocation of
the ressources (esp. Water) within the pop. In favour of the healthy ind.Negative effect of double stress less than at the individual level
An example of long-term response of ecosystems to extreme stresses
0
20
40
60
80
100
1930 1940 1950 1960 1970 1980
Effects of chestnut blight (Cryphonectria parasitica) on a deciduous forest ecosystem (after Day & Monk 1974)
Conclusions and future prospects
Interactive effects of drought and disease favor two types of damage :
drought-induced diseases (Predisposition) declines (Multiple stress effects)
In both cases, the severity of water stressexperienced by trees is crucial
Conclusions and future prospects (2)
Considerations for management
Measures aimed at limiting pathogen spread : seeds (S. sapinea), nursery plants (Phytophthoraspp)
Favour silvicultural practices that promote elastic responses of stands to drought(heat) stresses (cf physiology group), including use of inter- and intra- specific diversity
Conclusions and future prospects (3)
Future needs for research
Heat stress effects
Long-term effects of multiple stresses (ex :N deposition * drought * disease)
Shifts between mutualism and parasitism : genetic and environmental control
Population (community)-wide studies of the impact of multiple stresses (on yield and diversity) ; implications for breeding programs and sylviculture