Arthropods in Agricultural Landscapes: Challenging and...
Transcript of Arthropods in Agricultural Landscapes: Challenging and...
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Nancy Schellhorn Principal Research Scientist Team Leader – Spatial Ecology
Arthropods in Agricultural Landscapes: Challenging and Supporting Food and Fibre
Production
AGRICULTURE FLAGSHIP
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Presentation title | Presenter name | Page 2
‘Despite a clear increase in pesticide use, crop losses have
not significantly decreased during the last 40 years’ (Oerke, 2006, J Ag Sc)
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Yield loss (pre-farm gate) and efficacy of control
(Oerke, 2006, J Ag Sc)
Loss
Pre-harvest 18%
+ post-harvest = 37%
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Increasing Food Demand Global challenges (Keating et al 2014):
1. Reducing food & fibre loss
2. Minimizing degradation of Ag landscapes
3. Reducing farm inputs
Entomology
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Key message:
Entomology will be part of the solution
• Connect scales
• Demonstrate impact
Global challenge of food & fibre demand
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Presentation title | Presenter name | Page 6
Arthropods are habitat linkers!
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Spatial & Temporal Scale
Population processes occur at various spatial scales
Stiling & Strong 1982, Heads & Lawton 1983; Weins & Milne 1989; Thies & Tscharntke 1999; Bommarco & Banks 2003, Schellhorn
& Andow 2005; Tscharntke et al 2005; Schellhorn et al 2015 (in press)
Temporal scales
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Farming Practices
Presentation title | Presenter name | Page 8
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Measures of Impact
Must be linked to the management objective
Examples are many and varied but must provide
evidence of:
• lesser problem
• greater savings
• science-based solution is being adopted
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• Movement • Landscapes • Farming practices
Research approach:
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Presentation title | Presenter name | Page 11
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OUTLINE: 2 examples - global challenges
1. Link between perennial habitat and crop pest control
Minimizing degradation of Ag landscapes
2. Moth behaviour across cotton / grain landscapes
Reducing Farm Inputs
Reducing food & fibre loss
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Thies & Tscharntke 1999, Science
Seminal paper – Landscape Structure and Biological Control in Agro-ecosystems
Meligethes aeneau
Ichneumonidae
Tersilochus heterocerus,
Phradis interstitialis,
P. morionellus
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What’s the global state of play 15+?
> 65 Studies rl/sp landscape metrics (% area) and
abundance and diversity of NE
Trend is positive – higher abundance and diversity of NE
with higher % non-crop habitat;
Most studies = NE abundance and diversity – a few
measure pest suppression;
Demonstrates a clear link b/t spatial scales -- field, farm &
landscape.
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The ‘problems’ and gaps
Schellhorn et al Insect Sci 2015
Strong focus on NE abundance / diversity & landscape
Need more examples of pests abundance & landscape
Most Northern Hemisphere;
Need examples from Asia;
Need more examples that integrate farming practice with
landscape ecology studies
Several have demonstrated pest suppression = pest control
Need evidence of > control or > savings; evidence of impact (Chaplin-Kramer et al 2012; Jonnson et al 2012; Rusch et al 2013; Costamanga et al 2014 (in press))
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1. Link between perennial habitat and crop pest control
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Presentation title | Presenter name
|
Bethugra, NSW
Ex. 1. The problem: Focus has been on pest and natural enemies in crops – not other habitats in landscape.
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Key Predators & Pests, juveniles & adults
Ex. 1. The solution: Where are pests and predators found?
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Method
Landscape
Year/ Month
Sites
Region
Crop Near
Sites
Native Veg.
Weeds
Sites
Monthly Samples
F M A M J J A S O N D J F M A M J J A S O N D
2009 2010
Crop Far Sites
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Ex. 1. The solution: Where are pests and predators found?
Pest = Region (40%) (F2,282=209.92 P<.001 ) and habitat type (31%) (F2,282=163.01 P<.001 )
Predators = 50% habitat type alone (F2,282=159.46 P<.001)
Bianchi et al, 2013; Ag & For Ent ; Parry et al, 2015, Basic & App Ecol (in press)
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In native remnants, on which plant species are they found?
Pests = 47% of the variance was explained by plant type alone (F2,154=72.59 P<.001)
Predators = region (35%) (F2,152=67.03 P<.001 ) and plant type (4%) (F2,152=8.12 P<.001 )
Bianchi et al, 2013; Ag & For Ent; Parry et al, 2015, Basic & App Ecol (in press)
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The solution: When are they there?
Photo credit: Keith Power, Beatsheet
Adult Nymph
Rutherglen Bug Nysius vinitor
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NSW: January-March 2010
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NSW: April-June 2010
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NSW: July-September 2010
canola
canola
canola
canola
canola
canola
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NSW: October-December 2010
canola
canola
canola
canola
canola
canola
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More weeds in pastures = more Rutherglen bug juveniles
0
25
50
75
100
0.5 2.5 3 5 7.5 15 35 50weed percentage
Mea
n de
nsity
of r
gbJ
per
m2
Me
an
Ruth
erg
len b
ug juvenile
s p
er
m2
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The Solution: When are they there?
0.0
100.0
200.0
300.0
400.0
500.0
Tota
l per
mo
nth
m2
NV Adult
NV Juv
0
100
200
300
400
500
600
Jan
Feb
Mar
ch
Ap
ril
May
Jun
e
July
Au
g
Sep
t
Oct
No
v
De
c
Jan
Feb
Mar
ch
Ap
ril
May
Jun
e
July
Au
g
Sep
t
Oct
2010 2011
Tota
l per
mo
nth
m2
Canola Adult
Canola Juv
Wheat Adult
Wheat Juv
Photos credit: www.goodbugs.org.au
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Pe
st d
en
sity
Time
Theory predicts: Early arrival of predators results in better pest suppression
Settle et al. 1996; Ives & Settle 1997; Landis & van der Werf 1997; Bianchi & van der Werf 2003; Bianchi et al 2009
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Sentinel plants (1000’s+)
The solution: Is pest suppression greater in fields near remnant veg patches compared to far?
Melon
Whitefly
nymphs
Cotton
Helicoverpa
eggs
Darling
Downs
Landscapes
simple
complex
X 19
Lockyer
Valley, QLD
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Period
Para
sitoid
s p
er
pla
nt
0.0
0.1
0.2
0.3
0.4
0.5
2007
2008
Early Mid Late
Remnant Near Far
0.0
0.2
0.4
0.6
0.8
North
South
Pa
rasito
ids p
er
pla
nt
Cotton
Bianchi et al. Ag, Ecosys, & Env (in review)
Darling
Downs
Spatially and temporally erradict
Significant factors - % NV @ 1km; TRT; Period; Year
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0 5 10 15
0
50
100
150
surv
ivin
g a
phid
s
% Lucerne at 2 km
Land-use predictors – Aphid predation
aphids = 70.29 - 5.29 (% Lucerne 1.5K); Adj. r2 = 0.37
Melon
% Lucerne 1.5K Costamanga et al. Ecol Appl (in press)
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Adj r2 = 0.41
Sources of Insect Predators
Costamanga et al. Ecol Appl (in press)
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Snap shot - Data Summary
Think beyond the crop -- Landscape context matters!
Native vegetation clearly provides
habitat for beneficials, especially
important out-of-cropping season
Weeds harbour pests, and some
beneficials;
Perennial pasture and lucerne plays key
role in landscape for beneficials AND for
pests if pasture is degraded and weedy!
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Presentation title | Presenter name 35 |
Parry et al., Basic
and Applied Ecology
(in press)
Relative benefit of a plant species
Predator Dominated
Pest Dominated
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Presentation title | Presenter name
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Lower for Longer
Pest suppression
Schellhorn et al. Insect Science 2015 – Special Feature
Pest control
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Presentation title | Presenter name | Page 38
Summary Ex. 1:
Link Conservation Biology
& Agricultural Production
? IMPACT
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2. Helicoverpa spp moth behaviour across a landscape
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Helicoverpa armigera
[GLOBAL PEST]
and H. punctigera
159 host spp,
~85 HA & HP
~34 HA (monocots) (Zalucki et al 1986)
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Bt Cotton (Bollgard®)
Helicoverpa armigera & H. punctigera
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0
2
4
6
8
10
12
95/9
6
96/9
7
97/9
8
98/9
9
99/0
0
00/0
1
01/
02
02/
03
03/
04
04/
05
05/
06
06/
07
ac
tiv
e in
gre
die
nt
(kg
pe
r h
a)
Conventional INGARD Bollgard II
IMPACTS of GM based IPM - Insecticide Reductions
Ist generation Bt cotton
44% reduction
2nd Generation Bt Cotton
85% reduction
Data courtesy of GP Fitt
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The Problem: Reduction in insecticide use depends on: 1. continued effective Resistance Mngt Plan;
and 2. biological control for other Helicoverpa
susceptible crops across landscape.
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Queensland, Australia
Darling Downs,
Field data collection
Cotton
Sorghum
Maize
Pigeon Pea
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Bt Cotton Other host crops
(e.g. Sorghum)
SINK
Grasses
SOURCE
Ha only
Helicoverpa armigera
and H. punctigera
Mandated Refuge
(Pigeon Pea)
SOURCE
Ha & Hp
159 host spp,
~85 HA & HP
~34 HA (monocots) (Zalucki et al 1986)
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Mandated Refuge (% of Bollgard Cotton)
• 5% Pigeon Pea
• 10% Unsprayed conventional cotton
• Within 2km of Bollgard Cotton
Planting Windows
Pupae Busting
$170-230 Ha
(seed, H2O,
cultivation, herbicide)
$2000-2800 Ha
(gross margin of cotton)
(pers. comm. Dr Paul Grundy)
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hypotheses E
gg
de
nsity
0 100
% Bt Cotton (km)
H. Armigera only
% Sorghum (km)
Eg
g d
en
sity
0 100
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100 %
of crop
1 2 6 5 4 3 8 7
fields
Selecting Fields for Sampling & Characterizing Land Use / Land Cover
sorghum
Bt cotton (sink)
Corn
Pigeon pea
26 different land use categories were
mapped for each landscape using Arc GIS
185 ha
30 ha
8 Bt cotton fields
3 landscapes
5 years
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Parasitized
H. armigera
H. punctigera
Helicoverpa spp
Infertile
Unviable
Parasitized unknown
Counted
Collected
a sub-set
Fates determined:
(23,819)
(15,934)
Eggs tell us about
female
moth behaviour
Eggs in Bt cotton tell
us about colonization
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Summary of spatio-temporal data
•Three landscapes
•Five Years
N C P N C P N C P N C P N C P
09/10 10/11 11/12 12/13 13/14
Drought Big Flood Regular Flood Drought
Bt cotton sorghum pigeon pea
Egg data: Approx 36,000 eggs counted;
20,000 eggs collected - fates for Helicoverpa
spp. and egg parasitoids.
Moth data -Sweep Net data: Caught and
disturbed Helicoverpa spp (♀ moths caught
12/13 and 13/14 dissected )
Moth data - Pheromone trap data: ♂
Helicoverpa both spp. approx 6000 traps deployed
75000 male moths caught
Pupae dig data: Helicoverpa spp. associated
parasitoids (5th instar = trigger) 15 sites
Moth data - UV Solar light trap data: 64 traps rpt
3 x for one landscape. Total 192 traps
♀Helicoverpa moths spp. dissected (approx 90
moths)
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PAMPAS
% L
and
Co
ver
0
20
40
60
80
100
0
20
40
60
80
100
CECIL PLAINS
NANDI
0
20
40
60
80
100
Matrix Source Bt cotton
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Pampas
2009-10
DROUGHT
2010-11
FLOOD
2011-12
NORMAL
2012-13
FLOOD
2013-14
DROUGHT
0
20
40
60
80
100
0
20
40
60
80
100
0
20
40
60
80
100
0
20
40
60
80
100
0
20
40
60
80
100
0
20
40
60
80
100
0
20
40
60
80
100
0
20
40
60
80
100
0
20
40
60
80
100
0
20
40
60
80
100
Cecil Plains
Dec 6Jan 6
Jan19Feb 9
Feb 23
Mar 16
0
20
40
60
80
100
Dec 6
Flood
Feb 8
Feb 22
Mar 8
Mar 22
Apr 6
0
20
40
60
80
100
Dec 6
Dec20
Jan 3
Jan 17
Jan 31
Feb 14
Feb 280
20
40
60
80
100
Dec 5
Dec 19Jan 2
Jan 15
Flood
Feb 2
Feb 20Mar 6
0
20
40
60
80
100
Dec 2
Dec 16
Dec 30
Jan 13
Jan 27
Feb 10
Feb 240
20
40
60
80
100
Helicoverpa armigera Helicoverpa punctigera
% H
elic
overp
a e
ggs c
olle
cte
d f
rom
Bt cotton
Date - Trip
*
* No eggs found
Nandi
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Helicoverpa armigera
and H. punctigera
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Random Forest Models What is it?
Machine learning technique
Average of a large series of de-correlated regression trees
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Random Forest Models What are the features?
• Distribution free; • Large # of predictors of diff. types (continuous and
categorical); • Handles missing data; • Handles collinearity – (i.e. landscape compositional data;
nested spatial scales) • Non-parametric modelling approach
4 spatial scales, 26 land uses, +temporal variables = 100+
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Top Predictors
from RF model –
Pruned Regression Tree
LARGEST
# predicted Ha eggs
(165) Yr 2;
>4.5 Hp eggs;
Sorghum @ 2km
< 15%
SMALLEST
# predicted Ha
eggs (3-6);
Cotdev pre-flwr
n=258
years (n=682)
LARGEST
# predicted Ha eggs
YR1,4,5; Lndscp B,C
Little fallow;
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Top Predictors
from RF model –
Pruned Regression Tree
TEMPORAL variables
Flowering Cotton,
Moon Phase,
Year,
& est. # Ha eggs
n=682
LARGEST
# predicted Hp eggs;
Waxing moon @ >80%,
or Cot flrw & lots of Ha
eggs;
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Random Forests Parametric models
Exploratory tool
- 100+ predictors
- Eg. 4 spatial scales, 3 temporal scales, egg
densities of each Helicoverpa spp, and 26
landuses;
confidence; shift question
-predictors affecting spp proportions & predict
abundance
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What predicts H. armigera egg abundance in cotton?
GLMM – fixed effects [Yr,Trip, unique field, season:lndscp random effects]
H. armigera
Eg
g d
en
sity
0 100
% Bt Cotton (km) % Bt Cotton @ 2 km
Landscape
N
CP
P E
gg d
ensity in c
ott
on
0 100
(adjusted R2 = 52.1 )
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• 20 x more eggs (1km radius) in
sorghum ‘surrounded’ by cotton, than
sorghum in a ‘sea’ of sorghum
•More moths too.
H. armigera eggs and moths in sorghum?
Early descriptive results
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What predicts H. punctigera egg abundance in cotton?
GLMM – fixed effects [Yr,Trip, unique field, season:lndscp random effects]
H. punctigera
Eg
g d
en
sity
0 100
% Bt Cotton (km)
Cotton
development
% of Full Moon % fallow (bare soil) @ 1km
No.
of
eggs in c
ott
on
(adjusted R2 = 47.9)
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Summary of Results:
Spatial drivers dominate for H. armigera
Temporal drivers dominate for H. punctigera
Local landscape
Host preference (sorghum over cotton)
80% waxing to full moon
Cotton Development (squares to open flowers)
No crops at 1km
‘Influence of the moon is likely to be
complex’ Zalucki 91; Zalucki et al 94; Morton et al. 81;
Walker 89; Scholz & Parker 2003;
Understanding of key drivers of global pests
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Presentation title | Presenter name | Page 63
Summary Ex. ‘2’:
? IMPACT
(Resistance Management
Plan)
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Future opportunities to reduce farm inputs:
N
Bommarco et al, Oecologia (in review) Lundin et al 2013, Proc Royal Soc B
YIELD
Termite and Ant Tunnels – No-till marginal grain systems
Evans et al, 2012, Nature Communications
H2O infiltration; N uptake;
YIELD 37%
Ecological intensification
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• Movement • Landscapes • Farming practices
Conclusion:
Impact • Capture of pest control services from
landscape mosaic = protect natural farm assets • Potential to refine resistance management
plan = reduce food fibre loss; reduce pesticide use
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Presentation title | Presenter name | Page 66
15-20-fold
increase in the
amount of
pesticides used
worldwide in
grain
(Oerke 2006)
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Presentation title | Presenter name | Page 67
AG Landscape Ex.
MANY THANKS TO:
Growers;
Funders; and
Collaborators
Svet Micic, Tony
Dore, Art Diggle
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Presentation title | Presenter name | Page 68
Bt Cotton Ex.
MANY THANKS TO:
Growers;
Funders; Tracey Parker;
and many casuals
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Thank you CSIRO Dr Nancy Schellhorn
T +61 7 3833 5710
e [email protected] w http://www.csiro.au/people/Nancy.Schellhorn
AGRICULTURE FLAGSHIP
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Egg Fates
H. armigera
H. punctigera
Unable to distinguish
Unviable
Parasitized (spp)
Unable to distinguish
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Presentation title | Presenter name | Page 72
Doubling of Grain Production since 1960’s (Oerke, 2006, J Ag Sc)
6.9-fold increase in N fertilizion
1.7-fold increase in amount of irrigated cropland
1.1-fold increase in land in cultivation
0.5-0.6 increase in genetic improvements by crop breeders (McLaren 2000)
15-20-fold increase in the amount of pesticides used worldwide
(No significant decrease in crops losses; has enabled farmers to
increase crop productivity without losing an economically non-acceptable
portion of their crop to pests)