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Page 1: 7th Quizzes - nature.berkeley.edu

7th Quizzes

Page 2: 7th Quizzes - nature.berkeley.edu

Descriptive stats of IFPs

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“Emergent diseases”:1: host

• New host-pathogen combinations:

exotic hostshosts planted off site

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Cypress canker by Seiridium cardinale

• Pathogen was first described in California in the 20s. Later it was described in Italy where it started a serous epidemic of Italian cypress

• Belief that pathogen is native to California: is that true and why is it then causing a significant disease in our state?

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Natural geographic distribution of Cupressus sempervirens (red).

Anthropic distribution of Cupressus sempervirens (blue).

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Conidia of Seiridium cardinale observed by

optical microscope and SEM

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Needs wounds

Canker kills cambium

Toxin affects stomatal opening

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In some places of Tuscany the situation of Cypresses is dramatic…

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RESULTS: CA vs. Europe

o California population diverse genetically

o California population has a genetic structure in agreement with sexual reproduction

o European population reproducing clonally

o European population show less diversity

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Distribution of Seiridium cardinale according to Wagener in 1939

Fig. 1.

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Presence of pathogen confirmed in 2008Symptoms observed without intense surveying in 2008

Fig. 5.

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Distrinution of pathogen where intensively surveyed

Symptoms caused by Seiridium cardinale on Cupressus macrocarpa (above) and xCupressocyparis leylandii (right)

Fig. 2.

Fig. 3

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Close-ups of symptoms leading to mortalityFig. 4.

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Why a disease in CA?

• If pathogen is native to California, why is it causing such a serious disease?

• We observed that disease incidence is variable with:– cypress species, – location, – abundance of planted cypresses

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Range of susceptibility

• Leyland cypress, Italian, monterey are listed as most susceptible

• Arizona and McKnob are regarded as more resistant

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Range of susceptibility• 90% of Leyland are heavily infected

• 10% of monterey

• LEYLAND CYPRESS IS AN ORNAMENTAL CROSS, NOT NATIVE

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Range of susceptibility

• Monterey is more susceptible in inland areas where it is NOT NATIVE: we believe that colder temperatures cause more wounds that lead to infection

• More disease where there are more cypresses: classical DENSITY DEPENDANCE effect

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One consequence of an outbreak of an emergent

disease…• It may become source for an

introduction

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CONCLUSIONS

• Cypress canker is a serious disease in Europe because pathogen was introduced

• Cypress canker is a serious disease in California because hosts were introduced either through planting off range (Monterey cypress) or because host is artificial creation (Leyland cypress); extinction of LEYLAND is most likely

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AFLP analysis identified 2 clusters in Europe, one that includes also California isolates, and one that does not, meaning it is exclusively European

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We now feel comfortable stating that

California population is the sourceMediterranean cluster 1 is the founder populationMediterranean cluster 2 is an adaptation in the Mediterranean

We can ask interesting questions on why S, cardinalehas been so successful as an invasive.

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Smaller spore size is selected for and adaptive in bothMed1 and Med2 in spite of trade off of reduced germination]of smaller spores

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Demographic plasticity increases in MED1 respect to CA, But then decreases in MED2, as the invasive adapts to Certain habitats

Table 6. Phenotypic plasticity index (PIv = max mean – min mean / max mean) and coefficient of variation (in brackets) of all the assayed traits calculated for the geographic S. cardinale populations and the genetic sub-populations. Genetic diversity was evaluated for the populations and sub-populations of the fungus using three different indices: Haplotype diversity; gene diversity and gene diversity as expected heterozygosity.

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However, one of the best option overseas is the use of resistant cultivars

Seiridum cardinale is listed as present in Europe and in California so no regulations apply, however virulence of California isolates is greater and resistant cypresses to the strains now present in the Mediterrenean, may be susceptible to new strains, this nullifying 30 years of research necessary to develop such cultivars

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Sporulation: sporulation in the short period does not Increase in either Med1 or Med2, suggesting lack ofCompetition in the new range in the Mediterranean Basin

Longer term sporulation increases, as expected due to fact that it is linked to transmission. However it appearsthat increased sporulation is not easily evolvable, as itonly evolves in Med2

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Ca and Med populations remain distinct not only genetically but also

1- Ability to grow at extreme temperatures is lost in med populations (and not regained in MED 2).

2- Virulence of Med populations is lower than that of CAPopulations. This is an advantage as the pathogen does not wipe out all of its hosts

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“Emergent diseases”:2: environmental changes

• Forestry and intensive forest use:timber productiontree felling and creation of stumpsfire exclusion and increase in densityoversimplified forest compositionchanges in forest compositionchanges in forest structure

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Heterobasidion root disease

• Heterobasidion (a bracket or shelf mushroom) infects trees through wounds and stumps, then it spreads through the roots to neighboring trees

• With tree felling,stumps and wounds are created, suddenly exponentially increasing infection levels

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Heterobasidion shelf fruit-body

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Stump creation and subsequent infection by Heterobasidion annosum

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Use of molecular genetics:

• Differentiate Heterobasidion on fir/sequoias (H. occidentale) from that on pine/junipers (H.irregulare)

• Show that airborne meiospores are responsible for most infection of Heterobasidion

• Show that in pines most infections start on stumps and that in true firs most infections on wounds

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True firs

Pines

Each spore is a genetically different individual:

In pines we found the same genetic individual in stumps andadjacent trees indicating direct contagion between the two

In true firs and true firs/sequoias we find same individual in adjacent standing trees indicating infection not linkedto stumps but to wounds on standing trees

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CONCLUSIONS:• Logging activities increase Heterobasidion

infection because of stump creation in pines and because of wounding in true firs sequoias

• We have shown that in pine stumps H. irregulare and H. occidentale can both be present and create a new hybrid entity

• We have shown that in the past these hybridization events have lead to sharing of genes among these two species (Horizontal gene transfers)

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Once Heterobasidion is established at high frequency

• Significant loss in timber value• Dangerous situations (campsites)• Mortality of valuable species such as

sequoia• With insects and pollution it makes trees

more susceptible to mortality• Can make fires more destructive

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Sequoia National Park

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Annosus root disease in giant sequoia

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Ponderosa pine Incense cedar

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Yosemite Lodge complex1972

cabin crushed by tree with rotted roots

since 19737 fatalities

19 serious injuriesOver $1M property damage

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Yosemite Lodge 1975 Root disease centers outlined

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Yosemite Lodge 1997 Root disease centers outlined

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Many gaps with very little regeneration and have not closed in

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Change in gap area 1972-1999

YearArea in gaps

(m2) Percent in gaps

1972 6125 3.5

1999 53,981 31

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Armillaria root diseases• Armillaria, the honey mushroom, normally infects the

roots of trees. It can be a saprobe and a pathogen and is common amongst oaks

• If woodland composition shifts to pine/oak, pines become the target of attacks and gaps in canopy enlarge over time. Stress (e.g. flooding) exacerbates susceptibility

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Clusters of Armillaria

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How Does it Infect?

SOURCE: http://www.forestpathology.org/dis_arm.html

Two means of dispersal to other trees:

1.Mycelium can grow through direct root contacts and grafts with uninfected trees.

2.Rhizomorphs can grow through soil to contact uninfected trees.

DEAD OAK

OAK or PINE

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What are Rhizomorphs?• …“conglomerations of differentiated parallel hyphae with a protectivemelanized black rind on the outside.”

• Rhizomorphs are able to transport food and nutrients long distances which allows the fungus to grow through nutrient poor areas located between large food sources such as stumps.

SOURCE: http://www.nifg.org.uk/armillaria.htm

SOURCE: http://botit.botany.wisc.edu/toms_fungi/apr2002.html

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Humongous Fungus

It’s One of U-HAUL’s “Bizarre Roadside Attractions”

http://botit.botany.wisc.edu/toms_fungi/apr2002.html

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CONCLUSIONS

Human activities shifting from oak woodlands to mixed oak-pine lead

to large mortality gaps in pines around oaks if honey mushroom is

presentCHANGING SPECIES

COMPOSITION LEADS TO SEVERE DISEASE

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Many gaps with very little regeneration and have not closed in

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How can people transport pathogens

• By transporting plants and plant parts– Crops, and seeds– Raw food– Ornamental plantsUntreated lumberSoilInsects vectoring fungiMilitary activity

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Invasion of an exotic root pathogen

of forest trees:

the case of Heterobasidion annosum

P. Gonthier1, R. Linzer2, G. Nicolotti1 & M. Garbelotto2

1 Di.Va.P.R.A., University of Torino, Italy2 E.S.P.M., University of California at Berkeley, USA

Eighth International Mycological Congress, Cairns, Australia, 20-25 August 2006

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The Heterobasidion annosum (Fr.) Bref.species complex

Presenter
Presentation Notes
These are my current projects.
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Italian Stone Pine (Pinus pinea L.) mortality centers in Castelporziano (Rome)

2002

Presenter
Presentation Notes
These are my current projects.
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Basidiomata of Heterobasidion sp. onpine stumps within Castelporziano’s

pine mortality centers

2002

Presenter
Presentation Notes
These are my current projects.
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H. insulare

0.1

H. insulare98307P12p 00 070 102 023 102 030 502 031 1203005203006791200 1 295092B13 4Cal1Cal2E14 2E18 11 3E3 1L1bL58 1T5 98297 B20 1 00 071 100 073 2810928 1 1417PB3 2211063B11115A1116 112023B 21A24086C323 365427 4 2 193199321 980019801298027 980349804098042Conk3 REU120cl3cl5cl62 1 398018 344 6390390 5BBbBBha2sda5sdc1sdc3sdc4sdc6sdc7sd 305 4310 7340 3354 1382 5327 5398 2 98008351 1 9801594190932094189980029800598028

98035 9800398029980069804198007 9801198016980179803698038cp0cp15cp18cp2cp7 cp3cp9Conk1stop1 10101041365F181 433230 3 BBe

1.0

1.0

1.0

1.0

1.0

1.01.0

1.0

1.01.0

1.0

1.01.0

1.0

1.0

1.0

1.0

0.51

0.51

0.520.68

0.50

0.50

0.59

0.88 0.99

0.50 0.67 0.86

0.51

H. abietinumH. parviporumH. annosum WNA S ISG

H. annosum ENA P ISG

H. annosum WNA P ISG

H. annosum ENA P ISG

H. annosum sensu stricto

Phylogram of Bayesian analysis of partitioned, multilocus dataset: GPD, EFA and ATP.

Gonthier et al., 2004Warner et al., 2005Linzer et al., in prep.

How it was discovered that the Castelporziano’s Heterobasidion population was exotic

Presenter
Presentation Notes
These are my current projects.
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The Estate of Castelporziano has been closed to thepublic since 1562, and…is comprised of an exclusively native Italian flora (Maneset al., 1997)

How was Heterobasidion introduced from Eastern North America?

June 5th - July 10th, 1944

training and resting camp

337th Regiment Review Castelporziano

Presenter
Presentation Notes
These are my current projects.
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20 km

Heterobasidion free

wood disks (%)

with EU Heterobasidion spores with NA Heterobasidion spores with both EU and NA Heterobasidion spores

Current distribution of the exotic pathogen

Presenter
Presentation Notes
These are my current projects.
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Why exotic outcompetes native

• It is equally pathogenic (can’t always blame lack of coevolution)

• It produces a lot more spores (transmission)

• It is a better saprobe (establishment)• It can colonize oak stands

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Hybridization: why care?

• Hybrid pathogens can change hosts• Hybridization allows for gene

introgression and can increase virulence

• We have documented that about 17% of alleles are completely new due to recombination: what will these alleles be able to do