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Threats to biological diversity 3: Exotic Species. Lecturer: James Reeler Material by: Sam Hopkins & Vanessa Couldridge. BCB 341: Principles of Conservation Biology. Introduction. Invasion by alien species can have a significant impact on biodiversity

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Threats to biological diversity 3 exotic species

Threats to biological diversity 3: Exotic Species

Lecturer: James Reeler

Material by: Sam Hopkins & Vanessa Couldridge

BCB 341: Principles of

Conservation Biology


  • Invasion by alien species can have a significant impact on biodiversity

  • Usually there are few predatory species/diseases for successful invaders (competitive advantage)

  • Exacerbated by habitat destruction/disturbance

  • Possibly exacerbated by climate shifts – expansion into new suitable ranges

  • Primary contemporary cause – humans

    • Deliberate (plants/animals with economic/aesthetic uses)

    • Accidental – “piggybacking” on other species

Invasion who
Invasion – who?

  • Not all species that are transported to new areas become invasive.

  • There are several characteristics of good invaders:

  • High reproductive rate (quickly build up a large population under favourable conditions)

  • Generalist species (variable diet, no strong habitat requirements)

  • Good dispersers (can rapidly spread to new areas & find suitable habitats)

Invasion where
Invasion – where?

  • Certain areas are more vulnerable to invasion

  • Disturbed areas/early succession

    • Tend to have unexploited resources/empty niches

    • Little competition

  • Remote islands with low diversity

    • Simple food webs/empty niche space

  • Remote islands/fragments with no predators

    • Often naive prey (included plants poorly adapted to herbivory

Invasion how
Invasion – how?

  • Generally follows three stages:

  • 1. Usually start with a few individuals

    • High initial likelihood of population extinction

    • Initial establishment phase – growing population, little size expansion

  • 2. Spreads from initial site and increases range (expansion phase)

  • 3. Fills all available habitat and enters saturation phase.

Case studies
Case studies

  • The following examples of invasive species have been selected for discussion:

    • Rinderpest

    • The black rat (Rattus rattus)

    • The toad/platanna – Xenopus laevis

    • Chestnut blight


  • Viral disease that affects primarily cattle (also known as cattle plague)

  • All cloven-hoofed wild and domestic are animals susceptible to the disease

  • Belongs to the genus Morbillivirus

  • Affects gastrointestinal and respiratory systems

  • Highly contagious and usually fatal; it can wipe out entire populations

  • Death occurs 6-12 days after the first symptoms

Rinderpest introduction to africa
Rinderpest: Introduction to Africa

  • Introduced to Africa from Asia in 1887

  • Disease was present in Indian cattle imported to the east coast of Africa to feed the Italian army, which was invading Ethiopia at the time

  • Quickly spread to local cattle and wildlife populations

  • From there the disease swept across eastern and southern Africa, with devastating consequences

  • Within 10 years it had reached South Africa

Rinderpest spread in africa
Rinderpest: Spread in Africa

  • This map shows the spread of the disease across the African continent

  • The fauna and flora of Africa south of the Sahara changed completely as a result

Rinderpest plague of 1890s
Rinderpest: Plague of 1890s

  • Millions of animals died, both wild and domestic

  • Reports indicate more than 90% of cattle and wildebeest were wiped out

Rinderpest devastation caused
Rinderpest: Devastation Caused

  • Wildlife killed by rinderpest included wildebeest, buffalo, giraffe, warthog, eland, kudu, and other buck species

  • Predators also suffered as their prey species disappeared; lions reportedly became man-eaters

  • Pastoralists depending on cattle for their livelihood faced severe hardship and death

  • Ox-wagon transport was brought to a standstill

  • Loss of grazers transformed the landscape

Rinderpest control
Rinderpest: Control

  • The disease was eventually brought under control through early attempts at vaccination and natural immunity among surviving animals

  • In the early 1960s a more reliable vaccine was developed and between 1962 and 1976 there was a large-scale attempt to eradicate rinderpest entirely from Africa through mass vaccination

  • This was largely successful – 15 out of 17 countries were freed of the disease

  • Outbreaks still occur from time to time, but none as severe as the original plague of the 1890s

Rinderpest recovery
Rinderpest: Recovery

  • Vaccination of cattle in the 1960s eliminated rinderpest from wildlife populations, as cattle could no longer act as a reservoir for the disease

  • Wildebeest numbers in the Serengeti increased by about six-fold over a period of 15 years; Buffalo numbers also increased dramatically

Rinderpest landscape change
Rinderpest: Landscape Change



  • This had an impact on the environment by changing grassland into woodland – an increase in grazers eliminated the fuel for fires that control tree growth. Fires are now less frequent and do not burn as hot!=/


Rinderpest and canine distemper
Rinderpest and Canine Distemper

  • Ironically, it has been suggested that eradication of rinderpest has led to an increase in canine distemper among lions

  • Lions feeding on wildebeest infected with rinderpest may have gained immunity to canine distemper, since the two viruses are very similar to each other (both Morbilliviruses)

The rat 1
The Rat1

  • The Black Rat (Rattus rattus) was originally from Asia

  • It made its way to the near East in Roman time

  • It was in Europe in the 8th century

  • From Europe it had a boat ticket to the rest of the world

  • Rats are nocturnal

  • Rats are omnivorous

  • They are good breeders

The rat and the plague 2
The Rat and the plague2

  • The rat and a number of other rodents are largely responsible for out breaks of plague through history

  • Humans as carriers of rats also participated in the spread of the disease

  • Often the rats would then infect native rodents with the disease

History of the plague
History of the Plague

  • An early example is the plague of Justinian 3

  • 544, The first great plague 4

  • 1348, Black Death 5

  • 1665, Great Plague 6

  • 1899, Plague in South Africa 7

  • Recent plague – 2005/ 2006 DRC 8,9

Other effects of rat invasion lundy puffins 10 11
Other effects of rat invasion – Lundy Puffins 10, 11

  • Lundy island is off the coast of North Devon, UK

  • Rats reached the island 200 years ago

  • Rat numbers reached 40,000

  • Extermination started in 2003

  • Puffin and Manx Shearwater numbers had declined

  • Now rats gone, hopefully bird numbers will increase

Other effects of rat invasion pacific islands 12 13
Other effects of rat invasion – Pacific Islands 12,13

  • Reached Pacific Islands in the 17th century

  • Now established on 28 groups of islands

  • Eat native snails, beetles, spiders, moths, stick insects, and fruit, eggs and young of birds

  • Largest threat to the Rarotonga flycatcher

  • Other Island birds affected

    • Sooty terns, Seychelles

    • Bonin Petrels, Hawaii

    • Galapagos dark-rumped petrels Galapagos islands

    • White tailed tropic birds Bermuda

The toad xenopus laevis 14
The Toad –Xenopus laevis 14

  • Xenopus laevis is the common platanna in Southern Africa

  • It is mainly aquatic

  • Females reach 130 mm

  • Eats insects, small fish, young and larvae of its own species or other species of frogs

  • Adults can breed more than once per season

The toad xenopus laevis 141
The Toad –Xenopus laevis 14

  • Xenopus laevis is found about the world owing to

    • Lab animals

    • Pet trade

    • Pregnancy tests

  • These animals escape and can form viable populations

  • Now found in USA, Chile, Mexico, France, Indonesia and the UK

  • These frogs are a great invader owing to

    • Good in disturbed environments

    • Has a varied diet

    • High reproductive rate

    • High salt tolerance

    • Disease resistant

    • Can move overland or through rivers and streams

The toad xenopus laevis 142
The Toad –Xenopus laevis 14

  • Xenopus laevis are a problem because they

    • Predate upon and compete with native species

    • Are toxic to predators

    • Make water turbid

The toad xenopus laevis
The Toad –Xenopus laevis

  • Seen in Southern California

  • X. laevis has been present since the 1960s

  • Preys on the Tide Water Goby

  • Preys on the Endangered Red-legged frog

  • Also managed to establish parasites that need alternate hosts 15

  • In South Wales, Xenopus were found to have a very varied diet ranging from zooplankton to bank voles to Xenopus eggs 16

The toad xenopus laevis 17
The Toad –Xenopus laevis 17

  • In South Africa X. laevis is an invasive

  • Animals are moved out of their natural range by fisherman

  • Animals make use of habitats disturbed by humans

  • Have hybridized with Xenopus gilli

Chestnut blight cryphonectria parasitica
Chestnut Blight (Cryphonectriaparasitica)

The american chestnut castanea dentata
The American Chestnut(Castanea dentata)

American chestnut range
American Chestnut: Range

  • Maine to Georgia and west to Ohio and Tennessee. (Braun, 1950)

  • Commonly made up 25% or more of mixed stands

  • Formed pure stands on many dry Appalachian ridgetops and near densely populated areas.

Map of Historical Range of Castanea dentata (Saucier, 1973)

American chestnut habitat

American Chestnut: Habitat

Redwoods of the east
“Redwoods of the East”

  • Mature chestnuts could be 600 years old and average up to five feet in diameter and 100 feet tall

  • Many specimens of 8 to 10 feet in diameter were recorded

American chestnut ecological importance
American Chestnut: Ecological Importance

  • Wildlife depended on the abundant crop of chestnuts

  • Many species of insects fed on the leaves, flowers, and nuts

American chestnut economic importance
American Chestnut: Economic Importance

  • Throughout much of the range chestnut had the most timber volume of any species

  • It was half the standing timber volume of CT

  • Was the major source of tannin for leather pro-duction (6-11 % tannin content)

  • Chestnuts

From cradle to casket

“From cradle to casket…”

From cradle to casket1
“From cradle to casket…”

  • Posts & railroad ties

  • Telephone poles (65 feet)

  • Construction

  • Fuel

  • Fine furniture & musical instruments

American chestnut economic importance1

American Chestnut: Economic Importance

  • Near densely populated areas Chestnut started when the country lost its most important hard wood species (Smith, 2000) often formed nearly complete stands

    • due to rapid growth from stump sprouts

    • repeated coppicing for fuelwood

Pure stand of chestnut in ct 90 years after clear cutting 1905
Pure stand of Chestnut in CT 90 years after clear-cutting, 1905.

  • Experts estimate that American Chestnut represented half the commercial value of all Eastern North American hardwoods

Introduction of cryphonectria parasitica
Introduction of the Eastern United States.”Cryphonectria parasitica

  • In 1904, Herman Merkel, a forester at the New York Zoological Garden, found odd cankers on American chestnut trees in the park

Introduction of cryphonectria parasitica1
Introduction of the Eastern United States.”Cryphonectria parasitica

  • "rapid & sudden death of many branches stems & trees"

Introduction of cryphonectria parasitica2
Introduction of the Eastern United States.”Cryphonectria parasitica

  • American Chestnut produces a sweet but small nut 

  • Chinese chestnut produces a large but generally tasteless nut

Introduction of cryphonectria parasitica3
Introduction of the Eastern United States.”Cryphonectria parasitica

  • Thomas Jefferson

    • imported European or Spanish chestnut (Castanea sativa)

    • grafted it onto native root stocks at Monticello.

  • In 1876, a nurseryman in Flushing, NY, imported the Japanese chestnut (C. crenata).

    • More were brought over in 1882 and 1886.

  • Chinese chestnut (C. Molissima) was brought across from Ichang in 1900.

    • to hybridize for ornamentals and nut production

Cryphonectria parasitica
Cryphonectria parasitica the Eastern United States.”

  • Ascomycete

  • Produces both conidia & ascospores

  • Pycnidia stromata break through the lenticels and produce conidia and perithecia producing ascospores are formed

Cryphonectria parasitica life cycle
Cryphonectria parasitica the Eastern United States.”: Life Cycle


  • Animals and insects the Eastern United States.”

  • Ascospores are shot into the air after rain storms in the fall

  • Rain (conidia)


active growth & sporulation

How does it kill the tree
How does it kill the tree? the Eastern United States.”

  • Enters through fissures or wounds in the bark

  • Grows in and under the bark, girdling the cambium.

  • Kill the tree above the point of infection.

How does it kill the tree1
How does it kill the tree? and trunks of the chestnut trees.

  • The leaves above the point of infection die, followed by the limbs.

  • Within two to ten years the entire tree is dead.

  • Not uncommon to find many cankers on one tree

How does it kill the tree2
How does it kill the tree? and trunks of the chestnut trees.

  • The fungus has girdled the tree and is producing yellow conidia asexual spores

Host range

  • Like most cankers - fairly specific host range and trunks of the chestnut trees.

  • Serious pathogen: American & European (infects Japanese and Chinese much less)

  • Moderate pathogen: Chinquapin & Live Oak 

  • Can also be found infecting/living on numerous oak species in the US

Host Range

Rate of spread
Rate of Spread and trunks of the chestnut trees.

  • Aggressive attempts to halt the spread of the blight were made by PA and NY

    • removed chestnut over a large area to halt southward spread

  • In 1911-1913, the U.S. Congress appropriated special funds to enable foresters to study and control the blight

Rate of spread1

  • Horticulturalists, found a blight-free area in Pennsylvania and quickly imported trees to form an experiment station

    • transported the blight and created a new epicenter

    • Accelerated spread in PA

  • Cuts in funding for Chestnut blight research:

    • With the onset of World War I in 1914

    • The evident futility of control efforts

Rate of Spread

  • By 1926, fungus reported throughout native range and quickly imported trees to form an experiment station

  • By 1940, virtually all (an estimated 4 billion) were dead or infected with the blight

  • Chestnut was the dominant wood processed at PA sawmills in the early 1920s,

    • salvage logging to make use of the dead and dying trees

Cumulative impacts

Cumulative Impacts

Cumulative impacts1
Cumulative Impacts ever experienced by this nation”

  • In 1974, the Oriental Chestnut Gall Wasp (Dryocosmus kuriphilus) was brought to the US

    • Female lays eggs in chestnut vegetative buds

    • Galls suppress shoot elongation and reduce fruiting

    • Heavy infestations can kill the trees (afflicts both American and Chinese chestnuts at the southern end of their ranges)

  • Threatening complete extinction

    (Anagnostakis, 1994)

Varying outcomes europe
Varying Outcomes: Europe ever experienced by this nation”

  • The fungus was later introduced into Europe (for tree breeding) from America

  • Moved through Europe killing European Chestnut

  • However, it was observed that many trees, while infected and full of cankers, did not die

Instead of sunken diffuse cankers, surviving  ever experienced by this nation” European chestnuts had swollen cankers with evidence of "healing" along the margins.

  • Noticed that a different colored fungus was recovered from "healing cankers"

  • Instead of the typical orange colored Cryphonectria parasitica fungus, a white-colored fungus was found. 

    • White fungus was slower growing and produced fewer spores

  • When you "sprayed" the white fungus on a "killing canker" the "killing canker"  became a "healing canker" (Europe)

Varying outcomes europe1

  • Grente reported in 1965 that ‘hypovirulent’ strains from Italy did not kill chestnut trees

  • Began a program of active intervention when blight was found in France

    • blight strains with dsRNA passed hypovirulence to lethal strains

  • Treatment of new cankers as they formed resulted in a successful ‘biological therapy’ of the disease.

    • treat every canker for several years

Varying Outcomes: Europe

Varying outcomes michigan
Varying Outcomes: Michigan blight does not work as well in the US

  • Hypovirulent strains were found in the United States

    • Most notably in Michigan

  • Successful because:

    • Few mating types

    • High number of Chestnut

    • Isolated from the native range   

  • Less diversity of pathogen in MI so that hypovirulence can transfer more readily

  • The transmission of hypovirulence from strain to strain of the fungus is restricted by a genetic system of vegetative incompatibility

  • Six loci, each with two alleles in a system of heterogenic incompatibility which keep the strains of the fungus from fusing and passing hypovirulence (Huber and Milgroom)

  • Virus transfer is restricted when there are different alleles at the vegetative incompatibility loci

Current status
Current Status the fungus is restricted by a genetic system of vegetative incompatibility

  • Reduced to a short lived sprouting understory tree

  • Fungus can not survive below the ground. 

    • roots continue to live and they send up stump sprouts.   

Current status1

  • Stump sprouts grow until infected the fungus is restricted by a genetic system of vegetative incompatibility

    • the stump re-sprouts again

  • Little chance for resistance to evolve

    • sprouts typically killed before they become sexually mature

    • sexual reproduction rare

Current Status

Last remaining stand of american chestnut
Last remaining stand of American Chestnut the fungus is restricted by a genetic system of vegetative incompatibility

  • Largest living (>3 ft dbh) about 20 miles east of La Crosse, WI.

  • 10 chestnuts planted in 1885

  • Seeds propagated around 50 acres and more than 3000 trees

  • Trees were blight free due to isolation until a canker was found in 1986

  • Now over 1600 cankers are present on 530 trees.

  • Virus was introduced in 1992 – not successful

Blight control and restoration
Blight Control and Restoration the fungus is restricted by a genetic system of vegetative incompatibility

  • Approaches:

    • Hypovirulent strains

    • Asian blight resistance

    • Natural resistance

    • Forest management practices



Concluding remarks
Concluding Remarks back

  • The selected examples demostrate the damage that invasive species can do to both the natural environment and human interests.

  • For more information on invasive species see the Invasion Biology course.

References for the rat and the toad
References for the Rat and the Toad back

  • Wikipedia contributors, Black Rat, [accessed 2006 July 30] Wikipedia, The free Encyclopaedia, Available Rat

  • Gross, L. (1995). How the plague bacillus and its transmission through fleas were discovered: Reminiscences from my years at the Pasteur Institute in Paris. Proceedings of the National Academy of Science 92: 7690-7611.

  • Dols, M. (1974) Plague in Early Islamic History Journal of the American Oriental Society 94:371-383

  • Maddicott, J. R.(1997) Plague in Seventh -Century England. The past and present society

  • Davis, D. The Scarcity of rats and the black death: an ecological history, Journal of Interdisciplinary history 16: 455-470

  • Storey of the Plague,(2006) channel 4 [accessed July 30th 2006]. Found at

  • May, J. M. (1952). Map of the world distribution of plague. Geographical review 42:628-630.

  • BBC news (2005)DR Congo plague outbreak spreads [accessed July 30th 2006]

  • the world health organization (2006). Plague in the DRC. [accessed July 30th 2006]

  • Lundy shore office [accessed July 30th 2006] http://www.lundy_

  • BBC news (2005) Lundy Rats. [accessed 30th July 2006]

  • Atkinson, I. A. E and Atkinson, T. J. (2000) Land vertebrates as invasive species on islands served by the south pacific regional ENVIRONMENT PROGRAMME. In: Invasive species in the pacific: A Technical review and draft regional strategy. South Pacific regional environment program Samoa: 19-84

  • G. McCormack. (2005). The Status of Cook Island Birds 1996, Cook Island Biodiversity and natural heritage

  • Measy, J. (2004). Global Invasive species database Xenopus laevis. [accessed 30th July 2006] Found at

  • Lafferty, K. and Page, C. (1997) Predation on the endangered Tide Water Goby, Eucyclobius newberryi, by the introduced African clawed frog I, Xenopus laevis, with notes on the frogs parasites. Copeia 1997: 589-592.

  • Measey, G. J. (1998) Diet of feral Xenopus laevis (Daudin) in South Wales, UK. Jnl Zool. 246:287-298

  • Measy G. J. (2004) Xenopus laevis. In Atlas and red data book of the frogs of South Africa, Lesotho and Swaziland, eds Minter, L. et al.