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Mimosa pigra
M.N. Madushan – PDN 23115
W.P.S.Madushika –PDN 23042
D.K.U.S.Deweniguru – PDN 23092
K.A.D.H.Jayatissa – PDN 23035
 Leguminous woody perennial shrub which can fix N
 Maximum 2-6 m in Height at maturity
 Bipennate leaves are sensitive and fold up once touched or nightfall
 Flower heads containing approximately 100 flowers.
 Each flower head produces a cluster of 10 to 20 seedpods
 Oblong shaped seed having hairs to float on water and stick
 Hard seed coat
Introduction to Mimosa pigra
 Native to tropical America
 Grow natively as scattered seldom plant in 2m height
 Widespread throughout the wet areas in tropics including Australia and Asia.
 One of the world's 100 worst invasive species
 Forms dense, thorny, thickets populations covering large extent once invade
 Problematic weed in Agricultural & environmental aspects
Global Context of Mimosa pigra
 First reported around Mahaweil river bank in Thennekumbura, Sri Lanka in 1997
 Entered with heavy machineries imported from Australia for Mahaweli project
 Covered a 20–25 km strip along the banks of the Mahaweli River by 2000
 Central and north-western provinces of Sri Lanka
 Abandoned paddy fields, river or stream banks and new construction sites.
Local context of Mimosa pigra
 Flowering at 12–14 weeks after planting
 The relative growth rate (RGR) increased until onset of flowers and then
decreased.
 Reproduce only by seed
 Abundant seed production (9000 seeds per square meter annually)
 Long-lived seed bank (>10 Y) in soil (23 Y in sandy soil)
 Seed viability decreases more rapidly on clay soil
 Soil seed-bank density within the canopy diameter is 2,336 to 46,410
seeds per square meter
Propagation of Mimosa pigra
 100% viable after four years of storage
at room temperature
 After sand scarification, 99% of seeds
germinated due to break of seeds
dormancy
Seed Dormancy of Mimosa pigra
Figure 1: Germination percentage of mimosa seeds
Source: Buddhi, M 2002, Distribution, biology and
management of Mimosa pigra in Sri Lanka, graph,
https://www.researchgate.net/publication/242701381
Mimosa pigra as an
Invasive Plant
First reported in Sri Lanka in early 1996
First identified Central and North-
western provinces of Sri Lanka,
Colonized along the river banks of
Mahaweli river.
Seed disperse with river sand that is used
for construction work
And with river water flow
Reproduces only by seeds
Why invasive
Non- Native Plant
A serious agricultural, environmental and
economic problem in Sri Lanka and also in many
other countries
Rapid spreading at alarming rate
Removing native vegetation and altering
the availability of water and nutrients
the height increased at a rate of 2.4-2.6 cm per
day during the first 8-12 weeks
•
Why invasive(continuous)
• Seed disperse
• with river water and river sand that is
used for construction work
• High soil seed bank density,
• within the canopy diameter of the
naturally grown mimosa plants varied
from 2,336 to 46,410 seeds per squire
meter.
• Aggressively behavior
• The plant behave aggressively, forming
dense thickets covering large extents of
land and threatening the natural
biodiversity.
Why invasive ( continuous)
• Higher seed viability
• Mimosa seeds were 100%
viable after four year of
storage at room temperature
28oC and also at 8oC after
sand scarification
• and can stay at least 23 years
in sand soil.
• A perennial scattered plant
or small tree
• may grow to a height of
about 4 -6m deep root
system
Why invasive
(continuous)
 Propagate by seeds
 produce seeds
throughout the
year
 containing 8-20
seeds per pod
Environmental Damage of
Mimosa pigra
Impact on Plants
Compete with native herbaceous plants.
Allelopathic activity that influences the
germination and growth of some plant
species.
Prevent establishment of other species.
Impact on Plants Cont.
It also provides cover for of rats and crabs which
damage crops.
Mimosa is able to outcompete young palm trees
in immature oil palm plantations and cause a
decrease in the production of palm oil.
Eliminate most other species of grasses and
forbs converting floodplains into unproductive
scrubland.
Impact on Animals
Disturb wildlife movements and their water availability from the water
front.
E.g. Population of large water birds in the M. Pigra infestation areas of
the bueng boraphet wetland in Thailand was reduced by
27% in 2003
2014 with the highest decline of 56% in ducks.
(Haq R.U., Eiam-Ampai K., Ngoprasert D., Sasaki N., Shrestha R.P.
Changing landscapes and declining populations of resident waterbirds)
Aquatic infestation (Photo: Land Protection, QDNRW)
Impact of Animals cont..
Reduce the available drinking water for cattle.
The fishing production in the river near the
floodplains was decreased in Africa.
Decrease available grazing areas for
herbivores and related carnivores including
birds and lizards.
.
Mimosa displacing floodplain grassland of Tram Chim ,
Vietnam
Spread of mimosa along the Malinde Channel of the Kafue Flats, Zambia (G.
Howard)
Impact on Humans.
M.pigra can block roads and pathways which can limit
accessibility to crop lands.
Disturbing farming livelihoods.
E.g. Average famers spend 11 days per ha annually to
clear the species in their farmlands in the Mekong River
floodplains in Cambodia.
Disturbs the day-to-day human recreational activities and
tourism opportunities that are dependent on accessible
water bodies.
Control of
Mimosa pigra
• Glyphosate AI 1.44 kg / Ha
effectively controlled
mimosa seedlings less than
six months old,
• Need to apply three times
at four-month intervals on
the same set of seedlings.
3.Burning
High temperature that can be killed
some proportion of seed
4.Agronomic methods
Younger stage of mimosa pigra with
use of panicum maximum the seeds
of mimosa are not germinated
5.Biological control agents
Introduce insects which can be
controlled seeds, flower, stem, root
6. Policy recommendation
short and long-term solution
7. Integrated management
Biological control agents with
herbicide
8. Prevention
Map infestation before
commencing control to enable
the development of a
coordinated management
strategy
References
Heard, T.A.; Paynter, Q. Mimosa pigra (Leguminosae). In Biological Control of Tropical Weeds Using Arthropods;
Cambridge University Press: Cambridge, UK, 2009; pp. 256–273. [Google Scholar
Barneby, R.C. Sensitivae censitae: A description of the genus Mimosa linnaeus (Mimosaceae) in the New World.
Mem. N. Y. Bot. Gard. 1991, 65, 1–835. [Google Scholar])
Walden, D.; van Dam, R.; Finlayson, M.; Storrs, M.; Lowry, J.; Kriticos, D. A risk assessment of the tropical
wetland weed Mimosa pigra in northern Australia. Superv. Sci. 2004, 177, 1–74. [Google Scholar]
Haq R.U., Eiam-Ampai K., Ngoprasert D., Sasaki N., Shrestha R.P. Changing landscapes and declining populations
of resident waterbirds:)
Beilfuss R. Adaptive Management of the Invasive Shrub Mimosa pigra at Gorongosa National Park. Department
of Scientific Services; Gorongoza, Mozanbique: 2007. pp. 1–19. [Google Scholar] [Ref list]
Witt A.B., Floyd K.S., Nunda W., Beale T., Shanungu G., Kriticos D.J. Mimosa pigra in eastern and southern Africa:
Distribution and socio-ecological impacts. Austral Ecol. 2020;45:788–799. doi: 10.1111/aec.12895. [CrossRef]
[Google Scholar] [Ref list])
Rijal S., Cochard R. Invasion of Mimosa pigra on the cultivated Mekong River floodplains near Kratie, Cambodia:
Farmers’ coping strategies, perceptions, and outlooks. Reg. Environ. Chang. 2016;16:681–693. doi:
10.1007/s10113-015-0776-3. [CrossRef] [Google Scholar] [Ref list])
(Mohamed M.S., Seman I.A. Occurrence of common weeds in immature plantings of oil palm plantations in
Malaysia. Planter. 2012;88:537–547. [Google Scholar] [Ref list])
Shanungu G.K. Management of the invasive Mimosa pigra L. in Lochinvar National Park,
Zambia. Biodiversity. 2009;10:56–60. doi: 10.1080/14888386.2009.9712844.
Marambe, Buddhi & Amarasinghe, L. & Silva, K. & Gamage, G. & Dissanayake, S. & Seneviratne, A.. (2002).
Distribution, biology and management of Mimosa pigra in Sri Lanka. Manual on Biology and Management of
Mimosa pigra.
CHAN, S., & MIHARA, M. (2018). The Impact of Mimosa pigra on Local Livelihood in the Stung Sen Core Area, Tonle
Sap Biosphere Reserve. International Journal of Environmental and Rural Development, 9(2), 128-135.
Northern Territory Government,Australia
Thank you

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Mimosa pigra invasive plant in Sri lanka

  • 1. Mimosa pigra M.N. Madushan – PDN 23115 W.P.S.Madushika –PDN 23042 D.K.U.S.Deweniguru – PDN 23092 K.A.D.H.Jayatissa – PDN 23035
  • 2.  Leguminous woody perennial shrub which can fix N  Maximum 2-6 m in Height at maturity  Bipennate leaves are sensitive and fold up once touched or nightfall  Flower heads containing approximately 100 flowers.  Each flower head produces a cluster of 10 to 20 seedpods  Oblong shaped seed having hairs to float on water and stick  Hard seed coat Introduction to Mimosa pigra
  • 3.  Native to tropical America  Grow natively as scattered seldom plant in 2m height  Widespread throughout the wet areas in tropics including Australia and Asia.  One of the world's 100 worst invasive species  Forms dense, thorny, thickets populations covering large extent once invade  Problematic weed in Agricultural & environmental aspects Global Context of Mimosa pigra
  • 4.  First reported around Mahaweil river bank in Thennekumbura, Sri Lanka in 1997  Entered with heavy machineries imported from Australia for Mahaweli project  Covered a 20–25 km strip along the banks of the Mahaweli River by 2000  Central and north-western provinces of Sri Lanka  Abandoned paddy fields, river or stream banks and new construction sites. Local context of Mimosa pigra
  • 5.  Flowering at 12–14 weeks after planting  The relative growth rate (RGR) increased until onset of flowers and then decreased.  Reproduce only by seed  Abundant seed production (9000 seeds per square meter annually)  Long-lived seed bank (>10 Y) in soil (23 Y in sandy soil)  Seed viability decreases more rapidly on clay soil  Soil seed-bank density within the canopy diameter is 2,336 to 46,410 seeds per square meter Propagation of Mimosa pigra
  • 6.  100% viable after four years of storage at room temperature  After sand scarification, 99% of seeds germinated due to break of seeds dormancy Seed Dormancy of Mimosa pigra Figure 1: Germination percentage of mimosa seeds Source: Buddhi, M 2002, Distribution, biology and management of Mimosa pigra in Sri Lanka, graph, https://www.researchgate.net/publication/242701381
  • 7. Mimosa pigra as an Invasive Plant First reported in Sri Lanka in early 1996 First identified Central and North- western provinces of Sri Lanka, Colonized along the river banks of Mahaweli river. Seed disperse with river sand that is used for construction work And with river water flow Reproduces only by seeds
  • 8. Why invasive Non- Native Plant A serious agricultural, environmental and economic problem in Sri Lanka and also in many other countries Rapid spreading at alarming rate Removing native vegetation and altering the availability of water and nutrients the height increased at a rate of 2.4-2.6 cm per day during the first 8-12 weeks •
  • 9. Why invasive(continuous) • Seed disperse • with river water and river sand that is used for construction work • High soil seed bank density, • within the canopy diameter of the naturally grown mimosa plants varied from 2,336 to 46,410 seeds per squire meter. • Aggressively behavior • The plant behave aggressively, forming dense thickets covering large extents of land and threatening the natural biodiversity.
  • 10. Why invasive ( continuous) • Higher seed viability • Mimosa seeds were 100% viable after four year of storage at room temperature 28oC and also at 8oC after sand scarification • and can stay at least 23 years in sand soil. • A perennial scattered plant or small tree • may grow to a height of about 4 -6m deep root system
  • 11. Why invasive (continuous)  Propagate by seeds  produce seeds throughout the year  containing 8-20 seeds per pod
  • 13. Impact on Plants Compete with native herbaceous plants. Allelopathic activity that influences the germination and growth of some plant species. Prevent establishment of other species.
  • 14. Impact on Plants Cont. It also provides cover for of rats and crabs which damage crops. Mimosa is able to outcompete young palm trees in immature oil palm plantations and cause a decrease in the production of palm oil. Eliminate most other species of grasses and forbs converting floodplains into unproductive scrubland.
  • 15. Impact on Animals Disturb wildlife movements and their water availability from the water front. E.g. Population of large water birds in the M. Pigra infestation areas of the bueng boraphet wetland in Thailand was reduced by 27% in 2003 2014 with the highest decline of 56% in ducks. (Haq R.U., Eiam-Ampai K., Ngoprasert D., Sasaki N., Shrestha R.P. Changing landscapes and declining populations of resident waterbirds)
  • 16. Aquatic infestation (Photo: Land Protection, QDNRW)
  • 17. Impact of Animals cont.. Reduce the available drinking water for cattle. The fishing production in the river near the floodplains was decreased in Africa. Decrease available grazing areas for herbivores and related carnivores including birds and lizards. .
  • 18. Mimosa displacing floodplain grassland of Tram Chim , Vietnam
  • 19. Spread of mimosa along the Malinde Channel of the Kafue Flats, Zambia (G. Howard)
  • 20. Impact on Humans. M.pigra can block roads and pathways which can limit accessibility to crop lands. Disturbing farming livelihoods. E.g. Average famers spend 11 days per ha annually to clear the species in their farmlands in the Mekong River floodplains in Cambodia. Disturbs the day-to-day human recreational activities and tourism opportunities that are dependent on accessible water bodies.
  • 22. • Glyphosate AI 1.44 kg / Ha effectively controlled mimosa seedlings less than six months old, • Need to apply three times at four-month intervals on the same set of seedlings.
  • 23. 3.Burning High temperature that can be killed some proportion of seed 4.Agronomic methods Younger stage of mimosa pigra with use of panicum maximum the seeds of mimosa are not germinated 5.Biological control agents Introduce insects which can be controlled seeds, flower, stem, root
  • 24. 6. Policy recommendation short and long-term solution 7. Integrated management Biological control agents with herbicide 8. Prevention Map infestation before commencing control to enable the development of a coordinated management strategy
  • 25. References Heard, T.A.; Paynter, Q. Mimosa pigra (Leguminosae). In Biological Control of Tropical Weeds Using Arthropods; Cambridge University Press: Cambridge, UK, 2009; pp. 256–273. [Google Scholar Barneby, R.C. Sensitivae censitae: A description of the genus Mimosa linnaeus (Mimosaceae) in the New World. Mem. N. Y. Bot. Gard. 1991, 65, 1–835. [Google Scholar]) Walden, D.; van Dam, R.; Finlayson, M.; Storrs, M.; Lowry, J.; Kriticos, D. A risk assessment of the tropical wetland weed Mimosa pigra in northern Australia. Superv. Sci. 2004, 177, 1–74. [Google Scholar] Haq R.U., Eiam-Ampai K., Ngoprasert D., Sasaki N., Shrestha R.P. Changing landscapes and declining populations of resident waterbirds:) Beilfuss R. Adaptive Management of the Invasive Shrub Mimosa pigra at Gorongosa National Park. Department of Scientific Services; Gorongoza, Mozanbique: 2007. pp. 1–19. [Google Scholar] [Ref list]
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