robinia_pseudoacacia (9)

Robinia pseudoacacia

Tree with bipinnate leaves, deciduous, with robust spines and white flashy flowers.

Scientific name: Robinia pseudoacacia L.

Common names: black locust, false acacia, locust tree, yellow locust

Family: Fabaceae (Leguminosae)

Status in Portugal: invasive species (listed in the annex I of Decreto-Lei n° 565/99, of 21 December)

Risk Assessment score: (in development)

Synonymy: Robinia pringlei Rose, Robinia pseudacacia L., Robinia pseudoacacia var. rectissima (L.) Raber, Robinia pseudoacacia L. var. rectissima Raber

Last update: 01/07/2014

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How to recognise it

Tree of up to 25 m; fissured rhytidome forming lozenges.

Leaves: deciduous, odd-pinnate, with 3-11 pairs of elliptic or ovate leaflets, with 15-60 x 4,5-30 mm, glabrous, with an apex generally retuse (less times, acute) and mucronate; robust spiny stipules.

Flowers: white, flashy, arranged in pendulous racemes.

Fruits: pods of 3-12 x 1-1,5 cm, flat, slightly constricted between the seeds.

Flowering: April to June.

 

Similar species

Gleditsia triacanthos L. honey locust) also has robust spines, but they are divided in three parts, have smaller leaflets and much larger pods (up to 40 cm). Sophora japonica L. (pagoda tree) has similar leaves, but doesn’t have spiny stipules, the leaflets have an acute apex and the pod is strongly constricted between the seeds. Amorpha fruticosa L. (indigobush) has similar leaves but is a shrub, has purple flowers and much smaller pods.

 

Characteristics that aid invasion

It propagates vegetatively, sprouting vigorously from the stump and root. Damaged trees regenerate vigorously from the stump.

Though it produces many seeds, most of them do not germinate.

 

Native distribution area

Central and Eastern North America.

 

Distribution in Portugal

Mainland Portugal (Minho, Trás-os-Montes, Douro Litoral, Beira Alta, Beira Baixa, Beira Litoral, Estremadura, Ribatejo, Alto Alentejo, Algarve).

Geographic areas where there are records of Robinia pseudoacacia

Other places where the species is invasive

Europe (Spain, France, Greece, Hungary, Germany, Holland, United Kingdom, Cypress), Asia (Israel, turkey), South Africa, North America (Canada, Mexico, USA), South America (Argentina), Australia, New Zealand.

 

Introduction reasons

For ornamental, medicinal and forest reasons, as well as to stabilize soils.

 

Preferential invasion environments

Roadsides and banks of watercourses, disturbed areas. It appears in the understory of arboreal vegetation, even though it prefers a sunny location.

It develops in all types of soils but it prefers the light, fresh, sandy and dry soils.

 

Impacts on ecossystems

It may form monospecific dense populations (sometimes they form a large clone connected by the root system) inhibiting the development of species that need sun.

It produces a lot of nitrogen-rich litter, which promotes soil change.

In some regions the flagrant flowers of Robinia pseudoacacia compete with other native species by the pollinators.

 

Economic impacts

Expensive control methodologies.

 

Natura 2000 network habitats more subject to impacts

– Alluvial forests with Alnus glutinosa (Alno-Padion, Alnion incanae, Salicion albae) (91E0);
– Riparian mixed forests of Quercus robur, Ulmus minor and Fraxinus angustifolia, along the great rivers (91F0);
Salix alba and Populus alba galleries (92A0);
– Galicio-Portuguese oak woods with Quercus robur and Quercus pyrenaica (9230);
Quercus faginea and Quercus canariensis Iberian woods (9240).

 

 

Controlling an invasive species demands a well-planned management, which includes the determination of the invaded area, identifying the causes of invasion, assessing the impacts, defining the intervention priorities, selecting the adequate control methodologies and their application. Afterwards it is fundamental to monitor the efficiency of the methodologies and recuperation of the intervened area as to perform, whenever necessary, the follow-up control.

The control methodologies used for Robinia pseudoacacia include:

 

Physical control

Hand pulling: preferential methodologyfor seedlings and small plants. When in more compacted substrates, hand pulling must be made during the rainy season as to facilitate the removal of the root system. It should be guaranteed that no main roots are left in the ground.

 

Physical + chemical control

Cut stump method: applied to adult plants. Cut the trunk as close to the ground as possible and immediately (in the following seconds) apply herbicide (active substance: glyphosate) to the cut stump. If shoots should latter on appear, these should be immediately eliminated through cutting, pulling or foliar application of herbicide (active substance: glyphosate); up to 25 to 50 cm high. Shoots of larger dimensions (from 2-3 cm diameter) may ring-barked off or else should be repeated the initial methodology (cut stump method).

 

Chemical control

Stem injection : preferential methodology for plants with a diameter larger than 5 cm. Apply the herbicide directly on the vascular system by making several cuts (with an axe or saw), at the height most convenient to the operator, in an angle of 45º until the sapwood, and immediately inject (in the following seconds) the herbicide (active substance: glyphosate or triclopyr) in each incision with a squirt bottle. Apply around 1ml (0,5 to 2ml, according to the size of the cut) of herbicide in each incision.

The several cuts should be made at the same height on the trunk as to nearly touch, leaving around 2-4 cm of uncut bark between them. For smaller individuals, only 2 or 3 cuts are necessary and they shouldn’t be deep (to prevent the plant breaking).

Foliar application of herbicide: over recent sprouts (25-50 cm tall) or when high germination rates occur. Spray with herbicide (active substance: glyphosate) limiting as much as possible its application to the target species.

Basal bark method: applied to seedlings up to 15 cm diameter. The herbicide application (active substance: glyphosate or triclopyr) should be made at a height of 30 cm. For larger plants, the herbicide application should be preceded by ring-barking.

 

Visit the webpage How to Control for additional and more detailed information about the correct application of these methodologies.

CABI (2012) Robinia pseudoacacia. In: Invasive Species Compendium. CAB International, Wallingford, UK. Available: http://www.cabi.org/isc/ [Retrieved 06/11/2012].

Dana ED, Sanz-Elorza M, Vivas S, Sobrino E (2005) Especies vegetales invasoras en Andalucía. Consejería de Medio Ambiente, Junta de Andalucía, Sevilla, 233pp.

Dufour-Dror J-M (2012) Alien invasive plants in Israel. The Middle East Nature Conservation Promotion Association, Ahva, Jerusalem, 213pp.

Global Invasive Species Database (2005) Robinia pseudoacacia. Available: http://www.issg.org/database/species/ecology.asp?si=572&fr=1&sts=sss [Retrieved 16/11/2012].

Hunter J (2000) Robinia pseudoacacia. In: Bossard CC, Randall JM, Hoshovsky MC Invasive Plants of California’s Wildlands. University of California Press, Berkeley, CA.  pp. 182-187.

Marchante E, Freitas H, Marchante H (2008) Guia prático para a identificação de plantas invasoras de Portugal Continental. Imprensa da Universidade de Coimbra, Coimbra, 183pp.

Wieseler S (2005) Black locust – Robinia pseudoacacia L. In: Plant Conservation Alliance’s Alien Plant Working Group. Weeds gone Wild: Alien Plant Invader of Natural Areas. Available: http://www.nps.gov/plants/alien/fact/rops1.htm [Retrieved 06/11/2012].

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