Latin name

  • Rhododendron ponticum

What’s the problem?

  • A killer of the countryside.
  • Outcompetes native plants and destroys habitats.
  • Invasive, spreading quickly across unmanaged landscapes.
  • Loss of native wildlife.
  • Rapidity of spread.
  • Poisonous.
  • Difficult to kill.
  • Congregates in inaccessible areas making control challenging.
  • Large root system.
  • Difficult to eradicate due to its large root system and extensive seed bank – may take years.
  • Unpalatable to herbivores.

What are the legal implications?

  • There are currently no legal obligations to deal with this species

In Detail


Rhododendron ponticum is a large evergreen shrub or small tree introduced to Britain in the 18th century. It is a very attractive dark green leaved shrub with showy trusses of flowers. In its native habit, it grows as an understory plant in mixed forest or as a dwarfed form above the snowline. The plant is now found as a native in two distinct zones: one extremely extensive – Eastern Europe (SE Bulgaria and NW Turkey) eastwards to beyond the Black Sea to Transcaucasia, and south to North Anatolia (hence its specific epithet ponticum, from Pontos); and a second, smaller area – the Iberian peninsula. These two zones are the surviving parts of a much larger range in western Eurasia in the Tertiary period; the fossil record shows it to have existed in Central Europe and as far north as Ireland even more recently, in one of the interglacial periods. Some authorities see the Iberian population as a distinct subspecies, subsp. baeticum, distinguished from the species by invariably having a densely short-hairy stem to the inflorescence.

Often viewed now as an escaped garden ornamental, it was also in earlier periods extensively planted as game covert and was also used as the rootstock onto which many later Rhododendron hybrids were grafted. All of these means of introduction into the wild mean that it has taken hold in many areas of Britain, and particularly forms expansive thickets in the milder areas. It has also hybridised with several other species, for example R. maximum and R. catawbiense.

Biology and ecology

The plant produces large quantities of viable seed – one source estimates that each inflorescence can be responsible for the production of from 3 – 7000 seeds, which can persist to make an enormous seed bank in the soil. It can also propagate itself by vegetative means, both by suckering from rootstocks and, more importantly, by layering, wherever branches touch the ground.

It can make dense stands within which light levels will not be sufficient for other plants to flourish; due to the presence of ‘free’ phenols and diterpenes (grayonoterpenes), the plant is unpalatable or possibly even toxic to mammals and probably invertebrates; these chemicals are present in the leaves, flowers and nectar. Phenols are most concentrated in the young emergent leaves and buds.

Seeds can be transported by:

  • Wind;
  • Movement of contaminated soil;
  • Poor management strategies.

The seed can remain dormant in the soil for several years and will germinate when conditions are favourable.


  • Evergreen shrub or small tree up to 8m tall.
  • Long oval shaped leaves, 10 – 20cm long, dark green above, paler and hairless beneath with a leaf stem 1 – -3cm long.
  • At the end of the branchlets with up to 15 flowers on a stalk opening in late spring.
  • It has flowers which appear around May – June. Calyx very small, with 5 blunt teeth c.25 mm long; corolla bell-shaped, c. 5cm wide, 3.5 – 5cm long, lilac, often with a pinkish or purplish tinge, and with green-yellow spots in throat; individual flower stalks c. 2 – 4cm long, hairless or slightly glandular-hairy; 10 stamens, filaments hairy at base, ovary and style hairless.

Control methods

Prior to any works commencing a bespoke management plan should be constructed in order to ensure that the correct works are undertaken.

Physical clearance

This involves physically clearing all the plants from the designated plants by hand or with machinery. The strategy is often dependent on the topography, with the plants being often found on craggy areas inaccessible to heavy machinery an element of intense labour is often required.

All plants should be cleared down to ground level, stumps appropriately treated, debris chipped or burnt and small growth chemically treated.

Typically methods of clearance are via chainsaws and forestry mulchers although larger forestry machinery can be used in certain situations should the tree density allow it.

Stumps can often be winched out of the ground to remove the most viable sections of the plants root system however this can present issues to man and animals. An on-going monitoring and chemical treatment regime or hand pulling should then be implemented for a number of years until both the seed bank and root system are depleted.

Chemical control

It is feasible on some sites to implement a chemical control programme to achieve eradication of this species. Herbicides are applied to all plants below 1.3m in height via knapsack sprayers, all plants above this are injected with herbicide at specific points. When undertaking injection works some element of hand clearance will obviously be necessary to create access to the relevant sections of the plants.

The treatment programme should be regularly reviewed to ensure that the herbicides are been applied at the correct growth stage and in the correct manner. Any amendments can then be easily made to suit the sites specific needs.

Eradication can take a number of years to be achieved depending on the size of the seed bank and root system.

If you have concerns over Rhododendron on your land, if you are unsure of your legal responsibilities, or, if you would like a quotation for control, please contact one of our specialist surveyors. Treatment costs start from £380.00 + VAT.