Start a consultation

Support Tree TSAR: Sponsorship Opportunities

Berberidopsis corallina Hook.f.

Red coralplant

Suggest a Correction

Introduction

Berberidopsis corallina Hook.f., the red coralplant, is an evergreen woody climber endemic to the coastal and temperate forests of south-central and southern Chile. Long, flexible stems can climb over neighboring trees and shrubs, carrying leathery dark-green leaves with sharply toothed edges and pendulous clusters of deep scarlet flowers. The species is the most familiar horticultural member of Berberidopsidaceae, yet it is officially Endangered in its native country (Veldkamp 1984; Ministerio del Medio Ambiente de Chile 2026; Trees and Shrubs Online 2026).

Joseph Dalton Hooker named the species in 1862 from material collected in Chile by Richard Pearce, whose introduction of the plant for the Veitch nursery established its place in British horticulture. Red coralplant is now understood as the closest living relative of B. granitica, a much smaller pink-flowered shrub discovered in the Chilean Andes and described in 2024. Nuclear and chloroplast analyses support this Chilean sister pair within a genus whose third species, B. beckleri, occurs in eastern Australia (Hooker 1862; Veldkamp 1984; Menegoz et al. 2024).

The red flowers are constructed from a spiral sequence of tepals, structures that gradually change from sepal-like outer parts to petal-like inner ones. They are borne in hanging racemes, rather than the usually solitary flowers of Australian B. beckleri. Developmental studies have made this species an important example for understanding the evolutionary origin of more regular five-part flowers among core eudicots (Ronse De Craene 2004).

Horticultural and Agricultural Uses

In mild maritime gardens, red coralplant is prized for its rounded crimson flowers and evergreen foliage. It is often trained over a sheltered wall or through a large shrub, where branches can arch outward and display their hanging flowers. The Royal Horticultural Society recommends a sheltered north- or west-facing position in shade or partial shade, with fertile, acidic and freely draining soil. Although it carries an H4 hardiness rating in Britain, cold winds and exposed winter sites can damage it; the RHS also advises against heavy pruning because old plants do not always reshoot well (Royal Horticultural Society 2026; Trees and Shrubs Online 2026).

Propagation is possible from softwood cuttings, layering, or seed, where viable seed is available. These approaches have different conservation consequences: vegetative methods duplicate the source plant, whereas seedlings produced by sexual reproduction can preserve additional genetic combinations. In the wild, seed availability may be intermittent, and horticultural success should not be taken as evidence that all natural genetic variation is secure in cultivation (Veldkamp 1984; Etisham-Ul-Haq et al. 2001; Royal Horticultural Society 2026).

Known locally as michay rojo, coralillo, and voqui pilfuco, the plant is also a traditional source of flexible stems for woven handicrafts and basketry in southern Chile. This cultural use has survived alongside increasingly fragmented native forest and is therefore inseparable from careful management of wild populations (Etisham-Ul-Haq et al. 2001; Ministerio del Medio Ambiente de Chile 2026).

Conservation Concerns

Red coralplant is classified as Endangered under Chile’s national species-classification regulations. Its native populations are scattered through coastal forest systems from approximately the Maule area southward toward Los Lagos, often in shaded, damp sites near watercourses. Its principal threats are the loss and degradation of native forest, plantation expansion involving Pinus radiata and Eucalyptus species, grazing, and the isolation of small forest fragments. The national designation refers to the wild Chilean species, irrespective of its successful cultivation in overseas gardens (Ministerio del Medio Ambiente de Chile 2026; Royal Botanic Garden Edinburgh 2026).

Field surveys show both the value of searching remnant habitat and the need to avoid relying on old locality totals. Alarcón and colleagues (2007) documented 123 occurrence records spread through 65 native-forest fragments in the Biobío region, adding significantly to the previously known distribution. These were records within forest fragments, not a census establishing 123 separate biological populations. The findings demonstrate that surviving native-forest patches can retain more of this endemic vine than the historical records alone suggest.

The deeper conservation problem is genetic as well as geographic. In an analysis of sampled wild populations and British cultivated accessions, Etisham-Ul-Haq et al. (2001) attributed 54.8% of the measured genetic variation to differences among populations and found a clear separation between northern and southern Chilean material. Their British samples most closely resembled northern Chilean plants, indicating that the sampled cultivated collections did not represent the full native range. Protecting populations across both regions, documenting provenance for living collections, and incorporating geographically diverse material in ex situ conservation would therefore preserve more evolutionary diversity than multiplying a narrow set of horticultural clones. Chilean seed-bank holdings provide one complementary safeguard (Etisham-Ul-Haq et al. 2001; Royal Botanic Garden Edinburgh 2026).

Additional Information

References and Further Reading

Alarcón D, Smith-Ramírez C, Hechenleitner P, Ramírez de Arellano P, Oliva M & Pinto M (2007) Nuevas poblaciones de Berberidopsis corallina Hook.f. (Berberidopsidales: Berberidopsidaceae) en la Región del Bío Bío, Chile: Ubicación y conservación de su hábitat. Gayana Botánica 64(2): 217–231. https://revistas.udec.cl/gayana_botanica/article/download/4320/4215/8921

Etisham-Ul-Haq M, Allnutt TR, Smith-Ramírez C, Gardner MF, Armesto JJ & Newton AC (2001) Patterns of genetic variation in in and ex situ populations of the threatened Chilean vine Berberidopsis corallina, detected using RAPD markers. Annals of Botany 87: 813–821. https://doi.org/10.1006/anbo.2001.1420

Hooker JD (1862) Berberidopsis corallina. Curtis’s Botanical Magazine 88: Plate 5343.

Menegoz K, Villarroel AE & Lavandero N (2024) Phylogeny of Berberidopsidales based on nuclear and chloroplast loci, with the description of a new species of Berberidopsis endemic to Central Chile. Taxon 73: 800–817. https://doi.org/10.1002/tax.13170

Ministerio del Medio Ambiente de Chile (2026) Ficha de especie: Berberidopsis corallina Hook.f. Plataforma SIMBIO. https://simbio.mma.gob.cl/Especies/Details/11380. Accessed 17 October 2026.

Ronse De Craene LP (2004) Floral development of Berberidopsis corallina: A crucial link in the evolution of flowers in the core eudicots. Annals of Botany 94: 741–751. https://doi.org/10.1093/aob/mch199

Royal Botanic Garden Edinburgh (2026) The Endemic Plants of Chile: Berberidopsis corallina Hook.f. https://chileanendemics.rbge.org.uk/taxa/berberidopsis-corallina-hook-f. Accessed 17 October 2026.

Royal Botanic Gardens, Kew (2026) Plants of the World Online: Berberidopsis corallina Hook.f. https://powo.science.kew.org/taxon/urn:lsid:ipni.org:names:106378-1. Accessed 17 October 2026.

Royal Horticultural Society (2026) Berberidopsis corallina. RHS Plant Profile. https://www.rhs.org.uk/plants/2075/berberidopsis-corallina/details. Accessed 17 October 2026.

Trees and Shrubs Online (2026) Berberidopsis corallina Hook.f. https://www.treesandshrubsonline.org/articles/berberidopsis/berberidopsis-corallina/. Accessed 17 October 2026.

Veldkamp JF (1984) Berberidopsis (Flacourtiaceae) in Australia. Blumea 30(1): 21–29. https://repository.naturalis.nl/document/565997