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A view across the Island from the Peaks National Park with the endemic St. Helena tree fern, Dicksonia arborescens in the  foreground

Volcanic in origin, St. Helena is a tropical island situated on the mid-Atlantic Ridge in the South Atlantic Ocean. The Island is approximately 121 sq. km. in area and is composed of soft basalt rocks and consolidated pyroclastic residues, which have been heavily-eroded, leaving a land surface dominated by steep gullies and harder igneous extrusions, which form prominent ridges and rock pillars such as 'Lot' and 'Lot's Wife.' Erosion by wave action has cut-away at the coasts leaving the Island encircled by steep cliffs, reaching 200-500 m in height (except where valleys reach the sea). The highest point is Diana's Peak, at 820m it forms part of the Peaks Ridge, a narrow spine mostly above 700m in height.

St Helena's sub-tropical latitude affords it fairly constant temperatures; the average annual temperature range at sea level is 21-28ºC, this reduces by 1.3 degrees every 100 m rise in elevation. Rainfall is often extremely localised, creating desert-like conditions of the outer part of the island where 175mm of rain falls per year, compared to the Peaks where cloud and mist accumulate bringing 290 days of overcast conditions and 1050mm of rain each year.

Vegetation and Plant Species

There are circa 420 plant species present in the wild on St. Helena, of these, 45 are endemic and 15-20 are native to the island. The rest, (350 spp. or 85% of the total) are introduced species that have become naturalised. At least 8 endemic species are now thought to be extinct and all of the endemic species on the island are scarce and probably critically endangered (although, no official assessment of their status has yet been made). The vegetation of St. Helena is largely determined by the amount of rainfall, which is in turn closely linked to elevation. As a result, the vegetation differs markedly from coast to mountain top. Despite the fact that the original vegetation of the island has been heavily modified since the arrival of humans in 1502, several ecological zones can be recognized on St. Helena: The Crown Wastes provides a hostile, semi-desert environment for plant growth

Semi-desert extends around much of the coastal fringe. Originally it was dominated by a very sparse community composed of endemics such as babies' toes Hydrodea crypthantha (Aizoaceae), salad plant Hypertelis acida (Molluginaceae), St. Helena boneseed Osteospermum sanctae-helenae (Asteraceae) and St. Helena tea-plant Frankenia portulacifolia (Frankeniaceae), and other native species such as purslane Portulaca oleracea (Portulacaceae). The current endemic populations are now very scattered.

Dry scrub developed on the higher ground where rainfall was sufficient to allow denser plant communities to establish. Originally it would have been dominated by the endemic scrubwood Commidendrum rugosum (Asteraceae - a shrub with daisy-like flowers) and the dwarf St. Helena ebony Trochetiopsis melanoxylon. Scrubwood is now mainly confined to cliffs, and the dwarf ebony has been extinct for 250 years. This zone is now dominated by a community of global invasive species such as Lantana camara (Verbenaceae), wild mango Schinus terebinthifolius (Anacardiaceae), tungy Opuntia cochenilifera and O. vulgaris (Cactaceae) and aloe Furcrea foetida (Agavaceae).

Condensation from early morning clouds are an important source of moisture for St. Helena's upland habitats

Above the scrub zone, a more luxuriant dry forest would have originally covered large areas of the mid-altitude zone and been heavily dominated by the endemic gumwood Commidendrum robustum, but also including the St. Helena ebony Trochetiopsis ebenus (Sterculiaceae) and bastard gumwood Commidenrum rotundifolium. Very few natural gumwoods remain, only a single mature bastard gumwood, and the ebony was thought to be extinct in the late 1800s until a group of 5 plants were rediscovered in 1980. Despite limited self-compatibility, the ebony has now been successfully reintroduced to a number of sites. However, this zone is now dominated by a mix of wild mango, spoor Pittosporum viridiflorum (Pittosporaceae), black olive Olea europaea ssp. africana (Oleaceae) and Bermudan cedar Juniperus bermudiana (Cupressaceae).

An emergent Black Cabbage tree, Melanodendron integrifolium, in the Peaks National Park

Moist forest, dominated by gumwood (including the false gumwood, C. spurium), had once covered the upper ridges. An understory of ferns, such as black scale fern Diplazium filamentosum (Woodsiaceae) and other upland species such as the St. Helena redwood Trochetiopsis erythroxylon form the understory. This habitat has all but disappeared apart from a single relict stand of gumwoods. Upland forest is now predominantly composed of plantations of pine, blackwood Acacia melanoxylon or Eucalyptus, although naturalized areas of Cape yew Podocarpus elongata and thorn - inkbush (Erythrina caffra- Cestrum laevigatum) woodland are also important.

The 'cloud forest', which would originally have occupied most of the highest ridges on the island, still persists but is restricted to a small area of the central ridge and a relict fragment further west, at High Peak. The community contains a moderately diverse variety of endemic species. These include four species of cabbage trees (all Astereaceae) and formerly, the now extinct stringwood Acalypha rubra (Euphorbiaceae) and St. Helena olive Nesotea eliptica (Rhamnaceae). The most exposed areas are dominated by the endemic St. Helena tree fern Dicksonia arborescens (Dicksoniaceae). A rich understory is also present, composed of herbs such as the lobelia Trimeris scaeivifolia and large bellflower Wahlenbergia linifolia (both Campanulaceae) together with circa 15 species of native and endemic ferns.

Threats to the Flora of St. Helena

Invasive species of New Zealand Flax (Phormium tenax) and Fushia xxx, taking over the natural habitat of the endemic tree fern in Peaks National Park Much of St. Helena's native flora has been devastated by and continues to endure the following problems:

  • A series of introduced grazing mammals, goats, pigs, sheep, rabbits, rats (goats and pigs have now been exterminated)

  • Habitat destruction, especially to the forests which clothed much of the inner zone and which were cut for timber and firewood

  • The introduction of large numbers of highly invasive plant species which have outcompeted the endemic flora in the outer parts of the island;

  • Invasive plant species cause major environmental, economic and social problems on St. Helena, but there is limited local botanical expertise to deal with the issues.

  • The removal of large areas of relict moist forest to make way for plantations of New Zealand flax (Phormium tenax);

  • In the early 20th century, the flax industry sustained the island's economy for over 50 years until the market for natural fibre products declined in the 1960s. The flax mills are now abandoned, but large areas of upland hillside are still covered in flax monocultures.

    Conservation

    The South Atlantic Invasive Species Project aims to increase regional capacity to manage invasive species by developing infrastructure and systems, building local capacity through research, training/public education and by funding specific eradication projects. A full survey of both the native and endemic flora of the island has recently been conducted. Data collected include: a simple abundance score for each species across each cell of the 1km Ordinance Survey grid; specific monitoring of 145 1 km transects; specific monitoring of 350 randomly selected 20m plots. Conservationists assess the St. Helena endemic Scrubwood, Commidenrum rugosum

    The information are being used to:
    provide a baseline for long term monitoring of changes in species distribution; formally assess the conservation status of St. Helena's threatened endemic and native flora; understand the ecological requirements of invasive species to inform control measures; develop ecological management advice for specific habitats; provide accessible literature on St. Helena's unique flora for use by conservation managers and the general public.

    During the survey, some 60 alien species were identified as new occurrences to the island. Some of these are threatening St. Helena's native flora and urgent steps are needed to control them before they become a serious problem. The most notable invasive species include, bridal creeper Asparagus asparagoides (Asparagaceae), African fountain grass Pennisetum setaceum (Poaceae) and Mexican creeper Maurandya erubescens (Plantaginaceae). On a more positive note, an endemic species has recently been rediscovered (2008); the neglected tuft sedge Bulbostylis neglecta (Cyperaceae) was last seen in 1806 and presumed extinct. A conservation strategy is currently in the early stages of development for this species.

    Original text by Phil Lambdon; edited by the UKOTs team
    © Copyright Board of Trustees of the Royal Botanic Gardens, Kew
    St. Helena Government
    St. Helena National Trust

    Kew's UK Overseas Territories team collaborates with the Agricultural and Natural Resources Department and with the St. Helena National Trust on plant conservation activities.


    Progress in implementing the Global Strategy for Plant Conservation Targets

  • Target 1
  • Species checklist complete
  • Target 2
  • Some endemics red listed, evaluation of remaining species and updating of earlier assessments underway
  • Target 3
  • Horticultural post secured to revitalise St. Helena's endemic plant nursery
  • Target 4
  • Co-ordinated internationally
  • Target 5
  • Baseline data collected to inform Important Plant Area (IPA) designation
  • Target 6
  • Production land limited to Longwood Farm
  • Target 7
  • Cloud forest endemics conserved within Peaks National Park; management plan complete
  • Target 8
  • Several endemics in long-term storage in the Millennium Seed Bank and many species in cultivation in St. Helena, at RBG Kew and other botanic gardens
  • Target 9
  • No activity
  • Target 10
  • A working checklist of non-native plant species complete; a draft invasive species management plan completed and initial control measures of invasive species in pasture lands underway; some bio-security measures in place
  • Target 11
  • No plant species in international trade
  • Target 12
  • No plant species in international trade
  • Target 13
  • No current indigenous use of plant products
  • Target 14
  • Regular conservation bulletins in the St. Helena Independent newspaper and on local radio stations; good awareness of St. Helena endemics amongst the general population
  • Target 15
  • OTEP-funded horticultural post in place to meet local training needs; several St. Helenians have undertaken training programmes at RBG Kew
  • Target 16
  • EU-funded South Atlantic Invasive Species Project providing a regional network for conservation initiatives and invasive species control


    Please use the links below to see further details on conservation activities in the UK Overseas Territories

    Anguilla

    Ascension Island

    Bermuda

    British Antarctic Territory

    British Indian Ocean Territory

    British Virgin Islands

    Cayman Islands

    Falkland Islands

    Gibraltar

    Montserrat

    Pitcairn Islands

    South Georgia and the South Sandwich Islands

    Sovereign Base Areas on Cyprus

    Tristan da Cunha

    Turks and Caicos Islands


    Homepage of the UKOTs Online Herbarium



    Site published by
    UK Overseas Territories Science Team, Royal Botanic Gardens Kew
    Please cite as
    UKOTs Online Herbarium (2011). Published on the internet at http://herbaria.plants.ox.ac.uk/bol/UKOT (date accessed).
    For further information
    Please contact Kew UKOTs Team


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