Country: New Guinea
Administrative region: Papua (Province)
Central co-ordinates: 1.37684 S, 133.92578 E
Area: 67.4km²
A(i)Site contains one or more globally threatened species, A(iii)Site contains one or more highly restricted endemic species that are potentially threatened
The Anggi Lakes has over 60 endemic plant species found nowhere else in New Guinea. The site contains the known global population of all of these species, which qualifies the site as a TIPA under Criterion A(iii). Some of these endemic species have completed global Red List assessments, of which 6 are Critically Endangered, 6 are Endangered, 5 are Vulnerable. The presence of these globally threatened species qualifies the Anggi Lakes under Criterion A(i). The botanical richness of the Anggi Lakes as compared to the rest of New Guinea has not been explored, but Vollering et al. (2017) defined it as a separate biogeographical region for orchids. Indonesian New Guinea is very poorly collected, so the high number of endemic and threatened species at the Anggi Lakes may be an artefact of it being comparatively well botanically surveyed. The socially, economically and culturally valuable plant species have not yet been surveyed at this site.
The Anggi Lakes is a pair of large freshwater montane lakes in the north-west of New Guinea within Indonesia’s West Papua province. Each lake is about 8km long. The site is about 50km south of Manokwari and 35km inland from the coast with the Arfak mountains to the north. The elevation is between 1880–2400 metres asl. This hotspot of plant diversity within the Bird's Head region is also one of the best collected sites (Cámara-Leret et al. 2020). However, it was found to be a separate phytogeographical region for orchids (Vollering et al. 2017). The Anggi Lakes themselves are an important freshwater habitat, and are inhabited by people from Arfak, Hatam, and Sougb language groups who use the majority of the lowlands close to the lakes for subsistence agriculture. The area is impacted by repeated burning for subsistence agriculture, the construction of roads and an increasing human population as a result of the creation of the new Pegunungan Arfak Regency.
The site is of high botanical importance as there are at least 60 vascular plant species which are so far only known from the Anggi Lakes. Of these endemic species which have been assessed so far (19 in total), 13 are considered threatened species: 5 Vulnerable, 6 Endangered, 6 Critically Endangered, with a further 6 assessed as Data Deficient. Among the habitats of particular conservation importance present at the Anggi Lakes are: Lower montane forest, Ericaceae-dominated montane shrubbery with Rhododendron, and mossy high elevation shrubbery with Hydnophytum.
The Anggi Lakes lies within the Vogelkop montane forests ecoregion and has a tropical moist montane climate. The elevation ranges from about 1880 metres asl at the lake surface to the highest peak Mount Gwamongga in the south-west which is c.2600 metres asl. The two lakes have differing hydrology and are separated by a mountainous ridge. Anggi Giji has darker water and brown sandy soils, deriving from low-grade metamorphic rocks including shale. Anggi Gida has lighter water and white sandy soils, deriving from high grade metamorphic rocks (quartzite) and granite to the south-east of the lake. The largest river in the area enters Anggi Giji at Irai.
The habitats present in the Anggi Lakes are are: Seasonally fluctuating lake edge: grassland, reedbeds; Lower montane forest; Swamp with Poaceae and Cyperaceae; Dodonea secondary shrubbery; Ericaceous-dominated shrubbery; Mixed montane shrubbery; Regularly burnt areas dominated by Pteridium aquilinum, Baekea frutescens and Poaceae.
The lowlands surrounding the lakes have mostly been cleared for agriculture and settlements. Both lakes are surrounded by roads which have expanded and improved since 2019, making the area more accessible to vehicles. Anggi Giji has a denser human population, and therefore more settlements and roads. The town of Irai is expanding as the capital of the new Pegunungan Arfak Regency. Anggi Gida has a lower human population and therefore more intact habitat.
The main threats to the habitats in the area are fires linked to agricultural activities and habitat conversion for settlements and new roads. The forest loss around Anggi Giji and the ridge between the two lakes is visible on recent satellite imagery. There forest loss around both lakes that have been ongoing since 2001 according to Global Forest Watch data, but this is higher around the more populated Anggi Giji. Some of these bare slopes may have been deforested before the satellite era, and fires were recorded by some of the early 20th century botanical expeditions. The area is vulnerable to the regional-level threats of climate-change-linked increasing instances of fire and drought. In normal years fires lit in grassland seldom penetrate further than forest edges, but in drought periods fires can be extensive (Hope 2014). Repeatedly burnt areas Anggi is within the ranges of two threatened mammals, the Arfak Ringtail possum (VU) and Ursine Tree Kangaroo (VU) but it is unknown if they occur in the area. The lakes are important for wetland birds, and there are several endemic to northwest New Guinea with a range including the Anggi Lakes: Grey-banded mannikin, Arfak Honeyeater, Arfak Astrapia. A lizard endemic to Anggi (Lobulia vogelkopensis, a single specimen known) was described by Slavenko et al. in 2022. Insects are very undersurveyed and there is likely to be a very high diversity e.g. 8 new Lycanidae (beetles) species and 1 new genus as yet unpublished found in recent surveys.
Major ecosystem services are food and fresh water provisioning, and habitats for species. The area is also used for recreation and tourism.
Laura Jennings, Royal Botanic Garden Kew
Liam Trethowan, Royal Botanic Gardens, Kew
Wendy Mustaqim, Universitas Samudra, Aceh
Tim Utteridge, Royal Botanic Gardens, Kew
Charlie D. Heatubun, The Provincial Government of West Papua and Universitas Papua
Jimmy Wanma, State University of Papua
Species | Qualifying sub-criterion | ≥ 1% of global population | ≥ 5% of national population | 1 of 5 best sites nationally | Entire global population | Socio-economically important | Abundance at site |
---|---|---|---|---|---|---|---|
Alsophila arfakensis A.Gepp | A(iii) | Unknown | |||||
Alsophila indiscriminata Lehnert | A(iii) | Unknown | |||||
Gaultheria berberidifolia Sleumer | A(iii) | Unknown | |||||
Rhododendron laetum J.J.Sm. | A(iii) | Frequent | |||||
Vaccinium dictyoneuron Sleumer | A(i) | Unknown | |||||
Vaccinium gjellerupii J.J.Sm. | A(i), A(iii) | Unknown | |||||
Vaccinium ligustrifolium J.J.Sm. | A(i) | Unknown | |||||
Vaccinium roseiflorum J.J.Sm. | A(i) | Unknown | |||||
Vaccinium tubiflorum J.J.Sm. | A(i), A(iii) | Unknown | |||||
Polyosma trimeniifolia Kaneh. & Hatus. | A(i) | Unknown | |||||
Agalmyla angiensis (Kaneh. & Hatus.) Hilliard & B.L.Burtt | A(iii) | Unknown | |||||
Agalmyla hirta Hilliard & B.L.Burtt | A(iii) | Unknown | |||||
Cryptocarya sericeo-triplinervia Kosterm. | A(i) | Unknown | |||||
Endiandra albiramea Kosterm. | A(i) | Unknown | |||||
Medinilla ferruginescens Ohwi | A(i) | Unknown | |||||
Poikilogyne mucronato-serrulata Ohwi | A(iii) | Unknown | |||||
Xanthomyrtus grandiflora A.J.Scott | A(i) | Unknown | |||||
Xanthomyrtus oreophila A.J.Scott | A(i) | Unknown | |||||
Aglossorrhyncha fruticicola J.J.Sm. | A(iii) | Unknown | |||||
Bulbophyllum adolinae Schuit., Wanma, Mambor & Heatubun | A(iii) | Unknown | |||||
Bulbophyllum triclavigerum J.J.Sm. | A(iii) | Unknown | |||||
Ceratostylis angiensis J.J.Sm. | A(iii) | Unknown | |||||
Crepidium grandiflorum (J.J.Sm.) Szlach. | A(iii) | Unknown | |||||
Crepidium productum (J.J.Sm.) Szlach. | A(iii) | Unknown | |||||
Cryptostylis arfakensis J.J.Sm. | A(iii) | Unknown | |||||
Dendrobium glaucoviride J.J.Sm. | A(iii) | Unknown | |||||
Dendrobium infractum J.J.Sm. | A(iii) | Unknown | |||||
Dendrobium papuanum J.J.Sm. | A(iii) | Unknown | |||||
Dendrobium riparium J.J.Sm. | A(iii) | Unknown | |||||
Glomera angiensis J.J.Sm. | A(iii) | Unknown | |||||
Glomera similis J.J.Sm. | A(iii) | Unknown | |||||
Goodyera gibbsiae J.J.Sm. | A(iii) | Unknown | |||||
Liparis gibbsiae J.J.Sm. | A(iii) | Unknown | |||||
Liparis lacus J.J.Sm. | A(iii) | Unknown | |||||
Mediocalcar bulbophylloides J.J.Sm. | A(i) | Unknown | |||||
Octarrhena cylindrica J.J.Sm. | A(iii) | Unknown | |||||
Phreatia densissima J.J.Sm. | A(iii) | Unknown | |||||
Platanthera klossii (Ridl.) Efimov | A(iii) | Unknown | |||||
Stigmatodactylus gibbsiae (Kores) P.Kores | A(iii) | Unknown | |||||
Phyllanthus poli-borealis Airy Shaw | A(iii) | Unknown | |||||
Pittosporum anggiense D.M.Hicks & Utteridge | A(iii) | Unknown | |||||
Embelia arfakensis Kaneh. & Hatus. | A(iii) | Unknown | |||||
Maesa fruticosa Gibbs | A(iii) | Unknown | |||||
Myrsine arfakensis (Kaneh. & Hatus.) Pipoly | A(iii) | Unknown | |||||
Helicia fragilis Foreman | A(iii) | Unknown | |||||
Hydnophytum caminiferum Wistuba, U.Zimm., Gronem. & Marwinski | A(iii) | Unknown | |||||
Acronychia glauca T.G.Hartley | A(iii) | Unknown | |||||
Pleioluma lanatifolia (P.Royen) Swenson | A(iii) | Unknown | |||||
Solanum gibbsiae J.R.Drumm. | A(iii) | Unknown | |||||
Riedelia exalata Valeton | A(iii) | Unknown | |||||
Heptapleurum arfakense (Gibbs) Lowry & G.M.Plunkett | A(iii) | Unknown | |||||
Dendromyza dendromyzoides (Stauffer) Byng & Christenh. | A(i), A(iii) | Unknown | |||||
Acronychia arfakensis Gibbs | A(i), A(iii) | Unknown | |||||
Kibara oligocarpella (Kaneh. & Hatus.) Philipson | A(i), A(iii) | Unknown | |||||
Vaccinium angiense Kaneh. & Hatus. | A(iii) | Unknown | |||||
Neolitsea arfakensis Kaneh. & Hatus. | A(i), A(iii) | Unknown | |||||
Helicia celata Foreman | A(iii) | Unknown | |||||
Plesioneuron angiense Holttum | A(iii) | Unknown | |||||
Rhododendron bullifolium Sleumer | A(iii) | Unknown | |||||
Rhododendron asperrimum Sleumer | A(iii) | Unknown | |||||
Saurauia angica Kaneh. & Hatus. | A(iii) | Unknown | |||||
Heptapleurum angiense (Gibbs) Lowry & G.M.Plunkett | A(i) | Unknown | |||||
Rhododendron bullifolium Sleumer | A(iii) | Unknown | |||||
Dimorphanthera thibaudifolia Sleumer | A(iii) | Unknown | |||||
Trochocarpa arfakensis (Kaneh. & Hatus.) Sleumer | A(iii) | Unknown | |||||
Trigonotis ciliolata I.M.Johnst. | A(iii) | Unknown | |||||
Astronidium subvaginatum Ohwi | A(iii) | Unknown | |||||
Freycinetia pseudopetiolata A.P.Keim, Kuswata & W.Sujarwo | A(iii) | Unknown | |||||
Freycinetia wiharjae A.P.Keim, Witono & W.Sujarwo | A(iii) | Unknown |
Alsophila arfakensis A.Gepp
Alsophila indiscriminata Lehnert
Gaultheria berberidifolia Sleumer
Rhododendron laetum J.J.Sm.
Vaccinium dictyoneuron Sleumer
Vaccinium gjellerupii J.J.Sm.
Vaccinium ligustrifolium J.J.Sm.
Vaccinium roseiflorum J.J.Sm.
Vaccinium tubiflorum J.J.Sm.
Polyosma trimeniifolia Kaneh. & Hatus.
Agalmyla angiensis (Kaneh. & Hatus.) Hilliard & B.L.Burtt
Agalmyla hirta Hilliard & B.L.Burtt
Cryptocarya sericeo-triplinervia Kosterm.
Endiandra albiramea Kosterm.
Medinilla ferruginescens Ohwi
Poikilogyne mucronato-serrulata Ohwi
Xanthomyrtus grandiflora A.J.Scott
Xanthomyrtus oreophila A.J.Scott
Aglossorrhyncha fruticicola J.J.Sm.
Bulbophyllum adolinae Schuit., Wanma, Mambor & Heatubun
Bulbophyllum triclavigerum J.J.Sm.
Ceratostylis angiensis J.J.Sm.
Crepidium grandiflorum (J.J.Sm.) Szlach.
Crepidium productum (J.J.Sm.) Szlach.
Cryptostylis arfakensis J.J.Sm.
Dendrobium glaucoviride J.J.Sm.
Dendrobium infractum J.J.Sm.
Dendrobium papuanum J.J.Sm.
Dendrobium riparium J.J.Sm.
Glomera angiensis J.J.Sm.
Glomera similis J.J.Sm.
Goodyera gibbsiae J.J.Sm.
Liparis gibbsiae J.J.Sm.
Liparis lacus J.J.Sm.
Mediocalcar bulbophylloides J.J.Sm.
Octarrhena cylindrica J.J.Sm.
Phreatia densissima J.J.Sm.
Platanthera klossii (Ridl.) Efimov
Stigmatodactylus gibbsiae (Kores) P.Kores
Phyllanthus poli-borealis Airy Shaw
Pittosporum anggiense D.M.Hicks & Utteridge
Embelia arfakensis Kaneh. & Hatus.
Maesa fruticosa Gibbs
Myrsine arfakensis (Kaneh. & Hatus.) Pipoly
Helicia fragilis Foreman
Hydnophytum caminiferum Wistuba, U.Zimm., Gronem. & Marwinski
Acronychia glauca T.G.Hartley
Pleioluma lanatifolia (P.Royen) Swenson
Solanum gibbsiae J.R.Drumm.
Riedelia exalata Valeton
Heptapleurum arfakense (Gibbs) Lowry & G.M.Plunkett
Dendromyza dendromyzoides (Stauffer) Byng & Christenh.
Acronychia arfakensis Gibbs
Kibara oligocarpella (Kaneh. & Hatus.) Philipson
Vaccinium angiense Kaneh. & Hatus.
Neolitsea arfakensis Kaneh. & Hatus.
Helicia celata Foreman
Plesioneuron angiense Holttum
Rhododendron bullifolium Sleumer
Rhododendron asperrimum Sleumer
Saurauia angica Kaneh. & Hatus.
Heptapleurum angiense (Gibbs) Lowry & G.M.Plunkett
Rhododendron bullifolium Sleumer
Dimorphanthera thibaudifolia Sleumer
Trochocarpa arfakensis (Kaneh. & Hatus.) Sleumer
Trigonotis ciliolata I.M.Johnst.
Astronidium subvaginatum Ohwi
Freycinetia pseudopetiolata A.P.Keim, Kuswata & W.Sujarwo
Freycinetia wiharjae A.P.Keim, Witono & W.Sujarwo
General site habitat | Percent coverage | Importance |
---|---|---|
Forest - Subtropical/Tropical Moist Montane Forest | Major | |
Shrubland - Subtropical/Tropical High Altitude Shrubland | Major |
Forest - Subtropical/Tropical Moist Montane Forest
Shrubland - Subtropical/Tropical High Altitude Shrubland
Land use type | Percent coverage | Importance |
---|---|---|
Agriculture (arable) | Minor | |
No use | Major | |
Residential / urban development | Minor |
Agriculture (arable)
No use
Residential / urban development
Threat | Severity | Timing |
---|---|---|
Residential & commercial development - Housing & urban areas | Medium | Ongoing - increasing |
Agriculture & aquaculture - Annual & perennial non-timber crops - Shifting agriculture | Medium | Ongoing - trend unknown |
Climate change & severe weather - Droughts | Unknown | Future - inferred threat |
Natural system modifications - Fire & fire suppression - Increase in fire frequency/intensity | Medium | Ongoing - increasing |
Residential & commercial development - Housing & urban areas
Agriculture & aquaculture - Annual & perennial non-timber crops - Shifting agriculture
Climate change & severe weather - Droughts
Natural system modifications - Fire & fire suppression - Increase in fire frequency/intensity
Management type | Description | Year started | Year finished |
---|---|---|---|
No management plan in place |
No management plan in place
Global Forest Watch 2023
The Sensitivity of the High Mountain Ecosystems of New Guinea to Climatic Change and Anthropogenic Impact
Arctic, Antarctic, and Alpine Research, Vol 46, page(s) 777–786
Indonesia's major freshwater lakes: A review of current knowledge, development processes and threats
Internationale Vereinigung für Theoretische und Angewandte Limnologie: Mitteilungen, Vol 24, page(s) 115-128
Phytogeography of New Guinean orchids: patterns of species richness and turnover
Journal of Biogeography, Vol 43, page(s) 204–214
Peta Geologi Lembar Ransiki (1: 250,000) SA 53-6
Revision of the montane New Guinean skink genus Lobulia (Squamata: Scincidae), with the description of four new genera and nine new species.
Zoological Journal of the Linnean Society, Vol 195, page(s) 220-278
Laura Jennings, Liam Trethowan, Wendy Mustaqim, Tim Utteridge, Charlie D. Heatubun, Jimmy Wanma (2024) Tropical Important Plant Areas Explorer: Anggi Lakes (New Guinea). https://tipas.kew.org/site/anggi-lakes/ (Accessed on 15/09/2024)