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Peat swamp forest

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Peat swamp forests are tropical moist forests where waterlogged soil prevents dead leaves and wood from fully decomposing. Over time, this creates a thick layer of acidic peat.[1] Large areas of these forests are being logged at high rates.

Satellite image of the island of Borneo on 19 August 2002, showing smoke from burning peat swamp forests

Peat swamp forests are typically surrounded by lowland rain forests on better-drained soils, and by brackish or salt-water mangrove forests near the coast.

They are a kind of peatland, which store and accumulate vast amounts of carbon as soil organic matter—much more than forests on mineral soil (i.e. non-peatland) contain. Peat formation is a natural carbon sink; because the decomposition of the organic matter is slower than its production rate, the surplus accumulates as peat. Their stability has important implications for climate change; they are among the largest near-surface reserves of terrestrial organic carbon.[2] Tropical peat swamp forests, which have ecological importance, are one of the most threatened, yet least studied and most poorly understood biotypes.

Since the 1970s, tropical peat swamp forest deforestation and drainage have greatly increased in South East Asia.[3] In addition, El Niño Southern Oscillation (ENSO) drought and large-scale fires are accelerating peatland devastation. Peat fires, drainage and deforestation enhances the decomposition of soil organic matter, increasing the release of stored carbon into the atmosphere as carbon dioxide.[4]

Tropical peat swamp forests are home to thousands of animals and plants, including many rare and critically endangered species such as the orangutan and Sumatran tiger, whose habitats are threatened by peatland deforestation.[5]

Distribution

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Tropical peat ecosystem are found in three regions: Central America, Africa and South East Asia.[2] About 62% of the world's tropical peat lands occur in the Indomalayan realm (80% in Indonesia, 11% in Malaysia, 6% in Papua New Guinea, and pockets in Brunei, Vietnam, the Philippines, and Thailand).[6][7] Peat in Indonesia is distributed over three islands, Sumatra (8.3 million ha), Kalimantan (6.3 million ha) and Papua (4.6 million ha).[8] 36% of the world's tropical peat occurs in Africa's central Congo Basin.[9]

Formation

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Tropical peat forms on low-lying areas, such as river deltas, floodplains or shallow oxbow lakes. The formation process usually follows hydrosere successional steps,[1][10] where the ponds or flooded area eutrophicated by water plants, then transform into waterlogged swamp with grasses or shrubs, and eventually formed a forest that continues to grow and accumulate.[10] Peat located on the fringing areas of domes in between domes might form through lateral expansion.[10][11] This peat accumulation often forms a convex shape called a dome, which could rise up to 4 m (13 ft) on coastal peat and up to 18 m (59 ft) on inland peat.[1] At the beginning of its formation, peat is largely topogenous or minerotrophic, receiving high nutrient input from rivers or groundwaters. As the peat thickens and the dome becomes elevated, the top of the peat is no longer affected by the river or groundwater input, instead they are becoming ombrotrophic, exclusively obtaining water from the precipitation[8][10] Input only from the rain causes a low nutrient and mineral content, especially calcium. The peat thus becomes highly acidic and only able to support low biodiversity and stunted forest.

South East Asia

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Inland and coastal peat differ greatly in their age, where coastal peat formed during the mid Holocene, about 8000 years ago.[12] Inland peat formed much earlier during the Late Pleistocene, more than 26000 BP.[13] Coastal peat formation is highly affected by the sea level rise with strong accumulation around 8-4000 BP when El Nino is less intense.[14] Because the Sunda Shelf is tectonically stable, the sea level change in this area is only affected by the eustatic sea level, and during the glacial period the Karimata Strait dried, causing Asian Peninsula, Sumatra, Borneo and Java to become connected.[15] After the Last Glacial Maximum, this coastline moved inland as the ice sheet melted, and finally reached the level of modern coastline around 8500 BP. Thus, the oldest age of coastal peat in this region is less than 8500 years old.[16]

Inland peat formation is highly affected by climate with little or no effect of sea level rise because it located around 15–20 m (49–66 ft) above sea level, where the most recent record of higher sea level was during about 125000 BP when sea level was 6 m above the modern level.[17] Peat cores from Sebangau, South Kalimantan show a slow growth of 0.04 mm/y around 13000 BP when the climate was colder, then accelerated to 2.55mm/y around 9900 BP in warmer Early Holocene, then slower again to 0.23–0.15 mm/y during intense El Nino.[18] A similar pattern is observed in cores from Sentarum, West Kalimantan, where the peat shows slower growth around 28-16000 BP, 13-3000 BP and on 5-3000 BP.[19] While the slower growth from 28 to 16000 BP and 5-3000 BP is explained by a drier climate during this period due to Heinrich Event I and the emergence of El Niño.[20][21]

Ecology

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Peat swamp forest in Kalimantan

Peat swamp forest are unusual ecosystems, with trees reaching as high in 70 m (230 ft) in South East Asian ecoregions—vastly different from the peatlands of the north temperate and boreal zones (which are dominated by Sphagnum mosses, grasses, sedges and shrubs).[10] The spongy, unstable, waterlogged, anaerobic beds of peat can be up to 20 m (66 ft) deep with low pH (pH 2.9 – 4) and low nutrients, and the forest floor is seasonally flooded.[22] The water is stained dark brown by the tannins that leach from the fallen leaves and peat – hence the name blackwater swamps. During the dry season, the peat remains waterlogged and pools remain among the trees. Water level on the peat is usually 20 cm (7.9 in) below the surface.[1] however, during a severe El Nino, this water level might drop to 40 cm (16 in) below the surface and increase the risk of burning.[12]

Peat forest contains high amount of carbon due to its soil nature, categorized as histosols with characteristics of high organic material content (70–99%).[10][23] This carbon pool is stabilized by the low temperature on temperate peat, and by the water logging on tropical peat. Disturbances that change the temperature or the water content of the peat will release this stored carbon into the atmosphere, exacerbating human-made climate change.[14] Estimation of carbon content of tropical peat ranges from 50 Gt carbon[14] to 88 Gt carbon.[2]

In Indonesia

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Peat swamp forest in Borneo

Peat swamp forests originally represented major ecosystems in Indonesia and ranged between 16.5 and 27 million hectares. In their original state, Indonesian peat swamp forests released between 0.01 and 0.03 Gt of carbon annually. In recent years, however, these important ecosystems have been reduced through deforestation, drainage, and conversion to agricultural lands and other activities. Their current status as carbon sequestering systems have thus also been reduced significantly. An understanding of the global importance of peat (and thus the urgency of maintaining peat swamp forests) and identifying alternative ways of making these areas productive in an environmentally sound and sustainable manner should have high priority among scientists and policy-makers alike.[24]

The problem

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Over the past decade, under the Mega Rice Project (MRP), the government of Indonesia has drained over 1 million hectares of the Borneo peat swamp forests for conversion to agricultural land. Between 1996 and 1998, more than 4,000 kilometers of drainage and irrigation channels were dug, and deforestation accelerated in part through legal and illegal logging and in part through burning. The water channels, and the roads and railways built for legal forestry, opened up the region to illegal forestry. In the MRP area, forest cover dropped from 64.8% in 1991 to 45.7% in 2000, and clearance has continued since then. It appears that almost all the marketable trees have now been removed from the areas covered by the MRP. What happened was not what had been expected: the channels drained the peat forests rather than irrigating them. Where the forests had often flooded up to 2 meters deep in the rainy season, now their surface is dry at all times of the year. The Indonesian government has now abandoned the MRP.

A study for the European Space Agency found that up to 2.57 billion tons of carbon were released to the atmosphere in 1997 as a result of burning peat and vegetation in Indonesia. This is equivalent to 40% of the average annual global carbon emissions from fossil fuels, and contributed greatly to the largest annual increase in atmospheric CO2 concentration detected since records began in 1957.[25] Additionally, the 2002–03 fires released between 200 million to 1 billion tons of carbon into the atmosphere.

Indonesia is currently the world's third largest carbon emitter, to a large extent due to the destruction of its ancient peat swamp forests.

Indonesia contains 50% of tropical peat swamps and 10% of dry land in the world. They have the potential of playing an important role in mitigating global warming and climate change under the reducing emissions from deforestation and forest degradation (REDD) scheme. Rather than reducing deforestation—in terms of claiming carbon credits from REDD initiatives—peatland conservation and rehabilitation are more efficient undertakings, due to the much larger reduced emissions achievable per unit area and the much lower opportunity costs involved.[26]

  •  
    Air pollution over Southeast Asia in October 1997
  •  
    Satellite photograph of the haze above Borneo on 5 October 2006
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    Borneo lowlands to the north-west and south-east shrouded with thick, grey smoke from dozens of fires in this satellite image from 2009

Conservation and preservation

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Attempts to preserve tropical peat swamp forests have been minimal in comparison to the widespread impact and devastation of commercial logging; in Sarawak, logging is ongoing and planned to intensify in Brunei. One plan by the environmental NGO Borneo Orangutan Survival is to preserve the peat swamp forest of Mawas using a combination of carbon finance and debt-for-nature-swap. About 6% of the original peat-forest area is contained within protected areas, the largest of which are Tanjung Puting and Sabangau National Parks.

The main causes of deforestation in Indonesia continue to be palm oil business (see palm oil production in Indonesia) and illegal logging, ongoing in areas such as South Sumatra. A survey by the University of Muhammadiyah Palembang in 2008 estimated that in 25 years most of the natural forests will be depleted due to illegal logging. Projects by REDD are designed to tackle deforestation and protect forests from the encroachment of agriculture, benefitting biodiversity and improving the quality of the environment to surrounding villages.[27]

To counter the destruction of mangroves and unsustainable palm oil expansion in Indonesia's peatlands, organizations, such as Wetlands International, work with the Indonesian government to improve policies and spatial planning. They engage with the palm-oil industry, promoting best management practices in tropical peat swamp forests and ensuring the participation of local communities, who lack awareness about natural resource management. In the field, they work with communities to restore mangroves and peatlands.

Habitat disturbance caused by logging was shown to affect orangutan density within a mixed swamp forest. The presence of a very large, self-sustaining orangutan population in this region emphasizes the urgency for greater protection of Kalimantan's peat swamp forests in light of recent and rapid habitat degradation.[28]

In Malaysia

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It has long been assumed that the peat underlying tropical peat swamp forests accumulates because the extreme conditions (waterlogged, nutrient poor, anaerobic and acidic) impede microbial activity. Studies in a tropical Malaysian peat swamp (North Selangor peat swamp forest) showed that although the sclerophyllous, toxic leaves of endemic peat-forest plants (Macaranga pruinosa, Campnosperma coriaceum, Pandanus atrocarpus, Stenochlaena palustris) were barely decomposed by bacteria and fungi, the leaves of M. tanarius, another plant species, were almost completely decomposed after one year. Thus it is intrinsic properties of the leaves (that are adaptations to deter herbivory in the nutrient poor environment) that impede microbial breakdown.[29]

Ecoregions

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See also

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References

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  1. ^ a b c d Anderson, J. A. R. (1963). "The structure and development of the peat swamps of Sarawak and Burunei". Journal of Tropical Geography. 18: 7–16.
  2. ^ a b c Page, Susan E.; Rieley, John O.; Banks, Christopher J. (1 February 2011). "Global and regional importance of the tropical peatland carbon pool". Global Change Biology. 17 (2): 798–818. Bibcode:2011GCBio..17..798P. doi:10.1111/j.1365-2486.2010.02279.x. ISSN 1365-2486. S2CID 86121682.
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  15. ^ Smith, D. E.; Harrison, S.; Firth, C. R.; Jordan, J. T. (2011). "The early Holocene sea level rise". Quaternary Science Reviews. 30 (15–16): 1846–1860. Bibcode:2011QSRv...30.1846S. doi:10.1016/j.quascirev.2011.04.019.
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  17. ^ Woodroffe, S. A.; Horton, B.P. (2005). "Holocene sea-level changes in the Indo-Pacific". Journal of Asian Earth Sciences. 25 (1): 29–43. Bibcode:2005JAESc..25...29W. CiteSeerX 10.1.1.693.8047. doi:10.1016/j.jseaes.2004.01.009.
  18. ^ Page, S. E.; Wűst, R. A. J.; Weiss, D.; Rieley, J. O.; Shotyk, W.; Limin, S. H. (2004). "A record of Late Pleistocene and Holocene carbon accumulation and climate change from an equatorial peat bog (Kalimantan, Indonesia): implications for past, present and future carbon dynamics". Journal of Quaternary Science. 19 (7): 625–635. Bibcode:2004JQS....19..625P. doi:10.1002/jqs.884. S2CID 128632271.
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  20. ^ Partin, J. W.; Cobb, K. M.; Adkins, J. F.; Clark, B. and Fernandez, D. P. (2007). "Millennial-scale trends in west Pacific warm pool hydrology since the Last Glacial Maximum". Nature. 449 (7161): 452–5. Bibcode:2007Natur.449..452P. doi:10.1038/nature06164. PMID 17898765. S2CID 128764777.{{cite journal}}: CS1 maint: multiple names: authors list (link)
  21. ^ Gagan, M. K.; Hendy, E. J.; Haberle, S. G.; Hantoro, W. S. (2004). "Post-glacial evolution of the Indo-Pacific Warm Pool and El Niño-Southern oscillation". Quaternary International. 118–119: 127–143. Bibcode:2004QuInt.118..127G. doi:10.1016/S1040-6182(03)00134-4.
  22. ^ Yule, C. M. (2010). "Loss of biodiversity and ecosystem functioning in Indo-Malayan peat swamp forests". Biodiversity and Conservation. 19 (2): 393–409. doi:10.1007/s10531-008-9510-5. S2CID 21924837.
  23. ^ Couwenberg, J.; Dommain, R.; Joosten, H. (2009). "Greenhouse gas fluxes from tropical peatlands in south-east Asia". Global Change Biology. 16 (6): 1715–1732. doi:10.1111/j.1365-2486.2009.02016.x. S2CID 86148666.
  24. ^ Sorensen, Kim W. (September 1993). Indonesian peat swamp forests and their role as a carbon sink.
  25. ^ Page, Susan E.; Siegert, Florian; Rieley, John O.; Boehm, Hans-Dieter V.; Jaya, Adi; Limin, Suwido (2002). "The amount of carbon released from peat and forest fires in Indonesia during 1997". Nature. 420 (6911): 61–65. Bibcode:2002Natur.420...61P. doi:10.1038/nature01131. ISSN 1476-4687. PMID 12422213. S2CID 4379529.
  26. ^ Mathai, J. (5 October 2009). Seeing REDD over deforestation.
  27. ^ Priyambodo, RH, ed. (21 March 2011). "RI's peat forests can play important role in climate change". Antaranews.com. Antara.
  28. ^ Hirano, Takashi. (29 November 2006). Carbon dioxide balance of a tropical peat swamp forest in Kalimantan, Indonesia.
  29. ^ Yule, Catherine M. (22 June 2008). Leaf litter decomposition in a tropical peat swamp forest in Peninsular Malaysia.
  30. ^ Lewis, Simon L.; Ifo, Suspense A.; Bocko, Yannick E.; Page, Susan E.; Mitchard, Edward T. A.; Miles, Lera; Rayden, Tim J.; Lawson, Ian T.; Dargie, Greta C. (16 January 2018). "Congo Basin peatlands: threats and conservation priorities" (PDF). Mitigation and Adaptation Strategies for Global Change. 24 (4): 669–686. doi:10.1007/s11027-017-9774-8. ISSN 1573-1596.
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