Tropical peatlands extensively occur in Southeast Asia, mainland East Asia, the Caribbean and Central America, South,America,Romania and southern Africa. Often located in lowlands, tropical peatlands are uniquely identified by rapid rates of peat soil formation, under high precipitation and high temperature regimes. In contrast, a high temperature climate accelerates decomposition rates, causing degraded tropical peatlands to contribute more substantially to global green house gas emissions.  Although tropical peatlands cover only 587,000 km, they store 119.2 Gigatonnes C at a density per unit area of 203,066 tonnes C km. For decades, these large carbon stores have succumbed to draining in order to cater for humanity's socio-economic needs. Between 1990 and 2015, cultivation (for management including industrial and small-holder agriculture) had increased from 11 to 50% of forested peatlands in Peninsular Malaysia, Sumatra, and Borneo. In Malaysia and Indonesia in the last twenty years, peat swamp forests have retreated from covering 77% of peatlands to 36%, endangering many mammals and birds in the region. In 2010, industrial agriculture covers about 3-3.1 million hectares, with oil palm accounting for 2.15 million hectares of this area. The conversion of natural tropical peatlands into other land uses leads to peat fires and the associated health effects, soil subsidence increasing flood risks, substantial greenhouse gas emissions and loss of biodiversity. Today efforts are being made to restore degraded tropical peatlands through paludiculture. Paludiculture is researched as a sustainable solution to reduce and reverse the degradation of peat swamp forests, and includes traditional local agricultural practices which predate the use of the term. Commercial paludiculture has not been trialled to the extent that it has in northern peatlands. Below are examples of paludiculture practices in tropical peatlands.