Threats to tropical forests



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Threats to tropical forests and what we can do about it Ryszard Laskowski Institute of Environmental Sciences Jagiellonian University www.eko.uj.edu.pl/laskowski 1/22

Human activities: dangers and hopes for the future Timber production (mostly for export and fuel) Slash-and-burn practices: for agriculture and cattle ranches main crops: coffee, cocoa, banana trees, mango trees, papaya, avocado, sugar cane (250 different fruits originate from tropical rainforests; only 20 from the temperate zone) Tourism the hope for tropical rainforests? already high and still increasing economic value 2/22

Deforestation: the most important problem for tropical rainforests Originally: 14% of the Earth surface now only 6%! Currentr annual deforestation rate: ca. 50 000 100 000 km 2 (Poland = 312 000 km 2 ) At this deforestation rate: tropical rainforests will vanish by 2050! Extremely high extinction rate: up to 50 000 species per year! 3/22

4/22 Deforestation: eastern Amazon (eye altitude ca. 50 km)

5/22 Deforestation: western Amazon (eye altitude ca. 500 km)

Deforestation in Uganda Total forest cover 2010: 2,937,000 ha Losses in 1990 2010: 1,763,000 ha (37.1% of forest cover) average of 88,150 ha (1.86% per year) 5000 Thousands ha 4000 3000 2000 1000 0 1980 1990 2000 2010 2020 2030 2040 2050 Year 6/22 http://rainforests.mongabay.com

Deforestation: slush-and-burn 7/22 Slush-and-burn in Southern Mexico

Deforestation plantations replacing rainforest in Venezuela 8/22

Main causes of deforestation: Brazil, 2000-2005 Logging (legal and illegal): 3% Large-scale agriculture: 1% Fires, mining, urbanization, road construction, dams: 3% Small-scale subsistence agriculture: 33% Cattle ranches: 60% 9/22

What we can do about it? REDD: Reducing carbon Emissions from Deforestation and Degradation 10/22

Two useful definitions Deforestation: "permanent removal of forest cover and withdrawal of land from forest use, whether deliberately or circumstantially" (IPCC) = entire loss of patches of forest via clearing Forest degradation: "changes in the forest negatively affecting its production capacity" may eventually result in deforestation 11/22

What is REDD and why do we need it? REDD = financial incentives to help developing countries reduce deforestation rates to meet C emission 'baseline' countries can sell 'carbon credits' on the international carbon market over 70 countries eligible Tropical deforestation = 1 2 bln tonnes C per year = 15-20% global C emission In Africa ca. 70% of total C emission 12/22

Annual change in forest area by region 1990 2010 13/22 FAO Global Forest Resources Assessment 2010

Net change in forest area by country 2005-2010 Change in ha/year 14/22 FAO Global Forest Resources Assessment 2010

Trends in forest characteristics by region and subregion, 1990 2010 15/22 FAO Global Forest Resources Assessment 2010

Historical and future deforestation scenarios in Democratic Republic of Congo 16/22 "The REDD+ challenge in DRC" (http://unfccc.int)

Some intriguing quotes: "Better REDD than dead", The Economist, 2012 Indonesia s peat-based plantations, a quarter of the total, contribute less than 1% to the country s GDP but nearly 20% of the national C emissions. Indonesia s National Council on Climate Change puts the opportunity cost of forgoing an oil-palm plantation at $30 a tonne C. Capturing and storing emissions from power stations is estimated to cost $75-115 per tonne C. $17 billion 30 billion between now and 2015 could cut deforestation by a quarter. (EU $17 000 bln) 17/22

Doubts and problems No trusted estimates of actual deforestation rates in many countries (especially in Africa) Lack of trust in keeping the promise by governments in developing countries No good control over deforestation and afforestation activities "Small scale deforestation on a large scale" non-commercial deforestation by forest folk Lack of knowledge among local people 18/22

Forest management plans urgently needed for tropical countries! 19/22 FAO Global Forest Resources Assessment 2010

20/22 Estimating forest C pools

Forest carbon pools: priorities and costs 1 = lowest priority/cost; 4 = highest Carbon pool Method Priority Cost Tree biomass DBH (H) + allometric equations 4 2 Understory Destructive sampling 2 4 Dead trees No-destructive measurements 2 2 Litter Destructive sampling 2 3 Soil carbon Destructive (density and C content) 3 4 21/22

Allometric relationships: AGB = f(dbh) Chave et al. (2005) Tree allometry and improved estimation of carbon stocks and balance in tropical forests. Oecologia 145: 87-89 22/22

AGB = f(dbh): empirical regressions Dry forest stands: AGB = ρ exp( 0.667 + 1.784ln( D) + 0.207(ln( D)) 2 0.0281(ln( D)) 3 ) Moist forest stands: AGB = ρ exp( 1.499 + 2.148ln( D) + 0.207(ln( D)) Moist mangrove forest stands: AGB = ρ exp( 1.349 + 1.980ln( D) + 0.207(ln( D)) Wet forest stands: AGB = ρ exp( 1.239 + 1.980ln( D) + 0.207(ln( D)) 2 2 2 0.0281(ln( D)) 0.0281(ln( D)) 0.0281(ln( D)) 3 3 3 ) ) ) 23/22 Chave et al. (2005) Oecologia 145: 87-89

Symbols and units ABG = above-ground biomass; kg dry weight D = tree diameter at breast height (1.3 m); = tree girth/π tree girth/3.14; cm ρ = wood specific gravity = oven-dry wood over green volume; g/cm 3 Reyes et al. 1992. Wood densities of tropical tree species. USDA Forest Service. OR: use 0.5 g/cm 3 the mean for Africa On average, C = 50% dry wood mass 24/22

Carbon stock in tree roots Shoot:root ratios humid tropical forests on normal soils: 4:1 tropical forests on permanently wet soils: 10:1 tropical forests in areas with long dry season and soils of very low fertility: 1:1 25/22

How many plots should be sampled? Assume the desired precision level (e.g., ±10%, ±20% of the mean) Select 5-10 adequate sized plots within each management type (e.g., mature forest, logged, secondary young, secondary medium age, burnt) Estimate C stock for each plot, calculate mean and standard deviation Calculate the required number of plots 26/22

Necessary preliminary calculations x n x i ( xi x) i= = 1 2 i= 1 s = n n 1 n 2 s = s 2 n number of sampled plots s 2 sample variance s sample standard variation 27/22

Calculating the required number of plots ( N s) 2 n = r N 2 E 2 + N 2 t s 2 n r number of required plots N number of possible sampling plots E allowable error 28/22 t sample statistics from the t-distribution for a chosen confidence levels (e.g., 95%); for unknown sample size t=2

Example of calculations Area = 10 000 ha Plot size = 0.1 ha N (number of possible sampling plots) = 100 000 Mean C stock = 150 t C/ha Standard deviation = 30 t C/ha Desired precision = 10% E (allowable error) = 150 x 0.1 = 15 29/22 n r = 2 (100000 30) 2 2 100000 15 + 100000 2 2 30 2 = 16

Forest biomass carbon matrix Forest condition Mature Logged Secondary (young) Secondary (med. age) Burnt Forest type Moist Seasonal Seasonal 30/22

Forest biomass carbon maps for Africa and Southeast Asia produced by using regression-based models to extrapolate forest inventory measurements 31/22 Gibbs et al. (2007) Tree allometry and improved estimation of carbon stocks and balance in tropical forests. Oecologia 145: 87-99.

Thank you Don't forget to prepare for the seminar! 32/22