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Spatial and temporal land use and carbon stock changes in Uganda: implications for a future REDD strategy

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Abstract

Using a map overlay procedure in a Geographical Information System environment, we quantify and map major land use and land cover (LULC) change patterns in Uganda period 1990–2005 and determine whether the transitions were random or systematic. The analysis reveals that the most dominant systematic land use change processes were deforestation (woodland to subsistence farmland—3.32%); forest degradation (woodland to bushland (4.01%) and grassland (4.08%) and bush/grassland conversion to cropland (5.5%) all resulting in a net reduction in forests (6.1%). Applying an inductive approach based on logistic regression and trend analyses of observed changes we analyzed key drivers of LULC change. Significant predictors of forest land use change included protection status, market access, poverty, slope, soil quality and presence/absence of a stream network. Market access, poverty and population all decreased the log odds of retaining forests. In addition, poverty also increased the likelihood of degradation. An increase in slope decreased the likelihood of deforestation. Using the stock change and gain/loss approaches we estimated the change in forest carbon stocks and emissions from deforestation and forest degradation. Results indicate a negligible increase in forest carbon stocks (3,260 t C yr-1) in the period 1990–2005 when compared to the emissions due to deforestation and forest degradation (2.67 million t C yr-1). In light of the dominant forest land use change patterns, the drivers and change in carbon stocks, we discuss options which could be pursued to implement a future national REDD plus strategy which considers livelihood, biodiversity and climate change mitigation objectives.

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Notes

  1. Wood fuel is the major source of energy for domestic cooking. Annual timber consumption in the country estimated at 100,000 m3 in 2005/06, is projected to rise mainly driven by the booming construction industry (Drichi 2005).

  2. In May 2009, NFA applied to the World Bank’s Forest Carbon Partnership Facility (FCPF) for funds to develop a National Readiness Plan (R-PIN) to implement a REDD program (World Bank 2008). It was accepted as a country participant and; signed a ‘grant agreement for formulating and executing a Readiness Preparation Proposal (R-PP)’in September 2009. This makes Uganda entitled to a grant of up to US$3.6 million (World Bank 2009). The REDD-PIN is supposed to provide a common framework for effective coordination and implementation of REDD.

  3. Initially the land use maps and multi-scale factor datasets were transformed into a uniform grid of 5 km X 5 km but we were not able to simulate important small-scale relationships such as the observed numerous small forest patches along streams (NFA 2009).

  4. The maximum probability assignment rule was used in allocating a pixel to a particular land use. In reality, most of the pixels in the images are not covered by one land cover type, but varying proportions of land cover types.

  5. These include the Saw log Production Grant Scheme (SPGS) for the private sector, the Farm Income Enhancement and Forest Conservation Programme (FIEFCO); the Northern Uganda Reforestation Programme; the Community Tree Planting Programme (at least 5% of degraded CFR is allocated to local communities living around the CFRs for tree planting); New forest plantations and re-planting of harvested forest reserves and the International tree planting programme (TIST). However, despite similarities in the objectives of these programs, they lack coordination.

  6. Deforestation as defined under the Kyoto Protocol, refers to a permanent change of land use from forest to non-forest and, therefore, involves a loss in forest area and carbon stocks. Forest degradation refers to a decrease in biomass, and hence a reduction in forest carbon stocks without loss of forest area or change in land use (UNFCCC 2006).

  7. Considering past trends as an indication of the future, a historic reference timeline which encompasses several years such as (1990–2005) reduces the impact of anomalous years from previous trends. However, a 5 year reference period (i.e 2000–2005) may have advantages of identifying changes in land use with more relevance to the present. Our selection of the period 1990–2005 was also based on the fact that this is the period for which we have comparable reliable data on land use area and biomass carbon stocks estimates. In addition, considering the possibility of REDD + options and the current Clean Development Mechanism (CDM) framework, in order to qualify as a CDM-AR eligible activity, reforestation is limited to “those lands that did not contain forest on 31 December 1989” (UNFCCC/CP/2001/13/Add.1).

  8. A census carried out by the NFA in May 2005 indicated that there were over 180,000 encroachers in the 506 Central Forest Reserves (NFA 2005) and the number has more than doubled in the last 5 years (Annon. 2009).

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Acknowledgements

This paper is part of a Ph.D research project on carbon sequestration effects on sustainable forest management and contribution to poverty alleviation in Uganda supported by the Norwegian Agency for Development Cooperation (NORAD), the Quota Programme and SIDA/SAREC through Makerere University, Faculty of Forestry and Nature Conservation and School of Graduate Studies respectively. We appreciate assistance offered by Olav Bjella and Edward Senyonjo to acquire the maps and thank Emmanuel Jjunju for writing the code used in the analysis.

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Correspondence to Charlotte Anne Nakakaawa.

Appendices

Appendix 1: Detailed description of the model processes

figure a

[i] current year, [i-1] refers to previous year, [i+1] is the next year, [0] then refers to the initial-year

1.1 Forests & new plantations

$$ Plant[i] = Plant[i - 1] + \Delta Plant[{\hbox{i}}] $$
(1)
  • Plant[i] is the cumulative new-plantation area in year i.

  • ΔPlant[i] is new area that has been converted to plantations from grasslands and cropland during year i. This is manually specified every year according to the desired scenario by a user.

$$ \Delta Plant[i] = \Delta PlantC[i] + \Delta PlantG[i] $$
(2)
  • ΔPlantC[i] and ΔPlantG[i] are user specified land area transfers from cropland and grassland to new plantations. This may have implications for satisfying cropland demand.

    $$ For[i] = For[i - 1] + \Delta For $$
    (3)
  • For[i] is the forest area for year i (the current year)

  • ΔFor then refers to the change in forest area

1.2 Grassland

$$ Gras[i] = \max (Gras*[i],Past\min ) - \Delta PlantG[i] $$
(4)
$$ Gras*[i] = Gras[i - 1] + \Delta Gras*[i] $$
(5)
$$ \Delta Gras[i] = Gras[i] - Gras[i - 1] $$
(6)
  • ΔGras [i] is the Actual change in grassland

    $$ \Delta GrasDfct[i] = \Delta GrasD[i] - \Delta Gras[i] $$
    (7)
  • ΔGrasDfct is the Deficit or unsatisfied grassland demand at current consumption and yield

  • Gras[i] is the grassland area for year i (the current year)

  • [i-1] then refers to the previous year

  • ΔGras then refers to the change in grassland based on demand and constraints such as the user defined minimum value of Pastmin.

  • ΔGras* is the change in grassland before correction to ensure that Pastmin is maintained

  • ΔGrasD is the change in demand for grassland as driven by livestock and biomass yields.

1.3 Cropland

$$ Crop[i] = if(Gras*[i] \geqslant Past\min, Crop[i - 1] + \Delta Crop*[i],Crop[i - 1] + \Delta Crop*[i] - (Past\min - Gras*[i]) - \Delta PlantC[i] $$
(8)
$$ \Delta Crop[i] = Crop[i] - crop[i - 1] $$
(9)
  • Crop[i] = the cropland area in current year

  • Gras*[i] = specified in Eq. 5

  • Past min = minimum grassland area. (It is specified by the user)

  • ΔCrop[i-1] = cropland area in previous year

  • Δcrop* = change in cropland before ensuring that the Pastmin is maintained.

  • ΔCrop[i] = Actual change in cropland which may be constrained by availability of land and Pastmin.

    $$ \Delta CropDfct[i] = \Delta CropD[i] - \Delta crop[i] $$
    (10)
  • ΔCropDfct = Deficit or unsatisfied crop demand at current consumption and yield

1.4 Others

$$ Oth[i] = Oth[i - 1] - \Delta UN[i] $$
(11)
  • Crop[i] is the cropland area for year i (the current year)

  • UN[i] is the component of the Others’ area that is user specified as available to transfer from Others(if positive) or to return to others (if negative)

  • ΔUN[i] is the change in the UN as an effect of transfers to/from Others.

Computing the land demand & supply for each land-use type

2.1 No-intensification process (BiomC = 4.6)

  • i.e when For[i-1]-LandFor[i]>Formin[i] i.e, LandFor<dEF)

    $$ {\hbox{dEF[i] = dEF[i - 1] - }}\Delta F{\hbox{or[i - 1] + DEF[i]}} $$
    (12)
    $$ FOR\min {\hbox{[i] }} = For[i - 1] - dEF[i] $$
    (13)
  • LandFor[i] is the sum of the changes in demand for cropland and pastures that are not satisfied by UN.i.e P+Q in the diagram.

  • FORmin[i] is the minimum area beyond which the forest should not reduce in year i.

  • dEF[i] is the actual deforestation that is allowed in a given year that ensures a correction to the deforestation rate for the next year in order to ensure that the cumulative value of DEF[i], the user specified rate, is maintained over a long period.

2.2 Grassland

$$ pas{t_d}[i] = f(BiomC = 4.6,Liv[i],BiomPY[i]) $$
(14)
$$ BiomPY[i]) = k*Rain[i] $$
(15)
  • K may vary from 0.001 to 0.004. This value has to be calibrated. Rain[i] is the average rainfall (mm) in particular year i.

  • Pastd is the demand for pastures by livestock

  • BiomC is the livestock Biomass consumption by an equivalent livestock unit

  • Liv is the number of livestock equivalent

  • BiomPY is the Biomass Yield in the grasslands

    $$ GrasD[i] = \max (Gras[i - 1],pas{t_d}[i]) $$
    (16)
  • GrasD is the required grassland area which may be equal to the existing area or the demanded pasture area, whichever is greater.

$$ \Delta GrasD[i] = \max (0,GrasD[i] - GrasD[i - 1]) $$
(17)
  • ΔGrasD is the change is GrasD. If it is negative, it not assigned, hence a value of zero is taken to mean there was no real change demanded. The negative value can be due to reduction in livestock numbers and or increase in biomass yields.

2.3 Cropland

$$ cro{p_d}[i] = f(FoodC,Popn[i],cropY[i],net{\rm Im} p[i]) $$
(18)
  • Cropd is the cropland area demand for crops intended for human consumption

  • FoodC is the food consumption per capita

  • Popn is the population

  • cropY is the crop yield (equivalent yield of a composite crop)

  • netImp is the difference between agricultural imports and exports

    $$ \Delta cro{p_d}[i] = \max (0,cro{p_d}[i] - cro{p_d}[i - 1]) $$
    (19)
  • Δcropd is the difference between cropd for the current year and crop d for the previous year. If it is negative, it not assigned, hence a value of zero is taken to mean there was no real change demanded. The negative value can be due to a large increase in crop yield or net-agricultural imports netImp.

    $$ Fal[0] = crop[0] - cro{p_d}[0] $$
    (20)
  • Fal is the the Fallow area in year i. We calculate the fallow for [i-1] as the fallow for [i] is unknown until Δfal, the change in fallow, has been calculated

    $$ cf[i] = \frac{{Fal[i]}}{{cro{p_d}[i]}} $$
    (21)
  • cf1 is the reference fallow for a year in the past. Usually the first year in the simulation. [i = 0] indicates the starting year.

    $$ \Delta Fal[i] = (\Delta cro{p_d}[i]*cf1) - (\Delta cropd[i] + \Delta GrasD[i] - UN[i])*\left( {1 - \frac{{past[i - 1]}}{{crop[i - 1]}}} \right) $$
    (22)

(Stéphenne and Lambin 2001)

$$ Fal[i] = Fal[i - 1] + \Delta Fal[i] $$
(23)
$$ \Delta cropD[i] = \Delta cro{p_d}[i - 1] + \Delta Fal[i] $$
(24)
  • ΔcropD is the change in total cropland demand including the change in Fallow.

2.4 Transfers

$$ R[i] = \min (\Delta cropD[i],UN[i]) $$
(25)
  • R[i] is the transfer of area between Others to Cropland

    $$ S[i] = \min ((UN[i] - R[i]),\Delta GrasD[i]). $$
    (26)
  • S[i] is the transfer of area between Others and Grasslands

    $$ P[i] = \max (\Delta cropD[i] - R[i],0) $$
    (27)
  • P[i] is the transfer from Forests to Croplands

    $$ Q[i] = \max (\Delta GrasD[i] - S[i],0) $$
    (28)
  • Q[i] is the transfer from Forests to Grasslands

    $$ LandFor[i] = P[i] + Q[i] $$
    (29)

    Check for intensification

    $$ if(For[i - 1] - LandFor > FOR\min [i]...then...\Delta For = LandFor $$
    (30)

If this condition is true then the changes in Land-use in Eqs. 2,4,5 and 6 are calculated as follows for year I (No intensification);

$$ \begin{array}{*{20}{c}} {\Delta For[i] = LandFor[i],} \hfill \\{\Delta Gras*[i] = \Delta GrasD[i],} \hfill \\{\Delta Crop*[i] = \Delta CropD[i],} \hfill \\{\Delta UN[i] = (R[i] + S[i])} \hfill \\\end{array} $$
(31a,b,c,d)

If this condition is False, then all above calculations from Eq. 8 are repeated as explained below.

2.5 Intensification process (BiomC = 2.3) In Eq. 8, BiomC becomes 2.3

Also recalculate Eqs. 9 to 15 which remain unchanged

2.6 Transfers

Recalculate Eqs. 25 and 26 which also remain unchanged. P& Q change slightly, but to avoid confusion we now call them U & V respectively and renumber to 23 and 24.

$$ U[i] = \min (\Delta cropD[i] - R[i],dEF[i]) $$
(32)
  • U[i] is the transfer from Forests to Croplands

    $$ V[i] = \min (dEF[i] - U[i],\Delta GrasD[i] - S[i]) $$
    (33)
  • Q[i] is the transfer from Forests to Grasslands

A new term T[i] to represent transfers from Grasslands to cropland. These transfers are possible during the intensification phase as livestock is increasingly fed on crop residues.

$$ T[i] = \Delta cropD - (R + U) $$
(34)

It then follows that the changes in Land-use in Eqs. 2,4,5 and 6 are calculated as follows for year i (under-intensification);

$$ \begin{array}{*{20}{c}} {\Delta For[i] = U[i] + V[i],} \hfill \\{\Delta Gras*[i] = S[i] + V[i] - T[i],} \hfill \\{\Delta Crop*[i] = \Delta cropD[i],} \hfill \\{\Delta UN[i] = (R[i] + S[i])} \hfill \\\end{array} $$
(35)

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Nakakaawa, C.A., Vedeld, P.O. & Aune, J.B. Spatial and temporal land use and carbon stock changes in Uganda: implications for a future REDD strategy. Mitig Adapt Strateg Glob Change 16, 25–62 (2011). https://doi.org/10.1007/s11027-010-9251-0

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