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Mlinga Forest Reserve: a biodiversity survey. - Coastal Forests of ...

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<strong>Mlinga</strong> <strong>Forest</strong> <strong>Reserve</strong><br />

12<br />

4.2.1.3 Disturbance transects<br />

Disturbance transects were used to record the intensity <strong>of</strong> pole and timber cutting and<br />

incidence <strong>of</strong> other disturbance types in the forest reserve. The disturbance transects were<br />

based on the 450m x 450m grid prepared for the vegetation plots (Figure 3). Each transect<br />

running east-west was sampled from border to border where accessible. Disturbance was<br />

recorded by 50m section along each transect.<br />

Every self-standing tree and sapling (not lianas or creepers) above 5cm dbh was measured<br />

within 5m either side <strong>of</strong> each transect line. Each plant was recorded under one <strong>of</strong> four<br />

categories: live, old cut, new cut or naturally dead. Within these categories a distinction was<br />

made between poles and timbers. Poles were classified as having a dbh (diameter at breast<br />

height) between 5 and 15cm and a minimum <strong>of</strong> 2m relatively straight trunk. Timber was<br />

classified as having a dbh > 15cm with a minimum 3m relatively straight trunk. These<br />

divisions were based on differences in use. New cut stems were determined by cream<br />

coloured slash and classified as freshly cut within recent months (approximately within the<br />

past 6 months). Old cut stems were determined by black coloured slash and classified as old<br />

cut (approximately more than 6 months old). Timber and pole cutting data are presented as an<br />

average per hectare and summarised in graphs and maps.<br />

The incidence <strong>of</strong> other signs <strong>of</strong> disturbance (such as fire, cultivation, animal trapping,<br />

pitsawing) were documented every 50m section and summarised in a table and maps. The<br />

most disturbed plots were calculated using pole and timber cutting counts and incidence<br />

figures for ‘other signs <strong>of</strong> disturbance’. Pole and timber cutting counts were combined,<br />

summed and then ranked, with the most disturbed plot ranked 1. All incidence records <strong>of</strong><br />

‘other signs <strong>of</strong> disturbance’ were summed and ranked, with the most disturbed plot ranked 1.<br />

The top six plots in each data set were combined to give the top twelve disturbed plots. Three<br />

additional border plots were additionally considered to be worthy <strong>of</strong> consideration.<br />

)<br />

16<br />

`15<br />

14<br />

14A<br />

Transect 0<br />

1 2<br />

3<br />

4 4A<br />

Transect 1<br />

24 23 22<br />

21<br />

20 19 18<br />

17<br />

17A<br />

Transect 5<br />

7 6 5<br />

4<br />

10<br />

9<br />

9A<br />

Transect 2<br />

29<br />

28 27A<br />

27 26A<br />

26<br />

25<br />

Transect 6<br />

11<br />

12 13<br />

33 34<br />

34A<br />

Transect 3<br />

Key:<br />

30<br />

Transect 7<br />

13<br />

Vegetation Plot<br />

31<br />

32<br />

Transect 4<br />

34A<br />

Incomplete 450m sections<br />

Scale:<br />

Accessible transect lines<br />

450m<br />

450m<br />

Figure 3 Location <strong>of</strong> vegetation plots and disturbance transects in <strong>Mlinga</strong> FR.<br />

(GPS co-ordinates <strong>of</strong> vegetation plots are summarised in Appendix 2).<br />

East Usambara Conservation Area Management Programme Technical Paper 56

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