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