Saving a forest- the composition and structure of a

NAT.H
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4
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:239-260,2006
SA
VINGA FOREST:THECOMPOSITIONANDSTRUCTURE
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1
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COMPOSITION AND STRUCTURE OF A COMMUNITY-MANAGED DECIDUOUS FOREST
241
MATERIALS AND METHODS
Study Area
Khok Bung Preu is a remnant, lowland deciduous forest located in Dan Khuntot
District, Nakhon Ratchas.ima Province, Northeast Thailand (Fig. 1). It is an isolated 560ha forest fragment surrounded mainly by agricultural land and settlements. T he topography
is f lat and at an elevation of 240 m msl. The soil is a well-drained sandy loam. The climate
is tropical seasonal monsoon with a rainy period from June to October and a mean ann ual
rainfall of about 950 mm (Fig. 2). There are three seasons, namely hot and dry from March
to April , rainy from May to October, and dry from November to May. The mean monthly
temperature is 27"C with the mean maximum of 31 ·c in April and minimum of 23 ·c in
December (Fig. 2). During the dry season, temperatures can reach 4o·c or more. The mean
monthly humidity of the study area is 70% . The vegetation is highly susceptible to fire in
the dry season.
N
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100
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Figure I. Study area. Black clot show in g the location of Khok Bung Preu forest in Nakhon Ratchasima Province
in Northeast Thailand .
242
MD. E NA MMU L K AB IR AND EDWARD
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Figure 2. Meteorological data (1981 - 2001) from meteorological station number 431201 based in Nakhon
Ratchasima. Source: Meteorologi cal Department of Thailand.
Survey Design
To understand the history of the site and contemporary management patterns, key
informant interviews and opportunistic informal group discussions were held with people
living in the vicinity of the forest. Key informants were purposively selected among elderly
villagers, village leaders, township administrative officials, local forest officials, and members
from the forest management committee. Informal group discussion and key informant
interviews provided us the inf01mation on site history, history of community forest forn1ation ,
forest management practices, and forest resources use.
We investigated the vegetation composition and structure ofKhok Bung Preu community
forest by using a 3-stage random sampling method to establish 31 0.03-ha temporary
sample plots. Using GPS combined with mapping of the existing forest patch from an
orthorectified Landsat ETM+ image (acquisition date February 18, 2002), we established
a temporary transect that bisected the forest in a N-S direction. Subsequently we randomly
selected 31 points along the transect. At each point, we randomly chose a direction (east
or west) by flipping a coin, randomly selected a distance between each point and the edge
of the forest using a random number generator, and then entered that coordinate into the
GPS. After finding the coordinate on the ground, we established the center of each vegetation
plot. In this way, every point in the forest had an equal chance of being selected as a plot
location. The final plot locations are shown in Figure 3.
Vegetation plots were concentric circles of 1, 3, and 10-m radius, totaling 0.01, 0.09,
and 0.97 ha, respectively. In each 1-m plot all woody stems with a diameter at 1.3 m height
(dbh) 2.5 em or with a height less than 1.0 m (referred to as seedlings) were identified
and tallied. In the _3-m plots, aU woody stems with a dbh 2.5-9.9 em (saplings) were
identified, and the dbh and height recorded. In the 10-m plots all trees with dbh 10 em
were identified and measured for dbh and height. In all plots, vines/woody climbers were
COMPOSITION ANDSTRUCTUREOFA COMMUNITY-MANAGEDDECIDUOUS FOREST
2 Kilometers
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COMPOSITION AND STRUCTURE OF A COMMUNITY-MANAGED DECIDUOUS FOREST
247
outside user groups had no access. Harvest of timber without permission was also banned
for the main user groups. With approval from the Management Committee, timber could
be harvested during stressful periods due to natural disasters such as fire and storms or for
building and/or renovating public buildings such as the school, temple or community
center. Fuel wood could be collected only for household use. Honey could only be harvested
without causing any damage to the vegetation of the forest. The only non-consumptive use
of the forest was utilization of a place in the forest called the ' house of spirits', locally
"san chao", which vil lagers would occas ionally visit to pray.
Species Composition and Diversity
A total of 97 species in 48 families were recorded: 39 species in 23 families were
trees, 31 species in 21 families were saplings, 48 species in 30 families were seedlings, and
10 species in 8 families were vines and woody climbers (Table 1). Families with the most
species were Leguminosae, Papilionoideae (8), Rubiaceae (7); Leguminosae,
Caesalpinioideae (6), and Gramineae (5). Approximately 23% of the total number of families
(11/48) had more than 3 species and the remaining 77 % of families (37 /48) had only 1 to
2 species each. Approximately 26% of tree species were represented by 1 individual
ha- 1 and 39% of the sapling species were represented 11 individuals ha- 1 (Figure 4).
Sindora siamensis var. siamensis, Xylia xylocarpa var. ke rrii , Erythrophloeum
succirubrum, and Bauhinia saccoca/yx were the 4 most common species in this forest,
accounting for 92% of the stems 2.5 em dbh. Shorea siamensis var. siamensis and
Dipterocarpus gracilis represented the only 2 species of Dipterocarpaceae. The tree
community was dominated by X. xy/ocarpa var. kerrii and Sindora siamensis var. siamensis.
The sapling community was dominated by Sindora siamensis var. siamensis, B. saccocalyx,
and E. succirubrum (Table I).
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Figu re 4. Spec ies-rank plots of trees and sapl ings of Khok Bung Preu forest in Northeast Thai land. Total area
sampled for trees 0.97 ha and for sap lings 0.09 ha.
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COMPOS ITION AND STRUCTURE OF A COMMUN ITY-MANAGED DECIDUOUS FOREST 251
Table 2. Diversity indices for trees and saplings of Khok Bung Preu forest in northeast
Thailand. Trees dbh 10 em and saplings dbh 2.5 to 9.9 em. N 0 is absolute
richness. R 1 (MARGALEF, 1958) and R2 (MENHINICK, 1964) are the two species
richness indices. Simpson' s A (S IMPSON, 1949) and Shannon's H' (SHANNON &
WEA YER, 1949) are the two species diversity indices. N 1 and N2 represent
the number of dominant and very dominant species (HILL, 1973) in the forest.
Pielou 's J or E 1 (PIELOU , 1975; 1977) and E 5 (HILL, 1973) are species evenness
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Sample Size
Figure 5. Rarefaction curves of trees and saplings of Khok Bung Preu fores t in Northeast Thailand show ing the
expected number of spec ies from a certain number of nmdomly selected individuals.
Trees and saplings in Khok Bung Preu forest were similar in species diversity (Simpson
A= 0.12 for trees and 0.09 for saplings, Shannon H' = 2.81 for trees and 2.67 for saplings),
evenness (Pielou J' or E 1 = 0.73 for trees and 0.82 for saplings, Hill's E 5 = 0.53 for trees
and 0.62 for saplings (Table 2), and in rarefraction (Fig. 5).
252
MD.ENAMMULKABIR刷 DEDWARDL
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