3.3.2.1
Seedlings
The average numberof
seedlings
was about2512seedlings ha"1
and 2488seedlings ha"1
in October 1998 andMarch 1999
respectively.
There was nosignificant
difference be¬tween the total number of
seedlings
orsaplings
found in October 1998 and March 1999(Table 3.24).
Theseedlings
ofthepioneer
groupmadeup about 91%) of thetotalseedling population
in both October 1998 and March1999,
while theprimary
andsecondary
groupscontributed 7% and 2%respectively
to the total in both seasons.Symplocos
seed¬lings
outnumbered otherseedlings, making
up48% of the total number ofseedlings.
Regeneration type
October 1998 df=19
March 1999 df=19
t-value P
Seedling 2,512.5 2,487.5 0.38 0.71
Sapling 2,435.0 2,175.0 1.27 0.22
(Boldp value=significant,
df-degreeoffreedom)Table 3.24 Paired
samples
tteston mean density(no ha"1)
of the total numberofseedlings forOctober 1998vs in March 1999 with 20plots in Asinabari forest.
3.3.2.2
Saplings
The
density
ofsaplings corresponded
tothat ofseedlings:
24135sapling ha"1
in October 1998 and 2175sapling ha"1
in March 1999(Table 3.24).
As withseedlings,
thepioneer
group dominated the
sapling population, making
up about 90%and 97% ofthe total in October 1998 and March 1999respectively.
Theprimary
grouprepresented
about 2% of thesapling population
forboth seasons,while thesecondary
group contributed 8% and1%to the
sapling population
in October 1998 andMarch 1999respectively. Except
forafew
damaged
Casaeriaseedlings (Table
3.25) andSymplocos saplings (Table 3.26)
seenin March
1999,
therewere nosigns
ofbrowsing, lopping
andtopping
of theseedlings
andsaplings.
Group/Genus
SeedlingsOctober 1998 Seedlings March 1999Total
ha"1
% Totalha"1
%Primary
187.5 7.48 175.00 7.03Acer 12.50 0.50 12.50 0.50
Betula 12.50 0.50 12.50 0.50
Quercus 12.50 0.50 12.50 0.50
Alcimandra 12.50 0.50 25.00 1.01
Persea 50.00 1.99 50.00 2.51
Castanopsis 62.50 2.49 50.00 2.01
Prunus 25.00 1.00 12.50 0.50
Secondary
62.5 2.49 50.0 2.01Macropanax 12,50 0.50 12.50
25.00
0.50
Ficus 12.50 0.50 1.01
Evodia 37.50 1.49 12.50 0.50
Pioneer 2,262.5 90.5 2,487.5 90.96
Viburnum 225.00 8.96 287.50 11.56
Eurya 350.00 13.93 337.50 13.57
Casaeria 487.50 19.40 448.50* 17.59
Symplocos 1,200.00 47.76 1,189.50 47.74
TOTAL 2,512.50 100.00 2,487.50 100.00
*37damaged (1.5% of the totalseedlings or8.2% ofSymplocos seedlings
Table3.25 Numberof
seedlings (no ha"1) by group/genus
in Asinabari forestin October 1998 and in March 1999.62
Group/Genus Saplings October1998 SaplingsMarch 1999
Total ha"1 % Total
ha"1
%Primary 62.50 2.55 50.00 2.30
Alcimandra 12.50 0.51 0.00 0.00
Castanopsis 12.50 0.51 12.50 0.57
Persea 12.50 0.51 12.50 0.57
Prunus 12.50 0.51 12.50 0.57
Quercus 12.50 0.51 12.50 0.57
Secondary
185.5 7.69 25.00 1.14Macropanax 12.50 0.51 12.50 0.57
Evodia 175.00 7.18 12.50 0.57
Pioneer 2,187.5 89.75 2,100 96.55
Eurya 250.00 10.26 250.00
387.50
11.49 17,82
Casaeria 387.50 15.90
Viburnum 450.00 18.46 375.00 17.24
Symplocos
1,100.00 45.13 1,087.50* 50.00TOTAL 2,437.50 100.00 2,175.00 100.00
*13damaged (0.5% ofthe totalsaplingsor 1.19%of
Symplocos sapling)
Table 3.26 Number of
saplings
(noha"1)
bygroup/genus
inAsinabari forest inOctober 1998 and in March 1999.3.3.3 Forest stands
Asinabari
forest2
was dominatedby
trees oftheprimary
group:Acer, Persea, Magnolia,
Prunus, Betula, Cinnammomum, Michelia,Betula,
Sloanea,Castanopsis, Quercus
andElaeocarpus. Together,
these made up about 91.85% ofthegross volume and49.07%of the totaldensity
of the forest. Thegrowing
stock ofprimary
trees,exceptforPersea,
was concentratedonlarger
diameter trees, whereasthey
wereunder-represented
in the lower diametertrees(Table 3.27).
The lowercanopy oftheforestwasdominatedby
thepioneer
group, which accounted for about 42.82% of totaltreesin the
forest,
whiletheircontribu¬tiontothe gross volume was
only
about 4.09%.Symplocos species
dominated thepioneer
group. The
secondary
group contributedonly
8,16% of the total numberoftrees and 4.05% of the totalgrowing
stock.Theaverage number oftrees inthe forest amountedto 166trees
ha"1 (±46
treesha"1),
andthe
corresponding
grossstanding
volume amountedto 277nfW^ilOS.ln^ha"1).
Thestand
density
andstanding
volume werehigher
than those on the southwestaspect, but both measurementswerelowerthan thoseonthenortheastaspect.The grossvolume wasslightly higher
than the240m3 ha"1
estimatedby Sargent
etal.(1985)
forasimilartypeof2. The foiestbelongedtotheoak/lamci foicstt\pe(Saigentetat 1985)whichischaracterizedbythedominance
ofCastanopsis,Quercus, Peisea,Cinnamomumand Litsca species
forestin the
study
area. The diameter distribution forallspecies
followedthe curve ofanormalclimax forest.
However,
therewas adip
in the mid-diameterrange(25-50 cm) (Figure 3.15).
This may be attributedto selectivelogging3
in thepast and charcoal mak¬ing4.
The volumedistribution trends for allspecies
were similarto those foundon the northeast and southwestaspects.
Thatis, therewere a number oflarge
diametertrees(90- 140+)
whichwere very old anddying,
and contributedsubstantially
to thehigh growing
stock. These
old, large
diametertreeswererepresented by
theprimary
group(3.14m3/
tree), notably by Elaeocapus (4.46 nrVtree), Castanopsis (4.04 m3/tree)
andQuercus (3.40 nrVtree) species.
Genus Density Volume Mid-stem vol¬
ume(m3
tree"1)
Stemha"1 % m3 ha"1 %
Primary 81 49.07 254.54 91.85 3.14
Acer 3 1.88 8.08 2.92 2.69
Magnolia 8 5.00 23.16 8.36 2.89
Elaeocarpus 7 4.06 31.21 11.26 4.46
Castanopsis 12 7.19 48.54 17.51 4.04
Quercus 6 3.75 56.55 20.40 3.40
Persea 33 20.63 64.80 23.38 1.96
Prunus 2 1.25 4.52 1.63 2.26
Michelia 3 1.88 5.32 1.93 1.44
Cinnamomum 5 2.81 7.43 2.68 1.48
Sloanea 1 0.31 2.11 0.76 2.11
Betula 1 0.31 2.82 1.02 2.82
Secondary 15 8.16 11.24 4.05 0.74
Unknown 2 1.26 0.38 0.14 0.19
Ficus 2 0.94 0.51 0.18 0.25
Garuga 2 0.94 0.95 0.34 0.47
Amoora 1 0.63 1.07 0.39 1.07
Kydia 1 0.63 1.61 0.58 1.62
Macropanax 3 1.56 1.97 0.71 0.98
Eriobotrya 1 0.63 4.25 1.53 4.2
Evodia 1 0.31 0.06 0.02 0.06
Turpinea 1 0.63 0.19 0.07 0.19
Glochidion 1 0.63 0.25 0.09 0.25
Pioneer 70 42.82 11.33 4.09 1.28
Symplocos 54 33.44 7.63 2.75 0.14
Zanthoxylum 1 0.31 0.06 0.02 0.12
Viburnum. 1 0.31 0.13 0.05 0.12
Daphniphyllum 1 0.63 0.38 0.14 0.38
Eurya 11 6.88 2.54 0.92 0.23
Casaeria 2 1.25 0.59 0.21 0.29
TOTAL 166* 100.00 277.11" 100.00 1.67
Standard errors 19.02 - 48.86
Table 3.27 Species composition, density and growing stock in Asinabari forest.
3. TheforestformedpartoftheGedu,ChangangkhaandDungna PlywoodResourcesManagementPlan 1982- 1987.
4. Charcoal-making utilizing loggingresidues wasrecentlyallowed in the forest. Duringtheinventory,wecame
acrossnumerouscharcoal-makingpits.
64
Diameter class
(cm)
Figure3.15 Number of trees and grossvolume inAsinabari forest.
About9trees
ha"1, corresponding
to5.42% of the totalstanding
treesin Asinabariforest,
had beenlopped (Table 3.28).
Thelopped
treespecies
Amoora,Castanopsis,
Ficus, Per¬sea,
Turpinea,
Cinnamomum,Symplocos
andUnknownbelonged
to all threegroups butlopping
incidenceswerehigher
in thesecondary
group. About26.67% ofthesecondary
group treeshad beenlopped,
while4.94% oftheprimary
group treesand 1.42% ofthepioneer
trees hadbeenlopped. Among
the treesin thesecondary
group, allAmoora, Tur¬pinia
andUnknown treesrecorded and 50% of Ficusspecies
had beenlopped.
Withintheprimary
group, Cinnamomumspecies
had thehighest lopping
incidences(20%)
and about 8.3% each of Persea andCastanopsis
treeshad beenlopped. Lopping
incidences in thepioneer
groupwerelow(1%)
andwereconfinedtoSymplocos species.
About 1.8%oftheSymplocos
trees had beenlopped.
Itiscorrect to assumethat alltrees, except forSymplo¬
cos and
Cinnamomum,
had beenlopped
for fodder as their leaves andtwigs
arereported by
herders tobepalatable
to cattle.Symplocos
and Cinnamomummay have beenlopped
as litter for the tethered calves in the sheds.
Group/Genus TotalDensity
(stemha"1) Stemha1 Lopped %
Primary 81 4 4.94
Persea 33 2 9
Cinnamomum 5 20
Castanopsis 12 83
Secondary 15 4 26.67
Turpinea 1 100
Ficus 2 50
Amoora 1 100
Unknown 1 100
Pioneer 70 1.42
Symplocos 54 1 8
TOTAL 166 9 5 42
Table3.28 Lopped trees by