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Kenzo2009b

Daniel Falster edited this page Nov 25, 2014 · 1 revision

Report for study: Kenzo2009b

Contact Information

Data contributor: Tanaka Kenzo

Email: [email protected]

Address:

  • Bureau of International Partnership, Forestry and Forest Products Research Institute, Tsukuba, Ibaraki, 305-8687, Japan

Data source

Citation: Kenzo T, Furutani R, Hattori D, Kendawang J, Tanaka S, Sakurai K and Ninomiya I (2009). 'Allometric equations for accurate estimation of above-ground biomass in logged-over tropical rainforests in Sarawak, Malaysia.' Journal of Forest Research, 14(6), pp. 365-372.

DOI: 10.1007/s10310-009-0149-1

Abstract: Although allometric equations can be used to accurately estimate biomass and/or carbon stock in forest ecosystems, few have been developed for logged-over tropical rainforests in Southeast Asia. We developed allometric relationships between tree size variables (stem diameter at breast height (dbh) and tree height) and leaf, branch, stem and total above-ground biomass in two logged-over tropical rainforests with different soil conditions in Sarawak, Malaysia. The study sites were originally classified as mainly lowland dipterocarp forest and have been selectively logged in the past 20 years. In total, 30 individuals from 27 species were harvested to measure above-ground parts. The correlation coefficients for the allometric relationships obtained for total above-ground biomass as a function of dbh had high values (0.99), although the relationships for leaf biomass had a relatively low coefficient (0.83). We also found relatively high coefficients for allometric relationships between tree height and plant-part biomass, ranging from 0.82 to 0.97. Moreover, there were no differences for allometric equations of total above-ground biomass between study sites. A comparison of equations of above-ground biomass in various previously reported tropical rainforests and pan-tropic general equations imply that our allometric equations differ largely from the equations for tropical primary forests, early successional secondary forest, and even for the general models. Therefore, choosing the biomass estimation models for above-ground biomass in the logged-over forests of Southeast Asia requires careful consideration of their suitability.

Overview of data provided

The dataset includes records for 52 individuals from 28 species belonging to 16 family(ies), presenting 1 functional type(s), growing in 1 condition(s) within 1 major type(s) of habitat, with data included for the following variables:

Variable Label Units N Min Median Max
latitude Latitude deg 52 0.92 1.1 3.6
longitude Longitude deg 52 111 111 114
a.lf Leaf area m2 27 0.015 0.18 87
a.stba Stem area at base m2 22 0.00002 0.000045 0.00086
a.stbh Stem area at breast height m2 30 0.000079 0.0095 0.15
h.t Height m 52 0.41 3.5 40
h.c Height to crown base m 18 0.11 0.43 1.4
d.ba Basal diameter m 22 0.005 0.0076 0.033
d.bh Dbh m 30 0.01 0.11 0.44
h.bh Height of d.bh measurement m 52 1.3 1.3 1.3
c.d Crown depth m 18 0.18 0.35 0.79
m.lf Leaf mass kg 52 0.0013 0.15 52
m.st Total stem mass kg 52 0.0019 0.57 1036
m.so Aboveground mass kg 52 0.0032 0.9 1088
m.br Branch mass kg 25 0.02 12 356
m.rt Total root mass kg 22 0.00089 0.0029 0.29
m.to Total mass kg 22 0.0041 0.019 2.2
ma.ilf Leaf mass per area kg m-2 27 0.068 0.068 0.089
r.st Wood density kg m-3 48 210 345 900

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And locally within the country:

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The sites sampled are:

Location Longitude Latitude Vegetation
Sabal Forest Reserve, Sarawak, Malaysia 110.9167 1.0500000 Tropical rainforest
Balai Ringin Protected Forest 110.7167 0.9166667 Tropical rainforest
Niah Forest Reserve, Sarawak Malaysia 113.7000 3.6500000 Tropical rainforest

The growing conditions of sampled plants was:

Location Grouping growingCondition
Sabal Forest Reserve, Sarawak, Malaysia location = Sabal Forest Reserve, Sarawak, Malaysia; contributor = Kenzo 2009 field wild
Balai Ringin Protected Forest location = Balai Ringin Protected Forest; contributor = Kenzo 2009 field wild
Balai Ringin Protected Forest location = Balai Ringin Protected Forest; contributor = Kenzo 2004 field wild
Niah Forest Reserve, Sarawak Malaysia location = Niah Forest Reserve, Sarawak Malaysia; contributor = Kenzo 2004 field wild

Species sampled

Species Family Pft
Unknown sp. 1 Anacardiaceae evergreen angiosperm
Unknown sp. 2 Anacardiaceae evergreen angiosperm
Alphonsea johorensis Annonaceae evergreen angiosperm
Unknown Annonaceae evergreen angiosperm
Santiria apiculata Burseraceae evergreen angiosperm
Kokoona ovatolanceolata Celastraceae evergreen angiosperm
Garcinia penangiana Clusiaceae evergreen angiosperm
Dryobalanops beccarii Dipterocarpaceae evergreen angiosperm
Shorea andulensis Dipterocarpaceae evergreen angiosperm
Shorea cf. stenoptera Dipterocarpaceae evergreen angiosperm
Shorea parvifolia Dipterocarpaceae evergreen angiosperm
Macaranga costulata Euphorbiaceae evergreen angiosperm
Macaranga trachyphylla Euphorbiaceae evergreen angiosperm
Endospermum cf. diadenum Euphorbiaceae evergreen angiosperm
Litsea castanea Lauraceae evergreen angiosperm
Litsea cauliflora Lauraceae evergreen angiosperm
Aglaia affinis Meliaceae evergreen angiosperm
Aglaia bernardoi Meliaceae evergreen angiosperm
Walsura pinnata Meliaceae evergreen angiosperm
Xylocarpus sp. Meliaceae evergreen angiosperm
Ficus sp. Moraceae evergreen angiosperm
Endocomia rufirachis Myristicaceae evergreen angiosperm
Xanthophyllum stipitatum Polygalaceae evergreen angiosperm
Adina sp. Rubiaceae evergreen angiosperm
Arytera littoralis Sapindaceae evergreen angiosperm
Adinandra dumosa Theaceae evergreen angiosperm
Trema sp. Ulmaceae evergreen angiosperm
Shorea ovata Dipterocarpaceae evergreen angiosperm

Methods used

Sampling strategy: All trees were harvested to measure all plant parts variables.

Stem cross sectional area: The area was calculated from stem diameter including bark

Height: Tree height was defined as the length from ground to the apex of the tallest shoot.

Biomass: Total fresh weight was measured in the field and representative subsamples were dried at 80degC for at least 72h to determine dry biomass.

Traits: Species traits were defined from flora record and our observations.

Growth environment: Growth environment was defined from our observations.

Year collected: 2001-2003

Acknowledgements: I. Ninomiya, K. Sakurai, J. J. Kendawang and D. Hattori

Plots of data

This is how the study Kenzo2009b fits in the entire dataset (grey). each colour represents a species. A legend of species names with colours is included at the end for reports with 1 < n < 20 species.

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