THA_2013-2017_NFI-R3_v01_M_v01_A_ESS
National Forest Inventory (Thaiform) Harmonized for REDD+ Forest Reference (Emission) Levels 2013-2017 (Cycle 3)
Name | Country code |
---|---|
Thailand | THA |
Forest resource survey
Thailand started implementing full scale National Forest Inventory in 2003 with the THAIFORM project supported by the International Timber Trade Organization (ITTO). This first NFI consisted in sampling clusters of five 0.1 ha circular plots. In the three phases of the project, from 2003 to 2010, clusters were first placed on a 20 km square grid across all lands (phase one), completed by 10 km grid inside forests in phase two (in-between the 20 km grid clusters), and additional plots on a 5 km grid in several protected areas in phase three. Between phase one and two, the responsibility of conducting THAIFORM moved from the Royal Forest Department (RFD) to the Department of National Parks, Wildlife and Plant Conservation (DNP). In 2011-2012, a partial remeasurement of the forest plots on the 10 km grid was caried out but limited to the center plot of each cluster. This campaign is acknowledged as NFI cycle 2 but was later dropped from the REDD+ Forest Reference (Emission) Levels (FREL/FRL) harmonization process.
Thailand NFI cycle 3 was implemented from 2013 to 2017 by the Department of National Parks, Wildlife and Plant Conservation (DNP). Its original purpose was monitoring forest resource in protected areas. The inventory built on cycles 1 and 2 with the remeasurement of forest plots in 10 and 5 km grids, but also added around 2,600 plots in selection of protected areas on a 2.5 km grid for greater understanding of the forest resource in these parks. In addition to the plots measured by DNP, 176 plots were measured by the Royal Forest Department in forest outside protected areas. This data was used to report on the status of the forest, including number of trees, their distribution per diameter class, volume, biomass stocks as well as biodiversity indicators. In 2018-2020, with support from FAO, this data was re-analyzed, with the data from Cycle 1 to generate carbon stocks for the country’s key forest types. During this process, the data was harmonized, few corrections were made to data entry errors and the plots from the 10 km grid only were kept for better consistency across cycles. Since the number of plots measured in the different cycles was not the same, especially much less plots were remeasured outside protected areas, a stratified approach was used to calculate forest carbon stock. In each plot, field crews inventoried all the standing vegetation, i.e. trees, seedling, sapling, rattan, and bamboo, as well as standing and lying dead wood. At plot level, access notes, reference points, geomorphological conditions and land use were reported. This survey consists of the inventory plots from the 3rd NFI cycle on the 10 km grid, harmonized for the REDD+ FREL/FRL.The Department of National Parks, Wildlife and Plant Conservation is the organism responsible for the series of NFIs. More information can be found in the FREL/FRL submission to the UNFCCC: https://redd.unfccc.int/submissions.html?country=tha
Sample survey data [ssd]
Sampling circular plots of 0.1 ha located on a 10 by 10 km grid across the whole country in forested lands. The plots were further subdivided in concentric subplots. More details are available in Thailand first REDD+ FREL/FRL submission to the UNFCCC (see Documentation).
The third inventory cycle combines inventory plots from DNP and RFD. Measurements target:
National coverage
Trees >1.3 m height and >15 cm girth at breast height.
Name | Affiliation |
---|---|
Department of National Parks Wildlife and Plant Conservation (DNP) | |
Ministry of Natural Resources and Environment | Government of Thailand |
Name |
---|
Food and Agriculture Organization of the United Nations |
Royal Forest Department |
Ministry of Natural Resources and Environment |
Kasetsart University Faculty of Forestry |
International Tropical Timber Organization |
Name |
---|
Government of Thailand |
The sampling procedure of NFI cycle 3 is based on a systematic 10 km grid across all forests, as designed in the NFI cycle 1. Due to the change of responsibility on NFI from the Royal Forest Department to the Department of National Parks, Wildlife and Plant Conservation, it was reduced to protected forests and only a few plots were remeasured outside protected areas for the cycle 3.
The original cycle 1 design was a cluster of 5 circular plots with 0.1 ha area each organized in a cross shape. This approach was discontinued at cycle 2 and since then only the center plot was measured. The number of plots measured was 572 in protected forest and 154 in non-protected forests, for a total of 726 plots. The reference areas for this cycle are 6.350 and 9.995 M.ha for unprotected and protected forest respectively.
For the purpose of National level carbon stock, the non-visited plots were not replaced and the discrepancy in sampling size between protected and non-protected areas was addressed by reconsidering the approach from systematic to stratified. This shift is considered not harmful to potential bias as the non-remeasured plots didn’t follow any particular trend or pattern.
According to the ITTO project report for the NFI Cycle 1, around 12% of the plots in Tropical Evergreen Forest could not be measured. No corrections were made to compensate this lack of data, and as Tropical Evergreen Forest is the highest carbon stock forest type, the overall carbon stock is considered conservative. Several plots were not visited for budgetary reasons as the cycle 3 original purpose was to report on protected areas independently. Few plots were also not measured because they were not accessible. No correction was made as the number of plot missing is considered small.
Trees were measured in one 0.1 hectare circular plot per cluster. A scale factor 10 was applied to plot level calculations to convert results per plot into results per hectare.
The plots were stratified into Evergreen and Deciduous forest types and protected vs non-protected forests. Variables such as biomass were calculated per forest type and protection status, then a weight was applied to reflect the difference in sampling intensity between protected and non-protected forests (See the technical annex to the first FREL/FRL from Thailand submitted to the UNFCCC in 2021).
Start | End |
---|---|
2013-01 | 2017-12 |
All the information collected on the field was entered in paper field forms then manually entered in an MS Access database. For the REDD+ FREL/FRL submission the data was then loaded into R and a sequence of scripts were designed to read the data, perform quality control checks and calculate forest carbon stocks. The full sequence of data checks, corrections and calculations was:
Conversion MS Access to CSV:
All the national level estimates were provided with a 95% confidence interval taking into consideration the sampling error. The formula was based on Stratification design (Cochran 1977). Error due to the biomass equation choice was not included in the sampling error, as not indicator was provided with the models. However, the equations were validated to minimize the error, and details provided in the technical annex to the first FREL/FRL. No QAQC remeasurement of plots was performed to test for measurement error.
Is signing of a confidentiality declaration required? | Confidentiality declaration text |
---|---|
yes | The confidentiality conditions will be based on the external repository. |
Data available from an external repository. The access conditions will be based on the conditions of the external repository.
Name |
---|
Director of the Department of National Parks, Wildlife and Plant Conservation |
DDI_THA_2013-2017_NFI-R3_v01_M_v01_A_ESS_FAO
Name | Affiliation | Role |
---|---|---|
Statistics Division | Food and Agriculture Organization of the United Nations | Metadata adapted for FAM |