Journal of Resources and Ecology >
Assessing Vulnerability to Environmental Changes of Freshwater Crab, Thaipotamon chulabhorn in the Dun Lumpun Non-Hunting Area, Thailand
Arika BRIDHIKITTI, E-mail: arika.bri@mahidol.edu |
Received date: 2023-01-29
Accepted date: 2023-04-30
Online published: 2023-08-02
Thaipotamon chulabhorn (Mealy Crab) is a freshwater crab, listed as ‘Least Concerned’ in the IUCN Red List of Threatened Species. Nonetheless, this crab is exclusively found in one small area of the Dun Lumpun Forest, Thailand, and currently faces high exposure to environmental changes. This study aims to investigate key dynamic factors that influence vulnerability to environmental changes of the Mealy Crab. The study was conducted between 15 March and 23 October 2016, covering the local summer until the end of the rainy season and being influenced by strong El Niño, thus suggesting drought episodes. This vulnerability assessment was carried out through crab population records from 1997 to 2016, field measurements/surveys, and interviews with experienced park rangers. The results revealed that drought is the major vulnerability factor that is threatening the population of the crabs and their livelihoods (7.96 out of 10), followed by an increased number of their natural enemies (7.41), variations in groundwater level (6.11), changes in groundwater quality (4.63), changes in forest soil (4.63) and human intervention (4.26). Since 1996, human intervention has been found to have a little direct impact on the crab population due to the restricted access to forest resources. The 2016 drought was accompanied by anomalously low rainfall and the early onset of the rainy season, contributing to an earlier and shorter mating period of the crabs. Nonetheless, a consistently increased number of the Mealy Crab population indicated that they are not significantly vulnerable to a larger number of their natural enemies, and even to the changes in groundwater and forest soil. In conclusion, the crab population was increasing along with changes in the habitat and climate and its growth cycle was unusual during the drought.
Arika BRIDHIKITTI , Bidur KHADKA , Suraj SHARMA . Assessing Vulnerability to Environmental Changes of Freshwater Crab, Thaipotamon chulabhorn in the Dun Lumpun Non-Hunting Area, Thailand[J]. Journal of Resources and Ecology, 2023 , 14(5) : 1092 -1103 . DOI: 10.5814/j.issn.1674-764x.2023.05.020
Fig. 1 Sampling sites in Dun Lumpun Non-Hunting Area |
Fig. 2 Hole configuration and scavenging zone |
Table 1 Weight, dimensions and sex distribution of the observed Mealy Crabs |
Weight (g) | Number | Carapace dimension (cm) | |||
---|---|---|---|---|---|
Female | Male | Upper length | Lower length | Width | |
10-15 | 3 | 3 | 2.17 | 2.33 | |
16-20 | 2 | 3.5 | 2.38 | 2.63 | |
21-25 | 5 | 5 | 3.63 | 2.44 | 2.99 |
26-30 | 5 | 4 | 3.87 | 2.74 | 3.09 |
31-35 | 8 | 8 | 3.95 | 2.83 | 3.27 |
36-40 | 2 | 4 | 4.24 | 3.15 | 3.4 |
41-47 | 2 | 4.4 | 3.15 | 3.25 |
Fig. 3 Colors of the crabs on different dates (a) first day and (b) fifth day in the exhibition zone |
Fig. 4 Percentage of active crabs in the exhibition zone |
Table 2 Biomass deposition rate (g m-2 d-1) and percent distribution of species accounting to total biomass (in 2016) |
Scientific name | Common name | Site 1 | Site 2 | Site 3 | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Mar 15th- May 20th | Jul 2nd- Aug 14th | Sep 18th - Oct 23rd | Mar 15th - Apr 9th | Apr 9th - May 20th | Jul 1st - Aug 14th | Sep 18th -Oct 23rd | Mar 15th -Apr 9th | Apr 9th -May 20th | Jul 3rd- Aug 14th | Sep 18th- Oct 23rd | ||
Biomass deposition rate (g m-2 d-1) | 0.684 | 0.535 | 0.633 | 7.111 | 0.141 | 3.207 | 0.701 | 8.533 | 1.852 | 0.893 | 0.426 | |
Bambusa arundinacea Willd. | Phai paa | 11.34 | 0.67 | 0.74 | 1.89 | |||||||
Diospyros mollis Griff. | Ebony tree | 14.43 | 8.02 | 21.74 | ||||||||
Casearia grewiaefolia Vent | Kruai Paa | 4.12 | 2.16 | 22.64 | 14.13 | |||||||
Alangium salviifolium (L.f.) Wangerin. subsp. Hexapetalum Wangerin | Pruu | 11.34 | 7.69 | 15.83 | 0.22 | 9.63 | 11.98 | 9.90 | 20.28 | 3.26 | 36.36 | 57.89 |
Terminalia alata Heyne ex Roth. | Laurel | 7.22 | 1.92 | 1.57 | 5.93 | 1.98 | 2.36 | 5.43 | 5.26 | |||
Spatholobus parviflorus (DC.) Kuntze | Thao phan saai | 1.03 | 2.92 | 7.41 | 0.99 | 3.77 | ||||||
Streblus asper Lour. | 24.74 | 89.21 | 31.11 | 10.89 | ||||||||
Eugenia cumini Druce | 3.09 | 10.37 | 1.84 | 1.98 | 14.62 | 27.17 | 54.55 | 31.58 | ||||
Maytenus marcanii (Craib) Ding Hau | Naam daeng | 16.49 | 21.15 | 2.70 | 11.85 | 0.47 | 6.52 | 2.63 | ||||
Cryptolepis buchananii Roem. & Schult. | Thao en on | 2.06 | 9.62 | 0.72 | 6.67 | 1.84 | 16.83 | 0.94 | 1.09 | 2.63 | ||
Olax scandens Roxb. | 4.12 | 2.70 | ||||||||||
Cassia siamea Lamk. | Thai Copper Pod | 13.46 | 26.86 | 68.20 | 30.69 | |||||||
Vitex pinnata Linn. | Teen nok | 3.85 | 23.02 | 12.59 | 9.43 | 14.13 | ||||||
Uvaria rufa Blume | 3.85 | |||||||||||
Diospyros montana Roxb. | Ma Kluea paa | 25.00 | 26.62 | 3.70 | 14.29 | 15.84 | 6.13 | |||||
Streptocaulon juventas (Lour.) Merr. | 1.92 | 1.38 | ||||||||||
Osbecfia chiuensis Linn. | En aa noi | 0.46 | 2.97 | 4.55 | ||||||||
Artocarpus lakoocha Roxb. | Haat | 6.13 | ||||||||||
Pluchea indica (L.) Less. | Indian March Fleabane | 3.30 | 2.17 | 4.55 | ||||||||
Capparis sepiaria Linn. | Naam wua sang | 2.17 | ||||||||||
Others | 11.54 | 10.79 | 7.92 | 2.17 |
Fig. 5 Time-series crab population and annual rainfall (left) and number of crab population against its corresponding annual rainfall (right) |
Fig. 6 Locations of observation wells and Nong Dun wetland (upper) and crab spatial distribution maps from several studies (lower) |
Fig. 7 Groundwater depth taken from 2-m depth wells (left) and groundwater level from the surface taken from 5-m depth wells (right)Note: * The observation well 5 has no depth information. |
Fig. 8 Groundwater quality and quantity observed at well 5 |
Table 3 Physical and chemical characteristics of soils from the Dun Lumpun forest and its adjacent areas |
Area | Site description | Depth | pH | OC (%) | Soil texture | Soil color | Hydraulic conductivity (μm s‒1) | Bulk soil density (g cm‒3) |
---|---|---|---|---|---|---|---|---|
Dun Lumpun Forest | Site 1: Forest soil | Surface | 8.00 | 2.5-2.75 | Silty Clay Loam | 7.5YR 2.5/1 Black | 1.1‒1.8 | 1.25 |
Underground | 8.35 | 1.5-2.25 | Clay Loam | 7.5 YR 3/1 Very dark gray | ‒ | ‒ | ||
Site 2: Forest soil | Surface | 8.15 | 2.25-2.5 | Clay Loam | 7.5 YR 3/1 Very dark gray | 3.2 | 0.97 | |
Underground | 8.13 | 2.5-2.75 | Clay Loam | 7.5 YR 3/1 Very dark gray | ‒ | ‒ | ||
Site 3: Forest soil | Surface | 8.27 | 2.25-2.5 | Silty Clay Loam | 7.5YR 2.5/1 Black | 0.9 | 1.07 | |
Underground | 8.26 | 2.25-2.5 | Silty Clay Loam | 7.5YR 2.5/1 Black | ‒ | ‒ | ||
Forest soil | Surface | 6.40 | 2.5-2.75 | Clay Loam | 7.5 YR 3/1 Very dark gray | 2.1 | 1.00 | |
Soils near the Dun Lumpun Forest | Grassland soil | Surface | 10.30 | 0-0.25 | Loamy Sand | 2.5YR 4/6 Red | 10.03 | 1.80 |
Dry Dipterocarp forest soil | Surface | 5.50 | 1.25-1.5 | Loamy Sand | 2.5YR 4/2 Weak Red | 9.27 | 1.92 | |
Rice field soil | Surface | 7.60 | 0.25-0.5 | Loam | 7.5YR 2.5/2 Very dark brown | ‒ | ‒ | |
Rice field soil | Surface | 8.20 | 0.5-0.75 | Loam | 7.5YR 2.5/1 Very dark brown | ‒ | ‒ | |
Rice field soil | Surface | 7.90 | 1.25-1.5 | Loamy Sand | 2.5YR 4/2 Weak red | ‒ | ‒ | |
Rice field soil | Surface | 8.30 | 1.5-2.25 | Sandy Clay Loam | 7.5 YR 3/1 Very dark gray | ‒ | ‒ | |
Rice field soil | Surface | 7.30 | 0-0.25 | Loamy Sand | 2.5YR 4/2 Weak red | ‒ | ‒ |
Note: ‒ means not measured. |
[1] |
Department of National Park, Wildlife and Plant Conservation, Ministry of Natural Resource and Environment Thailand. 2003. Crab population survey report for the year 2003 during May 15th-23rd, 2003, Dun Lumpun Non-Hunting Area. Ministry of Natural Resource and Environment (Thailand).
|
[2] |
|
[3] |
|
[4] |
Mahasarakham University. 1997. Study and investigation of biodiversity conservation in natural habitats in Mahasarakham Province. A final report submitted to the Department of Environmental Policy and Planning, Ministry of Science, Technology and Environment, Thailand.
|
[5] |
NOAA National Oceanic and Atmospheric Administration. 2016. Multivariate ENSO Index (MEI). Washington DC: Department of Commerce of USA.
|
[6] |
|
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