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. 2025 Jul 23;15(7):e71830.
doi: 10.1002/ece3.71830. eCollection 2025 Jul.

Population Dynamics of the Fiddler Crab Tubuca rhizophorae (Tweedie, 1950) in the Mekong Delta, Vietnam

Affiliations

Population Dynamics of the Fiddler Crab Tubuca rhizophorae (Tweedie, 1950) in the Mekong Delta, Vietnam

Anh Ngoc Tran et al. Ecol Evol. .

Abstract

This study investigates the population characteristics of the fiddler crab, Tubuca rhizophorae, at two sites in the Mekong Delta, Vietnam. Monthly samples were collected from March 2024 to February 2025 in Dong Hai, Bac Lieu and Dam Doi, Ca Mau. Population parameters, including asymptotic carapace width (CW = 23.18 mm), growth rate (K = 0.68/year), longevity (approximately 4.41 years), total mortality (3.22/year), natural mortality (1.55/year), fishing mortality (1.69/year), exploitation rate (0.52/year), and carapace width at first capture (CWc = 13.60 mm), were estimated. The results indicate that the T. rhizophorae population exhibits rapid growth, relatively short longevity, and is subject to significant fishing pressure; the exploitation rate was determined to be 0.52/year, which exceeds the E 50 value (0.401). The study also reveals two major annual recruitment peaks occurring at the beginning and end of the year. These findings provide critical baseline data for developing sustainable management strategies for this fiddler crab species, which are crucial for maintaining biodiversity and ecosystem health in the Mekong Delta.

Keywords: Mekong Delta; Tubuca rhizophorae; fiddler crab; growth; mortality.

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Conflict of interest statement

The authors declare no conflicts of interest.

Figures

FIGURE 1
FIGURE 1
Map of sampling sites (•: Sampling site; 1: Dong Hai, Bac Lieu; 2: Dam Doi, Ca Mau).
FIGURE 2
FIGURE 2
Illustration of carapace width (CW) of Tubuca rhizophorae.
FIGURE 3
FIGURE 3
Powell‐Wetherall plots of Tubuca rhizophorae (CW′: Cut off carapace in mm; Yellow data points: Not used; Dark data points: Used).
FIGURE 4
FIGURE 4
Growth curves of Tubuca rhizophorae estimated using ELEFAN I superimposed on restructured corrected carapace width‐frequency data (three curves represented for three cohorts in the population).
FIGURE 5
FIGURE 5
Catch curve based on carapace width for Tubuca rhizophorae (Z = 3.22 year−1, M = 1.55 year−1, F = 1.69 year−1, E = 0.52; Yellow data points: Excluded; Dark data points: Excluded; Open circles represent predicted abundance in partially selected size classes).
FIGURE 6
FIGURE 6
Probability of capture based on carapace width of Tubuca rhizophorae with CW25, CW50, and CW75 thresholds.
FIGURE 7
FIGURE 7
The relative yield‐per‐recruit (solid curve) and relative biomass‐per‐recruit (broken curve) using the knife‐edge selection procedure of Tubuca rhizophorae.
FIGURE 8
FIGURE 8
The relative yield‐per‐recruit isopleth diagram of Tubuca rhizophorae (CWc/CW = 0.617, CWc = 13.6 mm, CW = 23.18 mm, E = 0.52).
FIGURE 9
FIGURE 9
Annual recruitment pattern (%) of the Tubuca rhizophorae population at the study site.

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