The Effect of a Dam Construction on Subtidal Nematode Communities in the Ba Lai Estuary, Vietnam
Abstract
:1. Introduction
2. Materials and Methods
2.1. Study Area and Sampling Location
2.2. Sampling and Environmental Variable Analysis
2.3. Sampling and Analysis of Nematodes
2.4. Data Processing and Statistical Analysis
3. Results
3.1. Environmental Characteristics of Ba Lai and Ham Luong Estuaries
3.1.1. Water Environmental Characteristics
3.1.2. Sediment Environmental Characteristics
3.2. Nematode Assemblages in Ba Lai and Ham Luong Estuaries
3.2.1. Density of Nematode Communities in Ba Lai and Ham Luong Estuaries
3.2.2. Diversity of Nematode Communities in Ba Lai and Ham Luong Estuaries
3.2.3. Nematode Community Composition in Ba Lai and Ham Luong Estuaries
3.3. Correlation Between Nematode Communities and Environmental Variables
4. Discussion
4.1. Differences in Environmental Variables Related to Dam Effects
4.2. Differences in Nematode Communities Explained by Differences in Environmental Conditions related to Dam Effects
Author Contributions
Funding
Acknowledgments
Conflicts of Interest
Appendix A
Dammed Estuary and Reference Estuary (68.29%) | |||||
---|---|---|---|---|---|
Parodontophora | 7.2 | Metalinhomoeus | 3.56 | Monhystrella | 2.13 |
Theristus | 6.33 | Viscosia | 3.47 | Mononchulus | 2.12 |
Terschellingia | 3.92 | Sphaerotheristus | 3.21 | Comesoma | 1.89 |
Daptonema | 3.74 | Monhystera | 2.68 | Desmodora | 1.89 |
Rhabdolaimus | 3.63 | Mesodorylaimus | 2.58 | Halalaimus | 1.86 |
DD and DU (71.45%) | DD and RD (70.17%) | DD and RU (71.76%) | |||
Theristus | 6.67 | Parodontophora | 6.07 | Parodontophora | 6.59 |
Parodontophora | 5.39 | Pseudochromadora | 3.28 | Theristus | 5.86 |
Rhabdolaimus | 3.48 | Metalinhomoeus | 3.15 | Daptonema | 3.86 |
Metalinhomoeus | 3.25 | Viscosia | 3.06 | Pseudochromadora | 3.38 |
Pseudochromadora | 3.18 | Theristus | 2.7 | Terschellingia | 3.34 |
Terschellingia | 3.02 | Comesoma | 2.5 | Sphaerotheristus | 3.27 |
Monhystera | 2.54 | Trissonchulus | 2.48 | Viscosia | 2.42 |
Mesodorylaimus | 2.16 | Daptonema | 2.42 | Rhabdolaimus | 2.22 |
Daptonema | 2.14 | Marylynnia | 2.15 | Linhystera | 2.11 |
Halalaimus | 2.11 | Terschellingia | 2.03 | Halalaimus | 2.07 |
Linhystera | 2.05 | Amphimonhystrella | 2 | Amphimonhystrella | 2 |
Monhystrella | 2.02 | Halalaimus | 1.99 | Cobbia | 1.77 |
Viscosia | 1.97 | Rhabdolaimus | 1.95 | Oncholaimus | 1.75 |
Udonchus | 1.97 | Desmodora | 1.92 | Mesodorylaimus | 1.72 |
Amphimonhystrella | 1.9 | Sabatieria | 1.88 | Sabatieria | 1.59 |
Afrodorylaimus | 1.76 | Mesodorylaimus | 1.86 | Microlaimus | 1.52 |
Sphaerotheristus | 1.69 | Linhystera | 1.81 | Oxystomina | 1.49 |
Cobbia | 1.67 | Rhynchonema | 1.75 | Desmodora | 1.49 |
Mononchulus | 1.6 | Sphaerotheristus | 1.74 | Spilophorella | 1.44 |
Cobbia | 1.72 | Achromadora | 1.44 | ||
RD and RU (64.91%) | DU and RU (61.45%) | DU and RD (69.79%) | |||
Parodontophora | 9.18 | Parodontophora | 9.05 | Theristus | 8.41 |
Theristus | 8.3 | Theristus | 8.65 | Parodontophora | 7.34 |
Daptonema | 5.77 | Terschellingia | 6.2 | Rhabdolaimus | 5.35 |
Viscosia | 5.57 | Daptonema | 5.73 | Metalinhomoeus | 5.04 |
Sphaerotheristus | 5.04 | Rhabdolaimus | 5.24 | Viscosia | 4.79 |
Metalinhomoeus | 4.69 | Sphaerotheristus | 5.21 | Terschellingia | 4.4 |
Comesoma | 4.34 | Metalinhomoeus | 5.08 | Comesoma | 3.67 |
Terschellingia | 4.31 | Monhystera | 4.63 | Monhystera | 3.43 |
Trissonchulus | 3.9 | Mesodorylaimus | 3.68 | Mesodorylaimus | 3.24 |
Daptonema | 3.2 | ||||
Trissonchulus | 3.1 |
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P Value | |||
---|---|---|---|
Variable | pe | ps | Post Hoc Test |
Salinity | 0.028 | DD ≠ DU: 0.034, DU ≠ RD: 0.035 | |
pH | 0.035 | DD ≠ RU: 0.034, RD ≠ RU: 0.048 | |
DO | 0.037 | 0.026 | |
TSS | 0.034 | ||
TDS | 0.028 | DD ≠ DU: 0.034, DU ≠ RD: 0.035 | |
Pb | 0.035 | ||
Hg | 0.035 | 0.034 | DD ≠ DU: 0.049, DU ≠ RD: 0.044 |
Variable | p Value | |||
---|---|---|---|---|
pe&s | pe | ps | Post hoc Test | |
Density | 0.0466 | 0.028 | DD ≠ DU: 0.034, DU ≠ RD: 0.035 | |
Genus richness | 0.0466 | 0.035 | DD ≠ DU: 0.0001, DD ≠ RD: 0.00026, DD ≠ RU: 0.000003 | |
H’ | 0.0015 | 0.026 | DD ≠ DU: 0.014, DD ≠ RD: 0.0065, DD ≠ RU: 0.0025 | |
Genus composition (square-root transformation) | 0.0003 | 0.0001 | DD ≠ DU: 0.0001, DD ≠ RD: 0.0002, DD ≠ RU: 0.0001, DU ≠ RD: 0.0003, DU ≠ RU: 0.0039, RD ≠ RU: 0.0001 |
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Yen, N.T.M.; Vanreusel, A.; Lins, L.; Thai, T.T.; Nara Bezerra, T.; Quang, N.X. The Effect of a Dam Construction on Subtidal Nematode Communities in the Ba Lai Estuary, Vietnam. Diversity 2020, 12, 137. https://doi.org/10.3390/d12040137
Yen NTM, Vanreusel A, Lins L, Thai TT, Nara Bezerra T, Quang NX. The Effect of a Dam Construction on Subtidal Nematode Communities in the Ba Lai Estuary, Vietnam. Diversity. 2020; 12(4):137. https://doi.org/10.3390/d12040137
Chicago/Turabian StyleYen, Nguyen Thi My, Ann Vanreusel, Lidia Lins, Tran Thanh Thai, Tania Nara Bezerra, and Ngo Xuan Quang. 2020. "The Effect of a Dam Construction on Subtidal Nematode Communities in the Ba Lai Estuary, Vietnam" Diversity 12, no. 4: 137. https://doi.org/10.3390/d12040137