Significance of Submarine Groundwater Discharge in Nutrient Budgets in Tropical Sanya Bay, China
Abstract
:1. Introduction
2. Materials and Methods
2.1. Study Area
2.2. Sampling and Measurements
2.3. Radium Mass-Balance Model and Apparent Water Age Estimation
3. Results
3.1. Radium Isotopes in Sanya Bay
3.2. Parameters of the Estuary Water and of the Groundwater
4. Discussion
4.1. Apparent Water Age in Sanya Bay
4.2. SGD Estimation Using Radium Isotopes
4.3. Nutrient Fluxes Via SGD into Sanya Bay and Their Contributions to the Nutrient Budgets
Acknowledgments
Author Contributions
Conflicts of Interest
Appendix A
FSGD_226Ra (m3 d−1) | 2.16 × 102 | 2.46 × 105 | 4.08 × 105 | 1.25 × 106 | 3.86 × 105 | 1.39 × 106 |
FSGD_228Ra (m3 d−1) | 3.32 × 102 | 4.69 × 105 | 1.11 × 105 | 2.35 × 106 | 1.18 × 106 | 2.67 × 106 |
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Station | Latitude | Longitude | Water Depth (m) | Temp (°C) | Salinity | 223Ra | σ | 224Ra | σ | 226Ra | σ | 228Ra | σ |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
dpm 100 L−1 | |||||||||||||
J1 | 18.2718 | 109.4565 | 8 | 22.80 | 33.60 | 1.79 | 0.20 | 33.86 | 0.36 | 10.81 | 0.45 | 33.73 | 1.30 |
J2 | 18.2623 | 109.4423 | 9 | 22.66 | 33.62 | 0.80 | 0.13 | 21.52 | 0.68 | 10.50 | 0.39 | 31.74 | 1.09 |
J3 | 18.2531 | 109.4298 | 12 | 22.70 | 33.64 | 1.56 | 0.16 | 30.04 | 0.38 | 10.91 | 0.50 | 37.95 | 1.44 |
J4 | 18.2409 | 109.4118 | 11 | 22.81 | 33.70 | 0.60 | 0.14 | 11.92 | 0.40 | 10.78 | 0.39 | 28.24 | 1.02 |
J5 | 18.2261 | 109.3909 | 15 | 22.90 | 33.70 | 0.52 | 0.15 | 17.61 | 0.89 | 10.19 | 0.41 | 28.02 | 1.10 |
W1 | 18.2555 | 109.4832 | 5 | 23.12 | 33.70 | 1.36 | 0.23 | 26.66 | 0.39 | 12.04 | 0.49 | 30.35 | 1.23 |
W2 | 18.2466 | 109.4672 | 12 | 22.93 | 33.72 | 0.83 | 0.13 | 12.88 | 0.32 | 10.92 | 0.41 | 26.22 | 1.02 |
W3 | 18.2306 | 109.4413 | 16 | 22.97 | 33.89 | 0.59 | 0.13 | 11.93 | 0.53 | 10.63 | 0.43 | 23.11 | 1.06 |
W4 | 18.2154 | 109.4244 | 5 | 23.12 | 33.70 | 0.52 | 0.11 | 12.82 | 0.30 | 10.73 | 0.39 | 24.03 | 0.98 |
P1 | 18.2355 | 109.4940 | 5 | 22.98 | 33.62 | 1.22 | 0.19 | 42.60 | 0.85 | 11.93 | 0.54 | 28.87 | 1.34 |
P2 | 18.2296 | 109.4797 | 11 | 23.01 | 33.67 | 0.97 | 0.17 | 23.57 | 0.34 | 10.56 | 0.49 | 31.94 | 1.27 |
P3 | 18.2213 | 109.4660 | 16 | 22.75 | 33.84 | 0.54 | 0.13 | 15.49 | 0.59 | 10.99 | 0.41 | 24.26 | 1.08 |
P4 | 18.2105 | 109.4464 | 12 | 22.71 | 33.89 | 0.77 | 0.11 | 15.32 | 0.36 | 10.83 | 0.32 | 28.14 | 0.85 |
P5 | 18.1931 | 109.4296 | 26 | 22.69 | 33.81 | 1.38 | 0.11 | 18.51 | 0.65 | 10.95 | 0.33 | 28.90 | 0.89 |
L1 | 18.2219 | 109.4812 | 7 | 22.76 | 33.84 | 0.65 | 0.10 | 13.65 | 0.40 | 9.71 | 0.42 | 26.42 | 1.15 |
L2 | 18.2193 | 109.4812 | 11 | 22.81 | 33.85 | 0.74 | 0.11 | 22.99 | 0.67 | 11.98 | 0.44 | 26.33 | 1.16 |
L3 | 18.2201 | 109.4749 | 12 | 22.79 | 33.84 | 0.78 | 0.11 | 14.49 | 0.28 | 9.77 | 0.41 | 25.24 | 1.06 |
L4 | 18.2105 | 109.4674 | 20 | 22.76 | 33.85 | 0.70 | 0.11 | 13.82 | 0.42 | 10.59 | 0.42 | 25.53 | 1.13 |
L5 | 18.2111 | 109.4582 | 21 | 22.74 | 33.85 | 1.17 | 0.13 | 17.63 | 0.33 | 11.27 | 0.38 | 25.90 | 0.96 |
L6 | 18.1965 | 109.4694 | 23 | 22.79 | 33.82 | 0.84 | 0.12 | 16.34 | 0.38 | 10.21 | 0.43 | 23.77 | 0.95 |
L7 | 18.1966 | 109.4601 | 32 | 22.83 | 33.86 | 0.84 | 0.18 | 14.26 | 0.76 | 10.53 | 0.41 | 26.03 | 1.08 |
L8 | 18.1964 | 109.4476 | 25 | 22.78 | 33.88 | 0.43 | 0.15 | 12.18 | 0.40 | 9.58 | 0.43 | 27.01 | 1.20 |
H1 | 18.2348 | 109.4977 | nd * | 22.88 | 31.70 | 1.69 | 0.50 | 64.75 | 0.74 | 15.45 | 0.70 | 43.75 | 1.85 |
LE01 | 18.0000 | 110.0000 | 96 | 29.62 | 33.33 | nd | nd | nd | nd | 5.92 | 0.42 | 11.70 | 1.42 |
Parameter | Value | Unit | Reference | ||
---|---|---|---|---|---|
Estuary | FR | River discharge | 0.88 | m3 s−1 | [24,25] |
226RaR | Estuary water 226Ra | 15.5 ± 0.7 | dpm 100 L−1 | This study | |
228RaR | Estuary water 228Ra | 43.8 ± 1.9 | |||
CTSM | Concentration of total suspended matter | 25.33 | mg L−1 | ||
fd | Fraction of desorbed radium from particles | 0.43 | - | [37] | |
226Rap | 226Ra on particles | 2.5 | dpm g−1 | [36] | |
228Rap | 228Ra on particles | 2.09 | |||
Sediment | 228Fsed | 228Ra diffusive flux | 2.1 | dpm m−2 d−1 | |
226Fsed | 226Ra diffusive flux | 0.27 | [8] | ||
Groundwater | 226RaGW | Groundwater 226Ra | 246 ± 36 | dpm 100 L−1 | This study |
228RaGW | Groundwater 228Ra | 435 ± 18 | |||
Sanya Bay | 226RaB | Bay water 226Ra | 10.75 ± 0.66 | ||
228RaB | Bay water 228Ra | 27.81 ± 3.59 | |||
VB | Volume of the bay investigated | 1.04 × 109 | m3 | ||
AB | Surface area of the bay investigated | 6.49 × 107 | m2 | ||
τ | Residence time | 7.2 ± 3.2 | day | ||
Ocean | 226RaO | Ocean water 226Ra | 5.92 ± 0.42 | dpm 100 L−1 | |
228RaO | Ocean water 228Ra | 11.70 ± 1.42 |
Radium | Formula in Equation (1) | Value | Unit | ||
---|---|---|---|---|---|
226Ra | Sources | Sanya River | FR·226RaR | 1.17 × 107 | dpm d−1 |
FR·fd·226Rap·CTSM | 2.07 × 106 | ||||
Sediment diffusion | AB·226Fsed | 4.24 × 107 | |||
Groundwater | FSGD·226RaGW | 6.87 × 109 | |||
Sink | Mixing | VB·(226RaB − 226RaO)/τ | 6.93 × 109 | ||
228Ra | Sources | Sanya River | FR·228RaR | 3.32 × 107 | |
FR·fd·228Rap·CTSM | 1.73 × 106 | ||||
Sediment diffusion | AB·228Fsed | 1.01 × 109 | |||
Groundwater | FSGD·228RaGW | 2.21 × 1010 | |||
Sink | Mixing | VB·(228RaB − 228RaO)/τ | 2.31 × 1010 |
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Share and Cite
Wang, G.; Wang, S.; Wang, Z.; Jing, W. Significance of Submarine Groundwater Discharge in Nutrient Budgets in Tropical Sanya Bay, China. Sustainability 2018, 10, 380. https://doi.org/10.3390/su10020380
Wang G, Wang S, Wang Z, Jing W. Significance of Submarine Groundwater Discharge in Nutrient Budgets in Tropical Sanya Bay, China. Sustainability. 2018; 10(2):380. https://doi.org/10.3390/su10020380
Chicago/Turabian StyleWang, Guizhi, Shuling Wang, Zhangyong Wang, and Wenping Jing. 2018. "Significance of Submarine Groundwater Discharge in Nutrient Budgets in Tropical Sanya Bay, China" Sustainability 10, no. 2: 380. https://doi.org/10.3390/su10020380