1. Introduction
Nan Wan Bay, situated at the southernmost tip of Taiwan, is a well-known tourist destination and a part of the Kenting National Park. The bay is bounded by two capes that extend unequally to the south, as shown in
Figure 1. The west cape, locally known as Mou-Bi-Tou (MBT), does not reach as far south as the east cape, locally known as O-Luan-Bi (OLB). A seamount exists not far off the southeast point of MBT and partially obstructs the north–south passages. Toward the south and southwest, Nan Wan Bay opens up to the Luzon Strait (LS) and the South China Sea (SCS), respectively. The semi-enclosed basin is adjacent to the western Pacific Ocean (WPO) on the east side and the southern end of the Taiwan Strait on the west side. The part of the seamount closest to the surface is at a depth of approximately 50 m [
1]. The bay does not have a clear continental shelf on its west side, but it has a 4 km wide shelf on its east side. Between the seamount to the south and the landmass to the north, the terrain is deep, and this depth extends toward the two capes, forming an open-ended, arc-shaped channel.
The movement of water masses in Nan Wan Bay is primarily governed by robust tidal forces, including diurnal and semidiurnal tides, and is additionally influenced by seasonal monsoons [
3,
4]. In the offshore parts of Nan Wan Bay, during ebb tides, tidal currents typically flow eastward from the southern end of the Taiwan Strait to the western Pacific Ocean through the bay; conversely, they flow westward during flood tides. The tidal range peaks at about 1.6 m during spring tides but decreases to approximately 0.6 m during neap tides. Diurnal and semidiurnal tides have nearly equal energy [
1]. Locally, tidal currents are swift, especially outside the bay. During ebb spring tides, the speed of tidal currents can reach up to 1.7 m/s in and around the bay, especially around MBT, where it has been observed to exceed 2 m/s [
1]. In the continental shelf on the eastern half of the bay, circulation is relatively straightforward during neap tides, typically following the isobaths. However, during flood spring tides, the circulation pattern is more complex due to the appearance of anticyclonic eddies. On the western side of the bay, cyclonic eddies are easily generated in the flow field during ebb tides, irrespective of whether they are spring or neap tides.
Choi and Wilkin [
5] confirmed that thermal plumes, which are characteristic of regions in which the density of water on the surface is low, generally disperse in response to wind forcings [
6]. In winter, northeasterly monsoons usually blow from mid-September to April, peaking in December. Winter monsoons over the local mountain blow down toward the sea surface from the mountaintop. The seaward winds, locally known as downhill winds, become very intense and often lead to the destratification of the water column. The mixing layer’s thickness increases from 30 m in summer to 100 m in winter. Summer monsoons, which are much weaker than winter monsoons, last from July to August. In addition, the sea surface temperature (SST) in Nan Wan Bay is typically in the range of 22–26 °C in winter but 24–29 °C in summer [
1].
Almost without exception, nuclear power plants are always built near a coast or lake because a large amount of seawater is required to cool the reactors of these plants. Seawater is circulated through a nuclear reactor to transfer or remove heat, and the output of this process is thermal waste seawater. This seawater is frequently drained through a long diversion dike into an area near the shore, such as into a bay or an estuary [
3,
7]. The Third Nuclear Power Plant (NP_No. 3) of Taiwan is situated in the inner reaches of Nan Wan Bay, as shown in
Figure 1. Through a long diversion dike, considerable thermal seawater (also known as thermal pollution) is discharged into the bay on the east side of MBT. Thermal wastewater, which is less dense than seawater, typically floats on the sea surface layer and flows back and forth due to tidal currents. The fate of a thermal plume’s dispersal depends on the strength and direction of tidal currents, which features a fortnightly spring–neap cycle. As previously mentioned, the presence of eddies, particularly during spring tides, results in the higher complexity of a flow field.
Hessner et al. [
8] investigated the Rhine outflow plume around the river mouth using 41 synthetic aperture radar (SAR) images and a numerical model. They highlighted that the pattern and locations of the interface outcropping lines near the river mouth are primarily controlled by semidiurnal tides. Additionally, they thought that the factors related to tidal residual currents and river discharge that contribute to the Rhine River plume were of secondary importance. Additionally, by applying different tidal dynamics to distinguish seawater stratification in terms of temporal and spatial features, both regions of strong tidal currents and weak tidal currents were investigated by Huang et al. [
9]. These authors pointed out that thermal plume dispersion from a local power plant affects the area within 3 km around the outlet, and stratification occurs most significantly at 0.5 km–1.0 km from the outlet, where tidal currents are strong. Wei et al. [
10] employed a neural network combined with prior location knowledge to categorize the thermal plume types from 66 nuclear power plants worldwide. Their study indicated that surface plumes larger than 4 km
2 occur frequently in the Great Lakes, whereas smaller surface thermal plumes of less than 1 km
2 occur primarily in estuaries. In addition, employing a numerical model (OGCM) in their study, Lin et al. [
11] reported that winds, tides, and river forcing mainly dominate the behavior of small-scale plumes from the Ying-Yang Bay. In contrast to large-scale plumes, where wind-induced dispersal is primarily driven by Ekman drifts [
6,
12], small-scale plumes tend to disperse in the windward direction. One exception is when a landward wind compresses plume water toward the shore, leading to its dispersal influenced by tidal advection and density forcing. Lin et al.’s [
13] study also highlighted that alongshore tides generate recirculation eddies within the bay during flood and ebb tides. These eddies cause plume movements within the bay that are out of phase with the tidal currents over the shelf. The advection is rather asymmetric to the bay’s axis due to the earth’s rotation. Ho et al. [
14] emphasized that regardless of whether flood or ebb tidal currents are suppressed by strong Asian monsoons, this mechanism helps to prevent the contamination of the harbor’s water quality during northeasterly winds. In contrast, the southwesterly monsoon drives the geostrophic current northward along the coast. Simultaneously, the coastal sea level rises, creating a surface isobar slope up toward the coast, which generates a secondary flow to enhance alongshore geostrophic currents. The northward geostrophic currents deflect the plumes shoreward, resulting in the formation of a relatively narrow-band plume.
In addition to being breeding grounds for countless species of marine life and habitats, coral reefs are very important ecosystems. The coral reefs in Nan Wan Bay are among the most beautiful marine landscapes in Taiwan; they not only provide a breeding ground for marine animals, forming an ecosystem with considerable biodiversity, but also attract many tourists wishing to appreciate and explore this ecosystem. However, the dispersal of the thermal plume from NP_No. 3 conceivably affects the growth and status of this coral reef ecosystem within its vicinity [
15]. Therefore, the objective of the present work is focused on describing the behavior of thermal plume dispersion from NP_No. 3 during spring tides in summer and winter. Since the speed and direction of the local flow fields in Nan Wan Bay change with time, measured data cannot fully capture the comprehensive outline of the thermal plume distribution. Indeed, it is difficult to measure a thermal plume’s location at any given time point when relying solely on CTD samplings and satellite images. Hence, we adopt a numerical model to simulate the flow, temperature, and salinity field of Nan Wan Bay and compare the model results with satellite images. If successfully developed and applied, the circulation model can be used to simulate and evaluate the plume behaviors of thermal wastewater from the NP_No.3. A more detailed description of the model formulation is presented below. The historical data used in this study, including ADCP flow fields, hydrographic data, and other relevant materials, are detailed in
Section 2. The model configuration is introduced in
Section 3.
Section 4 presents the model results, while
Section 5 compares these results with observational data. Following that,
Section 6 also discusses the findings and makes conclusions.
5. Discussion
In this study, we incorporated tides and daily wind forcings into the MITgcm to examine their effects on the thermal plume from the NP_No.3 and its circulation in Nan Wan Bay. Regardless of flow fields or thermal plumes, the model results agree well with the observational data, which comprise satellite images and shipboard ADCP survey data. In terms of the output results, the model captures the major circulation features, which reveal that the current from the west side of MBT flows around MBT into the bay during early ebb tides. The weak ebb current often flows southeastward along the isobaths, running more or less parallel to the coastline, as shown in
Figure 7d,e. As the sea level progresses to the lower low water phase, a well-developed cyclonic eddy covers the western part of Nan Wan Bay and is accompanied by a fast and southeastward-flowing tidal current to the south of MBT. Our model results and the findings of the shipboard ADCP survey both capture the corresponding flow patterns (
Figure 7f and
Figure 9a). The thermal plume characteristics (
Figure 10a,b) derived from the model results correspond to those of the Landsat 8 SST fields in summer, as indicated in
Figure 8b,d,f. To this point, the recirculating flow of a cyclonic eddy, adhering to the inner MBT coast, pushes the thermal plume to stably flow southwestward. We propose that the force pushing the thermal plume southwestward always exists when the sea level is between the higher high water and the mid-lower high water phases, i.e., a cyclonic eddy dominates the ocean circulation on the west side of the bay.
Interestingly, a well-developed anticyclone subsequently covers Nan Wan Bay during the tidal phase between higher low water and higher high water, as shown in
Figure 9b and
Figure 7h, and the currents of the anticyclonic outer ring in the south flow northwestward to impact the thermal water pool at the outlet’s mouth. As a result, this leads to some of the thermal plume being pushed to the northeast by the north-separated branch, as shown in
Figure 8e and
Figure 10e,f. In summer, as the anticyclonic eddy gradually expands, the direction in which the thermal plume disperses appears to become more consistent with the eddy outer-ring circulation, as indicated in
Figure 10f,g. In winter, the strong northeasterly monsoon acts as an opposing force on the sea surface, resulting in the anticyclonic eddy structure being destroyed, as shown in
Figure 9d. As is the case with the prevailing northeasterly monsoon, the northeastward thermal plume is suppressed and further turns to disperse eastward, as indicated in
Figure 11f–h. In summer, the thermal plume in the same phase appears to diffuse to the northeast during the prevailing mild southwesterly monsoon, as shown in
Figure 10f–h. By examining the flushing time of the thermal plume in Nan Wan Bay, insights derived from analyzing
Figure 10,
Figure 11 and
Figure 12 indicate that the thermal plume remains either to the south or north of the outlet mouth for roughly 12 h each. Additionally, two selected model sites to the east and south of the outlet at a distance of approximately 500 m were sampled to illustrate their time series of temperature profiles in both summer and winter, as shown in
Figure 12. In both summer and winter, the thermal plume often exists between the sea surface and a depth of 6 m, floating on the surface layer due to the lighter density of water. During neap tides, the thermal plume consistently surrounds the outlet as it faces limitations in dispersing to distant regions through tidal advection, but an exception to this pattern is observed in the case of the east station in winter, as depicted in
Figure 12c. During spring tides, noticeable amplitude fluctuations can be observed in the appearance or disappearance of the thermal plume in line with the diurnal cycles. Therefore, the flushing time of the thermal plume is estimated to be roughly 10 h at the east station and 6 h at the south station.
In order to understand the interactions between the thermal plume dispersion and the eddies on the west side of the bay in detail, the model south station is selected as an instance to illustrate how the peripheral shear flow of the tide-generated cyclonic eddy influences thermal plume behavior. Examples of continuous traces are given in
Figure 13 and
Figure 14. In
Figure 13b, during neap tides between the 20th and the 25th day in summer, the southward tidal current (approximately 0.2 m/s) slowly carries the thermal plume water to the south or south–southwest. Hence, the water of the south station always keeps up a high temperature at about 30.5 °C on average (
Figure 13a). Conversely, most strong tidal currents during spring tides flow southwestward, and at this time, the peripheral shear flow of the tide-generated cyclonic eddy is generated near the east side of MBT. At the beginning, the southward shear flow carries the thermal water flowing southward, giving rise to the increase in water temperature. Subsequently, the strong shear flow readily dilutes the thermal water, immediately leading to decreased water temperature. For instance, the 28th day in
Figure 13a is a typical example. In winter, as a whole, the winter situation is similar to that in summer.
The water in
Figure 14a maintains a higher temperature at roughly 26 °C between the 20th and the 25th day during neap tides, and at this time, the slow shear flow of the model south station is flowing to the south in
Figure 14b. Therewith, most of the tidal currents during spring tides flow southwestward, and the circulating shear flow of the tide-generated cyclonic eddy carries the thermal plume from the outlet to the southwest. Meanwhile, the northeast monsoon enhances the strength of the tidal currents to dilute the thermal water, resulting in a rapid decrease in water temperature, such as the 26th day in
Figure 14a. Because of the prevailing northeast monsoon in winter, the northeastward tidal currents, in opposition to the direction of the monsoon wind stress, are barely visible and much weaker, with shorter durations. The high-temperature pulse becomes sharper in winter than in summer, as shown in
Figure 13 and
Figure 14.
The model stations around the outlet at a distance of approximately 500 m were sampled to create the rose diagrams displayed in
Figure 15. As indicated in
Figure 15a, the thermal plume is highly likely to disperse to the southwest (43%) in summer, although there is also a small probability of it drifting to the southeast (15%) or northeast (10.5%) because of the influence of the gentle southwesterly monsoon. In winter, as shown in
Figure 15b, the thermal plume is most likely to disperse to the southwest (40.5%) and highly unlikely to disperse to the northeast (3.5%) or southeast (5.5%) due to influence of the prevailing northeasterly monsoon.
To estimate the degree of influence of the thermal plume after one tidal cycle, the horizontal distribution of the plume is comprehensively estimated in terms of the equivalent depth of the thermal plume,
, defined as [
5]
where
Ta is an average or reference temperature representative of the typical coastal water of the bay,
T(
z) is the temperature of the water column,
η means sea level, and here,
h is 10 m at the bottom depth of the locally thermal water column. In summer, the distribution of the equivalent depth of thermal plume during neap tides is shown in
Figure 16a. When the winds blow the mild southwest monsoons over the bay in summer, the thermal water readily accumulates to form a semicircle bulge around the outlet, particularly during the neap tides, due to the lack of swift advection and dilution to far fields. The equivalent depth of the thermal plume after one tidal cycle gradually decreases with increasing distance from the outlet mouth (roughly 3 m thick). However, its distribution of equivalent depth still deflects to the southwest due to the influence of the weakly southwestward tidal currents, even existing in the outer of MBT, as given in
Figure 16a. On the contrary, during spring tides, the rapid current dilutes some of the thermal water flowing to the southwest, resulting in a situation where the thermal water equivalent depth to the southwest of the outlet becomes thinner, as depicted in
Figure 16b.
Overall, the distribution range of the equivalent depth of the thermal plume during neap tides is notably smaller compared with that observed during spring tides in summer, with a tendency for distribution toward the northeast. In winter, during neap tides, the distribution range of the equivalent depth of the thermal plume is significantly smaller than during summer neap tides, with its distribution also deflected toward the southwest. During spring tide, the distribution range of the equivalent depth is even smaller than during neap tide, as illustrated in
Figure 16c,d.
6. Conclusions
The primary objective of this study is to demonstrate how monsoons and a pair of counter-rotating eddies affect flow fields and how they alter the dispersion of the thermal plume from the NP_No.3 outlet. In this study, we incorporated tides and daily wind forcings into the MITgcm to examine their effects on the thermal plume from NP_No.3 and its circulation in Nan Wan Bay. The model results from the stick diagram analysis indicate that during summer, the probability of coastal currents flowing southwest along the eastern side of MBT is approximately 82%, and during winter, this probability increases to about 84%. Apart from the dominant southwest direction, tidal currents are almost exclusively oriented toward the northeast. Conceivably, the thermal plume from the NP_No.3 outlet either disperses to the southwest or the northeast, driven by local tidal currents. The rose diagrams reveal that the thermal plume is highly likely to disperse to the southwest (43%) in summer, although there is also a small probability of it drifting to the northeast (10.5%) as a result of the influence of the breezy southwest monsoon. During the winter northeast monsoon, there is a notable tendency for the thermal plume to disperse to the southwest (40.5%), with only a 3.5% probability of dispersion to the northeast. During spring tides, the equivalent depth of the thermal plume gradually decreases with increasing distance from the outlet mouth (approximately 3 m thick), and its distribution range of equivalent depth still deflects to the southwest, even extending to the outer part of MBT in summer. During the winter northeasterly monsoon, the distribution range of the equivalent depth of the thermal plume during neap tides is significantly smaller than during summer neaps. Moreover, similar to spring tides, its distribution also deviates toward the southwest direction during winter spring tides.
In conclusion, it is worth emphasizing that strong tidal currents generate a pair of counter-rotating eddies that predominantly influence the dispersion of the thermal plume, and seasonal monsoons also play an essential role in modifying the plume’s direction and dispersion.