Experimental Validation of Float Array Tidal Current Measurements in Agate Pass, Washington

Trevor W. Harrison aUniversity of Washington, Seattle, Washington

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Nate Clemett aUniversity of Washington, Seattle, Washington

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Brian Polagye aUniversity of Washington, Seattle, Washington

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Jim Thomson aUniversity of Washington, Seattle, Washington

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Abstract

Tidal currents, particularly in narrow channels, can be challenging to characterize due to high current speeds (>1 m s−1), strong spatial gradients, and relatively short synoptic windows. To assess tidal currents in Agate Pass, Washington, we cross evaluated data products from an array of acoustically tracked underwater floats and from acoustic Doppler current profilers (ADCPs) in both station-keeping and drifting modes. While increasingly used in basin-scale science, underwater floats have seen limited use in coastal environments. This study presents the first application of a float array toward small-scale (<1 km), high-resolution (<5 m) measurements of mean currents in energetic tidal channel and utilizes a new prototype float, the μFloat, designed specifically for sampling in dynamic coastal waters. We show that a float array (20 floats) can provide data with similar quality to ADCPs, with measurements of horizontal velocity differing by less than 10% of nominal velocity, except during periods of low flow (0.1 m s−1). Additionally, floats provided measurements of the three-dimensional temperature field, demonstrating their unique ability to simultaneously resolve in situ properties that cannot be remotely observed.

Significance Statement

The purpose of this research was to validate measurements of tidal currents in a fast-flowing tidal channel using a prototype technology composed of 20 drifting underwater sensors called μFloats (“microFloats”) and five surface buoys against standard devices (acoustic Doppler current profilers). Float measurements matched those from the standard devices within 10% of the mean water speed and simultaneously provided three-dimensional mapping of temperature in the test region. Results demonstrate how moderate numbers of simultaneously deployed μFloats can provide high-resolution sensing capacity that will improve our understanding of physical, chemical, and biological processes in coastal waters.

© 2023 American Meteorological Society. For information regarding reuse of this content and general copyright information, consult the AMS Copyright Policy (www.ametsoc.org/PUBSReuseLicenses).

Corresponding author: Trevor W. Harrison, twharr@uw.edu

Abstract

Tidal currents, particularly in narrow channels, can be challenging to characterize due to high current speeds (>1 m s−1), strong spatial gradients, and relatively short synoptic windows. To assess tidal currents in Agate Pass, Washington, we cross evaluated data products from an array of acoustically tracked underwater floats and from acoustic Doppler current profilers (ADCPs) in both station-keeping and drifting modes. While increasingly used in basin-scale science, underwater floats have seen limited use in coastal environments. This study presents the first application of a float array toward small-scale (<1 km), high-resolution (<5 m) measurements of mean currents in energetic tidal channel and utilizes a new prototype float, the μFloat, designed specifically for sampling in dynamic coastal waters. We show that a float array (20 floats) can provide data with similar quality to ADCPs, with measurements of horizontal velocity differing by less than 10% of nominal velocity, except during periods of low flow (0.1 m s−1). Additionally, floats provided measurements of the three-dimensional temperature field, demonstrating their unique ability to simultaneously resolve in situ properties that cannot be remotely observed.

Significance Statement

The purpose of this research was to validate measurements of tidal currents in a fast-flowing tidal channel using a prototype technology composed of 20 drifting underwater sensors called μFloats (“microFloats”) and five surface buoys against standard devices (acoustic Doppler current profilers). Float measurements matched those from the standard devices within 10% of the mean water speed and simultaneously provided three-dimensional mapping of temperature in the test region. Results demonstrate how moderate numbers of simultaneously deployed μFloats can provide high-resolution sensing capacity that will improve our understanding of physical, chemical, and biological processes in coastal waters.

© 2023 American Meteorological Society. For information regarding reuse of this content and general copyright information, consult the AMS Copyright Policy (www.ametsoc.org/PUBSReuseLicenses).

Corresponding author: Trevor W. Harrison, twharr@uw.edu

1. Introduction

Tidal currents play a central role in our coastal waters, impacting water quality (Deppe et al. 2013; Defne and Ganju 2015), larval transport (Mahadevan 2016), algae blooms (Livingston 2000), marine navigation (Cheng and Smith 1998; Chen et al. 2013), and energy production (Blunden and Bahaj 2007; Polagye and Thomson 2013). Driven by astronomical forcing, tides are predictable on a decadal time scale; however, the resulting water movements are less predictable (Godin 1983). Local bathymetry can produce currents exceeding 4 m s−1, strong horizontal and vertical heterogeneity, and significant variability over a matter of minutes (McCaffrey et al. 2015). Waterway management, ecosystem health monitoring, and improved scientific understanding all benefit from accurate characterization of local currents on horizontal spatial scales O(0.1–10) km, vertical scales O(0.1–100) m, and time evolution from O(minutestomonths).

Since their introduction in the early 1980s, acoustic Doppler current profilers (ADCPs) have become the standard instrument for measuring water velocity (Dickey et al. 1998). ADCPs produce estimates of 3D velocity at discrete distances from the instrument head by emitting a ping from three to five diverging transducers and measuring the Doppler shift on echoes returned from scattering sources in the water (e.g., particulate, bubbles) (Teledyne RDI 2019). A flexible instrument, ADCPs have been deployed on stationary platforms such as bottom landers (Guerra et al. 2017) and moored buoys (Mayer et al. 2007), as well as on mobile platforms such as autonomous underwater vehicles (An et al. 2001; Brown et al. 2011; Mullison et al. 2011; Todd et al. 2017), vessels (Geyer and Signell 1990; Willcox et al. 2001), and drifting surface buoys (Guerra and Thomson 2016; Shcherbina et al. 2018; Guerra et al. 2021). Stationary deployments provide long-duration O(daystomonths) time series essential for extracting tidal harmonic constituents at a given site (Foreman et al. 1995; Polagye and Thomson 2013; Jin et al. 2018). However, the spatial coverage of this strategy is limited. Conversely, mobile deployments can map horizontal variations in water velocity (Geyer and Signell 1990), though they are time limited to O(hourstodays). Corrections for platform motion such as translation velocity or heave can be achieved via bottom tracking (i.e., using acoustic reflections from the seafloor to estimate and account for horizontal instrument velocity) and/or through integration with GPS and inertial measurement units. Such correction techniques are commonly included in commercial systems (Muste et al. 2004; Fong and Monismith 2004; Heitsenrether et al. 2018; Velasco and Nylund 2019). Doppler noise can also reduce accuracy, but is addressed by averaging multiple independent samples (Lu and Lueck 1999; Teledyne RDI 2019). For stationary platforms, this is an effective solution, but for mobile platforms, averaging convolves spatial and temporal variability, resulting in a direct trade-off between spatial coverage and accuracy.

Underwater floats have a long history in oceanography (Gould 2005). The Argo program, with nearly 4000 floats distributed worldwide, and over a million profiles taken over the 20-yr program history, has provided incomparable data on ocean state variables (salinity, pressure, and temperature), as well as unprecedented resolution of ocean circulation patterns (Jayne et al. 2017). Given the demonstrated success for basin-scale problems, there is growing interest in extending this distributed sensing paradigm to smaller-scale coastal processes. To meet this need, a number of new buoyancy-controlled floats have been developed specifically to operate in the stronger density gradients, shallow and variable bathymetry, and faster currents present in coastal environments (McGilvray and Roman 2010; Roman et al. 2011; Jaffe et al. 2017). For example, Jaffe’s group deployed an array to measure larval dispersion resulting from interactions with internal waves (Jaffe et al. 2017; Garwood et al. 2020) and Roman’s group developed a system with increased actuation and bottom-tracking ability for coastal bathymetric surveys (McGilvray and Roman 2010; Roman et al. 2011). In Harrison et al. (2020), virtual experiments comparing float arrays and mobile ADCP surveys suggested that float arrays may provide similar accuracy when performing three-dimensional mapping of horizontal water velocity while simultaneously gathering in situ water property data (e.g., temperature, salinity, dissolved oxygen). Encouraged by that result, Harrison et al. (2023) developed the μFloat system to investigate this observational paradigm in practice.

This paper presents an experimental comparison of three-dimensional measurements of horizontal water velocity produced by a μFloat array (∼20 floats) to data from four drifting, downward-looking ADCPs and a station-keeping, vessel-mounted ADCP. Section 2 describes the test site, equipment, and data processing methods. Section 3 presents the observed site characteristics and comparisons across platforms. Implications of the outcomes are discussed in section 4.

2. Methods

a. Site description

Agate Pass, Washington (Figs. 1a,b), is a tidal channel in Puget Sound, Washington, bordered on the south by Bainbridge Island and on the north by the Kitsap Peninsula. The channel connects Port Madison, a bay (40–60 m deep) that is part of the main basin of Puget Sound, to Port Orchard, a shallower (20–30 m deep) strait separating Bainbridge Island from the Kitsap Peninsula. Tides in the region are mixed semidiurnal, with water level ranges reaching 4 m in Port Madison. At its narrowest point, Agate Pass is only 300 m wide and 9 m deep, and produces currents that exceed 2 m s−1 during periods of peak exchange. As a result of these high flow speeds, the site is of interest for tidal energy development, which motivated its selection for this study.

Fig. 1.
Fig. 1.

Map of (a) Puget Sound and (b) Agate Pass. Station-keeping (SK) locations are indicated in (b) and remained the same during ebb and flood. (c),(d) Initial drifting instrument positions during ebb and flood, respectively, with ∼20 μFloats deployed at regular intervals along the indicated line.

Citation: Journal of Atmospheric and Oceanic Technology 40, 4; 10.1175/JTECH-D-22-0034.1

b. Instruments

1) Vessel-mounted ADCP

Figure 2a depicts the RDI Workhorse Mariner (1200 kHz) four-beam ADCP mounted on a pole for deployment. Five-minute station-keeping surveys at three locations (Fig. 1b, SK1–3) were repeated during each deployment period. During these surveys, the vessel operator held station to within 50 m of the target location. To compensate for residual motion, the RDI VMDAS software integrated bottom track velocities from the ADCP to convert the measurements from a moving reference frame into a fixed reference frame. Ancillary GPS data recorded in VMDAS were integrated to provide positions and time stamps for the measurements. The raw ADCP data were sampled at 2 Hz and assembled into 15-s ensemble profiles. These profiles were screened to retain broadband Doppler correlations above 50% and trimmed to remove spurious values below the seafloor based on bottom-tracking depth. The ensemble horizontal velocity uncertainty was 0.017 m s−1. For each station and survey cycle, we compute the mean of all ensemble profiles taken within 25 m of the nominal station-keeping location, typically 20–30 total profiles over 5–7 min, as well as the standard deviation of these profiles as a measure of local variability. This short-term station-keeping strategy provided sufficient samples to reduce Doppler noise in the ensemble averages, while allowing moderate horizontal coverage (Palodichuk et al. 2013).

Fig. 2.
Fig. 2.

Primary instruments used in this survey: (a) a vessel-mounted ADCP, (b) 4 SWIFTs, (c) 20 μFloats, and (d) 5 surface localization buoys (SLBs).

Citation: Journal of Atmospheric and Oceanic Technology 40, 4; 10.1175/JTECH-D-22-0034.1

2) SWIFTs

The SWIFT (Fig. 2b) is a drifting surface buoy equipped with a downward-facing Nortek Signature1000 five-beam ADCP, Sutron Xpert datalogger and processing board, and SBG Ellipse GPS and inertial navigation system (INS) (Thomson 2012; Thomson et al. 2019). An Airmar WX200 provides supplementary wind speed and direction. The ADCP collected 1-Hz data in broadband mode during 512-s bursts. These repeated every 720 s (i.e., five bursts per hour), with the intermediary period used for onboard processing of the ADCP data. The ADCP was configured to collect data in 40 depth bins with a resolution of 0.5 m and a 0.35 m blanking distance. In postprocessing, the drift velocity of the buoy was added to the observed profiles to estimate the true velocity profile in a fixed reference frame. The velocity profiles were trimmed to remove values beyond the seafloor using an altimeter return from the center beam. Then, 30-s ensemble averages of the drift-corrected profiles were calculated, resulting in effective uncertainty of 0.005 m s−1 (Guerra and Thomson 2017). We note that for the highest drift speed of 2 m s−1, the ensembles effectively average over 60 m of along-track positions.

3) μFloats and surface localization buoys

The μFloat (Fig. 2c) is a prototype underwater float developed specifically for coastal environments (Harrison et al. 2023). Equipped with a solid-piston buoyancy engine, the float can change its density by 9%, providing vertical actuation speeds of ± 0.5 m s−1 and depth-holding accuracy within ±20 cm in quiescent water. Primary sensors include pressure (used for depth control), temperature, and an inertial measurement unit (IMU). The large buoyancy engine capacity allows for the addition of external sensors with minimal reballasting. When on the surface, the μFloats broadcast their GPS location via cellular and radio signals to facilitate recovery.

An array of five GPS-equipped surface localization buoys (SLBs) are deployed concurrently to track the μFloats while underwater (Fig. 2d). SLBs and μFloats are equipped with small acoustic “nanomodems” (Fenucci et al. 2018; Neasham 2018). The surface buoys broadcast uniquely coded pings on a round-robin schedule. All nanomodems within range record and time stamp these pings. In postprocessing, sent and received pings are aligned and time of flight is calculated from the associated time stamps. Distances between each source and receiver are then estimated based on sound speed. Sets of three or more pings from unique surface buoys are used to trilaterate float position (Norrdine 2012). Position data are smoothed by a robust moving local regression with a moving window size between 60 and 240 s, adjusted for each float depending on ping connectivity rates to ensure that at least 80% of the regression windows along the track included a minimum of 10 individual position points. Velocity is estimated by a first-order central difference of smoothed position data. Resulting position and velocity uncertainty is ±15 m and ±0.06 m s−1, respectively. Additional details on the localization process are presented in Harrison et al. (2023). To provide an apples-to-apples comparison with SWIFT data, we subsequently apply the same 30-s ensemble averaging procedure to the float and SLB tracks, reducing position and velocity uncertainty to ∼3 m and ∼0.01 m s−1.

During each survey cycle, between 18 and 20 floats were deployed. Two floats were lost during the experiment, with one subsequently recovered. For a given deployment, all floats were programmed to either hold constant depth or repeatedly profile between the surface and a target depth. Constant depth deployments were intended to provide consistent observational distributions. Profiling deployments were used to ensure along-track localizations by “bread crumbing” GPS data in case of poor acoustic connectivity, with the awareness that such a method may smear horizontal velocity measurements vertically through the water column. As the μFloats are prototype instruments, 16 out of 175 total float drifts were rendered invalid due to malfunctions (mechanical, electrical, or software) or human programming errors. Also, roughly 2.5 float drifts were excluded due to suspected float interactions with the seabed, determined by manual review of the IMU data. Consequently, analytical results from each survey cycle consisted of data from 14 to 18 floats, with the exact number indicated where relevant.

4) Water properties

A hand-deployed Xylem CastAway CTD was used to measure profiles of temperature and salinity. Derived quantities of density and sound speed were also provided by the instrument. One profile was collected during each survey cycle, though position ranged between SK3 and SK2, depending on flow speed and direction. Each cast took about 30 s to perform. The sound velocity data at this position were assumed representative of the channel and used to localize all μFloats during the survey cycle.

c. Deployment layouts and times

On 20 August 2020, four surveys were performed during ebb tide (E1–E4) and five during flood tide (F1–F5) for a total of nine surveys, each indicated by the gray regions in Fig. 3. Surveys were performed by two small vessels (10 m), each with a pilot and two crew members. The μFloats were programmed for underwater survey periods lasting 20 min, the approximate time necessary to traverse the region of interest at a speed of 1.5 m s−1. Survey start times were chosen to coincide with the beginning of SWIFT data collection intervals to maximize data overlap in the region of interest. Approximately three minutes prior to the start of the survey period, the vessels performed a coordinated deployment of the drifting devices, following the layout stencils shown in Figs. 1c and 1d. One vessel primarily deployed SWIFTs and upstream SLBs while the other vessel deployed the μFloats and downstream SLBs. For float deployments, the vessel maintained a steady, low speed (3 m s−1), and floats were tossed overboard every 5 s, providing an approximate cross-stream resolution of 15–20 m. For profiling surveys, maximum depths were assigned based on the anticipated cross-channel deployment location and corresponding water depth (accounting for tidal variation in water level). For constant depth surveys, target depths were similarly varied cross channel: every three to four floats were assigned a set of target depths that covered 1 m below the surface to 1 m above the bottom (based on the intended deployment location) in order to resolve cross-stream variation in the vertical velocity gradient. SLBs were deployed around floats with the goal of maintaining robust connectivity of the nanomodems. Based on lessons learned about drift rates and paths during each survey cycle, SLB and SWIFT placements were adjusted to improve correspondence with μFloat tracks. In addition, during two of the flood tests, an SLB was caught in an eddy and required manual relocation back into the main channel to ensure continued connectivity.

Fig. 3.
Fig. 3.

Predicted water level and tidal currents over the test day. Survey periods are indicated in light gray. Dark gray vertical lines indicate slack tide.

Citation: Journal of Atmospheric and Oceanic Technology 40, 4; 10.1175/JTECH-D-22-0034.1

After all instruments were deployed, the first vessel executed the station-keeping ADCP surveys, while the second vessel drifted downstream with the SWIFTs, μFloats, and SLBs. The CTD profiles were also acquired during this drifting period. Once the μFloats resurfaced and the station-keeping measurements were completed, both vessels participated in recovery efforts. Most instruments were found by sight, but locating some μFloats relied on reference to a custom-built cellular-based GPS tracking app. Once all instruments were recovered, they were redistributed to their respective deployment vessel, vessels returned upstream, floats were reprogrammed with a new start time, and the process began again. Because of the variable time required to recover all the instruments, the interval between surveys was irregular (Fig. 3). Recovery and reset during ebb tide typically took longer (∼1 h), with some instruments washing ashore on the north side of the channel and requiring assistance from friendly beach walkers, and some traveling out into Port Madison, where larger waves inhibited visual location of the μFloats. During flood tide surveys, most instruments converged within a small area, resulting in faster recovery and reset times (∼40 min).

d. Data analysis

To evaluate the effectiveness of μFloat data against SWIFT and station-keeping ADCP data, we compared horizontal velocity measurements across platforms in the following three modes: 1) time evolution, 2) vertical profiles, and 3) horizontal gradients. Additionally, we used these data to describe the spatial and temporal current variations in Agate Pass.

We examined the mean-flow time evolution by comparing measurements from all three instrument platforms against the NOAA current prediction (NOAA 2020). NOAA predictions are provided at 2.7 m (9 ft) depth relative to mean lower low water (MLLW) at a location approximately 50 m NE from SK2. NOAA generates these predictions using harmonic analysis (Parker 2007), with constituents derived from a 2015 ADCP deployment at that location (Kammerer et al. 2021). As all instruments sample in a surface-relative coordinate frame, they must be shifted to an MLLW-reference coordinate frame by subtracting the time-varying water level. To compute the water level for each survey cycle, we interpolated the depth relative to MLLW from NOAA bathymetric data (NOAA 2010) at SK2. We then subtracted this nominal depth from the bottom-tracking depths measured by the vessel-keeping ADCP during the survey cycle and calculated the mean to produce the nominal water level for the given survey. This water level was then used to shift sample positions of all platforms to the MLLW-reference frame. For all platforms, SK2 served as the reference location for comparison to the NOAA predictions. For SWIFT data, the nearest profile within 150 m of SK2 was interpolated at 2.7 m depth. For μFloat data, all samples within 50 m horizontal radius of SK2 were binned by depth (0.5 m bin width) and bin averaged to produce a vertical profile. The profile was then linearly interpolated at 2.7 m depth. During slack tide (E4), no μFloat samples were obtained near the NOAA prediction location. Note that for all other interplatform comparisons, data were left in surface-referenced coordinates.

To examine vertical structure, we compared velocity profiles from all platforms at each station-keeping location, using vessel-mounted ADCP data as reference ground truth. For SWIFT data, the closest profile within 50 m of the station-keeping location was selected. For μFloats, we assembled all 30-s-averaged μFloat data into a three-dimensional distance-weighted interpolation function. We queried the interpolation function at the station-keeping locations at 0.5 m depth intervals from surface to seafloor. Due to insufficient coverage during ebb deployments, interpolation at SK3 was not possible. To exclude erroneous interpolation near the water surface, the μFloat profiles were clipped to the depth of the shallowest μFloat sample within 100 m.

To extend these comparisons over the entire channel, the μFloat array data were compared to the SWIFT data. The interpolation functions constructed from μFloat data were queried at each SWIFT data point. Median, interquartile range, and interdecile range of the difference between SWIFT and array measurements were computed from all samples in a given survey cycle. The median absolute difference (MAD) serves as the overall figure of merit.

To examine the horizontal distribution of horizontal velocity magnitude, we interpolated the array data at 2 m depth over the entire domain. The nominal horizontal extent of the μFloat samples was identified using MATLAB’s “boundary” function, adjusting the “shrink” parameter to produce a realistic boundary. No extrapolations were made outside this boundary.

To compare the spatial coverage provided by the array relative to the SWIFTs, we computed the horizontal and vertical sample distributions for each platform across all survey cycles. Horizontal coverage was defined as the area within the μFloat sample boundary. Horizontal resolution was computed by spatially binning samples taken by the given platform onto a uniform grid with 100 m resolution and reported as the mean number of unique samples per grid cell. For SWIFTs, one profile was counted as one horizontal sample. Vertical resolution is similarly computed by vertically binning samples in 1 m depth bins and reported as the mean number of samples per bin for the given survey and platform.

3. Results

a. Time evolution

Figure 4 shows the time evolution of water level (Fig. 4a) and horizontal velocity (Fig. 4b) as compared with NOAA predictions, as well as the observed sound speed (Fig. 4c) and density profiles (Fig. 4d) taken during each survey cycle. A phase lag of about 1 h is evident in both water level and maximum ebb velocity, though not on the flood. The observed water velocity accelerates more quickly on flood than predicted, indicating the presence of a nonharmonic feature of the tidal currents (Parker 2007). This discrepancy relative to the NOAA prediction is unsurprising, given that harmonic analysis inherently removes such features as noise (Parker 2007), and was also observed in prior bottom-mounted ADCP measurements (Wang and Yang 2017). Overall, sound speed and density profiles are consistent in time. The mild sound speed and density gradients on ebb and slack (E4) surveys derive from a slight thermocline (Figs. 4c,d), indicating that the shallower waters of Port Orchard are warmer than Puget Sound. Additionally, the more uniform sound speed profile is favorable for acoustic localizations (i.e., the sound speed profile does not trap SLB localization pings above float depth).

Fig. 4.
Fig. 4.

Time evolution of (a) water level estimated from vessel-keeping ADCP and (b) horizontal velocity measured from all devices, as compared to NOAA prediction. Profiles of (c) sound speed and (d) water density were taken during each survey cycle.

Citation: Journal of Atmospheric and Oceanic Technology 40, 4; 10.1175/JTECH-D-22-0034.1

b. Vertical profiles

Figure 5 depicts the depth-varying water speed at each station-keeping location as a function of time. As is typical for open-channel flows, currents are strongest at the surface and diminish with depth. The velocity profiles observed are blunt, with velocities diminishing only 10%–25% from surface to near-seabed during all periods excepting slack tide (E4). Qualitatively, the velocity profiles derived from the μFloat data match the SWIFT and vessel-keeping profiles over most sites and surveys (e.g., SK1 during F1–F5 and SK2 during E2 and F2–F4), often within the observed variability at the location. Due to the variable coverage of the drifting platforms, there are insufficient samples within each survey and station-keeping to perform a robust statistical evaluation of patterns of difference between vessel, SWIFT, and μFloat profiles at this local level.

Fig. 5.
Fig. 5.

Current speed versus depth at each station-keeping location. Variable coverage and deployment locations resulted in insufficient data for float profiles at SK3 during ebb, and all stations at slack (E4), Similarly, SWIFT coverage was insufficient for various surveys and locations. Light blue indicates local variability measured by the station-keeping ADCP, and the gray box indicates the water depth at each location and time.

Citation: Journal of Atmospheric and Oceanic Technology 40, 4; 10.1175/JTECH-D-22-0034.1

An examination of the difference between SWIFT and float measurements across all surveys (Fig. 6) reveals MADs within about 10% of the nominal velocity (with the exception of slack tide E4, where flow speed is near zero). Additionally, no significant difference is observed between profiling (E1, E3, F1, F3, F5) and depth-tracking (E2, E4, F2, F4) float control modes.

Fig. 6.
Fig. 6.

Horizontal velocity measurement differences (m s−1) between SWIFTs and μFloats over tidal cycle. The white lines, thick gray bars, and thin gray lines indicate median, interquartile range, and interdecile range, respectively, evaluated over nEval samples. Percentage difference is mean absolute deviation (MAD)/speed.

Citation: Journal of Atmospheric and Oceanic Technology 40, 4; 10.1175/JTECH-D-22-0034.1

c. Coverage and resolution

As evident in the profile data, the SWIFTs and μFloats provide variable spatial coverage resulting from changes in deployment distribution and advection trajectories. Figures 7 and 8 offer an interplatform comparison of float and SWIFT sampling during a representative ebb (E2) and flood (F4) deployment, respectively. Because both SWIFTs and floats were deployed at similar streamwise locations and distributed evenly across the channel, the across-channel measurement extents are roughly equivalent and the along-channel extents are proportional to the advective velocity (Table 1). While the SWIFTs provide about twice as many samples as the float array (Table 1), they are horizontally sparse. Thus, the float array provides better horizontal resolution than the SWIFTs, as shown in Figs. 7a, 7c, 8a, and 8c. The SWIFTs provide consistent vertical resolution of 0.5 m from surface to the sea floor, with full range up to 20 m (Figs. 7b and 8b). Vertical coverage provided by the floats is less consistent and coarser, with sampling determined either by the set of depths for constant-depth floats (Fig. 7d), or the maximum depth for profiling floats (Fig. 8d). Profiling mode does appear to offer better distribution of vertical samples (Table 1), but may vertically average horizontal velocity in locations with stronger vertical shear than Agate Pass.

Fig. 7.
Fig. 7.

Distribution of (a),(b) SWIFT and (c),(d) float samples during E2 deployment. Gaps in SWIFT data occur during onboard processing periods. Floats were programmed to hold constant depth during this survey cycle. Note that (b) and (d) are projected onto the northing ordinate, with west pointing into the page. The light gray line in (a) and (c) indicates a 6 m depth contour. The dark gray line in (b) and (c) indicates bathymetry along the thalweg.

Citation: Journal of Atmospheric and Oceanic Technology 40, 4; 10.1175/JTECH-D-22-0034.1

Fig. 8.
Fig. 8.

Distribution of (a),(b) SWIFT and (c),(d) float samples during F4 deployment. Floats were programmed to profile during this survey. Note that (b) and (d) are projected onto the northing ordinate, with east pointing into the page. The gray line indicates bathymetry along the thalweg.

Citation: Journal of Atmospheric and Oceanic Technology 40, 4; 10.1175/JTECH-D-22-0034.1

Table 1

Sampling statistics for SWIFTs and μFloats over tidal cycle.

Table 1

d. Horizontal distribution of currents

Figure 9 shows the horizontal velocity magnitude at 2 m depth over the domain, as resolved by the float array. During the ebb tide (E2, E3), the flow accelerates as it enters the channel, with peak currents observed in the center of the channel. On the flood tide (F3, F4), both the distributions (Figs. 9c,d) and constituent floats trajectories (e.g., Fig. 8c) reveal a jet exiting the south end of the channel and extending along the thalweg of the bay (for bathymetry, refer to Fig. 1b).

Fig. 9.
Fig. 9.

Horizontal distribution of currents at 2 m depth, as interpolated from μFloat array data, for surveys (a) E1, (b) E2, (c) F3, and (d) F4. The light gray line indicates a 6 m depth contour.

Citation: Journal of Atmospheric and Oceanic Technology 40, 4; 10.1175/JTECH-D-22-0034.1

e. Eddies

Examination of the μFloat tracks during F3 and F4 reveal circular trajectories on the southeastern edge of the jet, indicating eddies shed from the jet (Fig. 10). Approximately five minutes after entering the eddies, the floats began recovery mode, and consequently surfaced and rejoined the primary flow. This behavior, along with the variations in trajectory with float depth (e.g., during F3, the three floats that were entrained in the eddy were at 2, 4, and 5 m) suggests a subsurface flow feature with depth-varying structure.

Fig. 10.
Fig. 10.

Float tracks during flood surveys (a) F3 and (b) F4 showed evidence of entrainment in eddies shedding from channel jet. The light gray line indicates a 6 m depth contour. (c),(d) Detail of float trajectories in the region of the probable eddy. Only a subset of tracks are shown for clarity and include floats at multiple depths. Note that this is the full-resolution float data, rather than the 30-s averages used for comparison with ADCP data, and dark gray lines connect float positions for visual continuity.

Citation: Journal of Atmospheric and Oceanic Technology 40, 4; 10.1175/JTECH-D-22-0034.1

4. Discussion

Note that the focus of this experiment was on short-duration surveys that captured the spatial structure (horizontal and vertical) of horizontal tidal currents in a small survey area O(1)km.

a. Characteristics of agate pass tidal currents

The nine surveys provide significant spatial and temporal details of the tidal current at the south end of Agate Pass, a domain roughly 2 km long and varying from 300 m across the channel to 1 km across Port Orchard.

Since tides here are mixed semidiurnal, ebb and flood velocities vary considerably throughout the lunar month: a full site characterization would require repeated surveys over multiple days. The surveys presented here only resolved one strong exchange from peak ebb to peak flood. Flow dynamics and the resulting horizontal and vertical gradients for weaker exchanges are expected to be different. As floats may quickly leave the area of interest and thus require near-constant supervision, they are not well-suited for long-duration surveys to extract tidal constituents. Such a task is better suited to bottom-mounted, stationary ADCPs for vertical resolution (McMillan and Hay 2017), shore-mounted X-band radar systems for horizontal resolution (Bell et al. 2012), or coastal acoustic tomography (Kaneko et al. 1994; Elisseeff et al. 1999; Zhang et al. 2017), though the last is better suited to larger-scale horizontal structures (5–10 km range, 100 m resolution). A comprehensive characterization of flow conditions could be achieved by collecting distributed samples (such as that from SWIFTs and float arrays) over several days that included a representative range of tidal current magnitudes, and coupling those measurements with continuous, multimonth data from a bottom-mounted ADCP.

b. Interplatform comparison

In general, we see agreement between horizontal water velocity inferred from μFloat trajectories and velocity measured by station-keeping and drifting ADCPs. This suggests that the μFloats track with the local water movements with negligible relative motion, such that they can provide horizontally and vertically distributed measurements of horizontal water velocity with accuracy comparable to ADCPs. Evidence of μFloat Lagrangian behavior is bolstered by individual float tracks that suggest entrainment in depth-varying eddies (Fig. 10). However, since the μFloats are actively controlling depth, they cannot be considered fully Lagrangian, particularly with regards to measuring vertical motion.

The μFloat array provides more economic sampling coverage and horizontal resolution than the four SWIFTs, as the array and SLBs collective cost ($75,000) is approximately one-quarter that of four SWIFTS ($300,000), albeit with some notable caveats. First, recovery of 25 drifting instruments—especially the μFloats which are smaller and harder to see—takes much more time than recovery of four SWIFTs. By deploying only SWIFTs, the intersurvey gaps could be reduced, thus increasing temporal coverage and total samples. Also, SWIFT recovery is not restricted by the preprogrammed time interval (as on the floats), allowing more flexible deployment schedules and locations. Conversely, the floats capture Lagrangian dynamics the ADCPs cannot easily resolve, such as the eddy tracks observed during surveys F2 and F3.

A common concern for Lagrangian sampling methods is convergence of the drifting devices, thus oversampling convergence zones while undersampling divergent zones (e.g., Ohlmann et al. 2017). The short surveys implemented here avert this problem: the float sample distribution remains strongly correlated to initial position and dive depth, which is directly controlled. Longer deployments may require active manipulation of float positions midsurvey to mitigate uneven sampling.

c. Contributions from SLBs

While the SLBs are necessary for localizing the μFloats, they are themselves surface drifters. Thus, if their motion is Lagrangian, their track data can be combined with the μFloat data to augment array coverage, providing velocity data at the surface that are not captured by the μFloats. To assess this possibility, we evaluated SLB track data in the same manner as SWIFT and μFloats (30-s averages, first-order central difference) to derive surface velocity estimates and interpolated them at the station-keeping locations (Fig. 5). The results agree with surface velocities measured by the SWIFTs within ± 0.06 m s−1 (median absolute difference), suggesting that both devices acted as Lagrangian drifters in the near-surface currents. Such dynamics are not guaranteed due to potential for wind-induced relative motion. The surface expression of the SLBs is large relative to the subsurface expression (∼1:1 ratio). As a result, even light winds can generate relative velocities between the SLB and surface currents, as was observed in quiescent flow lake tests when benchmarking the μFloat system (Harrison et al. 2023). Thus, SLB tracks can provide additional useful information, though careful consideration of wind effects is critical when integrating SLB and μFloat data. Last, given the need to deploy SLBs with the μFloat array, a clear next step would be merging the capabilities of the SWIFTs into the SLBs, thus providing an efficient multiplatform site characterization method.

d. In situ distributed array sampling

As discussed in Harrison et al. (2020), an important benefit of a Lagrangian float array is the potential to obtain in situ data that, unlike velocity, cannot be remotely sensed. The μFloats are all equipped with a temperature sensor (Blue Robotics, ±0.1°C accuracy, 1-s response time). Figure 11 shows the vertical temperature gradients estimated from μFloat data over all surveys. To produce these estimates, we depth binned the float data at 0.5 m resolution, then performed a distance-weighted average of samples within 100 m of the CTD profile location (e.g., black circles in Fig. 12). The μFloat data match the CTD within ±0.1° ± 0.1°C (median absolute deviation over all samples in Fig. 11), with differences likely attributable to spatial interpolation, given the site exhibits cross-channel gradients of 0.5°–1.5°C. Figure 12 displays float trajectories during surveys F2–F5, colored by temperature. These reveal a consistent temperature gradient across the channel, with water cooler on the southern edge and warmer on the northern, which may be indicative of water originating from different locations in Puget Sound. While further benchmarking of μFloat temperature measurements is required, this is a compelling demonstration of distributed array measurements that capture vertical and horizontal gradients of in situ properties.

Fig. 11.
Fig. 11.

Temperature profiles estimated from the μFloats relative to CTD measurements.

Citation: Journal of Atmospheric and Oceanic Technology 40, 4; 10.1175/JTECH-D-22-0034.1

Fig. 12.
Fig. 12.

Horizontal distributions of temperature as measured by the μFloats during surveys (a) F2–(d) F5. Note that float depths vary along the tracks, but temperature during flood is well-mixed vertically, as seen in Fig. 11. Black circles indicate the 100 m boundary for samples used in profile reconstructions in Fig. 11, F2–F5.

Citation: Journal of Atmospheric and Oceanic Technology 40, 4; 10.1175/JTECH-D-22-0034.1

Additionally, one μFloat was equipped with a downward facing camera (GoPro Session 5) and LED dive lights for opportunistic benthic composition surveys between SK2 and SK3. The resulting imagery was of variable quality, but did show that bottom composition in the area of the channel with strong currents was primarily scoured to cobble, as expected for high energy sites. A video taken during slack tide east of this region revealed a sandy bottom populated by crabs, starfish, and a few fish—evidence that flow in that area remains low throughout the tidal cycle. However, two control behaviors of the μFloat degrade the quality of benthic surveys. First, the buoyancy engine motor induces considerable rotational motion while holding depth. Second, because the float holds constant depth, the relative distance to bottom is difficult to assess and the size of objects on the bottom is ambiguous. Addition of an altimeter, as implemented by Roman et al. (2011), would improve these results, as would a control algorithm that reduces actuation. Additional details are available in the online supplementary materials.

5. Conclusions

Here, we have described the first tidal channel deployment of the μFloat array in Agate Pass over a series of nine survey cycles performed from ebb to flood, during which maximum observed currents exceeded 2 m s−1. While the hydrodynamics of Agate Pass are not scientifically novel, the results are technologically compelling. Measurements of horizontal velocity magnitude derived from the μFloats matched those from the four drifting SWIFT ADCPs to within 10% of the nominal flow speed. The array was also able to resolve vertical gradients in agreement with those measured by stationary and drifting ADCPs, while providing 2–4 times the horizontal resolution of the drifting ADCPs over the same region, all with lower instrument cost. Additionally, the μFloats provided in situ temperature measurements that approximately matched those from CTD profiles and were able to resolve strong horizontal gradients. This suggests that low-cost, coastal floats are capable of gathering scientifically relevant data in energetic flows. The potential benefits extend beyond current measurements demonstrated here: as a modular platform, the μFloats can be adapted to measure salinity, dissolved oxygen, turbidity, or underwater sound. Such spatially and temporally resolved measurements would significantly enhance our ability to resolve a variety of physical, biological, and chemical conditions and processes in coastal waters.

Acknowledgments.

The authors would like to acknowledge Alex de Klerk, E.J. Rainville, and Zachary Tully for providing essential help during the Agate Pass field work. All color maps used here came from the cmocean library (Thyng et al. 2016). We also thank three anonymous reviewers for their thoughtful feedback. The μFloat was developed based upon funds from NSF Graduate Research Fellowship (DGE-1762114) and array construction supported by ONR DURIP (N00014-17-1-2336). Agate Pass field work was funded by the U.S. DOD Naval Facilities Engineering Command (N0002410D6318/N0002418F8702). The authors have no conflicts of interest to disclose.

Data availability statement.

The data and software supporting this work are openly available in University of Washington–ResearchWorks Archive at http://hdl.handle.net/1773/48360.

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Supplementary Materials

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  • An, E., M. R. Dhanak, L. K. Shay, S. Smith, and J. Van Leer, 2001: Coastal oceanography using a small AUV. J. Atmos. Oceanic Technol., 18, 215234, https://doi.org/10.1175/1520-0426(2001)018<0215:COUASA>2.0.CO;2.

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  • Bell, P. S., J. Lawrence, and J. V. Norris, 2012: Determining currents from marine radar data in an extreme current environment at a tidal energy test site. 2012 IEEE Int. Geoscience and Remote Sensing Symp., Munich, Germany, IEEE, 76477650, https://doi.org/10.1109/IGARSS.2012.6351856.

  • Blunden, L. S., and A. S. Bahaj, 2007: Tidal energy resource assessment for tidal stream generators. Proc. Inst. Mech. Eng., 221A, 137146, https://doi.org/10.1243/09576509JPE332.

    • Search Google Scholar
    • Export Citation
  • Brown, J., C. Tuggle, J. MacMahan, and A. Reniers, 2011: The use of autonomous vehicles for spatially measuring mean velocity profiles in rivers and estuaries. Intell. Serv. Rob., 4, 233, https://doi.org/10.1007/s11370-011-0095-6.

    • Search Google Scholar
    • Export Citation
  • Chen, C., S. Shiotani, and K. Sasa, 2013: Numerical ship navigation based on weather and ocean simulation. Ocean Eng., 69, 4453, https://doi.org/10.1016/j.oceaneng.2013.05.019.

    • Search Google Scholar
    • Export Citation
  • Cheng, R. T., and R. E. Smith, 1998: A nowcast model for tides and tidal currents in San Francisco Bay, California. Ocean Community Conf., Baltimore, MA, Marine Technology Society, 537–543, https://pubs.er.usgs.gov/publication/70174365.

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    • Search Google Scholar
    • Export Citation
  • Deppe, R. W., J. Thomson, B. Polagye, and C. Krembs, 2013: Hypoxic intrusions to Puget Sound from the ocean. 2013 OCEANS, San Diego, CA, IEEE, https://doi.org/10.23919/OCEANS.2013.6741234.

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    • Search Google Scholar
    • Export Citation
  • Fenucci, D., A. Munafo, A. B. Phillips, J. Neasham, N. Gold, J. Sitbon, I. Vincent, and T. Sloane, 2018: Development of smart networks for navigation in dynamic underwater environments. 2018 IEEE/OES Autonomous Underwater Vehicle Workshop, Porto, Portugal, IEEE, https://doi.org/10.1109/AUV.2018.8729779.

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    • Search Google Scholar
    • Export Citation
  • Foreman, M. G., W. R. Crawford, and R. F. Marsden, 1995: De-tiding: Theory and practice. Quantitative Skill Assessment for Coastal Ocean Models, D. R. Lynch and A. M. Davies, Eds., Coastal and Estuarine Studies, Vol. 47, 203–203, https://doi.org/10.1029/CE047p0203.

  • Garwood, J. C., A. J. Lucas, P. Naughton, M. H. Alford, P. L. D. Roberts, J. S. Jaffe, L. DeGelleke, and P. J. S. Franks, 2020: A novel cross-shore transport mechanism revealed by subsurface, robotic larval mimics: Internal wave deformation of the background velocity field. Limnol. Oceanogr., 65, 14561470, https://doi.org/10.1002/lno.11400.

    • Search Google Scholar
    • Export Citation
  • Geyer, W. R., and R. Signell, 1990: Measurements of tidal flow around a headland with a shipboard acoustic Doppler current profiler. J. Geophys. Res., 95, 31893197, https://doi.org/10.1029/JC095iC03p03189.

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  • Fig. 1.

    Map of (a) Puget Sound and (b) Agate Pass. Station-keeping (SK) locations are indicated in (b) and remained the same during ebb and flood. (c),(d) Initial drifting instrument positions during ebb and flood, respectively, with ∼20 μFloats deployed at regular intervals along the indicated line.

  • Fig. 2.

    Primary instruments used in this survey: (a) a vessel-mounted ADCP, (b) 4 SWIFTs, (c) 20 μFloats, and (d) 5 surface localization buoys (SLBs).

  • Fig. 3.

    Predicted water level and tidal currents over the test day. Survey periods are indicated in light gray. Dark gray vertical lines indicate slack tide.

  • Fig. 4.

    Time evolution of (a) water level estimated from vessel-keeping ADCP and (b) horizontal velocity measured from all devices, as compared to NOAA prediction. Profiles of (c) sound speed and (d) water density were taken during each survey cycle.

  • Fig. 5.

    Current speed versus depth at each station-keeping location. Variable coverage and deployment locations resulted in insufficient data for float profiles at SK3 during ebb, and all stations at slack (E4), Similarly, SWIFT coverage was insufficient for various surveys and locations. Light blue indicates local variability measured by the station-keeping ADCP, and the gray box indicates the water depth at each location and time.

  • Fig. 6.

    Horizontal velocity measurement differences (m s−1) between SWIFTs and μFloats over tidal cycle. The white lines, thick gray bars, and thin gray lines indicate median, interquartile range, and interdecile range, respectively, evaluated over nEval samples. Percentage difference is mean absolute deviation (MAD)/speed.

  • Fig. 7.

    Distribution of (a),(b) SWIFT and (c),(d) float samples during E2 deployment. Gaps in SWIFT data occur during onboard processing periods. Floats were programmed to hold constant depth during this survey cycle. Note that (b) and (d) are projected onto the northing ordinate, with west pointing into the page. The light gray line in (a) and (c) indicates a 6 m depth contour. The dark gray line in (b) and (c) indicates bathymetry along the thalweg.

  • Fig. 8.

    Distribution of (a),(b) SWIFT and (c),(d) float samples during F4 deployment. Floats were programmed to profile during this survey. Note that (b) and (d) are projected onto the northing ordinate, with east pointing into the page. The gray line indicates bathymetry along the thalweg.

  • Fig. 9.

    Horizontal distribution of currents at 2 m depth, as interpolated from μFloat array data, for surveys (a) E1, (b) E2, (c) F3, and (d) F4. The light gray line indicates a 6 m depth contour.

  • Fig. 10.

    Float tracks during flood surveys (a) F3 and (b) F4 showed evidence of entrainment in eddies shedding from channel jet. The light gray line indicates a 6 m depth contour. (c),(d) Detail of float trajectories in the region of the probable eddy. Only a subset of tracks are shown for clarity and include floats at multiple depths. Note that this is the full-resolution float data, rather than the 30-s averages used for comparison with ADCP data, and dark gray lines connect float positions for visual continuity.

  • Fig. 11.

    Temperature profiles estimated from the μFloats relative to CTD measurements.

  • Fig. 12.

    Horizontal distributions of temperature as measured by the μFloats during surveys (a) F2–(d) F5. Note that float depths vary along the tracks, but temperature during flood is well-mixed vertically, as seen in Fig. 11. Black circles indicate the 100 m boundary for samples used in profile reconstructions in Fig. 11, F2–F5.

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