4. Discussion
Using efficient MHK turbines [
24] to harvest tidal energy at locations with high power density [
4] is a state-of-the-art undertaking but less intensive use of tidal energy is not a new thing. Humans have exploited energy of the turning tide ever since they began to use fishing weirs and marine craft [
26]. Recently an intertidal fishing weir in Minas Basin was used to quantify fish species found in Minas Basin [
9]. The basic principle of a fishing weir is to collect fish that would otherwise pass by with the tide, and that is a conceptual starting point for quantifying an upper bound on the number of fish that might interact with an operating MHK turbine in Minas Passage.
To extract tidal energy, MHK turbines can be mounted to some stationary platform [
2]. If one were to replace the MHK turbine with a net that spans the same cross-current area
swept by the turbine blades then the fish caught could be considered to approximate the number of individuals (belonging to captured species) that might pass through the operating turbine. Such measurements of the flux of fish through
are in the Eulerian frame [
15]. Ecologists have similarly attempted to use active hydroacoustic devices to monitor backscatter from targets in a water volume similar to that which fluxes through
but it has not proven possible to enumerate individuals or identify species from the backscatter observed in Minas Passage [
18]. Optical cameras provide much higher resolution [
28] and visibility may be sufficient in Minas Passage for cameras to identify a subset of those fish that an active hydroacoustic device detected upstream as backscatter.
It would be most useful if the above Eulerian methods successfully measured the number of individuals (for some species) that might encounter a MHK turbine, but that would still leave outstanding issues. From a population point of view, what matters is not so much the number that encounter a MHK turbine, but rather the proportion of a local population that encounters a MHK turbine. That proportion is difficult to calculate from catch/backscatter numbers because the local population number is not known for any of the species captured by [
9]. Also, sometimes two fish belonging to the same species may belong to different populations [
11]. Such difficulties can be resolved by using acoustic tags [
10,
11] to track individuals belonging to a known population, which amounts to measuring in the Lagrangian frame [
15]. Tagging studies have been published for striped bass of Shubenacadie River origin [
10], Atlantic sturgeon that mostly originate from the Saint John River, New Brunswick [
11], and alewife of the Gaspereau River stock [
29]. Inner Bay of Fundy Atlantic salmon have also been acoustically tagged and released into tributaries of Minas Basin [
30]. Acoustically tagging fish subsampled from some population enables a Lagrangian estimate of the probability that individuals might encounter a MHK tidal turbine. Lagrangian methods provide population-specific information that augments the previously discussed Eulerian methods which attempt to count all fish that pass through
.
It was hoped that probabilities of fish-turbine encounter could be calculated from measurements of striped bass [
10] and Atlantic sturgeon [
11] which carried 69 kHz PPM tags. Such calculations require estimates of detection efficiency in order to transform detected signals into estimates of abundance or a probability distribution of distance from the detecting receiver [
13]. Detection range testing in Minas Passage [
23] showed poor detection efficiency for 69 kHz PPM tags when current speed was fast. Another study [
31] found that sturgeon carrying 69 kHz PPM tags were seldom detected in Minas Passage when current was fast. The present results confirm that fish carrying 69 kHz PPM tags are unlikely to be detected by the receiver array in fast currents and yet will be detected by many receivers in the array when current is slow. For estimating probability of encounter, being detected over too wide an area causes uncertainty and not being detected biases values low in fast currents for which the possibility of harmful fish-turbine encounters might be anticipated to be more likely.
Those shortcomings of PPM tags motivated the use of HR tags to track fish passing through the TED area in Minas Passage. Alewives carrying HR tags were detected at the TED area during a range of flood and ebb current conditions [
29] which supported further consideration of HR tags. Detection range measurements [
13] show that the HR signals are better detected than PPM signals in fast currents. A single PPM signal is extends over an interval
s whereas a HR signal takes only 6 ms so it is possible to transmit a great many more HR signals which gives more chances for a HR tag to be detected (
6). The present work quantifies how a higher transmission rate makes it more likely that a drifter carrying a HR tag (a proxy for a tagged fish) will be detected by fixed receivers (
Table 3).
When a PPM signal is reflected from the sea surface [
13] it can cause close proximity detection interference [
21] and prevent a nearby PPM tag from being detected. We observe that there are also geometric configurations of tag and receiver for which a HR signal overlaps with its reflection from the sea surface (
3) but that only happens for a narrow set of circumstances, mostly when the tag is very near the sea surface and the sea surface is calm (
Table 3). Under slightly different geometric circumstances, the reflected signal will not overlap with that taking a direct path and so the HR2 receiver has a second opportunity to detect the one HR transmission. Reflected signals are less likely to be observed, and less likely to cause interference, when the sea surface is rougher ([
13],
Table 5).
Another concern about both HR and PPM signal propagation was that previous detection range experiments [
13,
23] placed both receiver and acoustic tag close to the seafloor so that signals might sometimes be blocked by variable bathymetry. Those previous experiments could not unambiguously identify where signal paths were blocked. The present mooring layout (
Figure 1b) affords one obviously blocked path (mooring 9 to 10) plus a matching clear path (mooring 9 to 8) and results demonstrate that detection efficiency is profoundly diminished for the blocked signal path (
Figure 5). This justifies a decision to reject paths along which signal detection was poor in order to obtain an estimate for detection efficiency
that applies to tagged fish that swim well clear of the seafloor [
13].
Detection efficiency
is usually measured in the Eulerian frame with both acoustic tag and receiver being at fixed coordinates relative to the seafloor [
13,
20,
23]. On the other hand, a tagged fish is naturally described in Lagrangian frame [
15] as defined by its position at some initial time and subsequent trajectory due to movement by tidal current and swimming behaviour. To achieve a robust estimate for probability of fish-turbine encounter, we need to quantify that a fish carrying a HR tag will be detected as it passes over an array of HR2 receivers that monitor the TED area. Equation (
6) relates the Eulerian detection efficiency
[
13] to the number of times a HR signal is expected to be detected from a tagged fish (Lagrangian) as it passes a moored receiver. Given that
tended to overestimate the number of detection-positive intervals [
13], the presently reported experiments were deemed necessary to directly measure how many times a fixed receiver detects a drifting tag as it passes by. Equation (
6) was found to overestimate the number of passing trajectories for which there was at least one detected signal and that overestimation can be attributed to autocorrelation of variability about the general functional form of
. Nevertheless, most of the HR tags that drifters carried through the HR2 receiver array were detected, even during spring flood-tides when current speeds were near their greatest extent in the TED area. Sometimes a passing tag was detected only a small number of times, so there was little margin for error. Indeed, the HR tags transmitted every 1.8 to 2.2 s and if they had transmitted at longer intervals then more tags would have passed by without being detected. A tagged fish that actively swims in the same sense as the tidal current may be somewhat less likely to be detected than a tagged fish drifting with the current [
14].
The issue of tagged fish passing through a receiver array without being detected is also central to studies that use a sequence of receiver arrays to measure migration and mortality/loss of tagged fish [
29,
32,
33]. When fish are migrating, it is often possible to utilize detections of the tagged fish to roughly estimate detection efficiencies of most receiver arrays along the migration route, except for the last array [
29,
33]. It is very desirable, therefore, that the last array be designed so that it will detected all migrating fish as they pass by. The above work shows that detection range measurements are useful for obtaining a first estimate of the probability that the migrating fish will be detected by an array but that estimate will be biased a little high.
A total of four HR2 receivers were used to monitor the TED area during this experiment. Although this was sufficient to detect the majority of HR tags passing by on drifters, the number of signals detected during a passing event was often small when tidal currents were greatest. It would be better to have had more HR2 receivers monitoring the TED area in order to (1) provide some redundancy in case of instrument failure, (2) better ensure that every tagged fish would be detected as it passed by, and (3) increase the possibility of localizing the position of a passing tag when several receivers detect the same HR signal. Localization does not have to be perfect, but it would be very helpful to know if tagged fish passed directly over the TED area or a little to the north or south.
Additionally, it would be advantageous to have a mooring system that enables HR2 receivers to be held sufficiently off the seafloor so as to prevent signals from one HR2 from being blocked before they reached a neighbouring HR2. If this could be achieved then HR detection efficiency could be accurately monitored as a function of time throughout the period when tagged fish are also being monitored. Rather than only relying on a fitted function for detection efficiency , it would be advantageous to also have a direct measurement of detection efficiency for the minute before and after a tagged fish is actually detected.
In conclusion, we were fortunate not to have had HR2 failures in the TED area and it is now possible to demonstrate how
can be used to calculate probability of fish-turbine encounter when the array detects tagged fish as they pass through the TED area [
25].