Laboratory Acoustic Measurement of Prorocentrum Donghaiense Concentrations

Laboratory Acoustic Measurement of Prorocentrum Donghaiense Concentrations

Jieli Qin Shaoping Shang  

Department of Communication Engineering, Xiamen University, Xiamen 361005, China

Key Laboratory of Underwater Acoustic Communication and Marine Information Technology, (Xiamen University) Ministry of Education, Xiamen 361005, China

College of Oceanography and Enviromental Science, Xiamen University, Xiamen 361005, China

Corresponding Author Email: 
iqin_sea@163.com
Page: 
181-188
|
DOI: 
https://doi.org/10.18280/i2m.180213
Received: 
13 January 2019
|
Accepted: 
18 March 2019
|
Published: 
30 June 2019
| Citation

OPEN ACCESS

Abstract: 

Through lab acoustic measurement, this paper explores the features of backscattering ultrasound waves in Prorocentrum donghaiense (P. donghaiense) at different concentrations, and establishes the correlation curves between the integrated backscatter (IBS), an indicator of backscattering intensity, and P. donghaiense concentration. The experimental results show a highly linear correlation between the IBS with low concentration, and a reduced linear correlation between the IBS with high concentration; the reduction is attributable to the acoustic attenuation effect of dense algae particles in the high concentration solution. Then, the acoustic measurement performance was improved through particle size correction, leading to a good overall characterization effect. Finally, the proposed method was proved valid through data analysis. The research findings shed new light on acoustic monitoring of phytoplankton concentration, and provide a good reference to the forecast, prevention and control of marine red tides.

Keywords: 

backscattering, concentration measurement, integrated backscatter strength power (IBS), prorocentrum donghaiense (p. donghaiense), ultrasound

1. Introduction

Red tide is a natural phenomenon caused by the explosive growth of marine phytoplankton. Being a common concern in the international community, this marine environmental problem calls for urgent solutions [1, 2]. The red tide tilts the balance of the food chain and undermines the stability of the marine ecosystem, posing great threat to human health [3] and economic development. That is why the phenomenon has attracted attention from various parties.

Much research has been done to prevent and control red tide, resulting in many effective measures for disaster prevention and reduction [4]. In the current research, the focus is placed on the causes and species of red tide. On this basis, biological, physical and chemical methods [5-7] have been developed to control red-tide algae, namely, controlling algae growth using the nutrient antagonism in plant, killing the algae with chemical reagents and optically controlled ultraviolet radiation. In addition, field sampling and remote sensing [8, 9] have been adopted to monitor red tide. The former is to take samples of the target sea area and measure the sample liquid parameters, while the latter captures the algae information in the sea from the space via satellites and other means. However, field sampling is time-consuming and labor-intensive, and remote sensing only works in good weather and after the outbreak of red tide. By contrast, there is little report on red tide monitoring by the emerging method of acoustic monitoring, which requires direct contact with the water body.

To mitigate its damages, red tide should be forecasted in advance rather than only treated during the outbreak. With excellent real-time performance, the acoustic monitoring has a great potential of red tide forecast. Through direct contact with the water body, this emerging method eliminates the longtime of manual counting and high cost of instrument counting in traditional field monitoring, and outperforms remote sensing in early acquisition of red-tide algae dynamics. Despite its popularity in plankton research [10], the acoustic monitoring, especially ultrasonic monitoring, has not been widely adopted to monitor microalgae. Considering the size of zooplankton and phytoplankton, Frisk and Hays, Holliday and Pieper, Hwang et al. [11-13] select proper frequency bands between 25kHz and 25MHz for ultrasonic tests, and perform computations based on the volumetric scattering and equivalent radius of sound. Taking millimeter-scale krill and planktonic algae for instance, the abundance and distribution of these zooplankton and phytoplankton were estimated through the analysis on morphological and acoustic physical properties. However, the majority of phytoplankton has a particle size of 1~200μm, so the ultrasound frequency should reach the MHz level. Blanc et al. [14] measured the bulk scattering intensity of Skeletonema costatum in a lab with 2.6MHz ultrasonic signals, and compared the waveform and frequency domain of water containing Skeletonema costatum and the pure water, but did not make any further analysis. Focusing on red-tide algae species in South Korea, Bok et al. [15] conducts an experiment on the diurnal division of algae cells and analyzes the variation in acoustic signal features. Using 5MHz ultrasound, Kim et al. [16] carries out lab tests on the backscattering intensity of algae solutions of six different concentrations, and measures the density ratio and sound velocity ratio of algae cell to the seawater medium. Bok et al. [17] employ two high-frequency ultrasounds, whose probe frequencies are 5 MHz and 10 MHz respectively, to a lab research and a marine test on acoustic backscattering of an algae solution of a certain concentration.

In light of the above, it is of great scientific and practical significance to enhance the monitoring of Prorocentrum donghaiense (P. donghaiense), a common red-tide species in China’s coastal areas [18]. From the perspective of particles, this paper introduces the principles of experimental design, and sets up an ultrasonic testing system. The acoustic backscattering signals of P. donghaiense at different concentrations were acquired in the lab. Then, the relationship between acoustic signals and algae cell concentrations were determined through analysis, and subjected to descriptive verification, leading to meaningful conclusions.

2. Experimental Principles

2.1 Basic ultrasonic scattering features of particles

During the propagation in particle-containing medium, the incident ultrasound wave may change direction due to the presence of particles, which does not occur in the traditional continuous medium. When a plane wave reaches a particle, part of it will continue to propagate forward, and another part of it will be scattered by the particle to the surrounding or backwards. Both parts contain the information on the scatterers.

The scattering behavior of the particle is determined by the ratio of particle size and wavelength. The dimensionless expression of the wave number can be expressed as:

$k a=\frac{2 \pi}{\lambda} \cdot \frac{d}{2}=\frac{\pi \cdot d}{\lambda}=\frac{\pi \cdot f \cdot d}{c}=\frac{2 \pi \cdot f \cdot a}{c}$         (1)

where, d is the particle diameter; a is the particle radius; f is the acoustic frequency; λ is the wavelength..

Considering the scattering in the Rayleigh model [19, 20], the scattering intensity of the incident plane wave by a single hard particle at the angle $\theta$  corresponding to the far-field distance r can be defined simply as:

$I_{S}(r, \theta)=\frac{p_{0}^{2}}{2 \rho_{0} c_{0}} \cdot \frac{a^{2}}{r^{2}}|R(\theta)|^{2}=I_{0} \frac{a^{2}}{r^{2}} \cdot|R(\theta)|^{2}$

$=I_{0} \frac{a^{2}}{r^{2}} \cdot \frac{1}{(k a)^{2}} \sum_{l, n=0}^{\infty}\left[b_{l} b_{n}^{*} e^{j \frac{l-n}{2} \pi} P_{l}(\cos \theta) P_{n}(\cos \theta)\right]$         (2)

where, $|R(\theta)|^{2}$  is the squared value of the absolute value (modulus) of the complex number $R(\theta)$ . This complex number stands for the directivity of the scattering sound field:

$\begin{aligned} R(\theta)=\frac{1}{k a} \sum_{l=0}^{\infty} b_{l} e^{j \frac{l+1}{2} \pi} P_{l}(\cos \theta) & \\ &=\frac{1}{k a} \sum_{l=0}^{\infty}(-j)^{l}(2 l+1) \frac{\frac{d\left[j_{l}(k a)\right]}{d(k a)}}{\frac{d\left[h_{l}^{2}(k a)\right]}{d(k a)}} \\ & \cdot e^{j \frac{l+1}{2} \pi} P_{l}(\cos \theta) \end{aligned}$           (3)

 

where, $P_{l}(\cos \theta)$  is the Legendre function; $j_{l}(k a)$  is the spherical Bessel function; $h_{l}^{2}(k a)$  is the Hankel spherical function of the second kind; a is the particle radius.

Figure 1. Polar coordinate profiles of particle acoustic scattering (the variation of normalized scattering amplitude with scattering angles) (a) Particle scattering profile of ka=0.03, (b) Particle scattering profile of ka=6, (c) The polar coordinates ratio of backscattering to forward scattering as a function of ka

Figure 1 shows the polar coordiante profiles of particle acoustic scattering at different ka values. It can be seen that scattering amplitude differs in the range of the 360° scattering angle. Then, the acoustic scattering intensity was normalized. The scattering in the 0° direction, which coincides with the direction of the incident wave, was defined as forward scattering; the scattering in the opposite direction was defined as backscattering, the scattering in the 180° direction, the directivity was expressed as both forward scattering and backscattering.

It can be seen from Figure 1(a) that the backscattering was relatively uniform when the 1MHz incident acoustic wave reached a 14μm particle (ka≈0.03), and much greater than forward scattering. With the increase of the ka, the intensity of the scattered acoustic waves exhibited an obvious non-uniform spatial distribution, and the number of petals grew in the scattering plot. After the ka increased to a certain value, the backscattering underwent a sharp decline. As shown in Figure 1(b) (ka≈6), the scattered sound waves mainly moved forward, and interfered with the incident wave, forming a prominent geometric shaded area.

According to Figure 1(c), both backscattering and forward scattering were strengthened with the increase of ka. Specifically, the backscattering fluctuated obviously near ka=1 and then gradually became stable (solid curve), while the forward scattering always increased with the value of ka (dashed curve). In addition, the polar coordinates ratio of backscattering to forward scattering (dotted curve) is inversely proportional to ka: the ratio was relatively large at a small ka, and decreased gradually to zero with the growth of ka.

Because of the huge number of microalgae (particles) being detected, it is feasible to detect the backscattering signals with a single transmit-receive (T-R) probe, although backscattering intensity of a single particle has a small absolute value. In other words, it is reasonable to collect the backscattering signals of microalgae with a particle size of micron using an MHz ultrasound probe (ka≪1).

2.2 Equivalent estimation of particle backscattering intensity

To estimate the particle backscattering intensity, it is assumed that the plural scattering is so small as negligible, the particles exist as individuals in the solution, and the P. donghaiense cells are equivalent to spherical particles with a certain hardness. Since algae particles exist as fluid spheres, $\sigma$ , the theoretical backscattering cross section of a single cell can be calculated as:

$\sigma=k^{4} a^{6}\left[\frac{1-g h^{2}}{3 g h^{2}}+\frac{1-g}{1+2 g}\right]^{2}$            (4)

where, g is the density ratio of algae cell to the seawater medium; h is the sound velocity ratio of algae cell to the seawater medium. The two parameters cannot be determined without advanced test devices. Here, their values are both estimated as 1.05 according to the measured results in the existing literature [16].

Then, the total volume backscattering strength $\mathrm{S}_{\mathrm{v}}$  can be obtained by accumulating the backscattering intensity of each particle:

$\mathrm{S}_{\mathrm{v}}=10 \log _{10}(\mathrm{N} \sigma)+\mathrm{C}_{\mathrm{e}}$            (5)

where, N is the number of particles in the seawater medium; $\mathrm{C}_{\mathrm{e}}$  is the environmental factor.

While it is difficult to measure the exact backscattering intensity through experiment, there is a certain correspondence between the integrated backscatter strength (IBS), and the theoretical total volume backscattering strength $\mathrm{S}_{\mathrm{v}}$ :

$\mathrm{IBS}=20 \log _{10}\left(\frac{\mathrm{V}_{\mathrm{rms}} \mathrm{Bs}}{\mathrm{V}_{\mathrm{rms}} \mathrm{Ref}}\right)$             (6)

where, $\mathrm{V}_{\mathrm{rms}}$  is the effective voltage of the backscattering signals in the seawater containing a certain concentration of P. donghaiense; $\mathrm{V}_{\mathrm{rms}}$  is the effective voltage of the backscattering signals in the pure seawater (the reference medium); rms is short for root mean square. Therefore, the number of particles can be estimated through comparative analysis on the acoustic and electrical signals of algae solutions at different concentrations.

3. Construction of Experimental Platform

3.1 Preparation of algae solutions

P. donghaiense is an earthy yellow, heliophilous single-cell red-tide algae. The cell is large (length: 15~22μm; width: 9~14μm), and shaped like an asymmetrical pear, with a slight dent on the top. Most cells have round bottoms and long flagella [21]. The aseptic strains of the P. donghaiense solutions at different concentrations were provided by State Key Laboratory of Marine Environmental Science (Xiamen University).

The seawater was collected from the sea to the west of Xiamen, filtered through a cellulose acetate membrane (0.2μm) to remove microalgae and particulate matters, and subjected to autoclave sterilization. Next, the pH and salinity of the seawater were adjusted to 8.0±0.2 and 30psu, respectively. After that, the seawater was enriched by sterilized f/2 nutrient solution [22]. The nutritive salts and vitamins of the P. donghaiense culture solutions are listed in Table 1 below.

Table 1. Compounds of P. donghaiense culture media

Compound

Quantity

Stock solution

(a) f/2 medium, added to 950 mL filtered seawater

NaNO3

1mL

75g/L dH2O

NaH2PO4.H2O

1mL

5g/L dH2O

Na2SiO3.9H2O

1mL

30g/L dH2O

f/2 trace metal solution

1mL

(b)

f/2 vitamin solution

1mL

(c)

(b) f/2 trace metal solution, added to 950 mL dH2O

FeCl3.6H2O

3.15g

 

Na2EDTA.2H2O

4.36g

 

CuSO4. 5H2O

1mL

9.8g/L dH2O

Na2MoO4.2H2O

1mL

6.3g/L dH2O

ZnSO4.7H2O

1mL

22.0g/L dH2O

(c) f/2 vitamin solution, added to 950 mL dH2O

Vitamin B12 (cyanocobalamin)

1mL

1.0g/L dH2O

Biotin

1mL

0.1g/L dH2O

Thiamine.HCl

200mg

 

The initial inoculation and culturing were carried out in a 250 mL conical flask, containing 180mL fresh f/2 culture solution, in a special sterile culture room at the temperature of 21°C, the light-dark cycle of 12h:12h, and the light intensity of 70μmol/(m2∙s). The flask was shaken twice a day to prevent precipitation and wall growth. After activation and repeated transfers, the number of P. donghaiense cells grew steadily. The number increased exponentially from the 2nd to the 4th day and stably from the 6th to the 8th day.

The observation was carried out using a Type B LISST-100 laser in situ particle size analyzer, and the results were recorded in Figure 2. It can be seen that the particle sizes of P. donghaiense cells mainly concentrated between 8 μm and 22μm. The equivalent particle size $D_{60}$  of the P. donghaiense in our experiment was measured as 14μm, about 5 % smaller on average than the general size. This means the wavelength of 1MHz ultrasound far exceeds the particle size of P. donghaiense cells (ka≪1), which satisfies the premise of the Rayleigh scattering model.

The P. donghaiense solutions at different concentrations were prepared from algae cell particles in pure seawater, the algae solutions were collected in the late phase of the exponential growth period for testing. The direct detection of the water samples show that the number of cells in each algae solution is as follows: 0, 70, 120, 2.38 $\times 10^{2}$ , 4.3 $\times 10^{2}$ , 7.6 $\times 10^{2}$ , 9.6 $\times 10^{2}$ , 1.9 $\times 10^{3}$ , 4.1 $\times 10^{3}$ , 9.4 $\times 10^{3}$ , 1.5 $\times 10^{4}$ , 2.4 $\times 10^{4}$  and 5.6 $\times 10^{4} \cdot$ cell $/ \mathrm{ml}$ .

Figure 2. Particle size distribution of P. donghaiense

3.2 Platform construction

Traditionally, the solution features are characterized by the attenuation of the ultrasound transmitting through the medium between two opposite acoustic probes. In our experiment, however, a single immersion ultrasonic T-R probe (nominal central frequency: 1MHz (±30kHz); half-power angle: 6°; sharpness angle: 14°; outer diameter: 8mm) is adopted to measure the backscattering of the ultrasound. As shown in Figure 3, the measurement system of our experiment mainly consists of four modules: algae solution storage and testing, programmable circuit board, digital oscilloscope and computer data analysis. The test tank is a 5L glass beaker with a height of 275mm and an inner diameter of 180mm. The size of the tank is sufficient to meet the distance requirements for far-field acoustic measurement, because the probe has a small diameter and a high frequency. The measurements were performed at 23 °C, and the room temperature was kept basically constant.

Figure 3. Block diagram of the measurement platform

The experiment was carried out through the following steps. Firstly, the transmitting signals for the algae solutions with pre-set parameters were written into the circuit system through the chip on the circuit board, and converted into ultrasound signals before being sent at the T/R probe attached to the end of the circuit board. Then, the ultrasound signals propagated through algae solutions at different concentrations, and interacted with the algae cells. The feedback signals (backscattering signals) were received by the same probe, and converted into electrical signals. Then, the signals were amplified and filtered on the circuit board, sampled by the digital oscilloscope UT2102CE (the maximum sampling frequency: 1GS/s), and uploaded to the PC for data analysis, yielding the final results.

To prevent interference and superposition between transmitted signals, the probe excited a square wave pulse of 1MHz and sent it at the interval of 30s. For each concentration, the measurement was repeated 60 times and the result of each measurement were recorded. Moreover, the solutions were stirred magnetically at the bottom once every 20 measurements, aiming to eliminate the effect of solution unevenness caused by cell sedimentation and that of bubbles formed in agitation. After each stirring, the solution was left to stabilize for a short while before entering the next measurement. During the ultrasonic measurement, three parallel samples were prepared for each concentration, and the collected signals were subjected to mean processing and were cut into 20μs-long segments for PC processing.

4. Experimental Results

A warning should be issued red tide once the P. donghaiense concentration reaches 5×105 cell/L [23,24]. Generally, low, medium and high concentrations are respectively defined as the concentration below, near and obviously higher than the warning level, and ultra-high concentration is defined as the concentration greater than the level at the outbreak of red tide. Focusing on red tide forecast, this paper mainly explores the acoustic features of algae at low and medium concentrations.

Ultrasonic measurements were performed on P. donghaiense sample solutions at 12 different concentrations. The measured results in Figure 4 show that the IBS (red solid dots) increased with the algae concentration.

The acoustic result of measured data (red dot) exhibited similar trend as that predicted by the Rayleigh theoretical model in Eq. (5) (red up arrows). Considering that P. donghaiense cells are poly-dispersed particles, the upper and lower bounds of particle size should be determined through theoretical calculation according to the particle size distribution features in Figure 2, and the main particle sizes should be selected for further correction by the following equation:

$\mathrm{S}_{\mathrm{vN}_{\mathrm{M}}}=10 \log _{10}\left(\sum_{\mathrm{i}=1}^{\mathrm{N}_{\mathrm{M}}} \mathrm{N}_{\mathrm{i}} \cdot \sigma_{\mathrm{i}}\right)+\mathrm{C}_{\mathrm{e}}$            (7)

where, $\mathrm{N}_{\mathrm{M}}$  is the number of main particle sizes being selected. Here, seven particles size (8.4~22.7μm) are selected, i.e. $\mathrm{N}_{\mathrm{M}}$ =7. For each particle size, the backscattering intensity $\sigma_{\mathbf{i}}$  of the single particle was computed, and multiplied with the number of particles $\mathrm{N}_{\mathrm{i}}$ . On this basis, the total backscattering intensity $\mathrm{S}_{\mathrm{VN}_{\mathrm{M}}}$  was obtained by adding up the results of the seven particle sizes. The revised theoretical equation contains information on particle size and concentration, providing a reliable reference for actual measurements. Compared with the results calculated by equivalent particle size only, the theoretical values corrected by the actual particle sizes of P. donghaiense (red curve with boxes) enjoy high intensity and close proximity to the measured values, indicating that it is feasible to monitor algae concentration by measuring backscattering sound signals.

Figure 4. Measured results vs. theoretical predictions

5. Discussion

5.1 Results analysis and verification

Through the lab acoustic measurements, the author acquired the basic acoustic features of backscattering intensity of P. donghaiense solutions at different concentrations, and derived similar linear trends with those predicted by the theoretical model. However, the theoretical model was simplified under the ideal condition. It can be seen from Figure 4 that the predicted result differed from the measured IBS in the rate of change.

In view of the above, the acoustic data of the 12 algae solutions were fitted in different concentration segments. As shown in Figure 5, the IBS increased much faster in the low and medium concentration segment (up arrows; <9×105cell/L) than in the medium and high concentration segment (down arrows; >4×106cell/L). This difference can be attributed to the following factors: The IBS is very sensitive to the growth in particle concentration, when the solution is as weak as low concentration algae solutions; thus, the intensity increased rapidly with the rise of the particle concentration. By contrast, the intense interactions between particles in high concentration algae solutions hindered the transmission of backscattering soundwave, which drags down the growth rate of the IBS.

After that, the acoustic data of all solutions were fitted again with quadratic polynomial and the results (R2=0.81) are drawn as a solid curve in Figure 5. It can be seen that the quadratic polynomial fitting achieved similarly good correlation with the linear fitting (dashed curve), and outperformed the latter in the correlation with the measured IBS in the two ends of high and low concentrations.

Figure 5. Measured acoustic features and the fitting results

The default equivalent particle size of P. donghaiense was 14μm. The scattering can be viewed as uncorrelated when the particle spacing is greater than 3 times the particle size. The warning concentration falls within this range. However, the high concentration above this range has a certain acoustic attenuation effect in the sound path range, and needs to be corrected in two steps: collecting the ultrasound signals received in each test on algae solution at a specific concentration into a sample set, and finding the mean square value of the set; conducting exponential fitting of the outer envelope of the mean squared waveform, and expressing the outer envelope signals as:

  $E_{i}(t)=E_{0} \cdot \exp \left(-\alpha_{i t} \cdot t\right)$            (8)

where, $E_{i}$ is the mean square value at the concentration $N_{i}$ ; t(μs) is the duration variable of the observation window; $\alpha_{i t}$  (dB/μs) is the attenuation coefficient for the exponential fitting of the outer envelope. Note that the scattering attenuation coefficient $\alpha_{s}=\alpha_{t} / C$ (dB/cm), with C being the sound velocity. Without considering the effects of particle concentration in the medium, the sound velocity is basically stable at the same conductivity, temperature and depth. Taking the logarithm on both sides, the sound attenuation effect can be linearized.

Figure 6. Pre- and post-correction IBS values

Figure 6 compares the IBS values of P. donghaiense solutions at different concentration before and after attenuation correction. The post-correction measured data are presented as red boxes. It can be seen that the IBS values of low concentration algae solutions increased linearly with the number of algae cells, indicating that the attenuation is rather weak. The IBS values of medium concentration algae solutions fluctuated with the increase of concentration, revealing a gradual enhancement of the attenuation. The attenuation was compensation in high concentration algae solutions, because the growth in backscattering was suppressed by the obvious attenuation. After the compensation, the IBS values (solid curve) were greater than the uncompensated values (dashed curve), and the linear features were improved. The correlations of both linear and nonlinear fittings were enhanced.

New P. donghaiense solutions were prepared at another six concentrations: 1.92 $\times 10^{2}$ , 3.6 $\times 10^{2}$ , 8.1 $\times 10^{2}$ , 1.17 $\times 10^{3}$ , 2.49 $\times 10^{3}$  and 6.35 $\times 10^{3}$ cell/mL, the results are shown in Figure 7 below.

Figure 7. Measured data vs. fitting curves

It can be seen that the IBS values (blue up arrows) of the new P. donghaiense solutions at the six concentrations conformed to the fitting curve (red dots) of the predictions at the 12 concentrations in the basic test, showing a positive correlation with algae concentration. The deviation from the original fitting curve fell within the allowable range. Comparing the results of all samples in the two tests, it is learned that the correlation between the IBS and concentration was weak and fluctuating in the medium concentration segment. However, the IBS and concentration had an obvious linear correlation in the low and medium concentration segment (dashed box), especially within the warning concentration 5×105cell/L (R2=0.96). In the high concentration segment (solid box), the correlation was also highly linear, for the linear growth rate was suppressed by the attenuation effect of high concentration algae cells on sound propagation. The above results show that our test method is feasible and may apply to other concentrations.

5.2 Uncertainty analysis

The uncertainty components of our measurement platform come from repeated measurements (type A) and defects of the platform or measurement method (type B) [25]. Type A uncertainty $U_{A}$  can be obtained by computing the statistical average of multiple independent measurements on the algae samples:

$U_{A}=S D_{n}(\overline{\alpha})=\sqrt{\frac{1}{n(n-1)} \sum_{i=1}^{n}\left(\alpha_{i}-\overline{\alpha}\right)^{2}}$         (9)

where, $\mathrm{S} D_{n}(\overline{\alpha})$  is the standard deviation of the average IBS. Table 2 lists the Type A uncertainties at different algae concentrations. It can be seen that the algae solution at 9.6 $\times 10^{5}$ cell/L had the greatest uncertainty.

Type B uncertainty components of measurement platform may come from the inconsistency of probe position, the deviation from electrical noise of the measuring instrument, the varied distributions of particle size, the change in experimental temperature, and the inaccurate measurement of solution volume. For our measurement platform, temperature change and volume inaccuracy are the main causes of type B uncertainties. This is because our tests use the same set of circuit system and the same probe, and the algae solutions were prepared after shaking and tested with magnetic stirring and standing. Here, it is assumed that the measurement errors of solution volume and temperature are ±1% and ±0.5℃, respectively.

During the analysis of type B uncertainties, $t^{+}$  and $t^{-}$  are the IBS values for each 0.5 °C increase and decrease of temperature, respectively; $V^{+}$  and $t^{-}$  are the IBS values for each 1 % of increase and decrease of volume, respectively; ARD/t and ARD/V are the average relative deviations of the IBS induced by volume change and temperature change, respectively. The IBS was measured at 23 °C (dB). The type B uncertainty $u_{B}$  can be calculated as:

$u_{B}=\frac{1}{2} \sqrt{u_{B t}^{2}+u_{B v}^{2}}$           (10)

The total uncertainty U can be computed as:

$U=k \sqrt{u_{A}^{2}+u_{B}^{2}}$           (11)

where, k=2. The type B uncertainties of backscattering coefficients in algae solutions at different concentrations are displayed in Table 3 below. Obviously, the algae solution at 9.6 $\times 10^{5}$  cell/L had the greatest uncertainty, which is basically the same with the result of Figure 7 (the deviation was relatively large at 8.1 $\times 10^{5}$ cell/L). Hence, the maximum measurement uncertainty of our measurement system was determined as 23.22 %.

Table 2. Type A uncertainties of backscattering coefficients in algae solutions at different concentrations

/ $\left( \times 10^{5} \cdot c e l l \cdot L^{-1}\right)$

1 $\mathrm{MHz}$

Concentration

0.7

1.2

1.9

2.38

3.6

4.3

7.6

8.1

Type A uncertainty

4.33%

3.61%

5.42%

5.06%

6.03%

6.14%

3.61%

6.68%

Concentration

9.6

11.7

19

41

94

152

248

564

Type B uncertainty

10.48%

5.35%

6.86%

5.78%

4.7%

6.5%

2.89%

6.14%

 

Table 3. Type B uncertainties of backscattering coefficients in algae solutions at different concentrations

Type B uncertainties

Concentration/ $\left( \times 10^{5} \cdot \operatorname{cell} \cdot L^{-1}\right)$

1.9

3.6

4.3

7.6

8.1

9.6

11.7

19

IBS (dB)

-3.501

-2.809

-2.661

-3.253

-3.114

-1.802

-2.553

-2.807

$t^{+}$

-3.469

-2.732

-2.614

-3.231

-3.082

-1.690

-2.484

-2.722

$t^{-}$

-3.560

-2.877

-2.736

-3.300

-3.176

-1.942

-2.624

-2.896

$\mathrm{ARD} / \mathrm{t}$

1.43%

2.64%

2.42%

1.21%

1.71%

7.25%

2.78%

3.21%

$t^{+}$

-3.563

-2.876

-2.745

-3.294

-3.184

-1.933

-2.638

-2.890

$t^{-}$  

-3.468

-2.736

-2.605

-3.229

-3.066

-1.692

-2.496

-2.723

$\mathrm{ARD} / \mathrm{V}$

1.50%

2.57%

2.76%

1.12%

2.05%

6.89%

2.98%

3.05%

$u_{B}$

1.04%

1.84%

1.83%

0.83%

1.33%

5.00%

2.04%

2.21%

$U$

11.03%

12.62%

12.82%

7.41%

13.63%

23.22%

11.44%

14.42%

6. Conclusions

In this paper, an acoustic measurement platform is designed and adopted for the ultrasonic measurement of P. donghaiense solutions at different concentration. The following conclusions were put forward after analyzing the measured results:

(1) The proposed single-probe acoustic measurement platform for P. donghaiense solutions can capture the backscattering sound signals of algae solutions at different concentrations. The IBS value gradually increased as the concentration rose from 1.92 $\times 10^{5}$  to 6.35 $\times 10^{6}$  cell/L. This correlation agrees well with the theoretical results. The prediction effect can be further improved through the particle size correction of the simplified theoretical formula.

(2) The IBS and concentration had an obvious linear correlation when the P. donghaiense concentration was below 1 $\times 10^{6}$ cell/L, especially within the warning concentration 5×$\times 10^{5}$ cell/L. This relationship satisfies the application scope and requirements of red tide forecast. With the growth in concentration, the linear correlation between the IBS and concentration weakened and fluctuated. After further increase of concentration, the linear growth rate and amplitude of the IBS were suppressed by the attenuation effect of high concentration algae cells on sound propagation.

(3) Within the concentration range of P. donghaiense in our experiment, the IBS value exhibited a linear growth trend with the increase in concentration. Considering the attenuation effect, the IBS variation was discussed in three phases. For high concentration sampling points, the attenuation effect was mitigated through compensation, thus improving the correlation between the IBS and concentration. The measured data were fitted by quadratic polynomial, and the fitting curves were divided into different segments. Then, the measurement platform was improved through comparison between the different segments.

(4) Despite some uncertainties in the experiment, the experiment process is generally reasonable. Thus, the proposed platform can be applied to monitor the solutions at other concentrations. The future research will probe deeper into the accuracy of the measurement.

To sum up, it is feasible and effective to measure the concentration of P. donghaiense by ultrasound. With high cost-effectiveness, the proposed measurement approach supports real-time online monitoring. The research findings provide valuable references to the observation and monitoring of red tides in China, shed new light on red tide forecast, prevention and control, and promote marine ecology and coastal economy.

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