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Article

Measurements of Dispersed Phase Velocity in Two-Phase Flows in Pipelines Using Gamma-Absorption Technique and Phase of the Cross-Spectral Density Function

by
Robert Hanus
1,*,
Marcin Zych
2 and
Anna Golijanek-Jędrzejczyk
3
1
Faculty of Electrical and Computer Engineering, Rzeszow University of Technology, Powstancow Warszawy 12, 35-959 Rzeszow, Poland
2
Faculty of Geology, Geophysics and Environmental Protection, AGH University of Science and Technology, Mickiewicza 30, 30-059 Krakow, Poland
3
Faculty of Electrical and Control Engineering, Gdansk University of Technology, Narutowicza 11/12, 80-233 Gdansk, Poland
*
Author to whom correspondence should be addressed.
Energies 2022, 15(24), 9526; https://doi.org/10.3390/en15249526
Submission received: 13 October 2022 / Revised: 21 November 2022 / Accepted: 9 December 2022 / Published: 15 December 2022
(This article belongs to the Special Issue Heat Transfer Characteristics and Two-Phase Flow Performance)

Abstract

:
This paper concerns the application of the gamma radiation absorption method in the measurements of dispersed phase velocity in two-phase flows: liquid–gas flow in a horizontal pipeline and liquid–solid particles in a vertical pipe. Radiometric sets containing two linear 241Am gamma radiation sources and two NaI(Tl) scintillation detectors were used in the research. Due to the stochastic nature of the signals obtained from the scintillation probes, statistical methods were used for their analysis. The linear average velocity of the dispersed phase transportation was calculated using the phase of the cross-spectral density function of the signals registered by the scintillation detectors. It is shown that in the presented cases, the phase method can be more accurate than the most commonly used classical cross-correlation one.

1. Introduction

Multiphase liquid–gas, liquid–solid particle, and gas–solid phase flows are often transported by pipelines in such industry sectors as chemistry, mining, and agri-food industries, as well as energy and environmental engineering [1,2,3]. For example, in the mining industry, two-phase mixtures such as liquid–gas, liquid particulate matter, or liquid I–liquid II ones are transported via pipelines. The analysis and control of such flows require the application of dedicated measurement techniques and devices [1,4,5,6]. To measure the parameters of the two-phase flows in both open channels and pipelines, radioisotope methods have been used for many years [7,8,9,10,11]. Due to the non-invasive measurement and relatively high accuracy of it, the absorption method using closed sources of radiation is particularly useful for testing two-phase flows in pipelines [12,13,14,15,16]. A significant problem limiting the taking of measurements with the use of radioactive sources is the compliance with strict legal regulations related to radiation protection.
Due to the stochastic nature of the signals obtained from the scintillation probes, statistical methods are used for their analysis. The best known one is the classic method of cross-correlation [17,18]. The other methods include a correlation analysis with the Hilbert transform [19], Hilbert–Huang transform [20], the method of the phase of cross-spectral density [21], differential and combined methods [18,22,23], and the methods using the conditional averaging of the signals [24].
The application of the phase method to measure the time delay of the random signals is known, and it has been described in the literature, e.g., [21,25,26]. This method was used to analyse the vibroacoustic signals [25,27,28,29,30], as well as the signals obtained in biological and medical research [31,32]. However, so far, it has not been used in radioisotope studies of two-phase flows. The works of the authors of this article are, therefore, pioneering in this field.
The present paper describes the application of the gamma absorption method for investigations of the liquid–gas and liquid–solid particles mixtures flows in pipelines, and it provides example measurement results of the velocity of dispersed components obtained using the spectral analysis of the recorded signals. This article is a revised and significantly extended version of the conference publications [33,34].

2. Gamma Absorption Method for Measuring the Velocity of Dispersed Phase

The principle of the application of gamma absorption to test the two-phase flows in pipelines is shown in Figure 1. Part (a) shows the transport of a gas by a liquid in a horizontal pipe, while part (b) shows the hydrotransport of a solid phase in a vertical pipeline. In both of the cases, the purpose of the measurements was to determine the transport velocity of the minority components, which were air bubbles and solid grains, respectively.
A typical single-absorption setup consists of a closed radioactive source and a scintillation detector. The use of two such setups allows one to measure the velocity of the dispersed phase and possibly determine its concentration in the flowing mixture [19]. The sources used were placed at a specified distance from each other, L. The pipeline with the flowing medium was subjected to radiation by two parallel photon beams shaped by collimators. On the other side of the pipeline, mounted at the same distance from each other, were the detectors. At their outputs, counts I1(t) and I2(t) were obtained, depending on the intensity of the γ radiation passing through the pipe. The presence of a mixture in the measuring section causes the absorption and diffusion of photons, providing the stochastic signals x(t) and y(t). These signals which describe the instantaneous state of the stream in the examined sections.
For the flow to be determined, the transport time delay τ0 and the average velocity of the minority phase υS were determined based on the analysis of the measurement signals using the following relationship:
υ S = L τ 0
When it is transporting a water–air mixture, shown in Figure 1a, the velocity υS is equal to the velocity of the air bubbles, which are marked as υP. The velocity determined by Equation (1) is the average value of the cross-section of the pipeline that is covered by the width of the gamma ray beam that is emitted by the sources and at the time of measurement.

3. Measurement Stands

The article uses the measurement signals recorded at the test installations which were constructed at the AGH University of Science and Technology in Krakow and at the Wroclaw University of Environmental and Life Sciences. In the first one, liquid–gas flows (in this case water–air ones) were tested in a horizontal pipeline, with the flow rate ranging from 0.5 to 3.5 m/s. The pipeline measurement segment was made of a 4.5 m long plexiglass tube with an internal diameter of 30 mm. Radiation linear sources (241Am isotopes) and NaI(Tl) scintillation probes were located L = 97 mm apart on opposite sides of the tube. A general view of the measuring part of the laboratory stand is shown in Figure 2. A detailed description of the installation and measurement geometry is provided in [18,19]. Examples of the signals x(t) and y(t) registered during the BUB10 run (after centring and filtration) and their histograms are shown in Figure 3. The values on the vertical axis of the time distributions determine the number of counts achieved in 1 ms (1 kHz sampling rate). The time waveforms show the stochastic nature of the signals, and the histograms show their distributions, resembling normal distributions. Such symmetrical distributions indicate a properly set measurement geometry, which gives the method greatest sensitivity to the changes in the density of the flowing mixture at the selected energy of the gamma radiation sources. For filtering the signals, appropriately selected digital bandpass filters were used, which emphasise the useful components of the signals. The method of selecting the filter band and other methods of noise reduction are described in detail in [35].
In turn, the liquid–solid flows test system in a vertical pipeline was designed to model the hydrotransport of oceanic nodules from the Pacific seabed [34,36]. The main part of it is a vertical pipe with a diameter of 160 mm. Radiometric sets (241Am linear sources + NaI(Tl) probes) were mounted on the measuring section of an acrylic glass pipe. The distance between detectors in each set was L = 90 mm. Figure 4 shows fragments of the installation with the absorption kit installed. A diagram and detailed description of the installation can be found in [36]. Due to the mechanical strength of the nodules, specially prepared ceramic grains with the same geometric parameters and density as natural polymetallic nodules were used in the experiments.
Examples of signals recorded in the WRQ30 experiment (after centring and filtration) and the corresponding histograms are shown in Figure 5. The acquisition parameters were the same as in experiment BUB10, and there being a much smaller number of counts was due to the larger diameter of the pipe and higher absorption in the tested medium.
To analyse the registered stochastic signals, which were usually pre-processed, statistical methods such as cross-correlation, phase, differential, conditional averaging ones and other methods could be used [17,18,19,20,21,22,23,24]. The most often used one is the cross-correlation function (CCF), which allows one to determine the transport delay based on the identification of the main maximum of the CCF [14]. In this case, of the radioisotope measurements, the pass-band filtering of the measured signals is necessary due to noise and interference [34].

4. Phase Method of Signals Analysis

For the signals x(t) and y(t) in the frequency domain, we may use the analysis of the cross-spectral density function (CSDF) Gxy(f). In practice, a one-sided CSDF for the frequency range 0 < f < ∞ can be appointed. This is a complex quantity, which is described as follows [37]:
G _ x y ( f ) = 2 R x y ( τ ) e j 2 π f τ d τ
Rxy(τ) is the cross-correlation function defined by the dependents [17,37]:
R x y ( τ ) = lim T 1 T 0 T x ( t ) y ( t + τ ) d t
where T is the averaging time, and τ is the time delay.
The τ0 transportation delay time is designated by finding the position of the main maximum of the CCF.
The phase of the CSDF is related to the transport time delay τ0, as follows:
Φ x y ( f ) = a r c t g { Im [ G _ x y ( f ) ] Re [ G _ x y ( f ) ] } = 2 π f τ 0
Analysing the CSDF phase allows one to determine the transport time delay for the selected harmonic or a specific frequency interval. In the latter case, a linear approximation of the selected range Φxy(f) can be used. The basic characteristics of the method are discussed in [21,25,37,38].
The CSDF phase estimation is performed most often using the Welch procedure for discrete signal samples taken at constant sampling intervals Δt. The collection of samples is divided into Nd segments, each with a length of N. When one is using the discrete Fourier transform for each segment, the CSDF values are obtained for useful discrete frequency fk values (k = 0…(N − 1)/2), and the frequency domain resolution is Δ f = 1 / N Δ t . The numerical procedures used to calculate the value of the arc tg function result in discontinuities in the CSDF phase and the need to use the so-called phase unwrapping. The transport time delay is estimated from the CSDF phase Φ ˜ x y ( f k ) , which is smoothed using the segment averaging method (in the set of estimators determined for each data segment). The transport time delay is calculated using the formula [21]:
τ ^ 0 = 1 2 π k = 1 m f k Φ ˜ x y ( f k ) k = 1 m f k 2
where m is the number of CSDF phase values and frequencies included in the calculation of the simple regression.

5. Example Results of Measurements

Figure 6 shows the fragments Φ ˜ x y ( f k ) selected for analysis and obtained from experiments BUB10 (Figure 6a) and WRQ30 (Figure 6b), with the straight lines matched to a linear regression.
The behaviour of the estimator of the coherence function γxy(f), which is the normalised CSDF [37], can be used to select the appropriate frequency range for the linearisation of the characteristic Φ ˜ x y ( f k ) . In practice, the square of this function module is used, which for all of the frequencies take values that are from 0 to 1:
γ ^ x y 2 ( f k ) = | G ˜ _ x y ( f k ) | 2 G ˜ x ( f k ) G ˜ y ( f k )
where G ˜ x ( f k ) and G ˜ y ( f k ) are the autospectral density estimators for the x(t) and y(t) signals, respectively, which are smoothed in the segments, and G ˜ _ x y ( f k ) is the smoothed CSDF estimator.
The criterion for selecting m can be the frequency range for which γ ^ x y 2 ( f k ) achieves significant values [38]. Figure 7 shows the waveforms of the coherence functions for the signals obtained in experiments BUB10 (7a) and WRQ30 (7b). The dotted lines in both of the figures indicate the limit of the one-sided confidence interval Eα which was determined for significance level α = 0.05 using the relationship [39]:
E α = 1 ( 1 α ) 1 / ( N d 1 )
The standard uncertainty u ( τ ^ 0 ) that is calculated by use phase CSDF is given by [21,38]:
u ( τ ^ 0 ) = { 1 4 π 2 ( m 1 ) k = 1 m f k 2 [ k = 1 m Φ ˜ x y k 2 ( f k ) [ k = 1 m f k Φ ˜ x y k ( f k ) ] 2 k = 1 m f k 2 ] } 1 2
The complex uncertainty uc(υS) of the measurement of the velocity of the dispersed phase (with negligible uncertainty of the measurement track) depends on the uncertainty of the uncorrelated values of L and τ0:
u c ( υ S ) = ( υ S L ) 2 u B 2 ( L ) + ( υ S τ ^ 0 ) 2 u A 2 ( τ ^ 0 )
where the indices A and B represent the relevant uncertainties designated by the methods A and B, respectively [40,41].
For the analysis of the data obtained in the experiments, the presented phase method was used, and for comparison, the cross-correlation function was also used. Table 1 presents the velocity υS measurement results obtained for the CSDF phase and cross-correlation methods.
The uncertainties U0.95(υS) given in the table are the expanded uncertainties calculated using the assumption of the resulting normal distribution uc(υS):
U 0.95 ( υ S ) = k p u c ( υ S )
where kp—coverage factor (kp = 2 was assumed).
The measurements summarised in Table 1 for both the liquid–gas flow and the liquid–solids flow were selected from many experimental results based on the clearly occurring peak of the cross-correlation function between the analysed signals.
As it can be seen in Table 1, the results of the velocity measurement υS with both of the phase methods and with the use of CCF in individual experiments are practically the same. This confirms the convergence of the methods used. On the other hand, the values of the expanded uncertainty of velocity measurement for the phase method are several times smaller than they are for the cross-correlation method. This is due to the lower uncertainty values u A ( τ ^ 0 ) for the phase method.

6. Conclusions

The article discusses the use of the spectral density phase method to analyse the stochastic signals obtained using radioisotope measurements of two-phase liquid–gas flows in a horizontal pipeline and liquid–solid particles in a vertical pipeline. The analyses rely on the signals obtained from analysing the hydrotransport of the minority phase (air bubbles and ceramic models of ocean nodules) in the experimental setups. The purpose of the tests was to determine the average velocity of the minority phase in the analysed flows. The results of the measurements designated using the phase method were compared with those obtained for the comparative method of cross-correlation. In the former cases, the calculated uncertainties of the velocity measurements did not exceed 4% (phase method) and 9% (CCF) for the liquid–gas flow, and 1.5% (phase method) and 7% (CCF) for the liquid–solid particles flow, respectively. Furthermore, the cross-correlation method requires the filtering of the measurement signals with appropriate band filters, which is not necessary for the phase method. However, a difficulty in applying this method is the arbitrary choice of the analysis parameters related to the need to smooth the power spectral density estimators.

Author Contributions

Conceptualization, R.H.; Data curation, M.Z. and R.H.; Formal analysis, R.H.; Funding acquisition, R.H.; Investigation, R.H. and M.Z.; Methodology, R.H. and M.Z.; Project administration, R.H.; Resources, M.Z.; Software, R.H.; Supervision, R.H.; Validation, R.H., M.Z. and A.G.-J.; Visualization, M.Z. and R.H.; Writing—original draft, R.H.; Writing—review and editing, R.H.; Validation, R.H., M.Z. and A.G.-J. All authors have read and agreed to the published version of the manuscript.

Funding

This project is financed by the Minister of Education and Science of the Republic of Poland within the “Regional Initiative of Excellence” program for the years 2019–2023. Project number 027/RID/2018/19; amount granted 11 999 900 PLN.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Basic schema of measurement of gamma absorption of the following flows: (a) gas–liquid flow in a horizontal pipeline and (b) solid particles transported by a liquid in a vertical pipe; 1—sealed gamma-ray sources; 2—lead collimator of the source; 3—lead collimator of the scintillation probes; 4—scintillation probes; 5—pipeline.
Figure 1. Basic schema of measurement of gamma absorption of the following flows: (a) gas–liquid flow in a horizontal pipeline and (b) solid particles transported by a liquid in a vertical pipe; 1—sealed gamma-ray sources; 2—lead collimator of the source; 3—lead collimator of the scintillation probes; 4—scintillation probes; 5—pipeline.
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Figure 2. View of the measuring part of the hydraulic installation for liquid–gas flow tests in a horizontal pipeline.
Figure 2. View of the measuring part of the hydraulic installation for liquid–gas flow tests in a horizontal pipeline.
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Figure 3. Recorded signals (a) and their histograms (b) obtained in the experiment BUB10.
Figure 3. Recorded signals (a) and their histograms (b) obtained in the experiment BUB10.
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Figure 4. Fragments of the installation for testing liquid–solid particles flow in a vertical pipe: (a) view of the measuring part of the laboratory stand; (b) pipe with the water–solids mixture [36].
Figure 4. Fragments of the installation for testing liquid–solid particles flow in a vertical pipe: (a) view of the measuring part of the laboratory stand; (b) pipe with the water–solids mixture [36].
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Figure 5. Recorded signals (a) and their histograms (b) obtained in the experiment WRQ30.
Figure 5. Recorded signals (a) and their histograms (b) obtained in the experiment WRQ30.
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Figure 6. The phase of the CSDF in the experiments (a) BUB10 and (b) WRQ30.
Figure 6. The phase of the CSDF in the experiments (a) BUB10 and (b) WRQ30.
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Figure 7. The coherence function in the experiments (a) BUB10 and (b) WRQ30.
Figure 7. The coherence function in the experiments (a) BUB10 and (b) WRQ30.
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Table 1. Summary of the test results.
Table 1. Summary of the test results.
Type of FlowExperiment υ S ± U 0.95 ( υ S ) [m/s]
CSDF PhaseCCF
liquid–gasBUB60.71 ± 0.010.71 ± 0.04
BUB100.75 ± 0.010.75 ± 0.06
BUB151.55 ± 0.061.55 ± 0.14
liquid–solids WRQ302.98 ± 0.042.98 ± 0.20
WRQ511.99 ± 0.031.98 ± 0.13
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Hanus, R.; Zych, M.; Golijanek-Jędrzejczyk, A. Measurements of Dispersed Phase Velocity in Two-Phase Flows in Pipelines Using Gamma-Absorption Technique and Phase of the Cross-Spectral Density Function. Energies 2022, 15, 9526. https://doi.org/10.3390/en15249526

AMA Style

Hanus R, Zych M, Golijanek-Jędrzejczyk A. Measurements of Dispersed Phase Velocity in Two-Phase Flows in Pipelines Using Gamma-Absorption Technique and Phase of the Cross-Spectral Density Function. Energies. 2022; 15(24):9526. https://doi.org/10.3390/en15249526

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Hanus, Robert, Marcin Zych, and Anna Golijanek-Jędrzejczyk. 2022. "Measurements of Dispersed Phase Velocity in Two-Phase Flows in Pipelines Using Gamma-Absorption Technique and Phase of the Cross-Spectral Density Function" Energies 15, no. 24: 9526. https://doi.org/10.3390/en15249526

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