Difference between revisions of "Dilution gauging"

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=Quick summary=
 
=Quick summary=
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[[file:bms_sensor.png|thumb|500px|Figure 1: (a) Geophone and accelerometer installed in a watertight housing mounted on an impact plate and exemplary (b) geophone and (c) accelerometer signal of the identical single grain impact. SumIMP denotes the total number of peaks above the threshold amplitude Amin for the event shown. Amaxmax is the maximum amplitude registered during this event. Only positive amplitude values are considered.]]
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[[file:dilution_gauging2.png|thumb|250px|Figure 1: Dilution gauging in a fishway: making the dilution of the tracer (Rhodamine Wt) (source: Itagra.ct).]]
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[[file:bms_vortex_tube.png|thumb|500px|Figure 2: (a) Conceptual sketch of the vortex tube functionality and (b) vortex tube outlet at HPP Schiffmühle (source: VAW).]]
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[[file:dilution_gauging3.png|thumb|250px|Figure 2: Dilution gauging in a fishway: Mariotte device for continuous injection into the fishway (source: Itagra.ct).]]
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[[file:bms_vortex_tube2.png|thumb|500px|Figure 3: (a) Vortex tube outlet with mounted sensors and (b) vortex tube running during the field calibration (source: VAW).]]
 
  
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Developed by:
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Developed by:Francisco Javier Bravo, Itagra.ct
  
 
Date:
 
Date:
  
 
Type: [[:Category:Methods|Method]]
 
Type: [[:Category:Methods|Method]]
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Suitable for the following [[::Category:Measures|measures]]:
 
  
 
=Introduction=
 
=Introduction=
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The discharge for (a) is calculated as:
 
The discharge for (a) is calculated as:
  
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Q= c_0/c∙V/T
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<math>Q=\frac{c_0}{c}*\frac{V}{T}</math>
  
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Being c_0 the tracer concentration which is introduced in the watercourse with discharge Q. c is the concentration of the sample in volume V and T is equal to the time needed for the tracer to be transported downstream.
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being <math>Q={c_0}</math> the tracer concentration which is introduced in the watercourse with discharge ''Q''. ''c'' is the concentration of the sample in volume ''V'' and ''T'' is equal to the time needed for the tracer to be transported downstream.
  
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The formulae discharge for (b):
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The discharge formula for (b):
  
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Q=q.c_1/c_2
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<math>Q=q*\frac{c_1}{c_2}</math>
  
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Being c_1 the tracer concentration in the injection, q the constant injection flow for the tracer (e.g. using a Mariotte device) and c_2 the tracer concentration at the downstream point.
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being <math>{c_1}</math>  the tracer concentration in the injection, ''q'' the constant injection flow for the tracer (e.g. using a Mariotte device) and <math>{c_2}</math>  the tracer concentration at the downstream point.
  
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The choice of the tracer depends on several factors: the chemical characteristics of the water, the suspended sediment, the distance between the injection and measuring section, the type of flow to be measured, the sensitivity of the tracer measurement devices and the possible environmental impact of the tracer. Common tracers used: chemical (NaCl, NaI, NH4Cl) and fluorescent (fluorescein and Rhodamine WT).
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The tracer choice depends on several factors: chemical characteristics of the water, suspended sediment, distance between the injection and measuring section, type of flow to be measured, sensitivity of the tracer measurement devices and possible environmental impact of the tracer. Common tracers used: chemical (NaCl, NaI, NH4Cl) and fluorescent (fluorescein and Rhodamine WT).
  
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It is important to verify some conditions: the tracer cannot be absorbed in the medium and the solution must be well mixed. Emphasizing the last one, it is necessary to assure the good mixing length, which is the distance between the injection and measure sections ensuring a stable concentration of the diluted tracer.
+
It is important to comply with some conditions: the tracer cannot be absorbed and the solution must be well mixed. Emphasizing the last one, it is necessary to assure a good mixing length, which is the distance between the injection and measure sections, ensuring a stable concentration of the diluted tracer.
  
 
=Application=
 
=Application=
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This method has been used for ITAGRA-GEA to measure discharge into the fishways (Bravo-Córdoba y Sanz-Ronda, 2011; Fuentes-Pérez et al., 2016 and 2017; Sanz-Ronda et al., 2016; Bravo-Córdoba et al., 2018). One of the main aims was to improve the accuracy of the discharge coefficients related to technical fishways into the field. It was done through the continuous method, using Rodamine WT as a tracer and a portable fluorometer to measure the fluorescence of the samples (Figure 1).
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This method has been used for Itagra.ct to measure discharge into the fishways (Bravo-Córdoba y Sanz-Ronda, 2011; Fuentes-Pérez et al., 2016 and 2017; Sanz-Ronda et al., 2016; Bravo-Córdoba et al., 2018). One of the main aims was to improve the accuracy of the discharge coefficients related to technical fishways into the field. A continuous method, using Rodamine WT as a tracer and a portable fluorometer to measure the fluorescence of the samples,was applied (Figure 1 and 2).
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=Relevant mitigation measures and test cases=
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{{Suitable measures for Dilution gauging}}
  
 
=Other information=
 
=Other information=
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The total costs for the geophone and accelerometer sensors amount to approx. 885-1'330 €. The costs for the field computer, the analog-digital-converter, and the 3G modem are approx. 5'300-6'200 €. Additional costs for the installation, data transmission, and the calibration depending on the site conditions and set-up.
 
  
 
=Relevant literature=
 
=Relevant literature=
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*Albayrak, I., Müller-Hagmann, M., Boes, R.M. (2017). Calibration of Swiss Plate Geophone System for bedload monitoring in a sediment bypass tunnel. In Proc. 2nd Intl. Workshop on Sediment Bypass Tunnels (Sumi, T., ed.), paper FP16, Kyoto University, Kyoto, Japan
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*ISO 9555:1994. Measurement of liquid flow in open channels — Tracer dilution methods for the measurement of steady flow
  
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*Gray, J.R., Laronne, J.B., Marr, J.D.G. (2010). Bedload-surrogate Monitoring Technologies, US Geological Survey Scientific Investigations Report 2010-5091. US Geological Survey: Reston VA.
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*Tazioli, A. (2011). Experimental methods for river discharge measurements: Comparison among tracers and current meter. Hydrological Sciences Journal – Journal des Sciences Hydrologiques. 56. 1314-1324.  
  
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*Rickenmann, D., Turowski, J.M., Fritschi, B., Klaiber, A., Ludwig, A. (2012). Bedload transport measurements at the Erlenbach stream with geophones and automated basket samplers. Earth Surface Processes and Landforms, 37, 1000-1011.
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*Bravo‐Córdoba FJ, Sanz‐Ronda FJ. 2011. Evaluación de la eficiencia biológica de una escala de hendiduras verticales para la trucha autóctona (Salmo trutta L.) en la Cuenca del Duero. Master’s thesis. University of Valladolid, Spain.
  
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*Rickenmann, D., Turowski, J.M., Fritschi, B., Wyss, C., Laronne, J., Barzilai, R., Reid, I., Kreisler, A., Aigner, J., Seitz, H., Habersack, H. (2014). Bedload transport measurements with impact plate geophones: comparison of sensor calibration in different gravel-bed streams. Earth Surface Processes and Landforms, 39, 928-942.
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*Bravo‐Córdoba FJ, Sanz‐Ronda FJ, Ruiz‐Legazpi J, Celestino LF, Makrakis S. 2018. Fishway with two entrance branches: Understanding its performance for potamodromous Mediterranean barbels. Fisheries Management and Ecology 25(1): 12–21.
  
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*Wyss, C.R., Rickenmann, D., Fritschi, B., Turowski, J.M, Weitbrecht, V., Boes, R.M. (2016a). Laboratory flume experiments with the Swiss plate geophone bed load monitoring system: 1. Impulse counts and particle size identification. Water Resources Research, 52, 7744-7759.
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*Fuentes-Pérez JF, Sanz-Ronda FJ, Martínez de Azagra-Paredes A, García-Vega A, Martínez de Azagra A, García-Vega A. 2016. Nonuniform hydraulic behavior of pool-weir fishways: a tool to optimize its design and performance. Ecol Eng 86: 5–12.
  
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*Wyss, C.R., Rickenmann, D., Fritschi, B., Turowski, J.M, Weitbrecht, V., Boes, R.M. (2016b). Laboratory flume experiments with the Swiss plate geophone bed load monitoring system: 2. Application to field sites with direct bed load samples. Water Resources Research, 52, 7760-7778.
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*Fuentes-Pérez JF, García-Vega A, Sanz-Ronda FJ, Martínez de Azagra Paredes A. 2017. Villemonte’s approach: a general method for modelling uniform and non-uniform performance in stepped fishways. Knowl. Manag. Aquat. Ecosyst., 418, 23.
  
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*Sanz-Ronda FJ, Bravo-Córdoba FJ, Fuentes-Pérez JF, Castro-Santos T. 2016. Ascent ability of brown trout, Salmo trutta, and two Iberian cyprinids− Iberian barbel, Luciobarbus bocagei, and northern straight-mouth nase, Pseudochondrostoma duriense− in a vertical slot fishway. Knowledge and Management of Aquatic Ecosystems (417): 10.
  
 
=Contact information=
 
=Contact information=

Latest revision as of 15:25, 11 April 2020

Quick summary

Figure 1: Dilution gauging in a fishway: making the dilution of the tracer (Rhodamine Wt) (source: Itagra.ct).
Figure 2: Dilution gauging in a fishway: Mariotte device for continuous injection into the fishway (source: Itagra.ct).

Developed by:Francisco Javier Bravo, Itagra.ct

Date:

Type: Method

Introduction

This method requires the release of a known tracer concentration in a section of the river or fishway and the subsequent determination of the tracer concentration in a downstream section. It is based on the dilution relationships between the injection of the tracer and the discharge we want to know. There are two main different methods for the injection of the tracers into the flow: (a) instantaneous or integration method and (b) continuous method.

The discharge for (a) is calculated as:

being the tracer concentration which is introduced in the watercourse with discharge Q. c is the concentration of the sample in volume V and T is equal to the time needed for the tracer to be transported downstream.

The discharge formula for (b):

being the tracer concentration in the injection, q the constant injection flow for the tracer (e.g. using a Mariotte device) and the tracer concentration at the downstream point.

The tracer choice depends on several factors: chemical characteristics of the water, suspended sediment, distance between the injection and measuring section, type of flow to be measured, sensitivity of the tracer measurement devices and possible environmental impact of the tracer. Common tracers used: chemical (NaCl, NaI, NH4Cl) and fluorescent (fluorescein and Rhodamine WT).

It is important to comply with some conditions: the tracer cannot be absorbed and the solution must be well mixed. Emphasizing the last one, it is necessary to assure a good mixing length, which is the distance between the injection and measure sections, ensuring a stable concentration of the diluted tracer.

Application

This method has been used for Itagra.ct to measure discharge into the fishways (Bravo-Córdoba y Sanz-Ronda, 2011; Fuentes-Pérez et al., 2016 and 2017; Sanz-Ronda et al., 2016; Bravo-Córdoba et al., 2018). One of the main aims was to improve the accuracy of the discharge coefficients related to technical fishways into the field. A continuous method, using Rodamine WT as a tracer and a portable fluorometer to measure the fluorescence of the samples,was applied (Figure 1 and 2).

Relevant mitigation measures and test cases

Relevant measures
Baffle fishways
Fish lifts, screws, locks, and others
Fishways for eels and lampreys
Nature-like fishways
Operational measures (turbine operations, spillway passage)
Pool-type fishways
Vertical slot fishways
Relevant test cases Applied in test case?
Guma and Vadocondes test cases Yes

Other information

Relevant literature

  • ISO 9555:1994. Measurement of liquid flow in open channels — Tracer dilution methods for the measurement of steady flow
  • Tazioli, A. (2011). Experimental methods for river discharge measurements: Comparison among tracers and current meter. Hydrological Sciences Journal – Journal des Sciences Hydrologiques. 56. 1314-1324.
  • Bravo‐Córdoba FJ, Sanz‐Ronda FJ. 2011. Evaluación de la eficiencia biológica de una escala de hendiduras verticales para la trucha autóctona (Salmo trutta L.) en la Cuenca del Duero. Master’s thesis. University of Valladolid, Spain.
  • Bravo‐Córdoba FJ, Sanz‐Ronda FJ, Ruiz‐Legazpi J, Celestino LF, Makrakis S. 2018. Fishway with two entrance branches: Understanding its performance for potamodromous Mediterranean barbels. Fisheries Management and Ecology 25(1): 12–21.
  • Fuentes-Pérez JF, Sanz-Ronda FJ, Martínez de Azagra-Paredes A, García-Vega A, Martínez de Azagra A, García-Vega A. 2016. Nonuniform hydraulic behavior of pool-weir fishways: a tool to optimize its design and performance. Ecol Eng 86: 5–12.
  • Fuentes-Pérez JF, García-Vega A, Sanz-Ronda FJ, Martínez de Azagra Paredes A. 2017. Villemonte’s approach: a general method for modelling uniform and non-uniform performance in stepped fishways. Knowl. Manag. Aquat. Ecosyst., 418, 23.
  • Sanz-Ronda FJ, Bravo-Córdoba FJ, Fuentes-Pérez JF, Castro-Santos T. 2016. Ascent ability of brown trout, Salmo trutta, and two Iberian cyprinids− Iberian barbel, Luciobarbus bocagei, and northern straight-mouth nase, Pseudochondrostoma duriense− in a vertical slot fishway. Knowledge and Management of Aquatic Ecosystems (417): 10.

Contact information

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