Difference between revisions of "Salinity sensors"

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See also: [[Instruments and sensors to measure environmental parameters]]
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==Practical Salinity==
  
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In the course of time, various methods have been developed to determine the salinity of seawater, see the article [[Salinity]]. The most practical method currently used is through electrical conductivity. Because this is an indirect method, an accurate relationship has been established between the conductivity <math>C</math> and the salinity <math>S</math> as a function of temperature <math>T</math> and pressure <math>p</math>. The salinity determined in this way is called the 'practical salinity'. The accuracy with which the conductivity of seawater can be measured is limited for reasons listed later in this article. Possible measurement errors can be eliminated, at least partly, by considering the relative conductivity <math>R</math>, the seawater conductivity <math>C(S,T)</math> relative to the conductivity <math>C(35,15)</math> of a standard saline solution at 15<sup>o</sup>C containing 32.4356 g KCl in a mass of 1 kg. The salinity of this standard solution is exactly 35. We omit pressure because it is only relevant for the deep ocean. The relationship between the salinity <math>S(T)</math> and the relative conductivity <math>R=R(S,T)</math> reads:
  
==Salinity Definition==
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<math>S(T) = S(15) + \Delta S(T) , \qquad R=\Large\frac{C(S,T)}{C(35,15)}\normalsize \qquad (1)</math>
This definition is impractical and the procedure difficult to carry out with precision. Alternatively, other parameters have been used in recent history as a proxy to calculate salinity.
 
  
==='''Salinity measurements and definitions throughout history'''===
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<math>S(15)=0.008-0.1692\,R^{1/2}+25.3851\,R+14.0941\,R{3/2}-7.0261\,R^2+2.7081\,R^{5/2} , \qquad (2)</math>
  
Although attempts have been made throughout history (as far as Ancient Greece times) to address the "saltiness" of seawater, the low sensitivity of the analytic methods meant that measurements were not sufficiently accurate to be considered. During the Modern History new and more precise methodologies were developed: weighing after evaporation (Boyle,1693; see Birch, 1965), solvent extraction (Lavoisier, 1772) and precipitation (Bergman, 1784). In 1865, Forchhammer introduced the term salinity and dedicated himself to measure individual components of seasalt rather than the total salinity. He found that the ratio of major salts in samples of seawater from various locations was constant. This constant ratio is known as Forchhammer's Principle, or the Principle of Constant Proportions, from which the salinity could be calculated from the chlorine content. Towards the end of the nineteenth century, William Dittmar, following the work of Forchhammer, tested several methods to analyse the salinity and chemical composition of seawater. The Dittmar methods for chemical analysis of the seawater were extremely precise. Dittmar analysed the chlorine content in seawater using  silver nitrate precipitation of the chloride, and compared it with synthetically prepared seawater samples to vouch for the method's accuracy. Dittmar later analysed 77 samples taken during the Challenger expedition and noticed the same constancy of composition observed by Forchhammer: "although the concentration of the waters is very different, the percentage composition of the dissolved material is ''almost'' the same in all cases". <ref> William J. Wallace (1974). The Development of the Chlorinity/Salinity Concept in Oceanography. Amsterdam: Elsevier. 239. </ref>  
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<math>\Delta S(T)= \Large\frac{T-15}{1+0.0162(T-15)}\normalsize  (0.0005-0.0056\,R^{1/2} -0.0066\,R-0.0375\,R^{3/2}+0.0636\,R^2-0.0144\,R^{5/2}) , \qquad (3)</math>
[[Image:DittmarTbl.PNG |thumb|400px|align:right| Constant composition of seawater (Dittmar, 1884)]]Still, a clear definition of salinity and international standard were yet to be developed.
 
In 1889, Martin Knudsen was named by [[International Council for the Exploration of the Sea (ICES)| ICES]] to preside a commission to address the salinity issues, chlorine was established as a proxy to calculate salinity. Knudsen and his colleagues proposed the following equation to calculate salinity based on chlorine percentage, chlorinity.
 
S = 0.03 + 1.805Cl
 
  
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for <math> 2 \, \le S \le \, 42  </math>.  If R=1 we have S=35.
  
  
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==Sensors==
  
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===Platinum Electrode Conductivity Sensor===
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[[Image: electrode_conductivity.JPG | 300px| thumb |right| Electrode Conductivity principle]]
  
and in 1902 the following definition was published:
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As the practical salinity is not a physical parameter that can be measured directly, “Salinity Sensors” do not exist. What is commonly referred to as a salinity sensor is in fact a conductivity sensor.
"Salinity is the total amount of solid materials, in grams, dissolved in one kilogram of sea water when all the carbonate has been converted to oxide, the bromine and iodine replaced by chlorine and all organic matter completely oxidized <ref> http://www.aslo.org/lo/toc/vol_14/issue_3/0437.pdf </ref> <ref>KNUDSEN,  M. 1901. Hydrographical tables.  G.E.C. Gad, Copenhagen, 63p </ref>.Although this is a correct definition, the methodology is impractical and difficult to carry out with precision.
 
 
 
 
 
  
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This Conductivity Sensor measures the ability of a solution to conduct an electric current between two electrodes. In solution, the current flows by ion transport; therefore, an increasing concentration of ions in the solution will result in higher conductivity values. Conductance is defined as the reciprocal of resistance. When resistance is measured in ohms, conductance is measured using the SI unit, siemens (formerly known as a mho). Since the siemens is a very large unit, aqueous samples are commonly measured in microsiemens, or µS.
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[[Image: conductivity cell.JPG | 400px| thumb| right| A conductivity cell. Current flows through the seawater between platinum electrodes in a cylinder of borosilicate glass 191 mm long with an inside diameter between the electrodes of 4 mm. The electric field lines (solid lines) are confined to the interior of the cell in this design making the measured conductivity (and instrument calibration) independent of objects near the cell. ''From Sea-Bird Electronics'']]
  
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Conductivity, <math>C</math>, is found using the following formula:
  
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<math>C=G\cdot kc  , \qquad (4)</math>
  
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where <math>G</math> is the conductance, and <math>kc</math> is the cell constant. The cell constant is determined for a probe using the following formula:
  
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<math>kc = \Large\frac{d}{A}\normalsize  , \qquad (5)</math> 
  
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where <math> d </math> is the distance between the two electrodes, and <math>A</math> is the area of the electrode surface. The conductivity value is found by multiplying conductance and the cell constant.
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A potential difference is applied to the two probe electrodes in the Salinity Sensor. The resulting current is proportional to the conductivity of the solution. This current is converted into a voltage.
  
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===Electrodeless Conductivity Sensor (Inductive)===
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[[Image: Induktive_Messung__eng.jpg|thumb|250px|right| Inductive conductivity sensor
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principle]]
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Electrodeless conductivity sensors use inductive coils. The inductive conductivity sensor consists of two coils which are incorporated next to one another in a polymer or ceramic body. These coils form current transformers. The sensor is designed so part of the liquid media forms a closed conductive current path passing through the coils. Current is applied to the primary coil (generating coil), which induces an alternating voltage in the liquid loop. In liquids which conduct electricity, this causes a current flow captured by the second coil (receiving coil), which is proportional to the conductivity of the sample solution.
  
  
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==Comparing the sensors==
  
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===Electrode Sensors===
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*The main advantages of electrode sensors are:
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**there is no proximity effect, the sensor can be mounted next to other sensors without interference
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**easily calibrated in small baths
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*The main disadvantages are:
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**any changes in the cell constant will be reflected in the conductivity, and the cell cannot be cleaned in the field
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**electrodes are subject to corrosion or damage (however, most sensors used in oceanography are inside a cell that prevents this, as shown in the image above)
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**electrodes inside a cell need seawater pumping which limits the measuring rate
  
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===Inductive Sensors===
  
==Sensors==
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*The main advantages of inductive sensors are:
Salinity is a ratio and not a physical parameter that can be measured. Thus, “Salinity sensors” do not exist. There are several different ways to calculate this ratio with pros and cons for each method.  
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**robust construction
 
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**they can be cleaned with soap or solvents and a brush.  
'''Salinity Scales'''
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**there are no electrodes, so there is no possibility of their damage.  
 
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*The main disadvantages are:
 
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**a significant part of the measurement is external leading to major consequences resulting from this external field. The inductive sensors require a 3 inches radius from  any other surface, from adjacent sensors. It is particularly difficult to address this problem in companion mounts such as ARGO floats or [[Biofouling | biological fouling]].
===Refractometer===
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**mounting  and calibration of the sensor to companion packages (Argo floats, current meters, AUVs, etc.) must be undertaken to avoid intrusion into the external area. Because final package geometry influences the results, the calibration must be performed on the fully assembled package.
 
 
===Conductivity meter===
 
 
 
 
 
 
 
 
 
 
 
'''Calibration'''
 
  
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==Calibration==
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*Zero Calibration Point: Simply perform this calibration point with the probe out of any liquid or solution (e.g., in the air). A very small voltage reading will be read. Call this value 0 ppt.
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*Standard Solution Calibration Point: Place the Salinity Sensor into a standard solution (solution of known concentration). Wait for the displayed voltage to stabilize. Enter the value of the standard solution (e.g., 35).
  
  
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==Related articles==
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:[[Salinity]]
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:[[Seawater density]]
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:[[Instruments and sensors to measure environmental parameters]]
  
==See also==
 
Historical overview of salinity measurements and definitions
 
  
[[Category:Theme 9]]
 
[[Category:Techniques and methods in coastal management]]
 
[[Category:Hydrological processes and water]]
 
  
==References==
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{{author
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|AuthorID=26289
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|AuthorFullName=Souza Dias, Francisco
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|AuthorName=Francisco Souza Dias}}
  
<references/>
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[[Category:Coastal and marine observation and monitoring]]
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[[Category:Observation of chemical parameters]]

Latest revision as of 20:36, 20 December 2020

Practical Salinity

In the course of time, various methods have been developed to determine the salinity of seawater, see the article Salinity. The most practical method currently used is through electrical conductivity. Because this is an indirect method, an accurate relationship has been established between the conductivity [math]C[/math] and the salinity [math]S[/math] as a function of temperature [math]T[/math] and pressure [math]p[/math]. The salinity determined in this way is called the 'practical salinity'. The accuracy with which the conductivity of seawater can be measured is limited for reasons listed later in this article. Possible measurement errors can be eliminated, at least partly, by considering the relative conductivity [math]R[/math], the seawater conductivity [math]C(S,T)[/math] relative to the conductivity [math]C(35,15)[/math] of a standard saline solution at 15oC containing 32.4356 g KCl in a mass of 1 kg. The salinity of this standard solution is exactly 35. We omit pressure because it is only relevant for the deep ocean. The relationship between the salinity [math]S(T)[/math] and the relative conductivity [math]R=R(S,T)[/math] reads:

[math]S(T) = S(15) + \Delta S(T) , \qquad R=\Large\frac{C(S,T)}{C(35,15)}\normalsize , \qquad (1)[/math]

[math]S(15)=0.008-0.1692\,R^{1/2}+25.3851\,R+14.0941\,R{3/2}-7.0261\,R^2+2.7081\,R^{5/2} , \qquad (2)[/math]

[math]\Delta S(T)= \Large\frac{T-15}{1+0.0162(T-15)}\normalsize (0.0005-0.0056\,R^{1/2} -0.0066\,R-0.0375\,R^{3/2}+0.0636\,R^2-0.0144\,R^{5/2}) , \qquad (3)[/math]

for [math] 2 \, \le S \le \, 42 [/math]. If R=1 we have S=35.


Sensors

Platinum Electrode Conductivity Sensor

Electrode Conductivity principle

As the practical salinity is not a physical parameter that can be measured directly, “Salinity Sensors” do not exist. What is commonly referred to as a salinity sensor is in fact a conductivity sensor.

This Conductivity Sensor measures the ability of a solution to conduct an electric current between two electrodes. In solution, the current flows by ion transport; therefore, an increasing concentration of ions in the solution will result in higher conductivity values. Conductance is defined as the reciprocal of resistance. When resistance is measured in ohms, conductance is measured using the SI unit, siemens (formerly known as a mho). Since the siemens is a very large unit, aqueous samples are commonly measured in microsiemens, or µS.

A conductivity cell. Current flows through the seawater between platinum electrodes in a cylinder of borosilicate glass 191 mm long with an inside diameter between the electrodes of 4 mm. The electric field lines (solid lines) are confined to the interior of the cell in this design making the measured conductivity (and instrument calibration) independent of objects near the cell. From Sea-Bird Electronics

Conductivity, [math]C[/math], is found using the following formula:

[math]C=G\cdot kc , \qquad (4)[/math]

where [math]G[/math] is the conductance, and [math]kc[/math] is the cell constant. The cell constant is determined for a probe using the following formula:

[math]kc = \Large\frac{d}{A}\normalsize , \qquad (5)[/math]

where [math] d [/math] is the distance between the two electrodes, and [math]A[/math] is the area of the electrode surface. The conductivity value is found by multiplying conductance and the cell constant. A potential difference is applied to the two probe electrodes in the Salinity Sensor. The resulting current is proportional to the conductivity of the solution. This current is converted into a voltage.

Electrodeless Conductivity Sensor (Inductive)

Inductive conductivity sensor principle

Electrodeless conductivity sensors use inductive coils. The inductive conductivity sensor consists of two coils which are incorporated next to one another in a polymer or ceramic body. These coils form current transformers. The sensor is designed so part of the liquid media forms a closed conductive current path passing through the coils. Current is applied to the primary coil (generating coil), which induces an alternating voltage in the liquid loop. In liquids which conduct electricity, this causes a current flow captured by the second coil (receiving coil), which is proportional to the conductivity of the sample solution.


Comparing the sensors

Electrode Sensors

  • The main advantages of electrode sensors are:
    • there is no proximity effect, the sensor can be mounted next to other sensors without interference
    • easily calibrated in small baths
  • The main disadvantages are:
    • any changes in the cell constant will be reflected in the conductivity, and the cell cannot be cleaned in the field
    • electrodes are subject to corrosion or damage (however, most sensors used in oceanography are inside a cell that prevents this, as shown in the image above)
    • electrodes inside a cell need seawater pumping which limits the measuring rate

Inductive Sensors

  • The main advantages of inductive sensors are:
    • robust construction
    • they can be cleaned with soap or solvents and a brush.
    • there are no electrodes, so there is no possibility of their damage.
  • The main disadvantages are:
    • a significant part of the measurement is external leading to major consequences resulting from this external field. The inductive sensors require a 3 inches radius from any other surface, from adjacent sensors. It is particularly difficult to address this problem in companion mounts such as ARGO floats or biological fouling.
    • mounting and calibration of the sensor to companion packages (Argo floats, current meters, AUVs, etc.) must be undertaken to avoid intrusion into the external area. Because final package geometry influences the results, the calibration must be performed on the fully assembled package.

Calibration

  • Zero Calibration Point: Simply perform this calibration point with the probe out of any liquid or solution (e.g., in the air). A very small voltage reading will be read. Call this value 0 ppt.
  • Standard Solution Calibration Point: Place the Salinity Sensor into a standard solution (solution of known concentration). Wait for the displayed voltage to stabilize. Enter the value of the standard solution (e.g., 35).


Related articles

Salinity
Seawater density
Instruments and sensors to measure environmental parameters


The main author of this article is Souza Dias, Francisco
Please note that others may also have edited the contents of this article.

Citation: Souza Dias, Francisco (2020): Salinity sensors. Available from http://www.coastalwiki.org/wiki/Salinity_sensors [accessed on 22-11-2024]