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Data Descriptor

Determination of Soil Behavior during Evaporation Using Geotechnical Datasets

Systems Engineering, Faculty of Engineering and Applied Science, University of Regina, 3737 Wascana Parkway Regina, Regina, SK S4S 0A2, Canada
*
Author to whom correspondence should be addressed.
Data 2022, 7(12), 174; https://doi.org/10.3390/data7120174
Submission received: 12 August 2022 / Revised: 8 November 2022 / Accepted: 1 December 2022 / Published: 6 December 2022

Abstract

:
Evaporation from soils is critical for agricultural water management. This requires a clear understanding of the water retention and soil shrinkage behavior of soils during water escape and due to fertilizers usage. Based on laboratory testing, this paper provides a comprehensive dataset generated for the determination of the geotechnical properties of inert silty sand and active lean clay using distilled water and saline pore fluid under ambient conditions. The tests include fluid-independent general soil properties, fluid-dependent specific soil properties, low-demand evaporation as a baseline, and high-demand evaporation to capture summer.
Dataset: 10.5683/SP3/U6N4EF.
Dataset License: Creative Commons Attribution-Non-Commercial 4.0 International License.

1. Summary

The semi-arid Canadian Prairies face an acute water shortage to support the regional agriculture economy [1]. During the summer growing season, the weather in this inland physiographic unit is primarily windy, dry, warm and sunny [2]. Similarly, the relatively uniform terrestrial landform, derived from several glacial advances and retreats, exhibits a wide range of textures and compositions in surface soils [3] along with poorly drained water networks [4]. These characteristics result in high evaporation from soil surfaces thereby limiting water availability for plant growth [5]. Evaporative fluxes are governed by the behavior of soils (inert and active), as characterized by the water retention curve (WRC) and the soil shrinkage curve (SSC) [6]. Furthermore, the common practice of using fertilizers to improve crop yield gradually increases the salt concentration in the soils thereby affecting both water retention and soil shrinkage. Therefore, a clear understanding of soil behavior during evaporation is critical to ensure sustainable farming in the area. This requires an accurately determined experimental dataset.
The purpose of this paper is to provide a comprehensive dataset based on laboratory testing. For this purpose, the interaction of inert (silty sand) and active (lean clay) soils with deionized water and saline solution was investigated [6,7]. The manuscript is divided into two main sections. The data description section gives context to the development of the datasets, a framework for the folder structure containing the various datasets, and a summary of the contents and variables in each dataset. Similarly, the methodology section describes the soils and pore fluids and the methods and equations required to calculate the relevant parameters for general soil properties, specific soil properties, and low-demand evaporation tests. Details on the datasets for high demand (regionally prevalent during a summer day) were provided earlier [8]. The atmospheric conditions, surface conditions, soil properties, and pore fluid properties were used to develop datasets for irrigation in the Canadian Prairies. These datasets are critical for predictive modeling and field monitoring. Whereas the datasets had to be regionally developed, the parameters are universally applicable.

2. Data Description

Figure 1 presents the file structure of the folders containing laboratory test data for soil evaporation. The “Soil Evaporation” root folder contains two main subfolders, namely, “1. Silty Sand” and “2. Lean Clay”. The data in these organized folders are described later in this paper. For each soil type, the “1. General Soil Properties” contain data used to determine soil characteristics that were independent of the pore fluid, namely, wet sieve, hydrometer, and specific gravity. Similarly, these folders contain several subfolders with data for each soil mixed with distilled water (“2. Water Pore Fluid”) and brine (“3. Brine Pore Fluid”).
Table 1 gives a summary of the dataset variables in the folders. The “1. Specific Soil Properties” contains data used to determine soil characteristics that were dependent on the pore-fluid, namely, liquid limit test, plastic limit test, and soil suction tests. The “2. Low Demand Evaporation” folder contains three sub-folders. In “1. Raw Data” there are two data files that were generated during evaporation testing, including air temperature, humidity, pressure, and total mass change. In “2. 3D Models” are individual sub-folders for each model that includes a folder of exported data files, a folder that contains all the pictures captured of the sample, and a folder that holds all of the project files used to construct the 3D model. In “3. Analyzed Data” are three data files that combine raw atmospheric data, evaporation data, and soil data, respectively. The “3. High Demand Evaporation” folder contains two sub-folders. The “1. Raw Data” contains eight separate files that were developed during testing, namely, air pressure, air temperature and humidity (four datasets at four sensor locations), air velocity, surface temperature, and sample weight. The analyzed folder contains one data file that combines all of the data in a single dataset.

3. Methodology

3.1. Soil Selection and Retrieval

The Canadian Soil Information Service (CanSIS) database contains water retention data for soils in the form of volumetric water content (θ) at critical matric suction values. Generally, regional soils range from sandy loam to clayey loam with variable amounts of sand (2.0–0.5 mm), silt (0.5–0.002 mm), and clay (<0.002 mm). To appreciate the range of agricultural soils, 25 irrigation districts from across southern Saskatchewan (Figure 2) were analyzed. These districts are in the form of variably shaped polygons, as delineated by the Saskatchewan Irrigation District Map (SIDM). The CanSIS and SIDM databases were merged to extract the weighted average values of θ and grain sizes for each district; the latter were converted to the Unified Soil Classification System (USCS) using [9]. Figure 3 gives the θ values corresponding to various soils in the irrigation districts. Regional soils range from silty sands (SM) to lean clays (CL) with θ varying as follows: 43–54% at 0 kPa, 15–45% at 33 kPa, and 8–27% at 1500 kPa. The selected soils, namely, silty sand (SM) from Avonlea [10] and a lean clay (CL) from Belle Plain [11], had θ values within the above ranges [6].
Representative soil samples were retrieved using a shovel, sealed in plastic bags to preclude impurities, and preserved in 20 L buckets. Soils were brought to and stored at the Advanced Geotechnical Testing Laboratory at the University of Regina following the Standard Practices for Preserving and Transporting Soil Samples (ASTM D4220/D4220M-14).

3.2. Pore Fluid Selection

The pore fluids were classified as “non-saline” and “very saline” in accordance with the salinity classes for agricultural soils, as defined by [12]. The non-saline fluid was essentially distilled water that contained less than 10 ppm of dissolved salts. In contrast, the saline fluid was prepared by mixing 1 L of distilled water with 5.50 g of NaCl and stirring until all of the solids had completely dissolved [7]. Based on molarity (0.15 M), the saline solution represented a pore fluid that would cause significant yield decrease [13].

3.3. General Soil Properties

The soils were classified as per the Standard Practice for Classification of Soils for Engineering Purposes (Unified Soil Classification System) (ASTM D2487-17). For this purpose, the general soil properties tests were conducted using distilled water. Located in “1. General Soil Properties”, the folders contain data for the following analyses: (i) wet sieve, (ii) hydrometer, and (iii) specific gravity. These tests are needed in part for classifying soils under the USCS and calculating various geotechnical parameters [14].
The wet sieve analysis was performed to determine the soil portion greater than 0.002 mm. The tests were conducted following the Standard Test Methods for Particle Size Distribution (Gradation) of Soils Using Sieve Analysis (ASTM D6913/D6913M-17). The stack included sieve numbers 4, 10, 20, 40, 60, 120, and 200 as well as a bottom container to collect material finer than 0.075 mm. The measured pan weight ( M s e ; g) pertained to the empty sieves and the measured total weight ( M s t ; g) was that of the sieve and the retained soil after oven drying. The soil weight ( M s s ; g) retained in each sieve was calculated according to the following equation:
M s s = M s t M s e
The percent retained ( P R s ; %) on each sieve and the pan was calculated from the soil weight ( M s s ; g) (Equation (1)) and the total weight ( M s f ; g), which was the sum total of all retained soil weights, using the following equation:
P R s = M s s M s f
The percent finer ( P F s ; %) was calculated using cumulative percent retained ( C P R s ; %), which was the cumulative sum of percent retained ( P R s ; %) (Equation (2)) in the following equation:
P F s = 1 C P R s
The percent lost ( P T s ; %) was the amount of soil unaccounted for during the sieving process and was calculated as follows:
P T s = 1 M s f M s i
The hydrometer analysis was performed to determine the soil portion less than 0.002 mm. The tests were conducted following the Standard Test Method for Particle Size Distribution (Gradation) of Fine-Grained Soils Using the Sedimentation (Hydrometer) Analysis (ASTM D7928-21). Fourteen data points at pre-determined times were collected over 48 h. The hydrometer reading ( R h ; mm) was measured at the top of the meniscus and was adjusted by the corrected hydrometer reading ( R c p ; mm) using temperature correction ( F t ; mm) (Equation (6)) and the measured zero correction ( F z ; mm) in the equation:
R c p = R h + F t F z
The temperature correction was an adjustment required because the test may not have occurred at exactly 20 °C water and was calculated using measured water temperature ( T ; °C) in the equation:
F t = 4.85 0.25 · T
The percent finer ( P F h ; %) was calculated using the measured dry soil weight ( W s h ; g), corrected hydrometer reading ( R c p ; mm) (Equation (5)) and specific gravity correction ( a s ) (Equation (8)) in the equation:
P F h = a s · R c p W s h · 100
The specific gravity correction ( a s ) was an adjustment required because the hydrometer was calibrated for a specific gravity value of 2.65, and calculated using the measured specific gravity ( G s ) in equation [14]:
a s = G s · 1.65 ( G s 1 ) · 2.65
The combined percent finer ( C P F h ; %) was calculated using the percent finer ( P F h ; %) (Equation (7)) and the percent finer than the number 200 sieve ( P F s 200 ; %) (Equation (3)) in the equation:
C P F h = P F h · P F s 200 100
The grain size ( D h ; mm) was calculated using the adjustment factor ( A h ) (Equation (11)), the effective length ( L h ; cm) (Equation (13)), and the measured time ( t h ; min) in the equation:
D h = A h · L h t h
The adjustment factor ( A h ) was calculated using the viscosity of water ( η ; g∙s∙cm−2) (Equation (12)) and the measured specific gravity ( G s ) in the equation:
A h = 30 · η ( G s 1 )
The viscosity of water ( η ; g∙s/cm2) was calculated using the measured temperature of water ( T h ; °C) in the equation:
η = ( 2.414 · 10 5 ) · ( 10 247.8 ( T h + 273.15 ) 140 ) 100
The effective length ( L h ; cm) pertains to the settling zone of soil particles with a known diameter in a given time. The length was calculated using the corrected reading for determination of effective length ( R c l ; cm) (Equation (14)) in the equation:
L h = 10.5 10.5 2.3 50 · R c l + 0.5 · 14 67 27.7
The corrected reading for determination of effective length ( R c l ; cm) was calculated using the hydrometer measurement ( R h ; mm) and meniscus correction measurement ( F z ; mm) in the equation:
R c l = R h + F z
The specific gravity ( G s ) tests were conducted following the Standard Test Methods for Specific Gravity of Soil Solids by Water Pycnometer (ASTM D854-14). Three replicate samples were tested, and the values were averaged. Specific gravity was calculated using the mass of soil ( M g s ; g) (Equation (16)) and the mass of equal volume of water as the soil solids ( M g s w p ; g) (Equation (17)) in the equation:
G s = M g s M g s w p
The mass of soil ( M g s ; g) was calculated using the measured mass of empty pan ( M g p ; g) and the mass of the pan and oven-dried soil together ( M g s p ; g) in the equation:
M g s = M g p + M g s p
The mass of equal volume of water as the soil solids ( M g s w p ; g) was calculated using the measured mass of the flask and water ( M g f w ; g), mass of the flask, water and soil ( M g f w s ; g), and mass of soil ( M g s ; g) (Equation (15)) in the equation:
M g s w p = ( M g f w + M g s ) M g f w

3.4. Specific Soil Properties

The specific soil properties include tests that were affected by pore fluid salinity. Located in “1. Specific Soil Properties”, the folders contain data for the following analyses: (i) liquid limit, (ii) plastic limit, and (iii) water retention. These tests were needed for classifying soils under the USCS and understanding soil behavior.
The liquid limit and the plastic limit analyses were performed to determine the gravimetric water contents at which the soil transitioned from liquid-to-plastic and plastic-to-semi-solid states, respectively. The tests were conducted following the Standard Test Methods for Liquid Limit, Plastic Limit, and Plasticity Index of Soils (ASTM D4318-17e1). Three tests were performed for each analysis to develop linear relation between water content (Equation (18)) and measured number of blows ( N L ) for liquid limit. The liquid limit ( L L ; %) water content corresponds to 25 blows ( N = 25 ). Three tests were performed to obtain a diameter ( D P = 3.18   mm ) of a soil thread without crumbling for plastic limit ( P L ; %). In both cases, water content ( w A ; %) was calculated using the measured mass of empty pan ( M A p ; g), measured mass of the pan and oven-dried soil together ( M A s p ; g), and measured mass of the pan and wetted soil together ( M A s p w ; g) in the equation:
w A = M A s p w M A s p M A s p M A p
Soil suction was determined following the Standard Test Method for Measurement of Soil Potential (Suction) using Filter Paper (ASTM D5298-16) through the Whatman No. 42 filter paper for simultaneous measurement of total and matric suction [15]. Details on the preparation steps are given by [6]. The bi-linear calibration curve (developed by Greacen et al. [16] and endorsed by ASTM) was used to ensure data accuracy [17]. The wetting and drying suction tests were both performed beginning with 100 g of oven-dried soil in ten separate glass jars. Wetting suction tests had between 1 g to 37 g of fluid (distilled or saline) added to achieve target gravimetric water contents ranging from 1% to 37%, in four percent increments. In contrast, drying suction tests had 38 g of fluid added and then sealed for 24 h to allow homogenization. The samples were allowed to desiccate under the ambient laboratory environment (with a measured temperature of 19.6 ± 0.4 °C and relative humidity of 21.7 ± 6.5%) until the target gravimetric water contents were achieved. The wetting and drying samples were then stored inside an insulated box for 30 days to ensure equilibration of filter paper for water content. Afterward, each jar was opened to measure the water content in the filter paper ( w f ; %) using the mass of filter paper ( M f ; g) (Equation (20)) and the mass of filter paper water ( M w ; g) (Equation (21)) in the equation:
w f = M w M f · 100
The mass of filter paper ( M f ; g) was calculated using mass measurements of the oven-dried filter paper and the warm metal container together ( M 2 ; g) and the warm metal container alone ( T h ; g) in the equation:
M f = M 2 T h
The mass of filter paper water ( M w ; g) was calculated using mass measurements of the cold metal container alone ( T c ; g), wet filter paper and cold metal container together ( M 1 ; g), oven-dried filter paper and warm metal container together ( M 2 ; g) and the warm metal container alone ( T h ; g) in the equation:
M w = M 1 M 2 T c + T h

3.5. Low Demand Evaporation

The low-demand evaporation tests were performed under ambient laboratory conditions, continuously capturing water loss from the soil and intermittently capturing 3D model information. Located in “3. Analyzed Data” of “2. Low Demand Evaporation”, the folders contain data for the following analyses: (i) atmosphere, (ii) evaporation, and (iii) soil. These tests were needed to study the interactions that occur between evaporation and the types of soil and pore fluids.
The atmospheric analyses were performed to characterize atmospheric conditions above the evaporating surfaces. Atmospheric measurements taken at 30 s intervals included pressure ( e a ; Pa), relative humidity ( h ; %), and temperature ( T a ; °C). Air density ( ρ a ; g∙m3) was calculated using air pressure ( e a ; Pa), air temperature ( T a u l ; °C), molar mass of dry air ( M a ; 28.96546 g∙mol1), molar mass of water ( M v ; 1.801528 g∙mol1), molar gas constant ( R ; 8.314472 J∙mol1∙°K1), mole fraction of water vapor ( x v ) (Equation (23)) and compressibility factor ( Z ) (Equation (25)) with the following equation [18]:
ρ a = P · M a Z · R · ( T a + 273.15 ) · [ 1 x v ( 1 M v M a ) ]
The mole fraction of water ( x v ) was calculated using air pressure ( e a ; Pa), relative humidity ( h ; %), enhancement factor ( f ) (Equation (24)), and saturated vapor pressure ( e s ; Pa) (Equation (28)) with the equation [18]:
x v = h · f · ( e s P i )
The enhancement factor ( f ) was calculated using air temperature ( T a ; °C), air pressure ( e a ; Pa), and the constants A (1.00062), B (3.14 × 10−8 Pa−1), and C (5.6 × 10−7 °C−2) with the equation [18]:
f = A + B · P + C · T a 2
The compressibility factor ( Z ) was calculated using air temperature ( T a ; °C), air pressure ( e a ; Pa), mole fraction of water ( x v ) and the constants a 0 (1.58123 × 10−6 °K∙Pa−1), a 1 (−2.9331 × 10−8 Pa−1), a 2 (1.1043 × 10−10 °K−1∙Pa−1), b 0 (5.707 × 10−6 °K∙Pa−1), b 1 (−2.051 × 10−8 Pa−1), c 0 (1.9898 × 10−4 °K∙Pa−1), c 1 (−2.376 × 10−6 Pa−1), d 0 (1.83 × 10−11 °K2∙Pa−2), and e 0 (−0.765 × 10−8 °K2∙Pa−2), with the equation [18]:
Z = 1 P i T a + 273.15 · [ a 0 + a 1 · T a + a 2 · T a 2 + ( b 0 + b 1 · T a ) · x v + ( c 0 + c 1 · T a ) · x v 2 ] + P i 2 ( T a + 273.15 ) 2 · ( d 0 + e 0 · x v 2 )  
The partial vapor pressure ( e a ; Pa), the force per unit area exerted by gas-state water in the atmosphere, was calculated at each atmospheric point using dew point temperature ( T d ; °C) (Equation (27)) [19]:
e a = 61.08 · exp ( 17.27 · T d T d + 237.3 )
The dew point temperature ( T d ; °C) was calculated using relative humidity ( h ; %) and air temperature ( T a ; °C) with the equation [19]:
T d = 237.3 ( ln ( h / 100 ) 17.27 + T a 237.3 + T a ) 1 ( ln ( h / 100 ) 17.27 + T a 237.3 + T a )
The saturated vapor pressure ( e s ; Pa), air temperature at which water vapor is in equilibrium with the surface boundary of liquid water, was calculated using air temperature ( T a ; °C) with the equation [20]:
e s = 61.08 · exp ( 17.27 · T a   o r   s 237.3 + T a   o r   s )
The vapor pressure deficit ( e d ; Pa), capacity in the atmosphere for water vapor to enter from the surface boundary of liquid water, was calculated at each atmospheric point using partial vapor pressure ( e a ; Pa) (Equation (26)) and saturated vapor pressure ( e s ; Pa) (Equation (28)) with the equation [21]:
e d = e s e a
The vapor density ( ρ v ; g∙m−3), mass per unit volume of water vapor in the climate chamber atmosphere, was calculated at each atmospheric point air temperature ( T a ; °C) and partial vapor pressure ( e a ; Pa) (Equation (26)) with the equation [19]:
ρ v = 2165 · e a 1000 · ( T a + 273.15 )
The vapor pressure gradient ( Δ ; Pa∙°C−1), gradient of the saturated vapor pressure function, and was calculated using saturated vapor pressure ( e s ; Pa) (Equation (28)) and measured air temperature ( T a ; °C) [20]:
Δ = e s · 4098 ( 234.3 + T a ) 2
The incoming longwave irradiation ( L i ; W∙m−2) was calculated using air temperature ( T a ; °C), air emissivity ( ε a ) (Equation (33)), and the Stefan–Boltzmann constant ( σ ; 5.670∙10−8 W∙m−2∙°C−4) with the equation [22]:
L i = ε a · σ · ( T a + 273.15 ) 4
The air emissivity ( ε a ) was calculated using air temperature ( T a ; °C) and partial vapor pressure ( e a ; Pa) (Equation (26)) with the equation [23]:
ε a = 0.7 + 5.95 e 5 · ( e a 100 ) · exp ( 1500 273.15 + T a )
The evaporation analyses were performed to characterize the evaporative flux conditions occurring at the surface. Evaporative flux ( Φ ; g∙s−1∙m−2) was calculated using change in measured mass ( Δ M ; g∙s−1) (Equation (35)) and average surface area ( S A ; cm2) (Equation (36)) with the equation:
Φ = Δ M · 1 S A 10 , 000
The change in measured mass ( Δ M ; g∙s−1) was calculated using mass measurements during 3D model captured in the CPS at time point one ( M 1 ; g) and time point two ( M 2 ; g), in the equation:
Δ M = M 2 M 1
The average surface area ( S A A ; cm2) was calculated using total surface area measurements (Equation (41)) at time point one ( S A 1 ; cm2) and time point two ( S A 2 ; cm2) in the equation:
S A A = ( S A 1 + S A 2 ) 2
The soil analyses were performed to characterize the soil conditions below the evaporating surface. The fluid mass ( M s f ; g) was calculated using mass measurements of the total sample ( M s t ; g), oven-dried soil ( M s s ; g), and sample cup ( M s c ; g) in the equation:
M s f = M s t M s s M s c
The volume of soil ( V s ; cm3) was calculated using measurements of oven-dried soil mass ( M s s ; g) and the specific gravity of the soil ( G s ) (Equation (15)) in the equation:
V s = M s s G s
The volume of fluid ( V f ; cm3) was calculated using fluid density ( ρ f ; g∙cm−3), total sample mass ( M s t ; g), oven-dried soil mass ( M s s ; g), and sample cup mass ( M s c ; g) in the equation:
V f = M s t ( M s s + M s c ) ρ f
The volume of voids, ( V v ; cm3) was calculated using volume of soil ( V s ; cm3) (Equation (38)) and measured sample volume ( V t ; cm3) obtained from 3D models in the equation:
V v = V t V s
The total surface area ( S A ; cm2) was calculated using measurements of the top surface area ( S A t o ; cm2) and the side surface area ( S A s i ; cm2) in the equation:
S A = S A t o + S A s i
The void ratio ( e ) was calculated using volume of soil ( V s ; cm3) (Equation (38)) and the volume of voids ( V v ; cm3) (Equation (40)) in the equation:
e = V v V s
The degree of saturation ( S ; %) was calculated using specific gravity ( G s ) (Equation (15)), void ratio ( e ) (Equation (42)) and gravimetric water content ( w ; %) (Equation (45)) in the equation:
S = e · G s w
The volumetric water content ( θ ; %) was calculated using fluid density ( ρ f ; g∙cm−3), specific gravity ( G s ) (Equation (15)), void ratio ( e ) (Equation (42)) and gravimetric water content ( w ; %) (Equation (45)) in the equation:
θ = G s e + 1 · w w
The gravimetric water content ( w ; %) was calculated using total sample mass ( M s t ; g), oven-dried soil mass ( M s s ; g), and sample cup mass ( M s c ; g) in the equation:
w = 100 · M s t ( M s s + M s c ) M s s
The surface area deformation ( D s ; %), the ratio of surface area (Equation (41)) at time ( S A t ; cm2) to the initial exposed area at 0 h ( S A o ), was calculated in the equation:
D s = 100 · ( 1 S A t S A o )
The volume deformation ( D v ; %), the ratio of measured total volume by 3D model at time ( V t t ; cm3) to the initial volume at 0 h ( V t 0 ), was calculated in the equation:
D v = 100 · ( 1 V t t V t o )
The axial deformation ( D h ; %), the ratio of measured 3D model height at time ( H t ; cm) to the initial height at 0 h ( H 0 ), was calculated in the equation:
D h = 100 · ( 1 H t H o )
The radial deformation ( D d ; %), the ratio of average 3D model diameter (Equation (50)) at time ( D t ; cm) to the initial diameter at 0 h ( D 0 ), was calculated in the equation:
D d = 100 · ( 1 D t D o )
The radial diameter ( D ; cm) was calculated using measured diameter on the 3D model in the X ( D x ; cm) and Y ( D y ; cm) Cartesian coordinate directions in the equation:
D = D x + D y 2

3.6. High Demand Evaporation

The high-demand evaporation experiments were performed under Canadian Prairie summer day conditions [24], continuously capturing water loss from the soil. Located in “3. Analyzed Data” of “2. High Demand Evaporation”, the folders contain data for atmosphere and evaporation in the “Data Summary” file. The high-demand tests include surface atmosphere information in addition to Equations (22) to (50) for integration into prediction models, which are described in detail by [8].

Author Contributions

Data curation and analysis, J.S.; supervision, S.A.; writing—original draft, J.S.; writing—review and editing, S.A. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by Natural Science and Engineering Research Council of Canada.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The root data folder was last accessed on 6 November 2022. The folder can be downloaded from https://borealisdata.ca/dataverse/soil-evaporation.

Acknowledgments

The authors would like to thank the University of Regina for providing laboratory and data repository space.

Conflicts of Interest

The authors declare no conflict of interest.

List of Symbols

ItemSymbolUnit
Adjustment FactorAhDimensionless
Aerodynamic ResistancerAs/m
Air EmissivityεADimensionless
Air Pressure (Interpolated)eAPa
Air Pressure (Measured)eAMPa
Air Velocity vm/s
Available EnergyQW/m2
Axial DeformationDh%
Bowen RatioβDimensionless
Cold Metal ContainerTcg
Cold Metal Container and Wet Filter PaperM1g
Combined Percent Finer CPFh%
Compressibility FactorZDimensionless
Corrected Hydrometer ReadingRcpmm
Cumulative Percent Retained CPRs%
Density (Air)ρAg/m3
Density (Vapor)ρVg/m3
Density (Water, Air Saturated)ρWSg/m3
Density (Water, Corrected)ρWg/m3
Dry Soil MassWshg
Effective LengthLhcm
Enhancement FactorfDimensionless
Evaporation RateEmm/day
Evaporative Latent HeatλJ/g
Evaporative Latent Heat FlowλEW
Filter Paper Water Contentwf%
Fluid Densityρfg/cm3
Fluid MassMsfg
Grain SizeDhmm
Gravimetric Water Contentw%
Heat Flux (Conductive Thermal)GW/m2
Heat Flux (Evaporative Latent)λEW/m2
Heat Flux (Longwave Radiant, Incoming)LiW/m2
Heat Flux (Longwave Radiant, Outgoing)LOW/m2
Heat Flux (Net Radiant)RnW/m2
Heat Flux (Sensible Thermal)HW/m2
Heat Flux (Shortwave Radiant, Incoming)SiW/m2
Heat Flux (Shortwave Radiant, Outgoing Corrected)SOW/m2
Heat Flux (Shortwave Radiant, Outgoing Measured)SOMW/m2
Height at Time tHtcm
Height at Time tDtcm
Hydrometer Reading Rhmm
Initial HeightH0cm
Initial HeightD0cm
Initial Mass Msig
Initial Sample VolumeVt0cm3
Initial Surface AreaSA0cm2
Isothermal CompressibilityκTDimensionless
Liquid LimitLL%
Mass of Empty PanMgpg
Mass of Empty PanMApg
Mass of Equal Volume of Water as SoilMgswpg
Mass of Filter PaperMfg
Mass of Filter Paper WaterMwg
Mass of Flask and WaterMgfwg
Mass of Flask, Water and SoilMgfwsg
Mass of Pan and Dry SoilMgspg
Mass of Pan and Dry SoilMAspg
Mass of Pan, Soil and WaterMAspwg
Mass of SoilMgsg
Mole Fraction of Water VaporXDimensionless
Number of BlowsNLDimensionless
Oven-Dried Soil MassMssg
Pan Weight Mseg
Percent Finer PFs%
Percent Finer than No. 200 SievePFs200%
Percent Lost PTs%
Percent Retained PRs%
Perfect FinerPFh%
Plastic LimitPL%
Psychrometric ConstantγPa/°C
Radial DeformationDd%
Radial DiameterDcm
Radial X DiameterDxcm
Radial Y DiameterDycm
Relative Humidityh%
Sample Cup MassMscg
Sample Mass (Interpolated)Mg
Sample Mass (Measured)MMg
Sample Mass (Rate of Change)∆Mg/s
Sample Surface AreaAm2
Sample VolumeVm3
Sample Volume at Time tVttcm3
SaturationS%
Side Surface AreaSAsicm2
Smallest Achievable DiameterDpmm
Soil Weight Mssg
Specific GravityGsDimensionless
Specific Gravity CorrectionasDimensionless
Surface Area at Time tSAtcm2
Surface Area DeformationDs%
Temperature (Air)TA°C
Temperature (Dew Point)TD°C
Temperature (Surface)TS°C
Temperature CorrectionFtmm
Temperature of WaterTh°C
Timethmin
Top Surface AreaSAtocm2
Total Mass Msfg
Total Sample MassMstg
Total Surface AreaSAcm2
Total Weight Mstg
Vapor FluxΦg/s∙m2
Vapor Pressure (Deficit)eDPa
Vapor Pressure (Gradient)Pa/°C
Vapor Pressure (Partial)eVPa
Vapor Pressure (Saturated, Atmosphere)eSPa
Vapor Pressure (Saturated, Surface)efPa
Viscosity of Waterηg∙s/cm2
Void RatioeDimensionless
Volume DeformationDv%
Volume of FluidVfcm3
Volume of SampleVtcm3
Volume of SoilVscm3
Volume of VoidsVvcm3
Volumetric Water Contentθ%
Warm Metal ContainerThg
Warm Metal Container and Dry Filter PaperM2g
Water ContentwL%
Water ContentwA%
Zero CorrectionFzmm

References

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Figure 1. File structure of the folders containing data.
Figure 1. File structure of the folders containing data.
Data 07 00174 g001
Figure 2. Saskatchewan irrigation districts and weighted average USCS classifications.
Figure 2. Saskatchewan irrigation districts and weighted average USCS classifications.
Data 07 00174 g002
Figure 3. Soil characterization of irrigation districts: (a) soil distribution and (b) water retention.
Figure 3. Soil characterization of irrigation districts: (a) soil distribution and (b) water retention.
Data 07 00174 g003
Table 1. Description of the dataset variables in the Prairie Climate folder.
Table 1. Description of the dataset variables in the Prairie Climate folder.
VariableUnitsDescription
General Soil Property Folder
Hydrometer
TimeminTime format in decimal minutes.
RcmMeasured hydrometer reading.
RcpcmCorrected hydrometer reading.
Percent Finer%Fraction of soil finer than corresponding grain size.
Pt%Combined fraction of soil finer than corresponding grain size.
RcLcmCorrected reading for the determination of effective length.
LcmEffective length of hydrometer from water surface.
A Calculation variable for diameter.
DmmSoil particle diameter.
T°CMeasured temperature reading.
FtcmTemperature correction to the measured reading.
FmcmMeniscus correction to the measured reading.
FzcmZero correction to accommodate deflocculating agent.
a Correction for specific gravity.
Gs Specific gravity.
ng∙s/cm2Water viscosity.
Specific Gravity
Flask + WatergMass of flask and water.
Flask + Water + SoilgMass of flask, water, and soil.
PangMass of pan.
Pan + SoilgMass of pan and dry soil.
SoilgMass of soil.
Equal MassgMass of equal volume of water as the soil solids.
Gs Specific gravity.
Wet Sieve
Sieve No. Sieve designation.
GmmGrain size.
PangMass of pan.
Pan + SoilgTotal of pan and dried, retained soil.
SoilgMass of soil.
Retained Soil%Percentage of soil retained on pan.
Cumulative Retained Soil%Cumulative percentage of soil retained on pans.
Percent Finer%Fraction of soil finer than corresponding grain size.
Specific Soil Property Folder
Liquid Limit
Pan No. The pan used for the test.
PangMass of the pan.
MpwsgMass of pan and wet soil.
MpdsgMass of pan and dry soil.
w%Measured moisture content.
N Number of blows.
MsgInitial dry soil mass.
MwgInitial fluid mass.
Plastic Limit
Pan No. The test numbers.
PangMass of the pan.
Pan + Wet SoilgMass of pan and wet soil.
Pan + Dry SoilgMass of pan and dry soil.
w%Measured moisture content.
DiametermmSmallest diameter.
Dry SoilgInitial dry soil mass.
FluidgInitial fluid mass.
Soil Suction
TcgMass of container at room temperature.
M1gMass of container and wet filter paper.
M2gMass of container and dry filter paper.
ThgMass of container after removed from oven.
MfgMass of dry filter paper.
MwgMass of water in filter paper.
Wf%Filter paper water content.
SLog10 kPaSoil suction, original units.
TSkPaSoil suction, converted units.
w%Gravimetric water content of the prepared soil.
Low Demand Evaporation Folder
Raw Data: Air Temperature, Humidity, Pressure
Index Measurement counter.
Date Date format in DD/MM/YYYY
Time Time format in HH:MM:SS
°C°CMeasured air temperature.
%RH%Measured relative humidity.
hPahPaMeasured air pressure.
Raw Data: Total Mass Change
Column A Date format in DD.MM.YYYY
Column B Time format in HH:MM:SS
Column CgMeasured sample weight
3D Models: Exports
File 1 Cup mesh, the raw 3D soil sample model.
File 2 Precise crop ring, used to extract the soil surface.
Pictures
All files Digital images used to construct the 3D models.
3D Models: Project
File 1 Agisoft Metashape project file.
File 2 Ancillary project data folder.
Analyzed Data: Atmospheric Data
Time Time format in HH:MM:SS AM/PM.
Count Measurement counter.
Minutes Time format in M.MM.
Hours Time format in H.HHH.
Air PressurePaMeasured air pressure.
Relative Humidity%Measured relative humidity.
Air Densityg/m3Calculated air density.
Vapor Densityg/m3Calculated absolute humidity.
Partial Vapor PressurePaCalculated partial vapor pressure.
Air Saturated Vapor PressurePaCalculated atmospheric saturated vapor pressure.
Deficit Vapor PressurePaCalculated atmospheric vapor pressure deficit.
Gradient Vapor PressurePaCalculated vapor pressure gradient.
Dew Point Temperature°CCalculated dew point temperature.
Mole Fraction Water Vapor Calculated mole fraction of water vapor.
Enhancement Factor Calculated enhancement factor of water vapor.
Compressibility Factor Calculated compressibility factor of water vapor.
Air Temperature°CMeasured air temperature at the indicated thermometer location.
Air Emissivity Calculated longwave emissivity of the atmosphere above the sample.
Incoming Longwave Radiant Heat FluxW/m2Calculated incoming infrared radiant energy.
Analyzed Data: Evaporation Data
Date Time format in DD.MM.YYYY.
Clock Time format in HH:MM:SS.
Clock HourhTime format in HH.
Clock MinuteminTime format in MM.
Clock SecondsTime format in SS.
Count Measurement counter.
SecondssTotal seconds.
MassgMeasured mass.
Mass DifferencegChange in mass since previous reading.
Mass ChangegChange in mass over time.
Mass Fluxg/s∙m2Change in mass over time, considering exposed surface area.
Measured Surface Areacm2Measured exposed surface area.
Analyzed Data: Soil Data
No. 3D model test number.
Time Planned test time; time format HH.
Date Date of test; time format MMMM, DD, HH
Time Actual test time; time format HH.H
Avg. Total MassgAverage total measured mass during 3D modelling session.
Soil MassgMass of oven-dried soil.
Cup MassgMass of the container.
Fluid MassgCalculated mass of the fluid in the sample.
Total Volumecm3Volume of the soil and fluid.
Soil Volumecm3Calculated volume of the soil.
Top Surface Areacm2Exposed surface area on the top of the soil sample.
Side Surface Areacm2Exposed surface area on the side of the soil sample.
Total Surface Areacm2Total exposed surface area.
Volume of Fluid cm3Calculated volume of the fluid.
Volume of Voidscm3Calculated volume of the voids.
Void Ratio Calculated ratio of the void volume to soil volume.
Saturation%Calculated saturation.
Volumetric Water Content%Calculated volumetric water content.
Gravimetric Water Content%Calculated gravimetric water content.
Axial LengthmmVertical length of the soil sample.
Radial Length XmmX-axis horizontal length of the soil sample.
Radial Length YmmY-axis horizontal length of the soil sample
Radial Length Avg.mmAverage horizontal length of the soil sample.
Surface Area Deformation%Change in surface area since first measurement.
Total Volume Deformation%Change in total volume since first measurement.
Axial Deformation%Change in vertical length since first measurement.
Radial Deformation%Change in horizontal length since first measurement.
Raw Data: Air Pressure
Index Measurement counter.
Date Date format in DD/MM/YYYY
Time Time format in HH:MM:SS
°C°CMeasured air temperature at the barometer location.
%RH%Measured relative humidity at the barometer location.
hPahPaMeasured air pressure at the barometer location.
PaPaConverted air pressure value.
High Demand Evaporation Folder
Raw Data: Air Temperature-Air Humidity
No. Measurement counter.
Time Time and date format in YYYY-MM-DD HH:MM:SS
Temperature°CMeasured air temperature at the indicated thermometer location.
Humidity%Measured relative humidity at the indicated hygrometer location.
Raw Data: Air Velocity
Index Measurement counter.
Time Time format in HH:MM:SS
Wind Valuem/sMeasured air velocity at the anemometer location.
Temp°CMeasured air temperature at the anemometer location.
Raw Data: Surface Temperature
Data Point Measurement counter.
Log Date Date format in YYYY-MM-DD
Log Time Time format in HH:MM:SS AM/PM
°C°CMeasured sample surface temperature.
Raw Data: Weight
Column A Date format in DD.MM.YYYY
Column B Time format in HH:MM:SS
Column CgMeasured sample weight.
Analyzed Data: Data Summary
Time Time format in HH:MM:SS AM/PM.
Count Measurement counter.
Minutes Time format in M.MM.
Hours Time format in H.HHH.
Velocitym/sMeasured air velocity at the anemometer location.
Aerodynamic Resistances/mCalculated aerodynamic resistance.
Air PressurePaMeasured air pressure at the barometer location.
Air Pressure InterpolatedPaCalculated air pressure at 10 s intervals using linear equation between 30 s intervals.
Psychrometric ConstantPa/°CCalculated psychrometric constant.
Relative Humidity%Measured relative humidity at the indicated hygrometer location.
Air Densityg/m3Calculated air density.
Vapor Densityg/m3Calculated absolute humidity.
Partial Vapor PressurePaCalculated partial vapor pressure.
Air Saturated Vapor PressurePaCalculated atmospheric saturated vapor pressure.
Deficit Vapor PressurePaCalculated atmospheric vapor pressure deficit.
Gradient Vapor PressurePaCalculated vapor pressure gradient.
Dew Point Temperature°CCalculated dew point temperature.
Mole Fraction Water Vapor Calculated mole fraction of water vapor.
Enhancement Factor Calculated enhancement factor of water vapor.
Compressibility Factor Calculated compressibility factor of water vapor.
Incoming Shortwave Radiant Heat FluxW/m2Calibrated incoming solar irradiance.
Air Temperature°CMeasured air temperature at the indicated thermometer location.
Air Emissivity Calculated longwave emissivity of the atmosphere above the sample.
Incoming Longwave Radiant Heat FluxW/m2Calculated incoming infrared radiant energy.
Sample Mass MeasuredgMeasured sample mass.
Sample Mass InterpolatedgCalculated sample mass using a polynomial regression
Sample Mass Rate of Changeg/sCalculated change in sample mass using.
Air Saturated Water Densityg/m3Calculated air saturated density of water.
Isothermal Compressibility Calculated isothermal compressibility.
Corrected Water Densityg/m3Calculated corrected water density.
Sample Volumem3Calculated sample volume.
Sample Surface Aream2Calculated sample surface area.
Surface Saturated Vapor PressurePaCalculated atmospheric saturated vapor pressure.
Total Vapor Fluxg/s ∙m2Calculated evaporative flux.
Evaporation Ratemm/dayCalculated rate of evaporation.
Outgoing Shortwave Radiant Heat FluxW/m2Measured outgoing solar irradiance.
Corrected Outgoing Shortwave Radiant Heat FluxW/m2Corrected outgoing solar irradiance.
Surface Temperature°CMeasured sample surface temperature.
Outgoing Longwave Radiant Heat FluxW/m2Calculated outgoing infrared radiant energy.
Net Radiant Heat FluxW/m2Calculated net radiant heat flux at the surface.
Bowen Ratio Calculated Bowen Ratio.
Sensible Thermal Heat FluxW/m2Calculated atmospheric thermal heat flux.
Conductive Thermal Heat FluxW/m2Calculated ground heat flux.
Available EnergyW/m2Calculated available energy.
Evaporative Latent HeatJ/gCalculated evaporative latent heat energy.
Evaporative Latent Heat FluxW/m2Calculated evaporative latent heat flux.
Evaporative Latent Heat FlowWCalculated evaporative latent heat flow.
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Suchan, J.; Azam, S. Determination of Soil Behavior during Evaporation Using Geotechnical Datasets. Data 2022, 7, 174. https://doi.org/10.3390/data7120174

AMA Style

Suchan J, Azam S. Determination of Soil Behavior during Evaporation Using Geotechnical Datasets. Data. 2022; 7(12):174. https://doi.org/10.3390/data7120174

Chicago/Turabian Style

Suchan, Jared, and Shahid Azam. 2022. "Determination of Soil Behavior during Evaporation Using Geotechnical Datasets" Data 7, no. 12: 174. https://doi.org/10.3390/data7120174

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