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a USDA-ARS, George E. Brown, Jr. Salinity Lab., 450 W. Big Springs Rd, Riverside, CA 92507
b USDA-ARS, Water Management Research Lab., 9611 S. Riverbend Ave., Parlier, CA 93648
c Alterra-ILRI, P.O. Box 47, 6700 AA Wageningen, The Netherlands
d Dep. of Plants, Soils, and Biometeorology, Utah State Univ., Logan, UT 84322-4820
* Corresponding author (tkelleners{at}ussl.ars.usda.gov).
| ABSTRACT |
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Abbreviations: TDR, time domain reflectometry
| INTRODUCTION |
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Among the electromagnetic techniques, time domain reflectometry (TDR) is the most common method (e.g., Fellner-Felldeg, 1969; Topp et al., 1980; Baker and Allmaras, 1990; Heimovaara, 1994; Gardner et al., 2000; Noborio, 2001). However, the emergence of high quality, low-cost high frequency oscillators has led to increased interest in capacitance techniques (e.g., Dean et al., 1987; Evett and Steiner, 1995; Paltineanu and Starr, 1997). Capacitance probes are relatively inexpensive and easy to operate. Furthermore, the sensor geometry is very adaptable, facilitating the development of a variety of configurations (Robinson et al., 1998). However, capacitance probes are influenced by soil type and require calibration. Also, there is concern about the influence of soil salinity and soil temperature on capacitance sensors.
Several investigators have calibrated capacitance sensors for particular soil types (e.g., Bell et al., 1987; Evett and Steiner, 1995; Mead et al., 1995; Paltineanu and Starr, 1997; Morgan et al., 1999; Baumhardt et al., 2000). In these studies, the readout from the sensors (a frequency) is related directly to the water content of the soil. Generally, a scaled frequency is used to compensate for differences between sensors. From a theoretical standpoint, however, it must be realized that capacitance sensors actually react to the permittivity of the soil, which in turn is a function of the water content. Splitting the calibration into two stages, one in which frequency is related to permittivity, and one in which permittivity is related to soil water content, permits a more physically based calibration procedure.
A major advantage of the two-stage approach is that the relationship between permittivity and soil water content can be described by existing dielectric mixing models (e.g., Dobson et al., 1985; Dirksen and Dasberg, 1993; Friedman, 1998) or empirical models (e.g., Topp et al., 1980; Malicki et al., 1996). The relationship between frequency and permittivity, on the other hand, can be described with help of electric circuit theory as shown by Dean (1994) and Robinson et al. (1998). Electric circuit theory also makes it possible to account for the effect of dielectric losses due to ionic conductivity and relaxation on the sensor frequency reading. This implies that temperature effects on the sensor reading, which work primarily through an increase or decrease in ionic conductivity, can be accounted for as well.
In this work we develop an electric circuit model for capacitance probe sensors marketed as EnviroSCAN (Sentek Pty Ltd., Kent Town, South Australia). More specifically, the objectives of this study are (i) to determine the four sensor constants in the electric circuit model for the EnviroSCAN sensors, (ii) to demonstrate the effect of ionic conductivity on the sensor readings, (iii) to test the ability of the circuit model to correct for conductivity effects, and (iv) to develop a practical approach to calibrate the circuit model using only frequency readings in air and water.
| THEORY |
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![]() | [1] |
r is the relative permittivity (-) and
0 is the permittivity in vacuum (L3 T4 M1 I2) (= 8.8542 x 1012 F m1).
The capacitance can be assessed by measuring the resonant frequency in an oscillator circuit:
![]() | [2] |
It is assumed that the oscillator circuit of the capacitance probe sensors used in this study can be represented by the equivalent electric circuit shown in Fig. 1
. The figure shows that the total circuit capacitance is made up of three components, which act both in parallel and in series:
![]() | [3] |
r,m
0 and Cp = gp
r,p
0, where the subscript m denotes the medium and the subscript p denotes the plastic access tube.
|
![]() | [4] |
Equation [4] is valid if the medium behaves as a nonlossy dielectric. In reality, losses due to relaxation and in some circumstances due to ionic conductivity result in lossy dielectrics. The relative permittivity of the medium should then be represented by a complex quantity
*r that has a real part
'r describing energy storage and an imaginary part
''r describing losses:
![]() | [5] |
'r is referred to as
r. The
''r term in Eq. [5] is the sum of a conductivity term and a relaxation term (Kraus, 1984):
![]() | [6] |
is the ionic conductivity (L3 T3 M1 I2), expressed in S m1,
is the angular frequency (T1) ( = 2
F) and
''r,rel is the loss factor (-) due to relaxation.
The medium capacitance C is now also a complex quantity:
![]() | [7] |
It is convenient to write Eq. [7] as:
![]() | [8] |
+ gm
''r,rel
0 (in Siemens).
To describe the behavior of the (parallel) oscillator circuit in lossy dielectrics, we calculate the admittance Y (L2 T3 M1 I2) of the circuit expressed in Ohm1. The appropriate equation for the circuit in Fig. 1 is:
![]() | [9] |
Separating the real and imaginary components gives:
![]() | [10] |
![]() | [11] |
Equation [11] can be solved for the angular frequency
or for the medium capacitance C using the quadratic formula. Solving for angular frequency requires that G be estimated directly. The G term cannot be calculated analytically using G = gm
+ gm
''r,rel
0 because
is not known a priori. On the other hand, when solving for medium capacitance, it should be realized that C is also included in CA. Application of the quadratic formula to solve for C therefore requires some additional but straightforward algebraic operations. The resulting equations are given in the appendix.
| MATERIALS AND METHODS |
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Resonant frequency was measured in a variety of nonconductive dielectric media. We used air (
r = 1), motor oil (
2), corn (Zea mays L.) oil (
3), brasso (a siliceous polishing powder suspended in an ammonium soap jelly and dispersed in petroleum distillates, used for polishing metals,
8), propanol (
20), and deionized water (di-water
80). In addition, three mixtures of propanol and di-water (
r range 2532) and five mixtures of di-water and sugar (range 4575) were used. This resulted in 14 different media with a wide range of permittivities. The effect of ionic conductivity on the resonant frequency was measured by mixing different amounts of KCl in three media, namely propanol-di-water, sugar-di-water, and di-water. The electrical conductivity of the solutions was measured with an Orion model 170 conductivity meter (Orion Research Inc., Boston, MA) and ranged from 0.000 to 0.296 S m1. The frequency-permittivity experiments were conducted in 20-L plastic buckets with the polyvinyl chloride (PVC) access tube located in the center (running through the bottom of the bucket). Readings were taken by moving the sensors one by one into the center of the access tube. Air temperature in the laboratory was maintained at 25°C. The temperature of the media ranged between 23 and 28°C.
The dielectric properties (
r and
''r) of all of the media were measured with a network analyzer (Hewlett-Packard model 8753B, Hewlett-Packard, Palo Alto, CA) using a dielectric probe (Hewlett-Packard 85070B, Hewlett-Packard, Palo Alto, CA). Network analyzers are used in electronics to determine the reflection and transmission characteristics of devices and networks using a broad bandwidth signal (frequencies between 300 KHz and 3 GHz). In the frequency domain the reflection measurements can be used directly to obtain the
r and
r'' permittivities of a material as a function of frequency (Heimovaara et al., 1996). Measurements were conducted by placing the probe (basically a coaxial ring) in 50-mL subsamples that were taken from the 20-L buckets. In the subsequent analysis of the nonconductive media it was assumed that
= 0 so that
r'' equals
r,rel'' (Eq. [6]). For the conductive media,
r,rel'' was calculated by subtracting
/
0 from
r''.
To assess the value of the circuit inductance L for the sensors, the circuit board of Sensor 15 on Probe 2 was separated from the plastic sensor body with the brass rings. Single ceramic capacitors Cc ranging in value from 1 x 1012 to 56 x 1012 F were soldered onto the circuit board to replace the brass rings and to close the circuit. This eliminated C (= gm
r,m
0) and Cp (= gp
r,p
0) with the unknown geometric factors gm and gp from the electric circuit, reducing the unknown parameters in the circuit model to L and Cs. The resonant frequency was measured for each Cc. The appropriate equation for this simplified oscillator circuit is:
![]() | [12] |
The unknown parameters L and Cs in Eq. [12] were determined by minimizing the sum of the squared deviations between measured and calculated resonant frequency. The minimization was accomplished using the FMINSEARCH function in Matlab (The Mathworks Inc., Natick, MA), which uses the simplex search method (Coleman et al., 1999). Different seed values were used in the minimization to check the uniqueness of the solution.
Subsequently, the 14 combinations of resonant frequency and permittivity for the nonconductive media for each sensor were used to optimize Cs, gm, and gp for all sensors. During these optimizations the value of the inductance L was fixed to the value measured for Sensor 2.15. We did not fix the value of Cs because we anticipated that this value would alter in response to the change in the setup of the electric circuit. The optimization was done by solving Eq. [11] for C (= gm
r,m
0) and minimizing the sum of the squared deviations between measured and calculated relative permittivity. The minimization was again accomplished using the FMINSEARCH function in Matlab. Different seed values were used in the minimization to check the uniqueness of the solution. During all calculations the relative permittivity of the PVC access tube,
r,p was assumed to be 3 (e.g., Von Hippel, 1954).
The described two-step approach for determining the sensor constants proved necessary because simultaneous optimization of all four unknowns in the circuit model using Eq. [11] did not result in unique parameter values. Ideally, we would have determined the inductance L for all the sensors individually. This however would involve damaging all 29 sensors, which was considered too costly.
| RESULTS AND DISCUSSION |
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![]() | [13] |
The calculated value for Lcoil is either 1.07 x 107 H (using r = 0.00175 m, the average of the inner and outer radius of the coil and K = 0.72) or 8.16 x 108 H (using r = 0.0015 m, the inner radius of the coil and K = 0.75). The first value applies to low-frequency circuits while the second value applies to high-frequency circuits where the current crowds toward the inside of the coil. The optimized circuit inductance of 9.38 x 108 H for our (high-frequency) sensor is only slightly higher than the calculated Lcoil value of 8.16 x 108 H. This indicates that the stray inductance in the circuit is small (on the order of 1 x 108 H).
Sensor Constants
Initially we tried to determine the sensor constants by optimizing Eq. [11] using all 14 nonconductive media. This resulted in a relatively high sum of squares for all the sensors. The poor fit was mainly due to the brasso and the sugar-water mixture with the highest amount of sugar, both of which had measured relative permittivities that were less than the calculated values. Excluding the brasso and the five sugar-water mixtures from the optimization improved the fit considerably. The lack of fit for the sugar-waters is not well understood. The fact that the fit is especially bad for the sugar-water with the highest amount of sugar (approaching saturation) suggests that the formation of sugar crystals might be the reason for the discrepancy. But this is only speculation at this time. Formation of sugar crystals on the dielectric probe, for example, will result in an underestimation of the measured permittivity. We have no explanation for the lack of fit for the brasso.
The sensor constants optimized using the remaining eight media are listed in Table 1. The comparison between the measured and calculated relative permittivities is excellent for all sensors (R2 between 0.999 and 1.0). The values for the three optimized parameters show little variation between sensors. The stray capacitance Cs ranges from 9.75 to 10.47 x 1012 F, the geometric factor for the medium gm from 0.167 to 0.193 m, and the geometric factor for the plastic gp from 0.616 to 0.653 m.
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As an example, Fig. 3 shows the resonant frequency for Sensor 1.10 as a function of measured and optimized relative permittivity. The brasso and the five sugar-water mixtures are also shown, although they were excluded from the optimization. For the eight media that were included in the optimization, the model fits the data perfectly (R2 = 1.0). Of the five sugar-waters that were excluded from the optimization, four also show a reasonable fit. As mentioned earlier, the relative permittivities of the brasso and the sugar-water mixture with the highest amount of sugar are overestimated by the fitted curve.
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r'' (determining the total dielectric losses) is the sum of the conductivity loss factor 
1
01 and the relaxation loss factor
r,rel''. Part of the variation in
r,
r'', 
1
01, and
r,rel'' for the propanol-water and sugar-water mixtures is due not only to adding KCl but also to the experimental procedure. To increase the conductivity of the solutions, KCl was dissolved in pure water, and the resulting solution added to the mixtures. This procedure slightly altered the mixtures and therefore
r,
r'', 
1
01, and
r,rel''. These alterations do not affect the analysis because
r,
r'', and 
1
01 are measured for each mixture while
r,rel'' is calculated using Eq. [6].
|
r,rel'' on
r'' is less pronounced than the effect of 
1
01 (see also Eq. [6]). The ratio between 
1
01 and
r,rel'' is a measure of the importance of the conductivity effect over the relaxation effect. Except for the three lowest 
1
01 values, this ratio is always higher than 1, and ranges from 1.5 to 41.0 (numbers not shown). The observed dominance of the conductivity effect over the relaxation effect on the total dielectric losses might not hold for soils. The interaction between soil water and soil particles is expected to increase the relaxation effect.
The measured and calculated frequency response of Sensor 1.10 is shown in Fig. 5
. The calculated response is obtained by solving Eq. [11] for
(= 2
F) using seven different levels of the loss factor G
. The figure illustrates the effect of dielectric losses on the sensor frequency. It does not allow for a direct comparison between measured and calculated values (this will be done further on). Note the change of scale on the y-axis as compared with the previous figures. The effect of dielectric losses on the frequency response is most pronounced for the medium with the lowest relative permittivity (propanol-water). Even a relatively small increase in G from 0.003 to 0.023 S for the propanol-water leads to a drop in frequency of 2.71 MHz. For propanol-water with G = 0.023 S, not accounting for dielectric losses would result in an overestimation of
r by 14.79 [= 49.26 (Eq. [4]) 34.47].
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r may result in the same sensor frequency. This is a serious problem as it implies that in soils with high conductivity or relaxation losses it may be impossible to relate the sensor frequency reading to the correct relative permittivity and therefore to the correct soil water content.
We checked whether this nonuniqueness problem might explain the odd behavior of brasso and the sugar-water mixture with the highest amount of sugar observed earlier. For Sensor 1.10, we found for brasso F = 113.82 MHz,
r = 9.088, and
r'' = 2.719 with a calculated G value of 0.003 S. For the sugar-water mixture we found F = 105.87 MHz,
r = 45.134, and
r'' = 9.117 with a calculated G value of 0.009 S. Solving Eq. [11] for C with the quadratic formula using the appropriate sensor constants for Sensor 1.10 (Table 1) results in
r = 10.41 and
r = 18.35 for brasso and in
r = 9.34 and
r = 52.03 for the sugar-water. This shows that the G values for both the brasso and the sugar-water are not high enough to result in two positive values for
r. Nonuniqueness is therefore not an issue for these two media, leaving us without a satisfactory explanation.
The effect of the dielectric losses on the sensor frequency is investigated further by plotting the sensor frequency for the propanol-water, the sugar-water, and the water as a function of G (Fig. 6)
. The bounding lines in the figure indicate the range of relative permittivities for each of these three media as calculated by the circuit model (Eq. [11] solved for
). Figure 6 shows that the model describes the data reasonably well. Interestingly, at a G value of about 0.055 S, all three media generate about the same sensor frequency (103.2 MHz), despite the fact that their relative permittivities are significantly different (ranging from approximately 35 for propanol-water to approximately 78 for water). This again shows that in lossy media, nonuniqueness problems are likely to occur if the relative permittivity is inferred from the sensor frequency alone.
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r may be as high as 67.7 for the propanol-water (measured
r between 32 and 39), 47.2 for the sugar-water (measured
r 6163), and 30.1 for the water (measured
r 78).
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rF relationship approaches a horizontal line. Slight inaccuracies in the frequency or in the sensor constants may then result in serious errors in the calculated relative permittivity. For G values higher than those used in this study, the
rF relationship will become completely horizontal. The frequency reading is then no longer influenced by the permittivity of the media. Or in other words, at high G, the dielectric losses are completely overshadowing the effect of the real permittivity on the sensor frequency.
A way of refining the circuit model might come from transmission line theory (Hilhorst, 1998). The two brass rings of the EnviroSCAN sensor can be considered as an open ended lossy transmission line. The electromagnetic properties of a unit length of transmission line are described by its characteristic impedance, Z0 (L2 T3 M I2):
![]() | [14] |
Incorporating the capacitance of the plastic access tube, Cp into Eq. [14] results in:
![]() | [15] |
Note that C
, G
, and Cp (= gp
r,p
0) were already included in our circuit model (Fig. 1). The factors Rs and Ls are new and describe the resistance losses and the storage of magnetic energy in the transmission line (brass rings), respectively. Hilhorst showed that it is possible to calculate the correct
r for G values up to 0.1 S, by including Rs and Ls in a semi-empirical analysis of a sensor with two parallel electrodes. Incorporating Eq. [15] into our circuit model in a theoretically sound manner is hampered by the fact that the two brass rings do not constitute a uniform transmission line. Thus there is no straightforward method available to convert Z0 into an impedance value Z for the rings. Considering the above, we think that the circuit model as presented in Fig. 1 remains the best available method to describe the frequency response of the EnviroSCAN sensor in lossy media.
Simplified Procedure for Sensor Calibration
Conventionally, for the Enviroscan sensor, differences in frequency response between sensors are corrected for by taking frequency measurements in air (Fa) and in water (Fw). The frequency measurement in the medium of interest (Fm) is then scaled, SF = (Fa Fm)/(Fa Fw) (e.g., Paltineanu and Starr, 1997; Baumhardt et al., 2000). This normalization procedure becomes redundant if Eq. [11] is used to relate the sensor frequency to the permittivity of the medium. Equation [11], however, contains four unknown constants (Cs, L, gm, and gp). Frequency measurements in air and water alone do not suffice to determine these constants for each sensor. To avoid the need of using multiple media to calibrate each sensor (as is done in this study), we investigated whether it is possible to fix two of the constants based on the results obtained so far, and to calculate the other two based on Fa and Fw.
In the simplified approach, the value of L remains fixed at 9.38 x 108 H (consistent with the approach discussed earlier). From a theoretical standpoint, Cs should not be fixed as this parameter describes the stray capacitance in the electrical circuit and is likely to vary between sensors. This leaves us with the choice of either fixing gm or gp. Trial calculations showed that fixing gm gives much better results than fixing gp (highest R2 when the new constants are used to calculate the permittivity for the eight nonconductive media with Eq. [11]). If gm is fixed, the capacitances of the media only depend on the calculated relative permittivities, resulting in appropriate values for gp and Cs. In contrast, if gm is not fixed, the capacitances of the media change both with gm and the calculated relative permittivity, resulting in a good fit for the air and water, but also resulting in potentially inappropriate values for gp and Cs (and a potentially bad fit for the other six nonconductive media).
Based on this information we choose to fix L to 9.38 x 108 H, fix gm to 0.176 m (the average value in Table 1), and calculate gp (= Cp/
r,p
0) and Cs. Calculations were conducted by solving Eq. [4] using (Fa,
r = 1) and (Fw,
r = 78.54). We preferred Eq. [4] to the more general Eq. [11] because Eq. [4] results in a relatively simple analytical solution. Use of Eq. [4] implies that relaxation losses in the water are neglected. It also means that di-water must be used for measuring Fw because ionic conductivity losses are not accounted for. The calculated values for gp and Cs are shown in Table 3. The R2 values of between 0.999 and 1.000 show that the fit between measured and calculated permittivity for the eight nonconductive fluids are excellent with the new sensor constants.
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Capacitance Probe Sensors in Soil
The results of this study indicate that in nonlossy materials there is a clear relationship between the resonant frequency of the capacitance probe sensors and the permittivity of the medium. Applying the sensors in coarse and medium textured soils with low electrical conductivity should therefore give an accurate estimate of the soil permittivity and hence of the soil water content. However, applying capacitance probe sensors in fine textured soils or in saline soils might be problematic due to complications associated with high dielectric losses. Fine textured soils might generate high dielectric losses due to the presence of bound water with a relatively low relaxation frequency. Saline soils might result in high dielectric losses due to ionic conductivity.
High dielectric losses influence the frequencypermittivity relationship for the sensors in three different ways. First, it may prove impossible to relate the measured resonant frequency to the correct permittivity of the soil and hence to the correct soil water content because of nonuniqueness of the frequency-permittivity relationship in lossy media. Second, in saline soils, the sensor frequency may respond more to changes in soil salinity than to changes in soil water content because the frequency becomes insensitive to permittivity when ionic conductivity is high. And third, the susceptibility of the frequency to ionic conductivity implies that the sensor is also sensitive to soil temperature (conductivity in a saline soil changes as a function of soil temperature).
The performance of capacitance probe sensors in saline soils might be improved by increasing the frequency of operation of the sensors. The higher the frequency, the lower the 
1
01 term, and the lower the dielectric losses G. However, the frequency of operation cannot be increased too much because it should remain below the relaxation frequency of the soil water.
| CONCLUSIONS |
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We found a profound influence of ionic conductivity on the sensor resonant frequency. The higher the conductivity of the medium, the lower the sensor frequency. The effect was most pronounced for the medium with the lowest relative permittivity (propanol-water). The effect of ionic conductivity on the sensors was generally more significant than the effect of relaxation losses. The circuit model did a good job in correcting for the conductivity effects. As the dielectric losses increased however, the frequency became insensitive to permittivity and small inaccuracies in the measured frequency or in the sensor constants resulted in large errors in the calculated permittivity. The circuit model might be refined further by using transmission line theory to describe the electromagnetic properties of the sensor's brass rings in more detail.
A satisfactory simplified calibration procedure consisted of fixing the sensor constants L to 9.38 x 108 H and gm to 0.176 m, and calculating the constants gp and Cs using sensor readings in air and water. The error introduced by not optimizing all four constants was small (the R2 for the calculated permittivity of the eight nonconductive media was 0.9991.000 for all sensors). The use of one set of sensor constants for all sensors was not recommended because the R2 for individual sensors became as low as 0.988.
| APPENDIX: |
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![]() | [A1] |
![]() |
Equation [11] solved for medium capacitance results in:
![]() | [A2] |
![]() |
The appropriate sign in front of the square root of the discriminant in Eq. [A1] is always a minus. In Eq. [A2] the appropriate sign is a minus if the dielectric losses G are low. However, at high G, a plus sign may also result in positive values for C in Eq. [A2] (nonuniqueness).
| ACKNOWLEDGMENTS |
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| NOTES |
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Received for publication November 18, 2002.
| REFERENCES |
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