1. Introduction
As many recent studies have proved, laboratory measurements of leaf optical properties in the visible and infrared regions are a valuable technique for understanding different plant physiological processes and stress detection [
1,
2,
3,
4,
5], as well as photosynthesis efficiency evaluation, energy balance calculation, global terrestrial net primary productivity modelling [
6,
7,
8,
9] or vegetation stress detection [
10,
11,
12,
13,
14]. Despite its wide applications, significant measurement uncertainties and knowledge gaps exist. These are related mainly to non-flat leaves, such as coniferous needles exhibiting a long and thin leaf type spatially oriented around a shoot [
5,
15,
16,
17,
18].
Measurements of optical properties at the leaf level are typically acquired with a laboratory spectroradiometer coupled with an integrating sphere (IS). Within a sphere, light reflected or transmitted from a sample is integrated over a full hemisphere to yield measurements insensitive to sample anisotropic directional reflectance (transmittance) behaviour. This allows for repeatable measurements of vegetation samples.
Another mean of leaf optical properties’ acquisition includes contact measurements with a reflectance (contact) probe. A contact probe (CP) is a device mainly designed for contact measurements of solid raw materials such as minerals and grains, but also used for vegetation samples. Like an IS, a probe has its own light source (typically krypton halogen bulb) integrated within its body. A CP is retrofitted with a black, slip-on circular spacer that maintains a constant distance from the probe lens to the sample. In contrast to hemispherical measurements in an IS, a CP does not allow transmittance measurements. Also, some additional measurement ambiguities caused by multiple and multi-directional reflectance or possible damages of vegetation samples due to heat transferred from light source must be considered. However, use of a CP has some advantages like avoiding problems with stray light, operating flexibility and speed. Also, by its design, it allows for repetitive and non-destructive in-situ measurements of samples.
Though designed mainly for solid materials, CP measurements have also been successfully used for assessing metal stress in
Arabidopsis thaliana plants [
12], for estimating chlorophyll content in field crops [
19] or detecting water stress in poplar at both the leaf and canopy levels [
20]. Our research team used CP measurements within a framework of two projects. The first project focused on the assessment of mining-related impacts on selected tree species—Scots pine (
Pinus sylvestris L.) and silver birch
(Betula pendula Roth). We proved that measurements based on a CP (in our case an Analytical Spectral Devices, ASD Inc., Boulder, CO, USA contact probe) may provide valuable inputs for statistical modelling of vegetation parameters [
4,
21]. Laboratory spectroscopic data for the second project focused on the development and improvement of methods for monitoring of Norway spruce (
Picea abies L. Karst.) health status in the Krušné hory Mts., Czech Republic [
22,
23]. Here, both an ASD CP and ASD IS were used.
In order to be able to cross-compare leaf optical properties measured by either contact probes or integrating spheres, one should be aware of the constancy among the measurements. A literature review revealed studies comparing reflectance values measured with different spectroradiometers [
24,
25,
26], with a CP and a fore optic lens [
27]; however, up to now no study on mutual comparison of a CP and an IS has been published. Particularly in the case of coniferous needles spatially arranged on a shoot, the methodology of measurement matters remarkably, possibly affecting the values obtained by different devices. There is a gap in experiments that would compare spectra measured on identical samples (standard samples or vegetation specimens or other materials e.g., soils, rocks) using a CP and an IS or experiments comparing measurements acquired by two or more different types of ISs. Confirmation of comparability of reflectance measured by a CP and an IS could bring simplification of field/laboratory vegetation optical properties measurements and their interpretation in some cases.
To address the above mentioned scientific issues, we designed an empirical laboratory experiment to compare spectra measured with different devices. Our main research questions were: (1) Are there differences between spectra collected with a CP and an IS? (2) Are the retrieved leaf biochemical properties obtained from spectral measurements performed with a CP and an IS yielding comparable results? (3) To what extent does the leaf type (broadleaved leaf and coniferous needles with their spatial arrangement on a shoot) affects spectral leaf properties obtained with a CP and an IS? We measured both reference standards (a Spectralon, coloured papers) and vegetation samples of both leaf types (broadleaved leaves of N. rustica and P. abies needles) using an ASD CP and two integrating spheres: An ASD IS (RTS-3ZCr2) and a Labsphere IS (RTC-060-SF) and we proposed a methodology for comparison of measurements obtained with different devices at three levels: Using raw spectra, derived vegetation indices and the quantitative retrieval of leaf-level biochemical parameters.
2. Materials and Methods
2.1. Materials
2.1.1. Reference Materials
Although our methodology is focused on vegetation spectra, we also measured two types of artificial samples with stable optical properties—A Spectralon and a set of coloured papers. These represented stable reference materials, which do not change during the measurement process (e.g., due to a loss of water as in the case of some vegetation samples).
Reflectance was measured for a calibrated Zenith Lite
® Diffuse Reflectance Target (nominal reflectance of 95%, SphereOptics GmbH, Herrsching, Germany). The supplied calibration protocol was used as a reference. Next, reflectance spectra of nine different coloured papers were measured; the used paper-weight was 80 g/m
2 for five colours: white, black, blue, light green and red, and 160 g/m
2 for white, green, red and yellow colour. The impact of a substitution error (see
Section 2.2) on measurements acquired with an IS was examined on the coloured paper samples.
2.1.2. Vegetation Samples
In our experiments, two types of plant samples were measured: tobacco leaves (Nicotiana Rustica Roth) as a representative of a ‘broadleaved’ leaf type, i.e., dorsiventral leaf, and Norway spruce (Picea abies L. Karst.) needles as a representative of a ‘coniferous’ leaf type:
Tobacco leaves: Tobacco plants (36 individuals) were grown in pots in a greenhouse for two months during early summer. Three leaves were measured per each plant. First, a mature leaf located in the lower part of the plant was divided into thirds and measured simultaneously using both the CP and the two ISs. Further, two younger leaves of subsequent insertion were cut; one was measured using the CP and the other one was divided in halves and measured simultaneously in the two IS. Finally, two leaf samples were used for the biochemical determination of photosynthetic pigments and water content. The design of the experiment is shown in
Figure 1.
Norway spruce needles: The needles were collected in 2013 from mature even-aged forest stands in the Krušné hory mountains, Czech Republic [
28]. In total, 55 trees were sampled—Reflectance spectra of the first two needle age classes from three vertical crown levels were measured. Next, the chlorophyll, carotenoids and water contents were biochemically estimated. After excluding outliers, 96 samples were used for the analysis. A detailed description of the dataset and evaluation of relations between biochemical and spectral measurements for Norway spruce needles can be found in [
22,
23].
Examples of spectra of coloured papers, tobacco leaves and spruce needles collected with different devices are shown in
Figure 2.
2.1.3. Biochemical Measurements
Photosynthetic pigments were extracted using dimethylformamide according to [
29] and determined specrophotometrically. Pigment contents were calculated applying equations published in [
30] and expressed on dry weight basis (μg/cm
2). Norway spruce needles were scanned before the pigment extraction. The ratio between the needle dry mass and needle projection area was calculated and used for conversion of amount of pigments to μg/cm
2, the standard unit in vegetation spectroscopy and remote sensing [
16]. In case of tobacco, the samples of constant area were cut from the leaf and amount of pigments was directly related to a leaf unit area (cm
2).
The relative water content (RWC) was determined as the percentage of water in the fresh needles or leaves (the fraction of biomass weight decrease after drying). Fresh needles or leaves were weighed immediately after sampling, oven dried at 80 °C for 48 h and then weighed again.
2.2. Instruments
Spectral reflectance was measured in the range between 350 and 2500 nm using a FieldSpec 4 Wide-Res spectroradiometer (ASD Inc., Boulder, CO, USA). The ASD CP light source is a halogen bulb with colour temperature of approximately 2900 K whereas the ASD IS is supplied with a collimated tungsten light source [
31]. According to the manufacturer’s protocol, subsequent reflectance and transmittance measurements of a sample requires changing the lamp position between two ports of the IS. It requires some time and it may introduce additional uncertainty due to the shift in light source position and intensity. Thus, in the next step we also tested the Labsphere integrating sphere (Lab IS, North Sutton, NH, USA), light source (KI-120 Koehler Illuminator with 120 W, 3200 K tungsten halogen lamp, Lab IS, North Sutton, NH, USA) of which is fixed during the measurements and only the sample is exchanged between the ports. However, due to the noise in data collected with the Lab IS, all calculations were performed only in the spectral interval from 450 to 1800 nm. Thus,
Table 1 also characterises the ASD FieldSpec 4 Wide-Res spectroradiometer’s detectors just for this part of spectra: 512 elements silicon array for the visible and near infrared parts of the spectrum (350–1000 nm) and Graded Index InGaAs Photodiodes for the shortwave infrared part of the spectrum (SWIR1: 1000–1800 nm). Their wavelength accuracy is 0.05 nm and the final spectral curve is composed of bands 1 nm wide.
2.2.1. CP Measurements
Samples were placed on a plate coated with black paint (albedo < 0.05) to minimize the reflection of radiation transmitted through the sample (see also [
4,
22]). The relative reflectance spectrum for each measurement was calculated as a ratio of the measured radiance of the sample to the radiance of 99% spectralon panel (white reference), according to Equation (1):
where
Rsample_rel is the relative reflectance of the sample,
DNsample is the measured reflected radiation from the sample (in DN values),
DNWR is the measured reflected radiation of the non-calibrated 99% Spectralon (white reference; the calibration protocol was not available for this Spectralon panel).
Five measurements were taken on different parts of a sample. The sample-specific value was calculated as a median of these five individual measurements. In case of tobacco, single leaf was selected for the measurements, whereas for Norway spruce, needles of the same age class (same shoot) were arranged in a stack still keeping spatial orientation on a shoot (upper part of the needles oriented upwards), see also [
27]. Different scan averaging was applied for CP and IS measurements to avoid overheating of samples measured by the CP (
Table 2).
2.2.2. IS Measurements
All samples were measured according to the manufacturer’s protocol [
31]. Because only reflectance measurements could be compared between the IS and CP, transmittance was not in focus in our study and is not discussed in the present paper. The scan averaging for all measurements was set up to 100 (
Table 2) to improve the signal to noise ratio.
For narrow leaf samples (i.e., spruce needles) so called gap-fraction correction was further applied (see e.g., [
5,
15,
18]). To assess the impact of the substitution error (SE, the error caused by the difference in the total energy collected with the optical cable when the reference and sample are placed in the port) samples were measured in two configurations (see
Table 3);
Figure 3 shows the scheme of the ports of the ASD IS.
The relative reflectance spectra of the colour papers and tobacco leaves were computed based on the abovementioned standard Equation (1) described in the manufacturer’s manual [
31]. The stray light correction was not taken into account as the errors are negligible (it yields maximum of 0.01% of measured sample reflectance). In the case of the Spectralon, the absolute reflectance values were calculated as:
where
Rsample_abs is the absolute reflectance of the sample,
DNsample is the measured reflected radiation from the sample (in
DN values),
DNWR is the measured reflected radiation from the 99% Spectralon (white reference) and
RWR is the calibrated reflectance value of the 99% Spectralon.
Due to their size, measurements of Norway spruce needles require more complex approach, which includes the gap-fraction correction of samples placed in a special sample-holder [
33], revised by [
15], summarized and extended in [
5,
18]. The gap-fraction is typically retrieved from the scans of sample-holders. The relative reflectance spectra of the needles are then derived from the measured radiance and the gap-fraction according to the Equation (3) [
5,
15]:
where
Rneedle is the reflectance of individual needles,
DNsample is the measured reflected radiation from the sample, i.e., needles + gaps in
DN values,
DNstraylight is the measured stray light radiation in
DN values,
DNWR is the measured reflected radiation from the calibrated 99% Spectralon (white reference) in
DN values,
GF is the gap-fraction.
Measurements with all devices were carried out in a spectroscopic laboratory. In the case of the Spectralon, colour papers and spruce needles measurements, the ASD IS and ASD CP were subsequently connected to one ASD FieldSpec 4 Wide-Res spectroradiometer; another spectroradiometer of the same type was used for the Lab IS measurements. Tobacco samples were simultaneously measured with all three devices connected to three ASD FieldSpec 4 Wide-Res spectroradiometers.
2.3. Methodology of Spectra Comparison
The most reliable spectra comparison would be based on the absolute reflectance values calculated according to Equation (2). This approach was used in the case of the first test with the calibrated the 95% Zenith Lite® Diffuse Reflectance Target, further called the 95% Zenith Lite® Sepectralon calibrated reference. CP measurements were carried out with a non-calibrated 99% Spectralon. Equation (1) was then used for calculating reflectance values, which were relative to the 99% Spectralon. This approach widely applied in the field campaigns was utilized in the case of colour papers as well as vegetation experiments mostly for practical reasons—The diameter of an internal ASD IS 99% Calibrated Reference Standard just covers the ASD CP field of view and is therefore a potential source of errors. Using the 95% Zenith Lite® Spectralon as a white reference is complicated in the ASD IS measurements because the spectralon is relatively big and difficult to be held in the port. Moreover, it does not fit to the above mentioned internal 99% standard coating the inside of the IS.
The rationale for spectra comparison is based on the following idea. If we assume a theoretical case of equal absolute reflectance values derived from a CP and an IS, their difference can be expressed as:
where
Rrel and
Rabs are the absolute and relative reflectance values calculated according the Equations (1) and (2), respectively, and
RWR is the calibrated reflectance of the Spectralons used for the CP and IS measurements.
Thus, the relation between the relative measurements can be modelled with a linear function, multiplicative term of which corresponds to the unknown ratio
CWR between the reflectance values of the used Spectralons:
The test based on the calibrated Spectralon revealed an offset
COabs =
RCP_abs −
RIS_abs between the reflectance values derived from CP and IS measurements. Equation (5) was therefore extended to a full linear model described with Equation (6):
where
CO is the unknown offset of absolute values
COabs divided by
RWR_CP. The coefficients
CWR and
CO are spectrally dependent.
The measurements of colour papers, tobacco leaves and Norway spruce needles collected with different devices were first compared using selected statistical quantities. The mean absolute difference was applied as a measure of a mean magnitude of differences in reflectance. The median of differences quantifies a systematic shift between the compared spectra. The standard deviation was added to describe the variability of the differences around the mean value. First, the standard deviation was calculated from all samples of the same type of material acquired by one device for each wavelength between 450 and 1800 nm. To quantify the differences among spectra using a single quantity, a mean of standard deviations was then computed. Since the measurements were carried on the same samples with all devices, the similarity between the spectra was also evaluated on each wavelength and all combinations of devices by means of the paired-sample t-test with the level of significance α = 0.05. Furthermore, it was possible to estimate the coefficients of linear relation between the RCP_rel and RIS_rel values for each studied wavelength according to Equation (6). The similarity between the transformed spectral curves obtained from different devices was again evaluated based on the mean absolute difference, the mean standard deviation and the paired-sample t-test.
Normalized differential indexes (NDI) are commonly used when the relation between the spectral response of vegetation and its biochemical parameters are sought. Equation (7) represents a general expression of the normalised differential vegetation index calculated for reflectance values R on the wavelengths λ
1 and λ
2:
The NDI has a value from the interval <−1; 1>. It slightly differs if the relative or absolute reflectance is used for calculation. Due to the lack of calibrated spectralon for the ASD CP, the NDI were calculated from the relative reflectance values in our experiments. Based on the NDI values of samples measured either by the CP and the IS, the differences and correlation in NDI values were evaluated for colour papers and plant samples. In addition, the correlation of NDI with selected leaf compounds (total chlorophyll, carotenoids and water content) obtained from all three devices was calculated to demonstrate its applicability for quantitative remote sensing of vegetation.
Finally, we assessed the relationship between spectral indices often used in quantitative remote sensing of vegetation and leaf compounds. A linear regression and a calculation of a coefficient of determination R
2 for all used devices and about fifty indices, summarized for chlorophyll in [
34,
35], for carotenoids in [
36,
37] and for water in [
38] (pp. 232–233), were performed. Based on the results, four indices listed in
Table 4 are presented further in this study.
4. Conclusions
The objective of our study was to test whether the spectral measurements collected with a CP and an IS yield comparable results. The main motivation of this study arose from our practical experience with the CP measurements being both convenient for field work and also less time consuming than the IS measurements. The comparison of spectra collected with two ISs was another objective as the data exchange between research groups is frequent and comparability and quality are then important issues. It must be stressed out that the present conclusions are based on the datasets where the relative reflectance values were used due to a lack of a calibrated Spectralon used for the CP measurements. It is assumed that using of absolute reflectance values could result in further improvement.
The calibrated reflectance values of the 95% Zenith Lite
® calibrated reference and absolute reflectance measured with the ASD IS and ASD CP differed less than 0.5% (in relative units) in the best cases, which is on the level of the instrument performance [
47]. In order to achieve such a result, attention has to be paid to both the measurement itself in order to avoid possible measurement errors (such as a loose contact between the contact probe and the sample) and rigorous data post-processing (e.g., excluding outliers from the measurements). The effect of the stray light correction was small (less than 0.01%) and, thus, not significant for our experiments.
The experiment with the coloured papers revealed higher discrepancies between spectral reflectance values obtained from different devices and device settings in comparison to the Spectralon. It showed that differences exist even when two ISs of a different manufacturer are compared. The main conclusions are that (i) the best agreement was achieved between measurements from ASD IS and Lab IS when the correction for substitution error was applied; (ii) if the samples measured with the same devices exist, they can be used for derivation of parameters of a linear transformation (at each wavelength) that can bring the compared spectra to a better agreement. Based on following tests with two different leaf types—tobacco and Norway spruce—this transformation gave better results for broadleaved than for coniferous vegetation.
The last objective of the study was to show to what extent does the leaf type (broadleaved leaf and coniferous needles with their spatial arrangement on a shoot) affect spectral leaf properties obtained by a CP and an IS. The study revealed that in the case of broadleaved leaf type, the differences in using the IS and CP are smaller than in the case of coniferous needles. Coniferous needles have a thick cuticle and rhomboid shape on cross section. In addition, needles are attached to a shoot under different angles and this spatial architecture, which causes multidirectional reflectance, may affect measurements with a CP since needles are kept on a shoot during these measurements. In contrast to measurements with an IS where single, detached needles are laid parallel on a tray of a sample holder and, thus, shoot architecture does not interfere with measurements. In future studies, models for shoot spectral properties based on needle spectral measurements shall be applied and evaluated. As a broadleaved plant species in our case we used tobacco with a leaf type without a specific anatomic adaptation of epidermis. It may happen that broadleaved leaf types with pronounced epidermal structure corresponding to more xeropmorphic leaf adaptations could exhibit more differences, though.
The relation between NDI derived from spectra collected by different devices followed the observation that in spite of our effort to have an identical sample per one set of measurements, some individual variability had been present (increasing from papers, through tobacco to spruce needles). It caused higher differences in corresponding spectra and subsequently also higher differences in the derived NDI. The data collected with the ASD FieldSpec 4 Wide-Res spectroradiometer were sampled with the interval of 1 nm. The noise in data could influence the calculated NDI. Therefore smoothing original spectra with a suitable filter, e.g., a Savitzky–Golay filter [
48,
49] could improve the results. The conclusions about NDI are valid also for specific vegetation indices used in quantitative remote sensing for modelling of relation between spectral observations and the content of biochemical or biophysical compounds in vegetation.
The present study contributes to an effort in using a more coherent approach of leaf optical property acquisition, which is essential for using such data in standardization when upscaling to a canopy level. Leaf optical properties measured at leaf level can directly enter to radiative transfer models at canopy level and contribute significantly to their parametrization and further to simulation of imaging spectrometer data [
50]. The study shows that a direct comparison between the spectra collected with two devices is not advisable as spectrally dependent offsets may likely exist as we demonstrated for the compared devices and device settings. They are caused by the construction of the devices, light sources used, measurement procedures and properties of the measured material, e.g., leaf type and structure. As an implication of our results for remote sensing vegetation studies we can recommend to be very careful with comparisons of laboratory spectral measurements conducted with different devices and under different conditions. The experiments should be documented in detail in order to be repeatable and reproducible, and the same devices should be used in the case of mutual comparison. When using two or more devices a definition of a linear model transforming a spectrum of one device to another one is a solution that decreases the differences. In order to find parameters of such a model, a subset of the samples has to be measured with both devices which in principle corresponds to the approach of introducing an internal standard suggested for soil spectral measurements [
26]. Elaboration on procedures that enable to work with spectra on a leaf level acquired with different devices would open a possibility of using various open access spectral databases and spectral libraries as a robust data source for spectroscopy modelling on a leaf level.