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Article

Organic Matter Retrieval in Black Soil Based on Oblique Extremum Signatures

1
Geomathematics Key Laboratory of Sichuan, Chengdu University of Technology, Chengdu 610059, China
2
College of Mathematics and Physics, Chengdu University of Technology, Chengdu 610059, China
3
Tianjin Center of China Geological Survey, Tianjin 300170, China
*
Author to whom correspondence should be addressed.
Remote Sens. 2023, 15(10), 2508; https://doi.org/10.3390/rs15102508
Submission received: 31 March 2023 / Revised: 4 May 2023 / Accepted: 8 May 2023 / Published: 10 May 2023
(This article belongs to the Special Issue Remote Sensing for Soil Mapping and Monitoring)

Abstract

:
How to extract the indicative signatures from the spectral data is an important issue for further retrieval based on remote sensing technique. This study provides new insight into extracting indicative signatures by identifying oblique extremum points, rather than local extremum points traditionally known as absorption points. A case study on retrieving soil organic matter (SOM) contents from the black soil region in Northeast China using spectral data revealed that the oblique extremum method can effectively identify weak absorption signatures hidden in the spectral data. Moreover, the comparison of retrieval outcomes using various indicative signature extraction methods reveals that the oblique extremum method outperforms the correlation analysis and traditional extremum methods. The experimental findings demonstrate that the radial basis function (RBF) neural network retrieval model exposes the nonlinear relationship between reflectance (or reflectance transformation results) and the SOM contents. Additionally, an improved oblique extremum method based on the second-order derivative is provided. Overall, this research presents a novel perspective on indicative signature extraction, which could potentially offer better retrieval performance than traditional methods.

Graphical Abstract

1. Introduction

Black soil plays a vital role in maintaining food security. Unfortunately, the quality of black soil has deteriorated due to improper human use [1,2]. Soil organic matter (SOM) is a crucial indicator for soil fertility assessment and serves as the primary source of various nutrients necessary for plant growth [3]. Furthermore, SOM can enhance soil resilience and fertility retention, improve soil physicochemical properties, and help fix soil heavy metals and organic pollutants [4]. Consequently, accurate and timely measuring of SOM content is crucial to monitor land quality. However, traditional methods requiring field samples and expensive laboratory analyses [5,6] are impractical for large-scale land-quality monitoring. Therefore, a quantitative retrieval method based on spectral data is an efficient and viable solution to this problem.
Soil composition monitoring through spectral data analysis typically involves three major processes: spectral data analysis, indicative signature extraction, and retrieval modeling. Here, spectral data analysis ordinarily involves spectrum denoising [6,7], spectral transformation [6,8,9], standard normal variate (SNV) [7], multiplicative scatter correction (MSC) [10], and continuum removal (CR) [11,12,13]. As to the indicative signature extraction, correlation analysis is the most popular method [5,14]. Some other methods, such as genetic algorithm (GA) [15,16], successive projections algorithm (SPA) [8,17,18], and competitive adaptive reweighted sampling (CARS) [15], are also employed. Further, the quantitative retrieval models for soil components with soil spectra are categorized into statistical analysis and machine learning models, including multiple linear regression (MLR) [9], multiple stepwise linear regression (SMLR) [8,19], principal component regression (PCR) [20], partial least squares regression (PLSR) [7,8,9,21], back propagation (BP) neural network [14], extreme learning machine (ELM) [22], random forest (RF) [9,23], support vector machine regression (SVMR) [23], and radial basis function (RBF) neural network [24]. These retrieval models provide feasible solutions to disclose the linear and nonlinear relationship between reflectance and soil component contents. However, these methods rely on identifying indicative signatures from the spectral data curve’s absorption positions, i.e., the extremum points (local minimum points), to retrieve the contents. Unfortunately, for spectral data, some special indicative signatures, especially for the weak absorption features, are not indicated as the extremum points. Actually, these weak absorptions always manifest as the oblique extremum points [25]. Thus, this study focuses on how to combine both the local minimum points and the oblique extremum points to extract indicative signatures and retrieve the SOM in black soil based on these combinatorial points from spectral data. Then, this study discusses and compares the retrieval performance of the radial basis function neural network with different indicative signature extraction methods. The experimental results show that this new idea of extracting indicative signatures for further retrieval is superior to traditional methods.

2. Materials and Methods

2.1. Study Area

The study area is situated in the western part of Qixing Farm of Jiansanjiang River, Fujin of Jiamusi City, Heilongjiang Province, in the northeast of China. It is located within latitude 47 ° 0 7 N to 47 ° 2 3 N, and longitude 132 ° 36 E to 132 ° 4 6 E, with a total area about approximately 300 km 2 , which is a central black soil region in China (Figure 1). The Qixing Farm is located within the Three Rivers Plain, an extensive flat terrain that offers an ideal setting for large-scale mechanized farming operations. The soil surface is primarily composed of black, dark brown, and dark brown humus, with a granular structure. Below it lies a clayey sedimentary layer containing brown iron-manganese nodules and a brown-yellow clayey parent material underneath it. Black soil is known for its high fertility and is predominantly used in the cultivation of soybeans, rice, and corn.

2.2. Data Acquisition and Pre-Process

A total of 68 black soil samples, as shown in Figure 1, were collected from the study area. To eliminate errors caused by tillage and fertilizer application, S-shaped sampling was employed, avoiding certain special locations such as ridges and fertilizer accumulation areas. These surface soil samples, each weighing approximately 1 kg and collected at a depth of 10–20 cm, were first rid of impurities such as grains, weeds, and stones before being placed in cloth sample bags, numbered, and stored for processing. To remove any effects of moisture, particle size, or impurities in the soil sample on the spectral data, the samples were naturally air-dried and passed through a 120-mesh nylon screen. Following that, every 500 g of soil was subjected to hyperspectral detection and measurements of SOM content.
The spectrums of the samples were measured using an Analytical Spectral Devices (ASD) FieldSpec4 portable object spectrometer, while excluding the range of 350–400 nm and 2451–2500 nm due to interference from moisture and systematic errors associated with the instrument. The resulting data, consisting of 2050 spectral bands, were processed using the Savitzky-Golay (SG) smoothing method [26] to eliminate noise. Additionally, five nonlinear transformations were applied, namely reciprocal ( 1 / R ), reciprocal logarithmic ( ln ( 1 / R ) ), square ( R 2 ), cubic ( R 3 ), and root mean square ( R ), to the original spectrum to explore the indicative signatures further.
The SOM contents of all samples were determined through wet oxidation at 180 °C, using a mixture of potassium dichromate and sulfuric acid. The 68 samples were sorted in ascending order according to their SOM contents and divided into 17 categories, with four samples in each category, which was designed in a 3-to-1 ratio for modeling and validation datasets. Three random samples were then selected from each category and assigned to the modeling dataset, leaving the remaining 17 samples for validation. Table 1 shows some statistical parameters of the SOM contents for all 68 samples.

2.3. Indicative Signature Extraction

2.3.1. Pearson Correlation Analysis

The Pearson coefficients defined in Equation (1) were calculated to analyze the relationship between the different spectral transformations and the SOM contents. In Equation (1), j denoted the band number; r j was the correlation coefficient between the spectral data of soil samples in the j t h band and its SOM contents; n was the total number of the samples; i denoted the soil sample number; x i j was the spectral data of the i t h sample at the j t h band; x ¯ j was the average spectrum for all samples at the j t h band; y i was the SOM content of the i t h sample; and y ¯ denoted the average SOM content for all samples.
r j = i = 1 n ( x i j x ¯ j ) ( y i y ¯ ) i = 1 n ( x i j x ¯ j ) 2 i = 1 n ( y i y ¯ ) 2 .

2.3.2. Extremum Method

Commonly, the indicative signatures of the spectrum are selected with correlation analysis [6,14,27]. Although the correlation analysis can correlate well between reflectance and sample contents, the selected results lack physical significance because the indicative signatures are always presented as the absorption bands or points, not the maximum correlation coefficient bands. Thus, a combination of the absorption bands and the correlation coefficient analysis is usually used to extract the indicative signatures from the spectrum. In this study, this combination is called as the extremum method. Unfortunately, not all indicative signatures appeared as the extremum points, especially for some weak absorption features. So, how to extract this type of points is an interesting issue for the following retrieval process. In this study, we have improved a method to extract these signatures and subsequently retrieve the contents of SOM in black soil by utilizing the new extracted signatures. First, we will introduce the improved method, followed by a discussion and comparison of the results.

2.3.3. Oblique Extremum Method and Improved Oblique Extremum Method

Here, the oblique extremum points [25] are used to define this kind of special absorption phenomenon, in which absorptions are not indicated as the extremum points of the spectrum. To illustrate the detail, consider the signal defined in Equation (2), below.
y ( t ) = t + 0.9 sin ( t ) , t [ 1 , 64 ] .
As shown in Figure 2a, obviously, the signal y ( t ) is strictly monotonically increasing, without any extremum points. However, intuitively, there indeed exist some special signatures in this signal. To address this problem, Yang et al. [25] defined the oblique extremum points to characterize these special points and proposed an approach to detect them.
Given a signal y ( t ) , let ( t a , f ( t a ) ) and ( t b , f ( t b ) ) ( t a < t b ) be two consecutive inflection points of y ( t ) , and l ( t ) to be the straight line connecting these two inflection points. Denote
y l ( t ) = y ( t ) l ( t ) , t [ t a , t b ] ,
then, the local maximum (or minimum) point ξ of y l ( t ) is called an oblique local maximum (or minimum) point of y ( t ) .
Therefore, the key to extracting the oblique extremum points lies in identifying the inflection points of the signal. As described in [25], the first-order derivative of the original signal is used to detect the inflection points. The adjacent inflection points generate a line segment that forms the trend curve of the original signal. Thus, the oblique extremum points are determined as the extremum points of the subtraction result of the trend curve from the original signal. Figure 2b demonstrates that the extracted oblique extremum points of y ( t ) are all located as the gentle humps in the curve. These results in Figure 2b indicate that certain special signatures in remote sensing imagery and spectral data can also be identified as the oblique extremum points. Before we introduce the oblique extremum points in spectral data, let us first discuss the algorithm for detecting such points.
As described in the literature [25], the determination of the inflection points of a signal is crucial in defining the oblique extremum point and implementing the algorithm to extract them. Yang et al. [25] employed the first-order derivative to do that. However, in theory, the inflection point of a continuous signal is defined as the demarcation point between the concave and the convex intervals of the signal. The second-order derivative is more reasonable than the first-order derivative for detecting the inflection points of a signal. Therefore, we develop an improved algorithm for extracting oblique extremum points from a signal y ( x ( t ) ) based on the second-order derivative. Details on this algorithm can be found in Algorithm 1.
Algorithm 1 Improved algorithm to extract oblique extremum points.
1. Calculate the second-order derivative of original hyperspectral signal y ( x ( t ) )
y ( x ( t ) ) = y ( x ( t + 1 / 2 ) ) y ( x ( t 1 / 2 ) ) x ( t + 1 / 2 ) x ( t 1 / 2 ) = y ( x ( t + 1 ) ) y ( x ( t ) ) x ( t + 1 ) x ( t ) y ( x ( t ) ) y ( x ( t 1 ) ) x ( t ) x ( t 1 ) x ( t + 1 / 2 ) x ( t 1 / 2 ) , = y ( x ( t + 1 ) ) + y ( x ( t 1 ) ) 2 y ( x ( t ) ) ( Δ x ) 2 ,   t = 2 , , e n d 1
2. Extract the oblique maximum points of the signal.
Step 1.   Define   and   identify   the   k t h concave interval
I k h C C = [ x ( i ) , , x ( i + h 1 ) ] ,   k = 1 , , m s . t . y ( x ( t ) ) < 0 ,   t = i , , i + h 1 , y ( x ( i 1 ) ) 0 , y ( x ( i + h ) ) 0 , 2 i < e n d 1 , h 1 , ,
in which h is the interval length, m   is   the   total   number   of   concave   intervals ,   and   the   superscript   C C represents concave.
Step 2. Find   inflection   points   on   both   sides   of   the   concave   interval   I k h C C , and construct   the   trend   line   l k h C C ( x ( t ) ) .
  • Since   the   first   point   x ( i )   of   I k h C C is a concave point, so the previous point x ( i 1 ) must be a convex point or an inflection point, according to Equation (5) .   If   x ( i 1 )   is   a   convex   point ,   not   an   inflection   point ,   then   the   abscissa   and   ordinate   of   the   inflection   point   at   the   left   end   of   I k h C C is defined as the mean value of these two adjacent points in Equation (6)
    x C C l e f t _ inf = x ( i 1 ) + x ( i ) 2 , y C C l e f t _ inf = y ( i 1 ) + y ( i ) 2 ,
    else   if   x ( i 1 ) is an inflection point, then set
    x C C l e f t _ inf = x ( i 1 ) , y C C l e f t _ inf = y ( i 1 ) ,
    where the superscript l e f t _ inf represents the left inflection point.
  • Similarly ,   the   last   point   x ( i + h 1 )   of   I k h C C is a concave point, so the next point x ( i + h )   must   be   a   convex   point   or   an   inflection   point .   If   x ( i + h )   is   a   convex   point ,   define   abscissa   and   ordinate   of   the   inflection   point   at   the   right   end   of   I k h C C as
    x C C r i g h t _ inf = x ( i + h 1 ) + x ( i + h ) 2 , y C C r i g h t _ inf = y ( i + h 1 ) + y ( i + h ) 2 ,
    else
    x C C r i g h t _ inf = x ( i + h ) , y C C r i g h t _ inf = y ( i + h ) ,
    where the superscript r i g h t _ inf represents the right inflection point.
  • Connect   the   left   and   right   inflection   points   of   the   concave   interval   I k h C C ( k = 1 , , m )   with   a   straight   line   l k h C C ( x ( t ) )   as   the   trend   curve   of   I k h C C .
Step 3. Subtract   the   trend   line   from   the   original   signal :   y l k h C C ( x ( t ) ) = y ( x ( t ) ) l k h C C ( x ( t ) ) , where x ( t ) I k h C C .
Step 4. Obtain   all   oblique   maximum   points   x k h O M A X and construct a set
U O M A X = k = 1 , 2 , , m x k h O M A X = k = 1 , 2 , , m arg max ( y l k h C C ( x ( t ) ) ) ,
in which the superscript O M A X represents oblique maximum.
3. Extract the oblique minimum points of the signal.
Step 1. Define   and   identify   the   k t h convex interval
I k l C V = [ x ( i ) , , x ( i + l 1 ) ] ,   k = 1 , , n s . t . y ( x ( t ) ) > 0 ,   t = i , , i + l 1 , y ( x ( i 1 ) ) 0 , y ( x ( i + l ) ) 0 , 2 i < e n d 2 , l 1 , ,
in which l is the interval length, n is the total number of convex intervals, and the superscript C V represents convex.
Step 2. Find   inflection   points   on   both   sides   of   the   convex   interval   I k l C V , and construct   the   trend   line   l k l C V ( x ( t ) ) .
  • Since the   first   point   x ( i )   of   I k l C V is a convex point, the previous point x ( i 1 ) must be a concave point or an inflection point, according to Equation (11) .   If   x ( i 1 )   is   a   concave   point ,   define   abscissa   and   ordinate   of   the   inflection   point   at   the   left   end   of   I k l C V as
    x C V l e f t _ inf = x ( i 1 ) + x ( i ) 2 , y C V l e f t _ inf = y ( i 1 ) + y ( i ) 2 ,
    else
    x C V l e f t _ inf = x ( i 1 ) , y C V l e f t _ inf = y ( i 1 ) ,
    where the superscript l e f t _ inf represents the left inflection point.
  • Similarly ,   the   last   point   x ( i + l 1 )   of   I k l C V is a convex point, so the next point x ( i + l )   must   be   a   concave   point   or   an   inflection   point .   If   x ( i + l )   is   a   concave   point ,   define   abscissa   and   ordinate   of   the   inflection   point   at   the   right   end   of   I k l C V as
    x C V r i g h t _ inf = x ( i + l 1 ) + x ( i + l ) 2 , y C V r i g h t _ inf = y ( i + l 1 ) + y ( i + l ) 2 ,
    else
    x C V r i g h t _ inf = x ( i + l ) , y C V r i g h t _ inf = y ( i + l ) ,
    where the superscript r i g h t _ inf represents the right inflection point.
  • Connect   the   left   and   right   inflection   points   of   convex   interval   I k l C V ( k = 1 , , n )   with   a   straight   line   l k l C V ( x ( t ) )   as   the   trend   line   of   I k l C V .
Step 3. Subtract   the   trend   line   from   the   original   signal :   y l k l C V ( x ( t ) ) = y ( x ( t ) ) l k l C V ( x ( t ) ) , where x ( t ) I k l C V .
Step 4. Obtain   all   oblique   minimum   points   x k l O M I N and construct a set
U O M I N = k = 1 , 2 , , n x k l O M I N = k = 1 , 2 , , n arg max ( y l k l C V ( x ( t ) ) ) ,
in which the superscript O M I N represents oblique minimum.
Let’s consider the spectral data of a measured soil sample after SG smoothing as an example, to further illustrate the difference between the extremum method and the improved oblique extremum method for extracting the indicative signatures. As shown in Figure 3a, for the extremum method, only 30 local minimum points—also known as the absorption points—were extracted, with no local minimum points detected in 600–1700 nm. In other words, almost all the absorption signatures are located on either side of the signal. However, with the improved oblique extremum method, 133 points that covered the entire wavelength of the signal are extracted totally. Clearly, the extracted results of the improved oblique extremum method reflect more information and detail about the signal than the extremum method does. Moreover, the improved oblique extremum method has the ability to extract potential weak absorption points in the spectral data. The comparative details are all demonstrated in Figure 3.

2.4. Retrieval Method

In order to explore the nonlinear relationship between spectral transformations and SOM contents, a nonlinear regression model, radial basis function neural network, is utilized in this study. The RBF neural network is a feed-forward neural network with three layers: input layer, hidden layer, and output layer [24]. The input layer receives the training data. The hidden layer applies an activation function to perform a nonlinear transformation on the input data, where the Gaussian radial basis function is frequently utilized. The activation function for the output layer is the linear function. The final output is obtained by taking the linear weighted sum of the outputs of the neurons in the hidden layer. Therefore, the RBF neural network boasts a simpler structure, faster learning convergence speed, and better generalization ability in comparison to other machine learning algorithms [27].

3. Results and Discussion

3.1. The Spectral Characteristics Analysis

The original and denoised spectra of all the samples are demonstrated in Figure 4. Generally, the minor differences of the reflectance play a crucial role in revealing the undiscovered relationships between the SOM contents and the reflectance of the samples.
To gain a deeper understanding of the spectral characteristics and investigate the relationship between soil reflection spectra and SOM content, all the 68 samples were clustered into four classes using the K-means clustering method [28] (Figure 5). The number of the classes was determined with the Elbow method [29]. Based on Figure 5, it is apparent that there exists a negative correlation between soil spectral reflectance and SOM content, meaning that the higher the SOM content, the lower the spectral reflectance. Obviously, the significant absorption features are located near 1400 nm and 1900 nm, primarily due to the stretching vibration of hydroxyl and the bending vibration of Al-OH of the water molecules [12,30,31]. These features are also caused by the water vapor in the air during the laboratory spectroscopy measurements. Additionally, an absorption close to 2200 nm, a characteristic of kaolinite, can also be observed, resulting from the combination of Al-OH bend and O-H stretch [32].

3.2. Extraction Results of Indicative Signatures for SOM

3.2.1. Correlation Analysis between the SOM Contents and the Spectral Reflectance and Their Different Transformations

The correlation coefficients between the SOM contents of the samples and their spectral reflectance, as well as their five spectral transformations ( 1 / R , ln ( 1 / R ) , R 2 , R 3 , and R ), were calculated and illustrated in Figure 6. There is a strong negative correlation between the SOM contents and the original spectral reflectance within the range of 401–2450 nm, which is consistent with the findings of the clustering analysis discussed in Section 3.1. Regarding the five spectral transformations, R 2 , R 3 , and R coincide with the original spectral reflectance R , whereas the transformations 1 / R and ln ( 1 / R ) exhibit a mirror symmetry, as depicted in Figure 6a. From Figure 6, it can be observed that: (1) the coefficients between the original spectral reflectance and SOM contents fall within the range of [−0.615, −0.336]; and (2) the transformations 1 / R , ln ( 1 / R ) , and R can marginally improve the correlation between the original spectral reflectance and the SOM content.
Then, the indicative bands were chosen based on the correlation analysis results, guided by two principles: the first is that the selected bands must have higher correlation coefficients than others, and the second is that they should be separated from each other; in other words, they should not be adjacent. All the selected indicative bands are illustrated in Table 2, including the peaks of the correlation coefficients and corresponding bands. It is worth noting that most of the indicative bands extracted by the correlation analysis are situated within the range of 600–1000 nm, which is basically consistent with the finding of Yuan et al. [33].

3.2.2. Indicative Signatures Extracted by Extremum Method

For remote sensing imagery or spectral data, the absorption points are represented as the local minimum points in the spectral curve, and the indicative signatures are always extracted from these absorption points. Thus, the extremum method to extract the indicative signatures here means that the characteristic bands are extracted from the local minimum points of the spectral curve based on their corresponding correlation results. For this case data, the extracted results are demonstrated in Table 3.
Table 3 reveals an intriguing observation: that the extracted results for transformations R , R 2 , R 3 , and R are the same, i.e., 408 nm, 998 nm, and 1773 nm. For the transformations 1 / R and ln ( 1 / R ) , the results are the same, too, i.e., 463 nm, 1002 nm, and 2354 nm. The correlation results between the spectral data and SOM contents for these five transformations, namely 1 / R , ln ( 1 / R ) , R 2 , R 3 , and R , exhibit slight variations, suggesting that spectral transformations can marginally affect the correlation coefficients.

3.2.3. Indicative Signatures Extracted by Improved Oblique Extremum Method

As described in Section 2.3.3, the oblique minimum points in the spectral curve may hint at potential weak absorptions. Thus, we proposed a new idea to extract the indicative signatures based on oblique extremum points with the improved oblique extremum method. More specifically, the indicative signatures are derived from oblique minimum points, which encompasses all the local minimum points [25]. All the extracted indicative signatures are illustrated in Table 4. By utilizing oblique minimum points as the extracted indicative signatures, all absorption points of the spectral data are accounted for, and it also allows for the identification of potential weak absorptions depicted as oblique extremum points rather than local minimum points. Further, in order to compare the retrieval results based on oblique minimum points, another indicative signature that only contains the oblique minimum points without the local minimum points is also considered. Here, oblique minimum without local minimum means that the local minimum points of the spectral curve are deleted from the extracted oblique minimum points.

3.3. The Retrieval Results Analysis with Different Indicative Signature Extraction Methods

The determination coefficient ( R 2 ), root mean of squared error (RMSE), and the ratio of the performance to deviation (RPD) were used to evaluate the performance of the retrieval results. These three evaluation criteria were defined in Equations (17)–(19), respectively. Specifically, R 2 acted as the criterion to assess the effectiveness of the retrieval model. Commonly, the closer the value is to 1, the better the fitting results. RMSE is used to measure the accuracy of the retrieval model, and a smaller value of RMSE indicates higher accuracy. Further, the value of RPD always represents the predictive ability of the model, and a higher value signifies a better prediction result. Therefore, in general, high R 2 and high RPD, but low RMSE, are characteristics of an excellent retrieval model. As pointed out by Chang et al. [34], for R 2 > 0.5 , if RPD   <   1.4 , the model fails to predict the samples; if 1.4 RPD < 2.0 , the model can provide a rough estimation of the samples; and if RPD 2.0 , the model exhibits excellent predictive ability.
R 2 = i = 1 n ( y ^ i y ¯ ) 2 i = 1 n ( y i y ¯ ) 2 ,
RMSE = i = 1 n ( y i y ^ i ) 2 n ,
RPD = SD v RMSE v .
In Equations (17)–(19), i was the soil sample number; n denoted the total number of samples; y i and y ^ i were the observed and predicted value of the i t h sample, respectively; y ¯ was the mean of the observed data; and SD v and RMSE v were the standard deviation and the root mean of the squared error of the validation dataset, respectively.

3.3.1. The Retrieval Results Based on Indicative Signatures with Correlation Analysis

The evaluation results of the RBF neural network based on indicative signatures using correlation analysis are all illustrated in Table 5. The results indicate that: (1) the retrieval model relying on correlation analysis can only provide a rough estimation, given that the values of R m 2 and R v 2 exceed 0.5, and RPD ranges between 1.4 to 2.0 for both modeling and validation datasets; (2) among the six spectral transformations, original reflectance R displays the best-fitting performance for the modeling dataset, with the highest being R m 2 = 0.659 and the smallest being RMSE m = 11.900 g/kg; (3) ln ( 1 / R ) yields the most favorable prediction outcome, with an RPD of 1.885. Overall, the transformation ln ( 1 / R ) appears to be more appropriate for retrieving the SOM contents when utilizing correlation analysis to identify indicative signatures.

3.3.2. The Retrieval Results Based on Indicative Signatures with Extremum Method

The retrieval results based on the extremum method demonstrated in Table 6 indicate that: (1) only one model with R 2 transformation can be used to retrieve the contents of the SOM with R m 2 = 0.550 > 0.5 , R v 2 = 0.702 > 0.5 , and RPD = 1.643 > 1.4 ; (2) although the transformation R 3 retrieval model based on minimum indicative signatures achieved a good predictive effect with RPD = 1.818 > 1.643 , it did not fit well with the modeling dataset with R m 2 = 0.465 < 0.5 ; (3) combining the results listed in Table 3, the indicative signatures of four transformations, R , R 2 , R 3 and R , are the same, but the retrieval performances for them, as showcased in Table 6, varied significantly, indicating that the transformations R 2 are helpful to improve the SOM predictive result.

3.3.3. The Retrieval Results Based on Indicative Signatures with Improved Oblique Extremum Method

The retrieval results based on indicative signatures extracted by the improved oblique extremum method are all illustrated in Table 7. It is exciting that the retrieval model based on oblique minimum without the minimum performs better than oblique minimum for all six transformations, as compared in Table 7. Further, from the view of the RPD performance criterion, all six models are suitable for SOM retrieval with R m 2 > 0.5 , R v 2 > 0.5 , and RPD > 1.4 . Four of the models yield outstanding predictions, with RPD > 2.0 . This result reveals that the oblique minimum (non-minimum) signatures of soil spectra are crucial for retrieving SOM content, which is a new insight never reported in previous studies.
Upon comparing the results displayed in Table 5 and Table 6, it is clear that the RBF neural network based on improved oblique extremum method outperforms both correlation analysis and extremum methods. Specifically, for original reflectance R , the RPD value of oblique minimum without the minimum retrieval model is 2.376, whereas the RPD values for the correlation analysis and extremum methods are 1.705 and 1.397, respectively.
It is interesting to compare the correlation coefficients of the indicative bands obtained by the improved oblique extremum method with those extracted with only the correlation analysis. As illustrated in Table 2 and Table 4, the correlation coefficients of the indicative bands obtained by the improved oblique extremum method are not the highest. Thus, relying on only the correlation analysis to extract the indicative signatures seems to be unreasonable because the correlation coefficient can only disclose the linear relationship between reflectance and SOM contents. Actually, the relationship is always nonlinear, as the results show in Figure 6.

3.3.4. Comparison of Retrieval Results with Different Indicative Signature Extraction Methods

The performance comparison of the optimal models for six transformations with different indicative signature extraction methods are demonstrated in Figure 7. The results show that, on the whole, models based on indicative signatures extracted through the improved oblique extremum method outperform both correlation analysis and extremum methods; they have higher R 2 , lower RMSE, and higher RPD. These results reveal the fact that the improved oblique extremum method is capable of detecting the possible weak indicative signatures in the spectral data, which were hidden as the oblique minimum points rather than local minimum points. Further, these weak indicative signatures are of great importance in subsequent retrieval processes.

4. Conclusions

This study focuses on how to extract the indicative signatures from the spectral data during the retrieval process based on remote sensing technique. Herein, we provide a new insight into the indicative signatures as the oblique extremum points of the data. The oblique extremum points include not just the traditional local minimum points, also known as absorption points, but also potential weak absorption points. However, these weak absorption points are not presented as local minimum points of the signal. The results from a case study of the retrieval of SOM contents in black soil located in Northeast China indicate the effectiveness of this new insight. Thus, the oblique extremum points of the spectral data are suggested to be the extracted indicative signatures for further retrieval models. Commonly, the relationship between reflectance or their transformations and SOM contents is nonlinear, as indicated by the correlation analysis. In other words, the correlation coefficients between the SOM contents and the reflectance or their transformations reveal a nonlinear relationship in nature. Therefore, a retrieval model with nonlinear mapping capability, such as an RBF neural network model, is more appropriate than those that can only disclose linear relationships. Another important fact to note is that the spectral transformations used in this paper, namely the reciprocal, reciprocal logarithmic, square, cubic, and root mean square transformations, do not alter the indicative signatures extracted by the extremum method. However, it is worth mentioning that the square transformation improved the retrieval performance of the SOM. Therefore, identical indicative signatures are obtained in different spectral transformations, and it is still necessary to further explore their impact on the retrieval outcomes.

Author Contributions

M.Z.: conceptualization, investigation, data curation, methodology, writing—original draft preparation and editing, and software. M.W.: supervision, project administration, and funding acquisition, writing—review and editing. D.W.: supervision and project administration. S.W.: validation and formal analysis. W.X.: validation and visualization. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the National Natural Science Foundation of China (grant number 42272346), the Sichuan Science and Technology Program (grant number 2021YFG0319), the Opening Fund of Geomathematics Key Laboratory of Sichuan Province (grant number scsxdz2020yb08), and China Geological Survey (CGS) (grant number SYZXW2017101).

Data Availability Statement

Not applicable.

Acknowledgments

The authors are grateful for the helpful comments from the editors and reviewers, also the researchers and colleagues.

Conflicts of Interest

The authors declare that they have no known competing financial interest or personal relationships that could have appeared to influence the work reported in this paper.

References

  1. Gong, H.; Meng, D.; Li, X.; Zhu, F. Soil Degradation and Food Security Coupled with Global Climate Change in Northeastern China. Chin. Geogr. Sci. 2013, 23, 562–573. [Google Scholar] [CrossRef] [Green Version]
  2. Liu, X.B.; Zhang, X.Y.; Wang, Y.X.; Sui, Y.Y.; Zhang, S.L.; Herbert, S.J.; Ding, G. Soil Degradation: A Problem Threatening the Sustainable Development of Agriculture in Northeast China. Plant Soil Environ. 2010, 56, 87–97. [Google Scholar] [CrossRef] [Green Version]
  3. Bolton, D.K.; Friedl, M.A. Forecasting Crop Yield Using Remotely Sensed Vegetation Indices and Crop Phenology Metrics. Agric. For. Meteorol. 2013, 173, 74–84. [Google Scholar] [CrossRef]
  4. Wood, S.A.; Tirfessa, D.; Baudron, F. Soil Organic Matter Underlies Crop Nutritional Quality and Productivity in Smallholder Agriculture. Agric. Ecosyst. Environ. 2018, 266, 100–108. [Google Scholar] [CrossRef]
  5. Qiao, X.-X.; Wang, C.; Feng, M.-C.; Yang, W.-D.; Ding, G.-W.; Sun, H.; Liang, Z.-Y.; Shi, C.-C. Hyperspectral Estimation of Soil Organic Matter Based on Different Spectral Preprocessing Techniques. Spectrosc. Lett. 2017, 50, 156–163. [Google Scholar] [CrossRef]
  6. Shen, L.; Gao, M.; Yan, J.; Li, Z.-L.; Leng, P.; Yang, Q.; Duan, S.-B. Hyperspectral Estimation of Soil Organic Matter Content Using Different Spectral Preprocessing Techniques and PLSR Method. Remote Sens. 2020, 12, 1206. [Google Scholar] [CrossRef] [Green Version]
  7. Xie, X.-L.; Pan, X.-Z.; Sun, B. Visible and Near-Infrared Diffuse Reflectance Spectroscopy for Prediction of Soil Properties near a Copper Smelter. Pedosphere 2012, 22, 351–366. [Google Scholar] [CrossRef]
  8. Xie, S.; Li, Y.; Wang, X.; Liu, Z.; Ma, K.; Ding, L. Research on Estimation Models of the Spectral Characteristics of Soil Organic Matter Based on the Soil Particle Size. Spectrochim. Acta Part Mol. Biomol. Spectrosc. 2021, 260, 119963. [Google Scholar] [CrossRef]
  9. Han, C.; Lu, J.; Chen, S.; Xu, X.; Wang, Z.; Pei, Z.; Zhang, Y.; Li, F. Estimation of Heavy Metal (Loid) Contents in Agricultural Soil of the Suzi River Basin Using Optimal Spectral Indices. Sustainability 2021, 13, 12088. [Google Scholar] [CrossRef]
  10. Vašát, R.; Kodešová, R.; Klement, A.; Borůvka, L. Simple but Efficient Signal Pre-Processing in Soil Organic Carbon Spectroscopic Estimation. Geoderma 2017, 298, 46–53. [Google Scholar] [CrossRef]
  11. Gholizadeh, A.; Borůvka, L.; Saberioon, M.M.; Kozák, J.; Vašát, R.; Němeček, K. Comparing Different Data Preprocessing Methods for Monitoring Soil Heavy Metals Based on Soil Spectral Features. Soil Water Res. 2016, 10, 218–227. [Google Scholar] [CrossRef] [Green Version]
  12. Wu, Y.; Chen, J.; Ji, J.; Gong, P.; Liao, Q.; Tian, Q.; Ma, H. A Mechanism Study of Reflectance Spectroscopy for Investigating Heavy Metals in Soils. Soil Sci. Soc. Am. 2007, 71, 918–926. [Google Scholar] [CrossRef]
  13. Shen, Q.; Xia, K.; Zhang, S.; Kong, C.; Hu, Q.; Yang, S. Hyperspectral Indirect Inversion of Heavy-Metal Copper in Reclaimed Soil of Iron Ore Area. Spectrochim. Acta Part Mol. Biomol. Spectrosc. 2019, 222, 117191. [Google Scholar] [CrossRef]
  14. Chang, R.; Chen, Z.; Wang, D.; Guo, K. Hyperspectral Remote Sensing Inversion and Monitoring of Organic Matter in Black Soil Based on Dynamic Fitness Inertia Weight Particle Swarm Optimization Neural Network. Remote Sens. 2022, 14, 4316. [Google Scholar] [CrossRef]
  15. Jiang, Q.; Liu, M.; Wang, J.; Liu, F. Feasibility of Using Visible and Near-Infrared Reflectance Spectroscopy to Monitor Heavy Metal Contaminants in Urban Lake Sediment. Catena 2018, 162, 72–79. [Google Scholar] [CrossRef]
  16. Sun, W.; Zhang, X. Estimating Soil Zinc Concentrations Using Reflectance Spectroscopy. Int. J. Appl. Earth Obs. Geoinf. 2017, 58, 126–133. [Google Scholar] [CrossRef]
  17. Yuan, J.; Wang, X.; Yan, C.; Chen, S.; Wang, S.; Zhang, J.; Xu, Z.; Ju, X.; Ding, N.; Dong, Y.; et al. Wavelength Selection for Estimating Soil Organic Matter Contents Through the Radiative Transfer Model. IEEE Access 2020, 8, 176286–176293. [Google Scholar] [CrossRef]
  18. Shi, T.; Liu, H.; Chen, Y.; Wang, J.; Wu, G. Estimation of Arsenic in Agricultural Soils Using Hyperspectral Vegetation Indices of Rice. J. Hazard. Mater. 2016, 308, 243–252. [Google Scholar] [CrossRef]
  19. Shi, T.; Cui, L.; Wang, J.; Fei, T.; Chen, Y.; Wu, G. Comparison of Multivariate Methods for Estimating Soil Total Nitrogen with Visible/near-Infrared Spectroscopy. Plant Soil 2012, 366, 363–375. [Google Scholar] [CrossRef]
  20. Wu, Y.; Chen, J.; Wu, X.; Tian, Q.; Ji, J.; Qin, Z. Possibilities of Reflectance Spectroscopy for the Assessment of Contaminant Elements in Suburban Soils. Appl. Geochem. 2005, 20, 1051–1059. [Google Scholar] [CrossRef]
  21. Xu, X.; Chen, S.; Xu, Z.; Yu, Y.; Zhang, S.; Dai, R. Exploring Appropriate Preprocessing Techniques for Hyperspectral Soil Organic Matter Content Estimation in Black Soil Area. Remote Sens. 2020, 12, 3765. [Google Scholar] [CrossRef]
  22. Lu, Q.; Wang, S.; Bai, X.; Liu, F.; Wang, M.; Wang, J.; Tian, S. Rapid Inversion of Heavy Metal Concentration in Karst Grain Producing Areas Based on Hyperspectral Bands Associated with Soil Components. Microchem. J. 2019, 148, 404–411. [Google Scholar] [CrossRef]
  23. Wijewardane, N.K.; Ge, Y.; Morgan, C.L.S. Moisture Insensitive Prediction of Soil Properties from VNIR Reflectance Spectra Based on External Parameter Orthogonalization. Geoderma 2016, 267, 92–101. [Google Scholar] [CrossRef] [Green Version]
  24. Zhang, S.; Shen, Q.; Nie, C.; Huang, Y.; Wang, J.; Hu, Q.; Ding, X.; Zhou, Y.; Chen, Y. Hyperspectral Inversion of Heavy Metal Content in Reclaimed Soil from a Mining Wasteland Based on Different Spectral Transformation and Modeling Methods. Spectrochim. Acta Part Mol. Biomol. Spectrosc. 2019, 211, 393–400. [Google Scholar] [CrossRef]
  25. Yang, Z.; Yang, L.; Qing, C. An Oblique-Extrema-Based Approach for Empirical Mode Decomposition. Digit. Signal Process. 2010, 20, 699–714. [Google Scholar] [CrossRef]
  26. Steinier, J.; Termonia, Y.; Deltour, J. Smoothing and Differentiation of Data by Simplified Least Square Procedure. Anal. Chem. 1972, 44, 1906–1909. [Google Scholar] [CrossRef] [PubMed]
  27. Zhao, J.; Zhang, C.; Min, L.; Guo, Z.; Li, N. Retrieval of Farmland Surface Soil Moisture Based on Feature Optimization and Machine Learning. Remote Sens. 2022, 14, 5102. [Google Scholar] [CrossRef]
  28. Lloyd, S. Least Squares Quantization in PCM. IEEE Trans. Inform. Theory 1982, 28, 129–137. [Google Scholar] [CrossRef] [Green Version]
  29. Liu, F.; Deng, Y. Determine the Number of Unknown Targets in Open World Based on Elbow Method. IEEE Trans. Fuzzy Syst. 2021, 29, 986–995. [Google Scholar] [CrossRef]
  30. Rossel, R.A.V.; Behrens, T. Using Data Mining to Model and Interpret Soil Diffuse Reflectance Spectra. Geoderma 2010, 158, 46–54. [Google Scholar] [CrossRef]
  31. Liu, J.; Xie, J.; Han, J.; Wang, H.; Sun, J.; Li, R.; Li, S. Visible and Near-Infrared Spectroscopy with Chemometrics Are Able to Predict Soil Physical and Chemical Properties. J. Soils Sediments 2020, 20, 2749–2760. [Google Scholar] [CrossRef]
  32. Stenberg, B.; Rossel, R.A.V. Diffuse Reflectance Spectroscopy for High-Resolution Soil Sensing. In Proximal Soil Sensing; Springer: Dordrecht, The Netherlands, 2010; pp. 29–47. [Google Scholar]
  33. Yuan, J.; Hu, C.; Yan, C.; Li, Z.; Chen, S.; Wang, S.; Wang, X.; Xu, Z.; Ju, X. Semi-Empirical Soil Organic Matter Retrieval Model with Spectral Reflectance. IEEE Access 2019, 7, 134164–134172. [Google Scholar] [CrossRef]
  34. Chang, C.-W.; Laird, D.A.; Mausbach, M.J.; Hurburgh, C.R. Near-Infrared Reflectance Spectroscopy-Principal Components Regression Analyses of Soil Properties. Soil Sci. Soc. Am. J. 2001, 65, 480–490. [Google Scholar] [CrossRef] [Green Version]
Figure 1. Geographic distribution of collected samples in the study area. (a) A map of China; (b) A map of Heilongjiang Province; (c) A map of Jiamusi City and study area; (d) The sample distribution in the study area.
Figure 1. Geographic distribution of collected samples in the study area. (a) A map of China; (b) A map of Heilongjiang Province; (c) A map of Jiamusi City and study area; (d) The sample distribution in the study area.
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Figure 2. The original signal y ( t ) (a) and its oblique extremum points (b).
Figure 2. The original signal y ( t ) (a) and its oblique extremum points (b).
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Figure 3. Extracted results of minimum points with the extremum method and oblique minimum points with improved oblique extremum method. (a) Minimum points extracted with extremum method; (a1) and (a2) are partial enlargement of (a); (b) Oblique minimum points extracted with improved oblique extremum method; (b1) and (b2) are partial enlargement of (b).
Figure 3. Extracted results of minimum points with the extremum method and oblique minimum points with improved oblique extremum method. (a) Minimum points extracted with extremum method; (a1) and (a2) are partial enlargement of (a); (b) Oblique minimum points extracted with improved oblique extremum method; (b1) and (b2) are partial enlargement of (b).
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Figure 4. Spectral reflectance of 68 samples. (a) The original spectra; (b) SG smoothing results.
Figure 4. Spectral reflectance of 68 samples. (a) The original spectra; (b) SG smoothing results.
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Figure 5. Mean values of the spectral reflectance for four different categories after clustering.
Figure 5. Mean values of the spectral reflectance for four different categories after clustering.
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Figure 6. Correlation coefficients of the SOM contents and the original reflectance, as well as their five spectral transformations. (a) Correlation coefficients; (b) Range of correlation coefficients.
Figure 6. Correlation coefficients of the SOM contents and the original reflectance, as well as their five spectral transformations. (a) Correlation coefficients; (b) Range of correlation coefficients.
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Figure 7. Comparison of the fitting results ( R m 2 and R v 2 ), modeling accuracy ( RMSE m and RMSE v ), and predictive property (RPD) between the optimal models for six transformations with different indicative signature extraction methods. (a,b) are the comparison results of R m 2 and RMSE m for modeling dataset, respectively; (ce) are the comparison results of R v 2 , RMSE v , RPD for validation dataset, respectively.
Figure 7. Comparison of the fitting results ( R m 2 and R v 2 ), modeling accuracy ( RMSE m and RMSE v ), and predictive property (RPD) between the optimal models for six transformations with different indicative signature extraction methods. (a,b) are the comparison results of R m 2 and RMSE m for modeling dataset, respectively; (ce) are the comparison results of R v 2 , RMSE v , RPD for validation dataset, respectively.
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Table 1. Statistical characteristics of SOM in soil samples from the study area.
Table 1. Statistical characteristics of SOM in soil samples from the study area.
DatasetNumber of
Samples
Minimum
(g/kg)
Maximum
(g/kg)
Mean
(g/kg)
SD 1
(g/kg)
CV 2
(%)
Total dataset687.651133.67840.05519.2262.083
Modeling dataset517.651133.67840.43120.5791.965
Validation dataset1712.40876.43338.92914.9232.609
1 SD: Standard Deviation; 2 CV: Coefficient of Variation.
Table 2. Indicative bands and correlation coefficients between SOM contents and different spectral transformations.
Table 2. Indicative bands and correlation coefficients between SOM contents and different spectral transformations.
Spectral TransformationIndicative Bands (nm)Correlation Coefficients
R 838−0.607
1142−0.573
537−0.546
1442−0.521
1 / R 7620.643
8380.642
6970.638
ln ( 1 / R ) 8380.629
6830.616
10030.608
R 2 929−0.584
1280−0.541
574−0.519
R 3 1042−0.563
941−0.558
1145−0.552
R 838−0.619
1141−0.576
537−0.562
Table 3. Indicative signatures obtained by extremum method with different spectral transformations.
Table 3. Indicative signatures obtained by extremum method with different spectral transformations.
Spectral TransformationIndicative Bands (nm)Correlation Coefficients
R 408−0.477
1773−0.467
998−0.595
1 / R 23540.474
4630.544
10020.612
ln ( 1 / R ) 23540.463
4630.533
10020.607
R 2 408−0.464
1773−0.461
998−0.579
R 3 408−0.441
1773−0.453
998−0.559
R 408−0.478
1773−0.469
998−0.601
Table 4. Indicative signatures obtained by improved oblique extremum method with different spectral transformations.
Table 4. Indicative signatures obtained by improved oblique extremum method with different spectral transformations.
Spectral TransformationIndicative Signatures KindBands (nm)Correlation Coefficients
R Oblique Minimum841−0.607
951−0.601
605−0.567
Oblique Minimum Without Local Minimum841−0.607
951−0.601
701−0.588
605−0.567
1 / R Oblique Minimum8630.636
7030.637
9410.624
5570.605
Oblique Minimum Without Local Minimum8630.636
15870.494
5570.605
ln ( 1 / R ) Oblique Minimum8630.624
7030.617
9410.617
5570.583
Oblique Minimum Without Local Minimum8630.624
15870.494
R 2 Oblique Minimum841−0.577
415−0.486
1516−0.503
Oblique Minimum Without Local Minimum841−0.577
605−0.525
1516−0.503
1677−0.474
R 3 Oblique Minimum841−0.542
419−0.470
Oblique Minimum Without Local Minimum841−0.542
951−0.558
605−0.476
701−0.503
R Oblique Minimum841−0.618
951−0.609
605−0.584
Oblique Minimum Without Local Minimum841−0.618
951−0.609
701−0.604
Table 5. RBF neural network model performance results to retrieve the SOM contents based on indicative signatures extracted by correlation analysis.
Table 5. RBF neural network model performance results to retrieve the SOM contents based on indicative signatures extracted by correlation analysis.
Spectral
Transformation
Modeling DatasetValidation Dataset
R m 2 R M S E m   g / k g R v 2 R M S E v   g / k g RPD
R 0.65911.9000.7308.7551.705
1 / R 0.53413.9080.6398.0251.860
ln ( 1 / R ) 0.65312.0040.6027.9191.885
R 2 0.57913.2190.7258.1261.836
R 3 0.52714.0250.7518.4521.766
R 0.63812.2580.5628.7731.701
Table 6. RBF neural network model performance results to retrieve the SOM contents based on indicative signatures extracted by extremum method.
Table 6. RBF neural network model performance results to retrieve the SOM contents based on indicative signatures extracted by extremum method.
Spectral TransformationModeling DatasetValidation Dataset
R m 2 R M S E m   g / k g R v 2 R M S E v   g / k g RPD
R 0.58313.1630.58610.6791.397
1 / R 0.49814.4410.4329.7851.525
ln ( 1 / R ) 0.51814.1450.33711.7261.273
R 2 0.55013.6630.7029.0851.643
R 3 0.46514.8980.7428.2081.818
R 0.59912.8960.54111.9341.251
Table 7. RBF neural network model performance results to retrieve the SOM contents based on indicative signatures extracted by improved oblique extremum method.
Table 7. RBF neural network model performance results to retrieve the SOM contents based on indicative signatures extracted by improved oblique extremum method.
Spectral
Transformation
Indicative
Signatures Kind
Modeling DatasetValidation Dataset
R m 2 R M S E m   g / k g R v 2 R M S E v   g / k g RPD
R Oblique Minimum0.64212.1850.6608.6921.717
Oblique Minimum Without Local Minimum0.70611.0460.7476.2802.376
1 / R Oblique Minimum0.62412.5020.7367.7151.934
Oblique Minimum Without Local Minimum0.59812.9160.7456.7512.211
ln ( 1 / R ) Oblique Minimum0.62212.5320.5019.4401.581
Oblique Minimum Without Local Minimum0.55013.6620.5917.6771.944
R 2 Oblique Minimum0.56013.5120.73810.6251.405
Oblique Minimum Without Local Minimum0.61412.6550.8426.6522.243
R 3 Oblique Minimum0.41615.5770.51510.0961.478
Oblique Minimum Without Local Minimum0.54713.7210.7448.6391.727
R Oblique Minimum0.65611.9460.6688.3821.780
Oblique Minimum Without Local Minimum0.67111.6850.7726.6422.247
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MDPI and ACS Style

Zhang, M.; Wang, M.; Wang, D.; Wang, S.; Xu, W. Organic Matter Retrieval in Black Soil Based on Oblique Extremum Signatures. Remote Sens. 2023, 15, 2508. https://doi.org/10.3390/rs15102508

AMA Style

Zhang M, Wang M, Wang D, Wang S, Xu W. Organic Matter Retrieval in Black Soil Based on Oblique Extremum Signatures. Remote Sensing. 2023; 15(10):2508. https://doi.org/10.3390/rs15102508

Chicago/Turabian Style

Zhang, Mingyue, Maozhi Wang, Daming Wang, Shangkun Wang, and Wenxi Xu. 2023. "Organic Matter Retrieval in Black Soil Based on Oblique Extremum Signatures" Remote Sensing 15, no. 10: 2508. https://doi.org/10.3390/rs15102508

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