Next Article in Journal
Boosting Depth-Based Face Recognition from a Quality Perspective
Previous Article in Journal
Super Sub-Nyquist Single-Pixel Imaging by Means of Cake-Cutting Hadamard Basis Sort
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Canopy Nitrogen Concentration Monitoring Techniques of Summer Corn Based on Canopy Spectral Information

1
State Key Laboratory of Simulation and Regulation of Water Cycle in River Basin, China Institute of Water Resources and Hydropower Research, Beijing 100038, China
2
National Center of Efficient Irrigation Engineering and Technology Research-Beijing, Beijing 100048, China
*
Authors to whom correspondence should be addressed.
Submission received: 6 August 2019 / Revised: 10 September 2019 / Accepted: 20 September 2019 / Published: 23 September 2019
(This article belongs to the Special Issue Recent Advances in Remote Sensing of Plant Stress)

Abstract

:
Crop nitrogen monitoring techniques, particularly choosing sensitive monitoring bands and suitable monitoring models, have great significance both in theory and in practice for achieving non-destructive monitoring of nitrogen concentration and accurate management of water and fertilizer in large-scale areas. In this study, a lysimeter experiment was carried out to examine the characteristics of canopy spectral reflectance variation of summer corn under different fertilization levels. The relationship between canopy spectral reflectance and nitrogen concentration was investigated, based on which sensitive bands for the corn canopy nitrogen monitoring were selected and a suitable spectral index model was determined. The results suggest that under different fertilization levels, the canopy spectral reflectance of summer corn decreases with the increase of the canopy nitrogen concentration in the visible light band, but varies in the opposite direction in the near-infrared band, with a premium put on a higher correlation between the spectral reflectance of the characteristic bands and their first derivatives and the canopy nitrogen concentration. The most sensitive bands for monitoring the canopy nitrogen concentration using spectral reflectance and its first derivative are found to be 762 nm and 726 nm and the correlation coefficients are 0.550 and 0.795, respectively. The optimal band combination, generated by multivariate stepwise regression analysis, is composed of 762 nm, 944 nm and 957 nm bands. From the 55 reported spectral index models of crop nitrogen concentration monitoring, the most suitable index model, NDRE, is chosen such that this index model has the highest correlation with the canopy nitrogen concentration in summer corn. This model has a significant positive correlation with the canopy nitrogen concentration at each growth period, and the correlation coefficient is up to 0.738 during the whole growth period. Spectral monitoring models of canopy nitrogen concentration are constructed using sensitive bands, and a combination of bands and the spectral index, suggesting that these models perform well in monitoring. The models arranged in descending order of simulation accuracy are as follows: the suitable spectral index model, the optimal band combination model, the sensitive band reflectance first derivative model, the sensitive band reflectance model. The determination coefficients are 0.754, 0.711, 0.639 and 0.306, respectively.

1. Introduction

Corn is a widely grown food crop, and nitrogen fertilizer is one of the major limiting factors affecting its growth, playing an important role in growth, yield, and quality of corn. However, aimless increase in fertilizer application and low efficiency of use are having ever greater adverse effects [1]. In order to optimize the nitrogen management in the process of crop growth, it is necessary to understand the nitrogen status of crops accurately and in time [2]. Therefore, rapid but effective tracking and monitoring of crop nitrogen concentration situations, and then reasonable application of nitrogen fertilizer, are of great significance for improving corn quality and for sustainable land use. Crops show different spectral characteristics with different nitrogen concentrations, as has already confirmed by many studies [3]. Compared with traditional destructive sampling methods to monitor plant canopy nitrogen concentration, non-destructive methods that are able to acquire crop hyperspectral information over a large area are more convenient, straightforward and able to provide scientific support for accurate management of modern, large-scale agricultural water and fertilizer application.
Spectral technology allows quick, non-destructive monitoring of crop nutritional parameters. It is one of the important concentrations of agricultural remote sensing to analyze the spectral reflection characteristics of crop canopy and estimate the nitrogen status in the process of crop growth [4]. Many scholars have made similar studies on wheat [5,6,7], rice [8] and corn [9,10], all as field crops, and after analyzing the correlation between the nitrogen content of the plants and their spectral reflectance, built some spectral models for estimating the nitrogen content of the plants. Liu et al. point out that monitoring the nitrogen content of corn in the red and green light bands produces better results, though the sensitive bands vary from one growth period to another [1]. Wang et al. point out that the serious nitrogen deficiency, normal nitrogen application and excessive nitrogen application could be qualitatively distinguished by the spectral reflectivity curve of rice, which laid a foundation for the establishment of a rice canopy nitrogen nutrition diagnosis model in the future [11]. Zhao et al. think that the most sensitive bands were located at 710 nm and 512 nm [12]. Stroppiana et al. used two years of field experiments to propose a regression model for predicting nitrogen concentration in rice plants by spectral data; the model has good applicability through verification [13]. Regarding monitoring the nitrogen content of plants using a spectral index model, previous hyperspectral studies on N accumulation, (leaf area index) LAI and biomass of corn show that hyperspectral remote sensing can be used to comprehensively evaluate the growth of corn [14,15,16]. Clevers et al. note that the green chlorophyll index (CI green) and the red edge chlorophyll index (CI red-edge) are effective in monitoring the nitrogen content [17,18]; Hansen et al. point out that the normalized difference vegetation index (NDVI) and the double-peaked canopy nitrogen index (DCNI) can satisfactorily monitor the wheat canopy nitrogen content [19]. Rasooli et al. show that stepwise multiple linear regressions can be put to good use in constructing a fitted model of protein content in winter wheat leaf and grain [20]. In recent years, N nutrition index (NNI) has been considered to be a reliable index for crop diagnosis [21]. In summary, from the researches carried out on the quantitative relationship between the spectral reflectance of crops and the nitrogen concentration of their plants, it can be seen that large differences exist in both spectral extraction and analysis methods used in spectral remote sensing monitoring. Some of these studies are based on qualitative or semi-quantitative experiments but making use of sensitive bands or spectral index models to monitor the nitrogen concentration of plants is troubled by universality in applications. Moreover, as crops, growth period, and investigation region vary from study to study, the sensitive bands and spectral index models for monitoring plant nitrogen concentration vary from study to study too, making these models unable to meet the general needs of crop nutrition diagnosis and growth monitoring. In order to achieve large-scale, non-destructive monitoring of nitrogen concentration in main crop plants, it is urgent to carry out further spectral monitoring tests of nitrogen concentration in typical crops and to choose the most sensitive bands and spectral index models suitable for monitoring nitrogen concentration during the whole growth period, as an effort to solve the technical problem of universality associated with spectral characteristic variables.
The study reported in this paper focuses on summer corn. A hand-held ground spectrometer and a Kjeldahl nitrogen apparatus were used to investigate the spectral monitoring of canopy nitrogen concentration under different nitrogen fertilizer treatments. The sensitive bands and the suitable hyperspectral estimation models chosen may provide a scientific basis for hyperspectral diagnosis of nitrogen concentration in corn.

2. Materials and Methods

2.1. Brief Information of Experiment Area

The experiment was carried out at the water-saving irrigation experiment station of China Institute of Water Resources and Hydropower Research. The station is located at 39°37′N and 116°26′E, at an altitude of 40.1 m, dominated by warm and semi-arid continental monsoon climate, dry in winter and spring and rainy in summer. The mean annual precipitation is 540 mm. The mean annual temperature is 12.1 °C, and the mean annual wind speed is 1.2 m/s. The mean annual frost-free period is 185 d and the mean annual surface evaporation is above 1800 mm. The mean annual sunshine hours are about 2600 h.

2.2. Experiment Design

The summer corn variety studied was Jiyuan 168, sown on June 15, harvested on September 25 for 2017 and 2018 at plant spacing and row spacing both of 25 cm. The soil is sandy loam, and the initial nutrient status of the soil is shown in Table 1. The experiment involved a total of 12 lysimeters of 1 m × 0.75 m × 1 m size each, with six plants per box. The lysimeter experiment received four nitrogen fertilizer treatments and had two fertilizer applications throughout the growth period. More specifically, the base fertilizer was compound fertilizer (15% N, 15% P2O5, and 15% K2O), and during the shooting–tasseling period, urea was applied (46% N); the proportion of compound fertilizer to urea was 1:1. The setting of specific fertilizer level refers to the guidance of scientific fertilizer application of the main crops of the Ministry of Agriculture, and the gradient setting was carried out in combination with the local fertilizer level (450 kg/hm2) in the experimental site. The amount of fertilization was 0, 225, 450, 675 kg/hm2, that is, N0, N1, N2, and N3, and each treatment was repeated three times. Spectral monitoring for 2 years involved four growth periods. During the spectral determination period, three representative corn canopies in each box were selected for canopy spectral monitoring, the average values were used as the spectral reflectance of the box, and the average values of three boxes in the same treatment were used as the corn canopy spectral reflectance of the same treatment. Because the nitrogen concentration of corn canopy was determined as destructive sampling, only two representative plants were selected for the determination of nitrogen concentration for the same treatment. Other management practices such as sowing, farming, and weeding were kept in line with local farmers. Compared with the field plot experiment, the lysimeter experiment can strictly control the experimental variables, was subject to less interference and its data are more reliable.

2.3. Items to Be Measured and Methods

2.3.1. Monitoring of Canopy Spectra

During the growth period of summer corn, the canopy spectral reflectance was monitored at 10:00−14:00 using a Field-Spec HandHeld2, a hand-held ground spectrometer manufactured by American Analytical Spectral Devices (ASD), on a fine day with still wind or light breeze. The band was 325−1075 nm, the sampling interval was 1 nm, with a resolution of 3 nm. During the measurement, the sensor probe was aimed vertically downward above the canopy, the field of view angle of the spectrometer was 25°, and the vertical height from the top of canopy was about 15−20 cm.

2.3.2. Determination of Canopy Nitrogen Concentration

Young fully expanded leaves were sampled to determine canopy nitrogen concentration. Samples were cut from the plants and were immediately taken back to the laboratory for water-removing and oven-drying treatment. After drying, the sample was ground to a uniform powder, which was then boiled in H2SO4-H2O2 solution. Measurement was made with a Kjeldahl nitrogen apparatus. More details of this measurement method can be found in Soil Agrochemical Analysis [22].

2.3.3. Data Processing and Statistical Analysis

The monitored raw spectral reflectance data were resampled and exported by the processing software of the spectrometer. The arithmetic mean of the spectral reflectance at all sampling points was taken as the raw spectral reflectance of the canopy. From these raw spectral reflectance data, the first derivative was obtained. Then, correlations between the nitrogen concentration of the summer corn canopy on the one hand and the raw spectral reflectance and the first-order differential spectrum on the other hand were estimated.
The correlation coefficient r described above was estimated by:
r = i = 1 n ( x i x ¯ ) ( y i y ¯ ) i = 1 n ( x i x ¯ ) 2 i = 1 n ( y i y ¯ ) 2 ,
where n is the number of actual measurements; xi is the spectral reflectance or first-order differential spectrum of the i-th summer corn canopy; x is the mean of the spectral reflectance, or the mean of the first-order differential spectra of the summer corn canopy; yi is the nitrogen concentration in the i-th summer corn canopy; and y is the mean of summer corn canopy nitrogen concentration.

3. Results

3.1. Canopy Nitrogen Concentration and Yield of Summer Corn under Different Nitrogen Levels

The canopy nitrogen concentrations of summer corn plants under different nitrogen treatments are shown in Figure 1. The concentration dropped as the growth period progressed, being higher at the jointing and the tasseling periods and lower at the filling and the maturing periods. With the increase of nitrogen fertilization, the canopy nitrogen concentration of summer corn increased, with the concentration under different nitrogen fertilizer treatments differing to an extremely significant level (p < 0.01), but the difference between N2 and N3 treatments just reached a significant level (p < 0.05).
The yields of summer corn under different nitrogen fertilizer treatment are shown in Figure 2. The yield of summer corn increased with the increase of nitrogen fertilization. The maximum yield was 10.435 t/hm2 for 2017 and 9.508 t/hm2 for 2018 in the case of treatment N2. As the application rate of the nitrogen fertilizer was further improved, the yield was decreased, as in the case of N3 treatment. This demonstrates that rational fertilization promotes corn growth and ensures a high yield. Controlling surface source pollution caused by excessive fertilization, as can be seen, is conducive to sustainable and efficient agricultural production.

3.2. Canopy Spectral Characteristics of Summer Corn under Different Nitrogen Levels

The canopy spectral characteristics of summer corn plants under different nitrogen treatments are shown in Figure 3. In the photosynthesis process, chlorophyll plays a central role in light absorption because in the visible light band (380−760 nm) chlorophyll absorbs most of the red and violet light but reflects green light, with the result that the canopy spectral reflectance is low. Specifically, the reflection peak of the green light band (500−580 nm) appears around 550 nm, while at the red light band (620−760 nm) an absorption band occurs because a large amount of red light is absorbed in the photosynthesis process of chlorophyll. In the near-infrared band (760−1075 nm), there occurs a high reflection zone because the canopy spectral reflectance is controlled by the internal structure of the summer corn canopy: the canopy reflectance rises sharply near the 760 nm band to form a “red edge”.
Under the same nitrogen treatments, during the growth process from jointing period to tasseling period, because summer corn was in the vigorous growth period, photosynthesis increased gradually with the increase of leaf area, and the coverage also increased, which effectively reduced the influence of soil background and other external factors, and the spectral reflectance of summer corn decreased gradually in the visible light band. From tasseling period to filling period, photosynthesis decreased gradually because of the decrease of chlorophyll concentration and the absorption capacity of blue and red light bands decreased; the spectral reflectance of summer corn canopy increased gradually. After entering the maturity period, the leaves withered yellow and the canopy spectral reflectance increased. While in the near infrared band, the canopy spectral reflectance increased gradually due to the jointing period and tasseling period belonging to the period of nutrient growth and accumulation under the control of internal structure of summer corn canopy. However, the filling period and maturity period are the reproductive growth period centered on grain, at the same time, the spectral reflectance of the canopy of summer corn was gradually decreased by the effect of the concentration of chlorophyll and the photosynthesis.
In the visible light band, the spectral reflectance of summer corn showed a clear difference under different nitrogen application levels, since chlorophyll plays a main role in the photosynthesis process and its concentration will have a direct influence on photosynthesis ability. However, the important component element of chlorophyll is nitrogen, so the SPAD value of high nitrogen application is larger than that of low nitrogen application [23], which affects the photosynthesis. Therefore, the spectral reflectance of summer corn canopy decreased with the increase of nitrogen application amount, among which there was significant difference (p < 0.05), especially in the green light band during the filling period, as shown in Figure 3c. In the range of near infrared band, summer corn was controlled by the internal structure of plant canopy and the variation rule of the canopy spectral reflectance of summer corn showed an opposite trend under different nitrogen application levels. With the increase of nitrogen application, the spectral reflectance of canopy increased, and the difference between treatments was more significant than that of the visible light band, especially at the filling period, and reached a very significant level (p < 0.01).

3.3. Sensitive Bands for Spectral Monitoring of Canopy Nitrogen in Summer Corn

The correlation coefficient between the canopy spectral reflectance and canopy nitrogen concentration of summer corn is illustrated in Figure 4a. It can be seen that the two are relatively low at the jointing period which may be due to the fact that the jointing period is in the peak period of vegetative growth, and the changes of nutrient composition and cell structure lead to the instability of spectral reflectance. There was a positive correlation between the canopy spectral reflectance and canopy nitrogen concentration at the tasseling period and the maturity period, which reached their maximums at 937 nm and 762 nm, which were 0.526 and 0.281, respectively. At the filling period, the correlation coefficients formed wave valley and wave peak at 680 nm and 774 nm, and the correlation coefficients were –0.474 and 0.478, respectively. Over the whole growth period, the correlation coefficients formed wave valleys and peaks at 678 nm and 762 nm and were –0.492 (p < 0.05) and 0.550 (p < 0.01), respectively.
The correlation coefficient between the first derivative of the canopy spectral reflectance of summer corn and canopy nitrogen concentration is shown in Figure 4b. By comparing with Figure 4a, it can be seen that the correlation coefficient between the first derivative value and the nitrogen concentration in some bands was higher than that between the spectral reflectance and the nitrogen concentration, which was due to the removal of the influence of soil background on the spectral reflectance in the derivation process. It can be seen that in 700−750 nm band, there was a significant positive correlation in the whole growth period, among which the correlation of filling period and whole growth period were the highest, followed by tasseling period and maturity period, and the lowest correlation was at jointing period.
According to the above analysis results, the most sensitive band was selected according to the principle of maximizing the correlation value, and the optimal band combination was selected by stepwise regression analysis. The sensitive bands based on the synthesis of two-year data are listed in Table 2. For the sensitive band screened by spectral reflectance, it can be seen that the correlation between spectral reflectance of sensitive band and nitrogen concentration was not significant at the jointing and maturity periods. At tasseling and filling periods, the reflectance of the sensitive band was significantly correlated with nitrogen concentration, and there was a very significant correlation at filling period. During the whole growth period, the correlation between them was very significant at 762 nm; the fitting model of canopy nitrogen concentration based on spectral reflectance is shown in Figure 5a. The results showed that the spectral reflectance of summer corn was easily affected by soil background and leaf structure at jointing period maturity periods compared with tasseling and filling periods, so it was difficult to obtain an ideal sensitive band.
For the first derivative of spectral reflectance, except for the jointing period, the correlation between the first derivative of spectral reflectance and the nitrogen concentration was very significant. For the sensitive band of 726 nm in the whole growth period, the first derivative of spectral reflectance had the highest correlation with nitrogen concentration, and the correlation coefficient was as high as 0.795. The fitting model of canopy nitrogen concentration based on first derivative of spectral reflectance is shown in Figure 5b. Obviously, the use of spectral reflectance first derivative selection was more stable compared to the use of spectral reflectance to select sensitive bands.
Based on synthesis of two-year data, the optimal band combination selected by stepwise regression analysis was 762 nm, 944 nm and 957 nm. The fitting model was y = 0.881 – 10.194R762 – 20.056R957 + 11.469R944, and the determination coefficient was as high as 0.711.

3.4. Selecting Optimal Index Model for Monitoring Canopy Nitrogen Concentration in Summer Corn

This study was based on 55 published nitrogen spectral monitoring index models (Table 3). The correlation between the calculated value of nitrogen spectral monitoring index and the monitoring value of nitrogen concentration based on synthesis of two-year data was analyzed and the correlation coefficients are listed in Table 4.
The spectral index of monitoring canopy nitrogen concentration in summer corn during the whole growth period was selected based on two-years data, and the spectral indexes of the top 20 correlation coefficients were screened out as shown in Table 5. In order to enhance the applicability of the spectral index in monitoring canopy nitrogen concentration in each growth period of summer corn, the correlation coefficient between 20 spectral indexes and canopy nitrogen concentration in each growth period was considered synthetically, and finally the top five spectral indexes were selected as shown in Table 6; these were mNDVI, NDRE, R780/R740, ND (FD730, FD525) and CCCI. The fitting model of canopy nitrogen concentration based on the top five spectral indexes is shown in Figure 6.
The correlation coefficients between the five spectral indexes selected based on the comprehensive data of two years and the nitrogen concentration of the corresponding plant canopy were analyzed, as shown in Table 7 and Table 8. During the whole growth period, the spectral indexes reached very significant levels in 2017 and 2018, indicating that the spectral indexes had high interannual applicability. In 2017, the spectral indexes NDRE and R780/R740 were significantly correlated at all growth periods. In 2018, the five spectral indexes were significantly correlated at all growth periods. Considering the correlation between the spectral index and the nitrogen concentration of the plant canopy at each growth period, and combined with the difference of the nitrogen concentration of the canopy at different growth periods among different fertilizer treatments, NDRE was recommended as the most suitable monitoring model of the spectral index of nitrogen concentration in the whole growth period of summer corn.

3.5. Spectral Monitoring Technology of Canopy Nitrogen Concentration in Summer Corn

After the sensitive bands for the canopy nitrogen concentration monitoring were chosen and a suitable spectral index model recommended, we built a sensitive band reflectance model, a sensitive band reflectance first derivative model, an optimal bands combination model, and a suitable spectral index model (Table 9), obtained from the 762 nm spectral reflectance, the 726 nm spectral reflectance first derivative, the optimal bands combination obtained by stepwise discriminant analysis, and the spectral index NDRE. These models were compared for their monitoring performance in terms of determination coefficient (R2), root mean square error (RMSE), and mean absolute error (MAE), the specific meaning of which is given in [36], and the evaluation of the fitting model is shown in Figure 7. A monitoring model, incorporating the natural logarithmic function of the spectral reflectance of the sensitive 762 nm band, of summer corn canopy nitrogen concentration was established. So, this was a model based on the original spectral reflectance of the sensitive band. The R2, RMSE and MAE between the simulated values and the measured values were 0.306, 0.514 g.g–1, and 0.413 g.g–1 respectively. Another sensitive-band-based model, incorporating the natural logarithmic function of the spectral reflectance first derivative at the sensitive 726 nm band, was built for monitoring the canopy nitrogen concentration in summer corn. The R2, RMSE, and MAE between the simulated values and the measured values were 0.639, 0.368 g.g–1, and 0.298 g.g–1 respectively. A third model, based on the optimal combination of bands, was built by stepwise discriminant analysis. The R2, RMSE, and MAE between the simulated values and measured values were 0.711, 0.328 g.g–1, and 0.262g.g–1, respectively. A fourth model for monitoring the canopy nitrogen concentration in summer corn plants was based on the suitable spectral index model and incorporated a quadratic parabolic function of the calculated values of NDRE, the recommended suitable spectral index model. The R2, RMSE, and MAE between the simulated values and the measured values were 0.754, 0.322 g.g–1, and 0.258 g.g–1, respectively. It can be seen that the order of simulation accuracy from high to low was as follows: suitable spectral index model, band optimal combination model, sensitive band reflectivity first derivative model and sensitive band reflectivity model.

4. Discussion

It is very important to judge the nutritional status of crops accurately and in real time for achieving a high yield. In this study, the selection of spectral parameters such as sensitive band, spectral index and sensitive band combination are based on the simulation effect of the whole growth period as the evaluation standard. These can meet the requirements of spectral monitoring accuracy during the whole growth period of corn, break through the previous spectral model monitoring restricted by the growth period, and realize the accurate monitoring of nitrogen concentration during the whole growth period of corn. However, hyperspectral monitoring based on leaf scale could only represent the nitrogen concentration of a single plant and could only obtain hyperspectral reflectance in a small area, which is not representative. In order to facilitate crop nitrogen concentration monitoring in a large area, this needs to be achieved by means of remote sensing satellites in principle. However, most of the spectral reflectance obtained by satellite is crop canopy spectral reflectance. Therefore, it is very meaningful to study the spectral characteristics of crop canopy and establish the relationship between spectral reflectance and physiological and ecological parameters, which could be the basis of rapid diagnosis of crop nutritional status [37,38,39].
From the monitoring data of the canopy nitrogen concentration in summer corn and their canopy spectral reflectance data under different nitrogen levels, the spectral reflectance in the visible light band is mainly affected by the change of chlorophyll content. With the advance of growth period, the leaf area increases, while the soil background noise decreases. As a result, the spectral reflectance increases. In the near-infrared band, the spectral reflectance is mainly influenced by the optical properties and the canopy structure of the leaf structure; the multiple reflection and scattering of light inside the blade forms a high reflection platform, and the difference of cell gap, shape and composition also affect the spectral reflectance [26]. Therefore, the reflectance in the near infrared band decreases gradually with the advance of the growth period.
The sensitive bands and their suitable combination were put forward by analyzing the response relationship between the canopy nitrogen concentration and the canopy spectral reflectance. Compared with the original spectral reflectance, the correlation between the concentration of nitrogen in the canopy and the first derivative is higher, because the first derivative could reduce the influence of soil background and other noise. Osbome et al. pointed out that the sensitive band was in the green and red band for monitoring the canopy nitrogen concentration of the corn [40]. Li Zhen analyzed the nitrogen content in leaves and spectral reflectivity, which showed that the sensitive bands for monitoring nitrogen content were in blue light band and red light band [30]. This is consistent with our results, namely that the sensitive bands for monitoring nitrogen content are mainly in the red light band. Therefore, the sensitive band can be selected according to the change of spectral reflectance and its first derivative.
Because spectral reflectance is affected by many factors, spectral reflectance changes throughout the crop growth period. It is very difficult to obtain a simple and applicable spectral model for monitoring crop canopy nitrogen content. Four models for monitoring the canopy nitrogen concentration in summer corn, namely the sensitive band reflectance model, the sensitive band reflectance first derivative model, the suitable spectral index model, and the optimal band combination model were built based on the relationship between the spectral parameters and crop canopy nitrogen content for every growth stage. Compared with the regression model based on the sensitive band, the simulation precision based on spectral index and optimal band combination is higher. The spectral index and optimal band combination contain multiple band information, which can reduce the influence of soil background and other noise. The suitable spectral index model and the optimal spectral band combined regression model for monitoring the canopy nitrogen concentration in summer corn were proposed; these models had high correlation between the simulated values and the measured values for the whole growth period, which provides a reference for the spectral monitoring of nitrogen concentration in summer corn canopy.

5. Conclusions

The main conclusions are as follows:
(1)
The canopy reflectance of the plants is low due to the absorption by chlorophyll in the visible light band, but the multi-scattering effect of the canopy cell structure in the near-infrared region leads to a higher reflectance in this band. At the point of fertilization, the canopy spectral reflectance of summer corn plants in the visible light band decreases with the increase of fertilization, but the trend is reversed in the near infrared band.
(2)
Choosing the bands to which the plant canopy nitrogen concentration is sensitive reduces the redundancy of spectral information and improves the prediction accuracy of the spectral models. Investigation is made into the correlation between the summer corn plant canopy spectral reflectance and its first derivative on the one hand and the canopy nitrogen concentration on the other. From the correlation and factoring in the optimal band combination determined by the stepwise discriminant analysis, the sensitive bands for monitoring the canopy nitrogen concentration using the original spectra and their first derivative are found to be 762 nm and 726 nm respectively, the optimal combination of bands is 762 nm, 944 nm and 957 nm.
(3)
A total of 55 published nitrogen spectral monitoring index models were examined for the correlation between their calculated values and the measured values of the canopy nitrogen concentration. Five spectral index models with higher correlation coefficients are retained, namely mNDVI, NDRE, R780/R740, ND (FD730, FD525) and CCCI, and the principle of highest correlation at key growth period was taken into account, NDRE is recommended as the most suitable spectral index model for monitoring nitrogen concentration in summer corn canopy.
(4)
Once the sensitive bands were determined, the suitable spectral index model recommended, and the optimal band combination known, four models, namely the sensitive band reflectance model, the sensitive band reflectance first derivative model, the optimal band combination model, and the suitable spectral index model, were constructed and demonstrated to perform well in predicting summer corn canopy nitrogen concentration. The four models come in the following descending order of prediction accuracy: the suitable spectral index model, the optimal band combination model, the sensitive band reflectance first derivative model, and the sensitive band reflectance model.

Author Contributions

All authors read and approved the manuscript. L.L., Z.P. and B.Z. proposed the main idea of this research.

Funding

This study was supported by the National Key R&D Program of China (2018YFC0407703), IWHR Research & Development Support Program (ID0145B082017, ID0145B742017, ID0145B102019 and ID01881910), the Chinese National Natural Science Fund (51822907, 51379217, 91425302 and 51479210), the Special Fund of State Key Laboratory of Simulation and Regulation of Water Cycle in River Basin, and China Institute of Water Resources and Hydropower Research (2016TS06).

Acknowledgments

The authors greatly appreciate the anonymous reviewers and the academic editor for their comments and valuable suggestions. (Conceptualization, Z.P., L.L. and B.Z.; Data curation, L.L.; Formal analysis, L.L.; Funding acquisition, Z.P. and B.Z.; Investigation, L.L., N.H. and S.L.; Writing – original draft, Z.P., L.L. and B.Z.; Writing – review & editing, L.L., Z.P. and B.Z.)

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Liu, B. Study on Hyperspectral Remote Sensing Estimation Model of Nitrogen and Phosphorus Nutrition Monitoring in Summer Maize. Ph.D. Thesis, Northwest Agriculture and Forestry University, Xianyang, China, 2012. (In Chinese with English abstract). [Google Scholar]
  2. Ata-Ul-Karim, S.T.; Liu, X.; Lu, Z.; Zheng, H.; Cao, W.; Zhu, Y. Estimation of nitrogen fertilizer requirement for rice crop using critical nitrogen dilution curve. Field Crop. Res. 2017, 201, 32–40. [Google Scholar] [CrossRef]
  3. Yang, F. Studies on Hyperspectral Diagnosis and Application of Nitrogen Nutrition in Leaves and Plants of Wheat and Maize. Ph.D. Thesis, China University of Mining and Technology, Beijing, China, 2016. (In Chinese with English abstract). [Google Scholar]
  4. Li, F.; Miao, Y.; Feng, G.; Yuan, F.; Yue, S.; Gao, X.; Liu, Y.; Liu, B.; Ustin, S.L.; Chen, X. Improving estimation of summer maize nitrogen status with red edge-based spectral vegetation indices. Field Crop. Res. 2014, 157, 111–123. [Google Scholar] [CrossRef]
  5. He, J. Hyperspectral remote Sensing Monitoring Model of Eco-Physiological Parameters of Winter Wheat at Different Growth Stages. Ph.D. Thesis, Northwest Agriculture and Forestry University, Xianyang, China, 2015. (In Chinese with English abstract). [Google Scholar]
  6. Zhu, Y.; Yao, X.; Tian, Y.; Liu, X.; Cao, W. Analysis of common canopy vegetation indices for indicating leaf nitrogen accumulations in wheat and rice. Int. J. Appl. Earth Obs. Geoinf. 2008, 10, 1–10. [Google Scholar] [CrossRef]
  7. Broge, N.; Mortensen, J. Deriving green crop area index and canopy chlorophyll density of winter wheat from spectral reflectance data. Remote Sens. Environ. 2002, 81, 45–57. [Google Scholar] [CrossRef]
  8. Cao, W.; Dai, T.; Xue, L.; Luo, W.; Zhu, Y. Monitoring Leaf Nitrogen Status in Rice with Canopy Spectral Reflectance. Agron. J. 2004, 96, 135–142. [Google Scholar]
  9. Chen, P.; Haboudane, D.; Tremblay, N.; Wang, J.; Vigneault, P.; Li, B. New spectral indicator assessing the efficiency of crop nitrogen treatment in corn and wheat. Remote Sens. Environ. 2010, 114, 1987–1997. [Google Scholar] [CrossRef]
  10. Gao, X.; Gao, J.; Yu, X.; Wang, Z.; Zhang, B.; Hu, S.; Xie, M.; Sun, J.; Luo, R.; Lv, F.; et al. Study on estimation Model of SPAD value based on Leaf Hyperspectral of different Maize varieties. Corn Sci. 2016, 24, 108–114, (In Chinese with English abstract). [Google Scholar]
  11. Wang, S.; Zheng, B.; Zhang, C. Research on Hyperspectral Characteristics of Rice under Nitrogen Stress. Agric. Mech. Res. 2015, 8, 162–165, (In Chinese with English abstract). [Google Scholar]
  12. Zhao, B.; Duan, A.; Ata-UI-Karim, S.T.; Liu, Z.; Chen, Z.; Gong, Z.; Zhang, J.; Xiao, J.; Liu, Z.; Qin, A.; et al. Exploring new spectral bands and vegetation indices for estimating nitrogen nutrition index of summer maize. Eur. J. Agron. 2018, 93, 113–125. [Google Scholar] [CrossRef]
  13. Stroppiana, D.; Boschetti, M.; Brivio, P.A.; Bocchi, S. Plant nitrogen concentration in paddy rice from field canopy hyperspectral radiometry. Field Crop. Res. 2009, 111, 119–129. [Google Scholar] [CrossRef]
  14. Quemada, M.; Gabriel, J.L.; Zarco-Tejada, P.J. Airborne Hyperspectral Images and Ground-Level Optical Sensors as Assessment Tools for Maize Nitrogen Fertilization. Remote Sens. 2014, 6, 2940–2962. [Google Scholar] [CrossRef]
  15. Cilia, C.; Panigada, C.; Rossini, M.; Meroni, M.; Busetto, L.; Amaducci, S.; Boschetti, M.; Picchi, V.; Colombo, R. Nitrogen Status Assessment for Variable Rate Fertilization in Maize through Hyperspectral Imagery. Remote Sens. 2014, 6, 6549–6565. [Google Scholar] [CrossRef] [Green Version]
  16. Xia, T.; Miao, Y.; Wu, D.; Shao, H.; Khosla, R.; Mi, G. Active Optical Sensing of Spring Maize for In-Season Diagnosis of Nitrogen Status Based on Nitrogen Nutrition Index. Remote Sens. 2016, 8, 605. [Google Scholar] [CrossRef]
  17. Clevers, J.G.P.W.; Kooistra, L. Using Hyperspectral Remote Sensing Data for Retrieving Canopy Chlorophyll and Nitrogen Content. IEEE J. Sel. Top. Appl. Earth Obs. Remote Sens. 2012, 5, 574–583. [Google Scholar] [CrossRef]
  18. Clevers, J.; Gitelson, A. Remote estimation of crop and grass chlorophyll and nitrogen content using red-edge bands on Sentinel-2 and -3. Int. J. Appl. Earth Obs. Geoinf. 2013, 23, 344–351. [Google Scholar] [CrossRef]
  19. Hansen, P.M.; Jørgensen, J.R.; Thomsen, A. Predicting grain yield and protein content in winter wheat and spring barley using repeated canopy reflectance measurements and partial least squares regression. J. Agric. Sci. 2002, 139, 307–318. [Google Scholar] [CrossRef]
  20. Sharabian, V.R.; Noguchi, N.; Ishi, K. Significant wavelengths for prediction of winter wheat growth status and grain yield using multivariate analysis. Eng. Agric. Environ. Food 2014, 7, 14–21. [Google Scholar] [CrossRef]
  21. Zhao, B.; Ata-Ul-Karim, S.T.; Liu, Z.; Ning, D.; Xiao, J.; Liu, Z.; Qin, A.; Nan, J.; Duan, A. Development of a critical nitrogen dilution curve based on leaf dry matter for summer maize. Field Crop. Res. 2017, 208, 60–68. [Google Scholar] [CrossRef]
  22. Bao, S. Analysis of Soil Agrochemistry; China Agricultural Press: Beijing, China, 2000. [Google Scholar]
  23. Liu, L.; Peng, Z.; Zhang, B.; Han, Y.; Wei, Z.; Han, N. Monitoring of Summer corn canopy SPAD values based on Hyperspectrum. J. Soil Water Conserv. 2019, 33, 355–362, (In Chinese with English abstract). [Google Scholar]
  24. Yao, F. Study on the Hyperspectral Characteristics of Winter Wheat and Its Physiological and Ecological Parameters Estimation Model. Ph.D. Thesis, Northwest Agricultural University of Science and Technology, Xianyang, China, 2012. (In Chinese with English abstract). [Google Scholar]
  25. Wu, G. High-Spectrum Quantitative Extraction and Application Study of Main Physiological Indexes of Cotton in Xinjiang. Ph.D. Thesis, Hunan Agricultural University, Changsha, China, 2004. (In Chinese with English abstract). [Google Scholar]
  26. Li, Y. Maize Growth Information Monitoring Study Coupled with an Imaging Spectrometer Based on a Figure Spectrometer. Ph.D. Thesis, Northwest Agricultural University of Science and Technology, Xianyang, China, 2017. (In Chinese with English abstract). [Google Scholar]
  27. Ju, C. Monitoring of Nitrogen Status and Growth Characteristics of Wheat by Ground-Space Hyperspectral Remote Sensing. Ph.D. Thesis, Nanjing Agricultural University, Nanjing, China, 2008. (In Chinese with English abstract). [Google Scholar]
  28. Liang, L.; Yang, M.; Deng, K.; Zhang, L.; Lin, H.; Liu, Z. A new high spectral index for estimating nitrogen content in wheat canopy. Acta Ecol. Sin. 2011, 31, 6594–6605, (In Chinese with English abstract). [Google Scholar]
  29. Winterhalter, L.; Mistele, B.; Schmidhalter, U. Assessing the vertical footprint of reflectance measurements to characterize nitrogen uptake and biomass distribution in maize canopies. Field Crop. Res. 2012, 129, 14–20. [Google Scholar] [CrossRef]
  30. Li, Z. Monitoring of Nitrogen Nutrition and Growth Index Based on Hyperspectral Corn. Ph.D. Thesis, Shandong Agricultural University, Tai’an, China, 2012. (In Chinese with English abstract). [Google Scholar]
  31. Yao, X.; Zhu, Y.; Tian, Y.; Feng, W.; Cao, W. Study on Optimal Hyperspectral Parameters for Estimating Nitrogen Content in Leaf of Wheat. China Agric. Sect. 2009, 42, 2716–2725, (In Chinese with English abstract). [Google Scholar]
  32. Barnes, E.M.; Clarke, T.R.; Richards, E.; Colaizzi, P.D.; Haberland, J.; Kostrzewski, M.; Waller, P.; Choi, C.; Riley, E.; Thompson, T.; et al. Coincident detection of crop water stress, nitrogen status and canopy density using ground-based multispectral data. In Proceedings of the International Conference on Precision Agriculture and Other Resource Management, Bloomington, MN, USA, 16–19 July 2000. [Google Scholar]
  33. Wang, W.; Yao, X.; Yao, X.; Tian, Y.; Liu, X.; Ni, J.; Cao, W.; Zhu, Y. Estimating leaf nitrogen concentration with three-band vegetation indices in rice and wheat. Field Crop. Res. 2012, 129, 90–98. [Google Scholar] [CrossRef]
  34. Feng, W.; Yao, X.; Zhu, Y.; Tian, Y.; Cao, W. Study on Nitrogen Content Monitoring Model of Wheat Leaves Based on Hyperspectral Remote Sensing. J. Wheat Crops 2008, 25, 851–860, (In Chinese with English abstract). [Google Scholar]
  35. Tang, Q.; Li, S.; Wang, K.; Xie, R.; Chen, B.; Wang, F.; Diao, W.; Xiao, C. Study on Nitrogen Abundance Monitoring in Winter Wheat Growth Stage Based on High Spectral Reflectivity. Spectrosc. Spectr. Anal. 2010, 30, 3061–3066, (In Chinese with English abstract). [Google Scholar]
  36. Peng, Z.; Zhang, B.; Liu, Y.; Cai, J.; Wang, L.; Du, L. Regional Water consumption Simulation and Irrigation Optimization of Winter Wheat in typical area of North China. J. Agric. Mach. 2017, 48, 238–246, (In Chinese with English abstract). [Google Scholar]
  37. Chen, Z. High Spectral Response and Nutrition Diagnosis of Maize Leaves under Different Nitrogen Fertilizer Dose. Ph.D. Thesis, Chinese Academy of Agricultural Sciences, Beijing, China, 2013. (In Chinese with English abstract). [Google Scholar]
  38. Wang, W. Review on Development and Application of Hyperspectral Remote Sensing in Agriculture. Acta Agric. Jiangxi 2009, 21, 23–26, (In Chinese with English abstract). [Google Scholar]
  39. Vigneau, N.; Ecarnot, M.; Rabatel, G.; Roumet, P. Potential of field hyperspectral imaging as a non destructive method to assess leaf nitrogen content in Wheat. Field Crop. Res. 2011, 122, 25–31. [Google Scholar] [CrossRef] [Green Version]
  40. Osbome, S.L. Detection of phosphorus and nitrogen deficiencies in corn using spectral radiance measurements. Agron. J. 2002, 94, 1215–1221. [Google Scholar]
Figure 1. Effect of nitrogen application level on summer corn canopy nitrogen concentration.
Figure 1. Effect of nitrogen application level on summer corn canopy nitrogen concentration.
Sensors 19 04123 g001
Figure 2. Effect of nitrogen application level on yield of summer corn.
Figure 2. Effect of nitrogen application level on yield of summer corn.
Sensors 19 04123 g002
Figure 3. Effect of nitrogen application levels on canopy spectral reflectance curve of summer corn.
Figure 3. Effect of nitrogen application levels on canopy spectral reflectance curve of summer corn.
Sensors 19 04123 g003aSensors 19 04123 g003b
Figure 4. Correlation between canopy spectral reflectance and its first derivative and nitrogen concentration in summer corn. (a) the correlation coefficient between the canopy spectral reflectance and canopy nitrogen concentration of summer corn; (b) the correlation coefficient between the first derivative of the canopy spectral reflectance of summer corn and canopy nitrogen concentration.
Figure 4. Correlation between canopy spectral reflectance and its first derivative and nitrogen concentration in summer corn. (a) the correlation coefficient between the canopy spectral reflectance and canopy nitrogen concentration of summer corn; (b) the correlation coefficient between the first derivative of the canopy spectral reflectance of summer corn and canopy nitrogen concentration.
Sensors 19 04123 g004
Figure 5. Fitting model of canopy nitrogen concentration and sensitive band.
Figure 5. Fitting model of canopy nitrogen concentration and sensitive band.
Sensors 19 04123 g005
Figure 6. Fitting model of canopy nitrogen concentration based on top five spectral indexes.
Figure 6. Fitting model of canopy nitrogen concentration based on top five spectral indexes.
Sensors 19 04123 g006aSensors 19 04123 g006b
Figure 7. Comparisons between analog and measured values for the fitting models.
Figure 7. Comparisons between analog and measured values for the fitting models.
Sensors 19 04123 g007
Table 1. Initial nutrient status of soil.
Table 1. Initial nutrient status of soil.
Degree of Depth (cm)Initial Nitrate Nitrogen Concentration (mg/kg)Initial Ammonium Nitrogen Concentration (mg/kg)
0−205.5583.231
20−402.8032.773
40−602.2882.710
60−802.5342.532
Table 2. Correlation coefficients between summer corn canopy nitrogen concentration and spectral reflectance and its first derivative.
Table 2. Correlation coefficients between summer corn canopy nitrogen concentration and spectral reflectance and its first derivative.
Spectral Characteristic VariableJointing PeriodTasseling PeriodFilling PeriodMaturity PeriodWhole Growth Period
spectral reflectanceCharacteristic band (nm)799937774762762
Correlation coefficient0.1600.526 *0.578 **0.2800.550 **
first derivative spectral reflectanceCharacteristic band (nm)737752738714726
Correlation coefficient0.2850.659 **0.767 **0.636**0.795 **
Note: ** p < 0.01, * p < 0.05.
Table 3. Indices used in the study for spectral monitoring of nitrogen.
Table 3. Indices used in the study for spectral monitoring of nitrogen.
CategorySpectral ParametersDefinitionReference
Spectral characteristic parametersGreen peak amplitude, RgMaximum band reflectance within the green band of 510−560 nm[5]
Red trough amplitude, RrMinimum band reflectance within the red
band of 640−680 nm
[5]
(Rg – Rr)
/(Rg + Rr)
Normalized value of green peak reflectance and red trough reflectance[5]
Rg/RrRatio between green peak reflectance and red trough reflectance[5]
Red trough skewness, SrBand reflectance skewness within 640−680 nm region[24]
Red trough kurtosis, krBand reflectance kurtosis within 640−680 nm region[24]
Green peak skewness, SgBand reflectance skewness within 510−560 nm region[24]
Green peak kurtosis, kgBand reflectance kurtosis within 510−560 nm region[24]
Sg/SrRatio between green peak skewness (Sg) and red trough skewness (Sr)[24]
kg/krRatio between green peak kurtosis (kg) and red trough kurtosis (kr)[24]
(Sg – Sr)/(Sg + Sr)Normalized value of green peak skewness (Sg) and red trough skewness (Sr)[24]
(kg – kr)/(kg + kr)Normalized value of green peak kurtosis (kg) and red trough kurtosis (kr)[24]
depth670Vegetation absorption depth at 670 nm[25]
Area670Vegetation absorption characteristic area at 560−760 nm, or the area between the envelope and the spectral reflectance in the spectral range of 560−760 nm.[25]
ND670Normalized vegetation absorption depth at 670 nm, or the ratio between absorption depth and absorption characteristic area[25]
Red edge amplitude, DrMaximum first differential value of red edge in 680−760 nm region[26]
Blue edge amplitude, DbMaximum first differential value of blue edge in 490−530 nm region[26]
Yellow edge amplitude, DyMaximum first differential value of yellow edge in 550−582 nm region[26]
Red edge area, SDrSum of first differential band values in the red edge waveband[26]
Blue edge area, SDbSum of first differential band values in the blue edge waveband[26]
Yellow edge area, SDySum of first differential band values in the yellow edge waveband[26]
SDr/SDbRatio between the sum of first differential values in the red edge and that in the blue edge[26]
SDr/SDyRatio between the sum of first differential values in the red edge and that in the yellow edge[26]
SDr – SDbDifference between the sum of first differential values in the red edge and that in the blue edge[26]
(SDr – SDb)/(SDr + SDb)Normalized value of the sum of first differential values in the red edge and that in the blue edge[26]
(SDr – SDy)/(SDr + SDy)Normalized value of the sum of first differential values in the red edge and that in the yellow edge[26]
Spectral vegetation indexNPCI(R430 − R680)/(R430 + R680)[5]
PRIb(R570 − R539)/(R570 + R539)[5]
Soil adjustment vegetation index, SAVI1.5 × (R870 − R680)/(R870 + R680 + 0.5)[5]
RVI (950, 660)R950/R660[6]
RVI (810, 660)R810/R660[6]
NRIR800/R550[9]
RVI (810, 560)R810/R560[9]
DCNI(R720 − R700)/(R700 − R670)/(R720 − R670 + 0.03)[9]
MSR sum(RNIR/RRED – 1)/(RNIR/RRED + 1)^0.5[27]
RNIR/RRED: ratio between sum of reflectance values in the near-infrared band (700−1075 nm) and that in the red light band (620−750 nm)
MSR mean(RNIR/RRED – 1)/(RNIR/RRED + 1)^0.5[27]
RNIR/RRED: ratio between mean of reflectance values in the near-infrared band (700−1075nm) and that in the red light band (620−750 nm)
ND (FD730
, FD525)
(R′730 − R′525)/(R′730 + R′525)[28]
ND (573, 440)(R573 − R440)/(R573 + R440)[28]
R810 – R680R810 − R680[28]
RVI (780, 740)R780/R740[29]
RVI (760, 510)R760/R510[30]
RVI (760, 460)R760/R460[30]
ND (760, 510)(R760 − R510)/(R760 + R510)[30]
ND (740, 460)(R740 − R460)/(R740 + R460)[30]
RSI (FD691
, FD711)
RSI(FD691, FD711) = R′691/R′711[31]
CCCI((R780 − R720)/(R780 + R720))
/((R780 − R670)/(R780 + R670))
[32]
NDRE(R780 − R720)/(R780 + R720)[32]
mNDVI(R816 − R732 × R537)/(R816 + R732 + R537)[33]
BNIR434/(R496 + R401)[33]
mNDVI(R924 − R703 + 2 × R423)/(R924 + R703 – 2 × R423)[33]
R′729R′729[34]
RNIR – RRED
MAX
Difference between maximum reflectance value in the near-infrared band (700−1075 nm) and that in the red light band (620−750 nm)[35]
RNIR – RRED MINDifference between minimum reflectance value in the near-infrared band (700−1075 nm) and that in the red light band (620−750 nm)[35]
RNIR – RRED sumDifference between sum of reflectance values in the near-infrared band (700−1075 nm) and that in the red light band (620−750 nm)[35]
RNIR – RRED meanDifference between mean of reflectance values in the near-infrared band (700−1075 nm) and that in the red light band (620−750 nm)[35]
Table 4. Correlation coefficients between summer corn canopy nitrogen concentration and spectral index (two years).
Table 4. Correlation coefficients between summer corn canopy nitrogen concentration and spectral index (two years).
Spectral IndexWhole Growth PeriodJointing PeriodTasseling PeriodFilling PeriodMaturity Period
1Green peak amplitude, Rg−0.344−0.5090.3450.025−0.167
2Red trough amplitude, Rr−0.542−0.4210.533−0.407−0.167
3(Rg – Rr)/(Rg + Rr)0.7430.004−0.6800.4600.054
4Rg/Rr0.7160.026−0.6680.4370.043
5Red trough skewness, Sr0.0870.2780.0750.3550.333
6Red trough kurtosis, kr−0.2430.2420.023−0.0660.297
7Green peak skewness, Sg−0.407−0.285−0.236−0.6690.535
8Green peak kurtosis, kg0.5340.3010.2570.549−0.574
9Sg/Sr−0.0780.206−0.134−0.1310.389
10kg/kr0.398−0.0820.2130.215−0.443
11(Sg – Sr)/(Sg + Sr)0.283−0.251−0.118−0.1070.016
12(kg – kr)/(kg + kr)0.355−0.0870.2150.184−0.468
13depth6700.7010.325−0.1220.5290.286
14Area670−0.349−0.5060.4140.031−0.145
15ND6700.6030.378−0.2640.5440.268
16Red edge amplitude, Dr0.498−0.3000.5570.5420.035
17Blue edge amplitude, Db0.167−0.4340.0650.086−0.229
18Yellow edge amplitude, Dy−0.5710.5650.231−0.3570.140
19Red edge area, SDr0.706−0.2900.4710.4790.231
20Blue edge area, SDb0.044−0.514−0.145−0.074−0.236
21Yellow edge area, SDy−0.6120.481−0.237−0.348−0.244
22SDr/SDb0.6050.3700.6210.6380.516
23SDr/SDy0.108−0.380−0.0450.5260.016
24SDr – SDb0.741−0.1810.5270.5200.353
25(SDr – SDb)/(SDr + SDb)0.6080.4190.6020.6780.538
26(SDr – SDy)/(SDr + SDy)0.612−0.429−0.1060.3060.275
27NPCI0.773−0.1490.7400.7340.313
28PRIb−0.782−0.321−0.399−0.563−0.243
29Soil adjustment vegetation index, SAVI0.762−0.0980.4100.5230.327
30RVI (950,660)0.6940.314−0.0280.4960.293
31RVI (810,660)0.6930.313−0.1350.5190.292
32NRI = R800/R5500.6120.3680.1880.4960.423
33RVI (810, 560)0.6110.3710.2590.5140.412
34DCNI0.4530.4200.2930.3300.425
35MSR sum0.7540.3590.2250.6150.425
36MSR mean0.7540.3590.2260.6150.424
37ND (FD730,FD525)0.6800.4770.6240.6820.543
38ND (573, 440)0.195−0.052−0.810−0.892−0.453
39R810 – R6800.613−0.2550.4730.4760.205
40RVI (780, 740)0.6870.3720.6370.7180.522
41RVI (760, 510)0.6110.328−0.2830.3460.248
42RVI (760, 460)0.6040.318−0.4740.1750.203
43ND (760, 510)0.7020.315−0.3390.3720.286
44ND (740, 460)0.6100.266−0.6030.0130.170
45RSI (FD691, FD711)−0.612−0.586−0.409−0.539−0.478
46CCCI0.6150.4120.6940.7030.547
47NDRE0.7710.3900.5240.7350.569
48mNDVI = (R816 – R732 – R537)
/(R816 + R732 + R537)
0.7040.3840.4440.5900.468
49BNI0.4020.018−0.1130.5690.145
50mNDVI = (R924 – R703 + 2 × R423)
(R924 + R703 – 2 × R423)
0.7380.4510.7990.8640.538
51R′7290.767−0.0310.5930.6070.458
52RNIR – RRED MAX−0.4020.2760.6090.0390.080
53RNIR – RRED MIN−0.297−0.512−0.241−0.176−0.279
54RNIR – RRED sum0.352−0.3420.4980.4200.029
55RNIR – RRED mean0.606−0.1810.5110.4850.226
Table 5. The top 20 spectral indexes in each growth period.
Table 5. The top 20 spectral indexes in each growth period.
RankingWhole Growth PeriodJointing
Period
Tasseling PeriodFilling
Period
Maturity
Period
1PRIbRSI(FD691,FD711)ND(573,440)ND(573,440)kg
2NPCIDymNDVI-1mNDVI-1NDRE
3NDRESDbNPCINDRECCCI
4R′729RNIR-RRED MINCCCINPCIND (FD730, FD525)
5SAVIRg(Rg − Rr)/(Rg + Rr)RVI(780,740)(SDr − SDb)
/(SDr + SDb)
6MSR meanArea670Rg/RrCCCImNDVI-1
7MSR sumSDyRVI(780,740)ND (FD730,
FD525)
Sg
8(Rg − Rr)
/(Rg + Rr)
ND (FD730,FD525)ND (FD730
,FD525)
(SDr − SDb)
/(SDr + SDb)
RVI (780, 740)
9SDr − SDbmNDVI-1SDr/SDbSgSDr/SDb
10mNDVI-1DbRNIR-RRED MAXSDr/SDbRSI (FD691, FD711)
11Rg/Rr(SDr − SDy)/(SDr + SDy)ND (740,460)MSR meanmNDVI-2
12SDrRr(SDr − SDb)
/(SDr + SDb)
MSR sum(kg − kr)/(kg + kr)
13mNDVI-2DCNIR′729R′729R′729
14ND (760, 510)(SDr – SDb)/(SDr + SDb)DrmNDVI-2ND (573, 440)
15depth670CCCIRrBNIkg/kr
16RVI (950, 660)NDRESDr − SDbPRIbDCNI
17RVI (810, 660)mNDVI-2NDREkgMSR sum
18RVI (780, 740)SDr/SDyRNIR-RRED meanND670MSR mean
19ND (FD730, FD525)ND670RNIR-RRED sumDrNRI = R800/R550
20CCCIRVI (780, 740)RVI (760, 460)RSI (FD691, FD711)RVI (810, 560)
Note: mNDVI-1 = (R924 – R703 + 2 × R423)/(R924 + R703 – 2 × R423); mNDVI-2 = (R816 – R732 – R537)/(R816 + R732 + R537).
Table 6. Correlation coefficients between corn canopy nitrogen concentration and spectral indexes (two years).
Table 6. Correlation coefficients between corn canopy nitrogen concentration and spectral indexes (two years).
Spectral IndexWhole Growth PeriodJointing PeriodTasseling
Period
Filling PeriodMaturity Period
mNDVI = (R924 − R703 + 2 × R423)
/(R924 + R703 − 2 × R423)
0.771 **0.451 *0.799 **0.864 **0.569 **
NDRE = (R780 − R720)/(R780 + R720)0.738 **0.3900.524 *0.735 **0.538 **
R780/R7400.687 **0.3720.637 **0.718 **0.522 **
ND(FD730, FD525)
= (R′730 − R′525)/(R′730 + R′525)
0.680 **0.477 *0.624 **0.682 **0.543 **
CCCI = ((R780 − R720)/(R780 + R720))/
((R780 − R670)/(R780 + R670))
0.615 **0.4120.694 **0.703 **0.547 **
Note: ** p < 0.01, * p < 0.05.
Table 7. Correlation coefficients between corn canopy nitrogen concentration and spectral indices (2017).
Table 7. Correlation coefficients between corn canopy nitrogen concentration and spectral indices (2017).
Spectral IndexWhole Growth PeriodJointing PeriodTasseling
Period
Filling PeriodMaturity Period
mNDVI = (R924 − R703 + 2 × R423)
/(R924 + R703 − 2 × R423)
0.849 **0.3190.821**0.744**0.589**
NDRE = (R780 − R720)/(R780 + R720)0.856 **0.550 **0.692 **0.583 **0.584 **
R780/R7400.824 **0.579 **0.714 **0.591 **0.436 *
ND (FD730, FD525) = (R′730 − R′525)/(R′730 + R′525)0.778 **0.831 **0.799 **0.548 **0.328
CCCI = ((R780 − R720)/(R780 + R720))/
((R780 – R670)/(R780 + R670))
0.762 **0.548 **0.746 **0.761 **0.363
Note: ** p < 0.01, * p < 0.05.
Table 8. Correlation coefficients between corn canopy nitrogen concentration and spectral indices (2018).
Table 8. Correlation coefficients between corn canopy nitrogen concentration and spectral indices (2018).
Spectral IndexWhole Growth PeriodJointing PeriodTasseling
Period
Filling PeriodMaturity Period
mNDVI = (R924 − R703 + 2 × R423)
/(R924 + R703 − 2 × R423)
0.618 **0.509 *0.818 **0.855 **0.884 **
NDRE = (R780 − R720)/(R780 + R720)0.696 **0.470 *0.600 **0.673 **0.808 **
R780/R7400.543 **0.477 *0.597 **0.662 **0.904 **
ND (FD730, FD525)
= (R′730 − R′525)/(R′730 + R′525)
0.566 **0.563 **0.721 **0.636 **0.936 **
CCCI = ((R780 − R720)/(R780 + R720))/
((R780 − R670)/(R780 + R670))
0.511 *0.612 **0.755 **0.774 **0.884 **
Note: ** p < 0.01, * p < 0.05.
Table 9. Evaluation of indexes of the fitting models during the whole growth period.
Table 9. Evaluation of indexes of the fitting models during the whole growth period.
Spectral ParametersFitted ModelModel Evaluation Indexes
R2RMSE
(g.g–1)
MAE
(g.g–1)
762 nmy = 3.3749R7620.86380.3060.5140.413
726 nmy = 42.042 (R726′)0.65370.6390.3680.298
762 nm, 944 nm,
957 nm
y = 0.881 − 10.194R762 − 20.056R957
+ 11.469R944
0.7110.3280.262
NDREy = 5.6378x2 + 0.48x + 0.7910.7540.3220.258

Share and Cite

MDPI and ACS Style

Liu, L.; Peng, Z.; Zhang, B.; Wei, Z.; Han, N.; Lin, S.; Chen, H.; Cai, J. Canopy Nitrogen Concentration Monitoring Techniques of Summer Corn Based on Canopy Spectral Information. Sensors 2019, 19, 4123. https://0-doi-org.brum.beds.ac.uk/10.3390/s19194123

AMA Style

Liu L, Peng Z, Zhang B, Wei Z, Han N, Lin S, Chen H, Cai J. Canopy Nitrogen Concentration Monitoring Techniques of Summer Corn Based on Canopy Spectral Information. Sensors. 2019; 19(19):4123. https://0-doi-org.brum.beds.ac.uk/10.3390/s19194123

Chicago/Turabian Style

Liu, Lu, Zhigong Peng, Baozhong Zhang, Zheng Wei, Nana Han, Shaozhe Lin, He Chen, and Jiabing Cai. 2019. "Canopy Nitrogen Concentration Monitoring Techniques of Summer Corn Based on Canopy Spectral Information" Sensors 19, no. 19: 4123. https://0-doi-org.brum.beds.ac.uk/10.3390/s19194123

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop