Literature DB >> 31832283

A noninvasive, machine learning-based method for monitoring anthocyanin accumulation in plants using digital color imaging.

Bryce C Askey1, Ru Dai1, Won Suk Lee2, Jeongim Kim1.   

Abstract

PREMISE: When plants are exposed to stress conditions, irreversible damage can occur, negatively impacting yields. It is therefore important to detect stress symptoms in plants, such as the accumulation of anthocyanin, as early as possible. METHODS AND
RESULTS: Twenty-two regression models in five color spaces were trained to develop a prediction model for plant anthocyanin levels from digital color imaging data. Of these, a quantile random forest regression model trained with standard red, green, blue (sRGB) color space data most accurately predicted the actual anthocyanin levels. This model was then used to noninvasively monitor the spatial and temporal accumulation of anthocyanin in Arabidopsis thaliana leaves.
CONCLUSIONS: The digital imaging-based nature of this protocol makes it a low-cost and noninvasive method for the detection of plant stress. Applying a similar protocol to more economically viable crops could lead to the development of large-scale, cost-effective systems for monitoring plant health.
© 2019 Askey et al. Applications in Plant Sciences is published by Wiley Periodicals, Inc. on behalf of the Botanical Society of America.

Entities:  

Keywords:  anthocyanin; digital color imaging; early stress detection; machine learning

Year:  2019        PMID: 31832283      PMCID: PMC6858293          DOI: 10.1002/aps3.11301

Source DB:  PubMed          Journal:  Appl Plant Sci        ISSN: 2168-0450            Impact factor:   1.936


The world's population is projected to reach 9.7 billion by 2050, and agricultural production must increase accordingly to match demand (FAO, 2018). However, the amount of arable land suitable for agricultural expansion is greatly limited by multiple factors, the most significant of which are climate change and land degradation. In addition, accessible freshwater resources (such as rivers and aquifers) in many countries are being depleted at a greater rate than they are regenerated (FAO, 2018). As a result, farmers in the coming decades must produce more food with less land and water inputs by increasing the efficiency of their agricultural systems. Traditional crop growing practices require the application of a treatment (e.g., additional water, fertilizer, or pesticides) to an entire field of crops, based on the assumption that all plants in the field will grow and produce yields relatively homogeneously; however, biotic factors such as pests and disease often affect a field of crops in a heterogeneous manner with respect to time and space (Mahlein et al., 2012). Abiotic stresses, including high temperature and drought, also negatively impact plant productivity, but affect fields of crops in a more homogeneous manner (Zhao et al., 2017). One of the aims of precision agriculture is to increase agricultural efficiency through the early, site‐specific application of treatments. This approach reduces the amount of inputs required while maintaining or increasing total yields (Gebbers and Adamchuk, 2010). A method of monitoring plant stress is an essential part of precision agriculture systems, as it allows for the early detection of abiotic and biotic factors that may impact plant health, giving growers the opportunity to apply specific corrective action before yields are harmed. Imaging‐based platforms are the most commonly applied system for monitoring plant health. These platforms record the intensity of light reflected, absorbed, or fluoresced by a plant at various wavelengths, which can change with the health of the plant and severity of any stress factors affecting it (Mutka and Bart, 2015). The popularity of these systems is a result of their capacity for nondestructive and easily automatable high‐throughput phenotyping. Imaging‐based platforms can also detect and provide a visualization of the heterogeneous development of stress symptoms in a plant, which is helpful for determining the type and severity of stress they are experiencing (Mutka and Bart, 2015). Hyperspectral, fluorescence, near‐infrared, and thermal imaging are several popular imaging techniques used in phenotyping platforms, and have proven to be effective in detecting the photosynthetic status, water content, presence of disease, and other parameters for a variety of plants (Li et al., 2014). However, the cameras and software required for the implementation of these systems are costly when compared to digital color imaging–based systems. The popularity of digital cameras has made them easily accessible and often included in many modern phones; however, while digital cameras work well for regular consumer use, their applications in spectroscopy are limited by their spectral resolution and range, as they can only detect visible light in three spectral bands: red, green, and blue (RGB). To account for this limitation while taking advantage of their low cost, we investigated a machine learning regression method for processing the color data recorded by a digital color camera. Once trained, a machine learning regression method can be used to predict the state or level of an output variable from the information contained in multiple predictor variables. Compared with traditional regression methods, machine learning regression methods have the potential to describe more complicated relationships between predictor and output variables through the application of flexible, data‐driven algorithms (Qin et al., 2011). Anthocyanins are a group of secondary plant metabolites believed to serve as antioxidants to quench reactive oxygen species (Kovinich et al., 2014). They are produced from the amino acid phenylalanine via the anthocyanin biosynthetic pathway. Many studies have shown that anthocyanin accumulation is positively correlated with various types of stresses (Appendix S1), including high‐intensity light, pathogens, wounding, drought, and nutrient deficiency (Shan et al., 2009). Anthocyanin accumulation can therefore be correlated with plant health, and acts as an indicator of the severity of stresses affecting the plant. Traditional chemical analysis methods for anthocyanin quantification can be time consuming, costly, and invasive (Yang et al., 2016); therefore, in this work, we investigated a noninvasive, digital color imaging–based method using a machine learning regression analysis to predict levels of anthocyanin accumulation in detached Arabidopsis thaliana (L.) Heynh. leaves.

METHODS AND RESULTS

A flowchart of the methodology followed to prepare the leaf samples, process image data, and evaluate the accuracy of the developed method is shown in Fig. 1. A detailed benchside protocol for the image background removal and processing, image sorting, regression training and testing, and false‐color heatmap generation is provided in Appendix 1.
Figure 1

Flowchart of methodology used to prepare the leaf data, train the regression analysis, and evaluate the regression accuracy. RMSE = root mean squared error; MAE = mean average error.

Flowchart of methodology used to prepare the leaf data, train the regression analysis, and evaluate the regression accuracy. RMSE = root mean squared error; MAE = mean average error.

Leaf sample preparation and imaging

To simulate the varying levels of anthocyanin accumulation caused by stress, four genotypes of Arabidopsis with different anthocyanin accumulation levels were used: Col‐0, ref2‐1 (ref2), cyp79b2 cyp79b3 (b2b3), and pap1‐D (Fig. 2). Col‐0 is A. thaliana wild type. pap1‐D is an activation tagging mutant with an enhanced expression of MYB75, which is a master regulator of the anthocyanin biosynthesis pathway (Borevitz et al., 2000). Due to the activation of MYB75 in pap1‐D, several genes encoding key enzymes in anthocyanin biosynthesis (e.g., chalcone synthase, dihydroflavonol reductase, and anthocyanidin synthase) are upregulated in this mutant, resulting in its overproduction of anthocyanin (Sawano et al., 2017). ref2 and b2b3 are mutants with defects in the enzymes involved in the biosynthesis of defense compounds called glucosinolates (Zhao et al., 2002; Hemm et al., 2003). The altered levels of glucosinolate intermediates in ref2 and b2b3 have been shown to influence the stability of phenylalanine ammonia lyase (PAL) functioning at the first step of the phenylpropanoid pathway in these mutants; as a result, ref2 contains a reduced level of phenylpropanoids, including anthocyanin, while b2b3 accumulates more phenylpropanoids than the wild type (Kim et al., 2015, 2019). Because the Col‐0, pap1‐D, ref2, and b2b3 genotypes accumulate different levels of anthocyanin under nonstressed conditions, we were able to consistently generate Arabidopsis plants with a broad range of anthocyanin contents without the use of additional stress treatments (Fig. 2A).
Figure 2

Different Arabidopsis genotypes used to simulate the range of anthocyanin accumulation caused by varying stress levels. Note that the cyp79b2 cyp79b3 genotype is abbreviated as b2b3. (A) Leaf images prior to the removal of the background pixels. (B) Leaf images after the background removal. The background pixels were manually removed from each image using the GNU Image Manipulation Program (GIMP, version 2.10.4). The magnitude of anthocyanin accumulation is indicated by the normalized anthocyanin index (NAI) under each leaf in (B), calculated using the spectrophotometer method. Scale bar = 1 cm.

Different Arabidopsis genotypes used to simulate the range of anthocyanin accumulation caused by varying stress levels. Note that the cyp79b2 cyp79b3 genotype is abbreviated as b2b3. (A) Leaf images prior to the removal of the background pixels. (B) Leaf images after the background removal. The background pixels were manually removed from each image using the GNU Image Manipulation Program (GIMP, version 2.10.4). The magnitude of anthocyanin accumulation is indicated by the normalized anthocyanin index (NAI) under each leaf in (B), calculated using the spectrophotometer method. Scale bar = 1 cm. The Arabidopsis seeds were planted on moist soil and grown for 4–6 weeks in a growth chamber at 23°C, with a light intensity of 140 μE m−2 s−1 in a 16‐h light/8‐h dark photoperiod. The plants were watered regularly to maintain soil moisture levels. Just before or soon after bolting, the mature rosette leaves were harvested by cutting the petiole using a pair of small scissors, and their fresh weights were determined using an analytical balance. A digital image of the leaves was taken with a Canon Powershot G15 digital camera (Canon USA Inc., Melville, New York, USA). To standardize the lighting conditions, all photos were taken in the same location, with the only source of lighting being ceiling fluorescent lights. The camera settings were also kept constant for all images, and were set as follows: image size = 12 megapixels (4000 × 3000 pixels), f‐stop = f/2.8, exposure time = 1/100 s, ISO speed = ISO‐800, exposure bias = –1 step, no flash. To calibrate the camera, its white balance was set using a grey card from the Vello White Balance Card Set (Vello, New York, New York, USA) prior to each imaging session. Eight leaves at a time were arranged on a sheet of nonreflective black paper with the top surface of the leaves facing upward. A tripod was used to position the camera 1–2 feet above the leaves, and the zoom of the camera was adjusted so that the leaves nearly filled the frame of the photograph. A photograph of the leaves was then taken in the standard RGB (sRGB) color space.

Anthocyanin extraction and measurement

The general methodology used for anthocyanin extraction and measurement follows that described by Shan et al. (2009). Immediately after weighing and imaging, each leaf was immersed in 1 mL of extraction buffer (18% 1‐propanol, 1% HCl, and 81% water) and boiled for 3 min. The leaves were then incubated in the buffer solution at room temperature in darkness for 24 h. A 1‐mL aliquot of the buffer solution from each leaf was transferred to a cuvette, and its absorbance at 535 nm and 650 nm was measured spectrophotometrically. The level of anthocyanin accumulation, designated as the normalized anthocyanin index, was calculated using the following equation:

Image processing and regression analysis

The background pixels of the leaf images were manually removed with GNU Image Manipulation Program (GIMP, version 2.10.4; https://www.gimp.org/). Each image contained multiple leaves; therefore, each leaf in an image was individually exported as a separate .png file. To quantify the color of the images, the mean color index values of five color spaces were calculated for each image using R (version 3.5.3; R Core Team, 2019). The five color spaces used were sRGB; hue, saturation, value (HSV); luminance, in‐phase, quadrature (YIQ); lightness, green to red, blue to yellow (L*a*b*); and luma, blue‐difference, red‐difference (YCbCr). For a given component in a color space, the mean color index values were calculated by summing together the color index value of each leaf pixel in an image and dividing by the total number of leaf pixels. For example, in the sRGB color space, the mean red (R) color index value for an image was calculated by summing together each leaf pixel's R color index value and dividing by the total number of leaf pixels in the image. By repeating this process for the green (G) and blue (B) components of the image, a set of three mean color index values were calculated for each image in the sRGB color space. To calculate the mean color index values in the four other color spaces, the images were first converted into the HSV, YIQ, L*a*b*, and YCbCr color spaces, after which their mean color index values could be calculated using the same method described for the sRGB color space. A set of 22 regression models were trained and evaluated for their ability to predict the NAI of a leaf from its mean color index values in each color space. The leaves were first randomly sorted into training/validation and test sets. Of the 147 leaves used, 80% were sorted into the training/validation set (n = 118) and the remaining 20% were used as the test set (n = 29). To train and validate the regression models, the “caret” package in R was used (Kuhn, 2008). The mean color index values were set as predictors, and the NAI was set as the response variable. The 22 regression models were then trained in each of the five color spaces previously described, producing a total of 110 trained models. The accuracy of each trained regression model was evaluated using the test set of leaf data. For each leaf in the test set, the NAI predicted by each trained regression model was compared to the actual NAI measured using the spectrophotometer method. The root mean squared error (RMSE), r 2, and mean average error (MAE) values were calculated for each regression model. The accuracy data of the 10 most accurate regressions, as determined using the RMSE value, are shown in Table 1. A complete list of all regressions and their respective accuracy parameters are provided at https://github.com/bryceaskey/anthocyanin_accumulation. Background pixel removal in GIMP is the only part of the image analysis process completed manually, as all downstream regression training and testing was automated in R. The complete analysis of the 147 leaf images required about 5–6 h of manual work in GIMP and about 8–10 h of computational time in R.
Table 1

Test set data (n = 29) for the 10 most accurate regressions of the 110 combinations evaluated, as determined by their RMSE values. The regressions are sorted from lowest to highest RMSE value.a

Color spaceRegression methodRMSE (NAI) r 2 MAE (NAI)
sRGBQuantile random forest9.4070.93516.597
YIQRandom forest10.230.92668.032
YCbCrQuantile random forest10.270.92577.783
YCbCrRandom forest10.320.92907.653
L*a*b*Bayesian neural network10.440.93237.909
sRGBStochastic gradient boosting10.620.92197.943
YIQBayesian neural network10.660.92967.867
YCbCrBayesian neural network10.680.92987.759
sRGBRandom forest10.710.92197.205
sRGBBayesian neural network10.860.92637.763

MAE = mean average error; NAI = normalized anthocyanin index; RMSE = root mean squared error.

Regressions trained using the “caret” package for R with data from the sRGB, HSV, YIQ, L*a*b*, and YCbCr color spaces.

Test set data (n = 29) for the 10 most accurate regressions of the 110 combinations evaluated, as determined by their RMSE values. The regressions are sorted from lowest to highest RMSE value.a MAE = mean average error; NAI = normalized anthocyanin index; RMSE = root mean squared error. Regressions trained using the “caret” package for R with data from the sRGB, HSV, YIQ, L*a*b*, and YCbCr color spaces. Of all the regression models tested, the quantile random forest model using the sRGB color space data most accurately predicted the actual NAI of the test set, with an RMSE of 9.407 NAI, an r 2 of 0.9351, and an MAE of 6.597 NAI. To confirm the regression accuracy, the predicted NAI values were plotted against the actual values (Fig. 3A), and a plot of the normalized residuals was also created (Fig. 3B). The normalized residuals were calculated by dividing the difference between the predicted and actual NAI values using the RMSE of the regression:
Figure 3

Evaluation of the quantile random forest model accuracy using the sRGB values of a test set of leaves (n = 29). (A) Normalized anthocyanin index (NAI) values predicted using the quantile random forest model plotted against actual NAI values calculated using the spectrophotometer method. (B) Normalized residuals from the predicted values. Normalized residuals were calculated by dividing the difference between the actual and predicted NAI values for each leaf by the root mean squared error (RMSE) of the regression model.

Evaluation of the quantile random forest model accuracy using the sRGB values of a test set of leaves (n = 29). (A) Normalized anthocyanin index (NAI) values predicted using the quantile random forest model plotted against actual NAI values calculated using the spectrophotometer method. (B) Normalized residuals from the predicted values. Normalized residuals were calculated by dividing the difference between the actual and predicted NAI values for each leaf by the root mean squared error (RMSE) of the regression model. The even spread of residuals around the x‐axis over the range of predicted NAI values indicates that the training/validation set of images was sufficiently large for training the regression.

Spatiotemporal monitoring of anthocyanin accumulation

To demonstrate its potential as an early detection system for plant stress, the trained sRGB quantile random forest model was used to make predictions of the spatiotemporal anthocyanin accumulation in detached leaves. Arabidopsis wild‐type plants (Col‐0) were grown for 4–6 weeks in the same growth chamber conditions described above. Mature leaves were harvested, and a digital color image was taken using the imaging method and camera settings described above. Because melatonin has been shown to enhance stress resistance (Zhang et al., 2014), various concentrations of melatonin were tested, with 1 mM melatonin found to be sufficient for reducing stress symptoms in Arabidopsis. The detached leaves were then individually placed into either water containing 0.05% Tween‐20, which is considered as a high‐stress environment due to mechanical wounding, or water containing 1 mM melatonin and 0.05% Tween‐20, in which melatonin can reduce stress symptoms caused by wounding (low‐stress environment). All Petri dishes were placed in a growth chamber at 23°C, with a light intensity of 140 μE m−2 s−1 in a 16‐h light/8‐h dark photoperiod. The leaves were imaged every 24 h for 96 h following the initial immersion. Prior to each imaging session, the leaves were removed from the solution and gently dried with a paper towel, as any liquid on the surface of the leaf could affect the color data recorded by the camera. The imaging was then performed as described above. After imaging, the leaves were re‐immersed in the appropriate solution, and the Petri dishes were returned to the growth chamber. The background pixels of the images were removed using GIMP, and the images of each leaf were individually exported as separate .png files. A false‐color heatmap of the anthocyanin accumulation in the leaves was created in R using the trained sRGB quantile random forest model (Fig. 4A, B). This model was then used to predict the NAI at each pixel in the leaf image. To generate the false‐color heatmap, a new image was created, and each pixel in the image was assigned a color based on the predicted NAI of the corresponding pixel in the original leaf image. Pixels with a low predicted NAI were colored white in the new image, while those with a high predicted NAI were dark pink/red (Fig. 4C). After 24 h of the immersion treatment, anthocyanin accumulation was barely visible in the RGB images as a slight discoloration in the primary vein; however, this accumulation was much more apparent in the heatmap images, allowing for the easy visualization of the distribution of anthocyanin, which might otherwise go undetected in a visual inspection. A quantitative prediction of anthocyanin accumulation in each leaf image was also performed by averaging the predicted NAI at each pixel over the entire area of the leaf (Fig. 4D).
Figure 4

sRGB quantile random forest model used to predict the spatiotemporal accumulation of anthocyanin. (A, B) RGB images (top) and the predicted anthocyanin accumulation (bottom) of detached leaves immersed in water (A), or in water containing 1 mM melatonin (B), over a 96‐h period. Scale bar = 1 cm. (C) Color scale used to create false‐color images. (D) Average predicted normalized anthocyanin index (NAI) for the leaves with (+) or without (–) melatonin over the 96‐h experimental period.

sRGB quantile random forest model used to predict the spatiotemporal accumulation of anthocyanin. (A, B) RGB images (top) and the predicted anthocyanin accumulation (bottom) of detached leaves immersed in water (A), or in water containing 1 mM melatonin (B), over a 96‐h period. Scale bar = 1 cm. (C) Color scale used to create false‐color images. (D) Average predicted normalized anthocyanin index (NAI) for the leaves with (+) or without (–) melatonin over the 96‐h experimental period.

CONCLUSIONS

This study demonstrated that the application of a machine learning regression to digital color image data enables the accurate prediction of the anthocyanin content of detached Arabidopsis leaves. Of the 22 regression models evaluated, a quantile random forest model in the sRGB color space most accurately predicted the actual accumulation of anthocyanin, with an RMSE of 9.407 NAI, an r 2 of 0.9351, and an MAE of 6.597 NAI (Table 1). To demonstrate its potential as an early detection system for plant stress, the trained model was then applied to leaf images to monitor the spatiotemporal accumulation of anthocyanin in leaves exposed to different stress conditions (Fig. 4). Anthocyanin accumulates heterogeneously in plants (Anderson et al., 2015), and the generated false‐color heatmaps allowed the visualization of its distribution. In comparison with the hyperspectral, thermal, near‐infrared, and fluorescence imaging–based methods for monitoring plant stress, digital color imaging–based methods are a more cost‐effective solution (Mutka and Bart, 2015). Digital cameras are cheap, accessible, and user friendly, and it is likely that most users are already familiar with their operation. In addition, both GIMP and R are open‐source software, meaning they are completely free to use. The application of a machine learning regression model accounts for the complex relationship between each component of a color space and the actual anthocyanin content of the leaf. This multivariate machine learning approach demonstrates an improved accuracy in the estimation of anthocyanin accumulation from a digital color image compared with single‐variable regression methods (Murakami et al., 2005; Yang et al., 2016). When compared with hyperspectral imaging–based methods for estimating anthocyanin accumulation, the digital color imaging–based method developed in this study provides a comparable accuracy in controlled conditions, without the need for more expensive hyperspectral imaging equipment (Gitelson et al., 2006; Qin et al., 2011). As our regression predictions are based on color data, the color accuracy in the digital images used is very important. In our study, images were taken in a laboratory setting under fluorescent ceiling lights, and the camera was calibrated with a grey card before each imaging session. Because the spectral signature of the leaves will change based on the primary source of light in the imaging environment, it is likely that a separate regression would need to be trained to account for the lighting in different environments, such as those lit by natural sunlight or wavelength‐controlled LEDs. Because this study was conducted with detached Arabidopsis leaves, the next step would be to test the applicability of the method at the whole‐plant level. Future work should include a comparison of the sensitivity and accuracy of this digital imaging–based method against standard phenotyping methods, as well as further testing with more economically viable crops that also accumulate anthocyanin when exposed to stress, such as cotton (Gossypium hirsutum L.) (Li et al., 2019), maize (Zea mays L.) (Pietrini et al., 2002), and tomato (Solanum lycopersicum L.) (Groher et al., 2018). The automation of the background removal process, the effect of variable lighting conditions on the regression accuracy, and larger‐scale field testing should also be a part of future investigations. Finally, the viability of using a cell phone camera as a replacement for the standalone camera used here should also be explored. Improvements in these areas would allow this method to be applied as a cost‐effective early detection system for plant stress.

AUTHOR CONTRIBUTIONS

B.C.A. and J.K. conceived and designed the experiments; B.C.A. and R.D. performed the experiments; B.C.A. and W.S.L. developed the methods used for data analysis; and B.C.A. and J.K. wrote the manuscript. All authors read and approved the final manuscript. APPENDIX S1. Drought stress induces anthocyanin accumulation. Side view (A) and overhead (B) photos of wild‐type Arabidopsis thaliana (Col‐0) under either well‐watered (control) or water‐limited (stress) conditions. Click here for additional data file.
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