| Literature DB >> 31850029 |
Salah E El-Hendawy1,2, Majed Alotaibi1, Nasser Al-Suhaibani1, Khalid Al-Gaadi3, Wael Hassan4,5, Yaser Hassan Dewir1,6, Mohammed Abd El-Gawad Emam2, Salah Elsayed7, Urs Schmidhalter8.
Abstract
The incorporation of nondestructive and cost-effective tools in genetic drought studies in combination with reliable indirect screening criteria that exhibit high heritability and genetic correlations will be critical for addressing the water deficit challenges of the agricultural sector under arid conditions and ensuring the success of genotype development. In this study, the proximal spectral reflectance data were exploited to assess three destructive agronomic parameters [dry weight (DW) and water content (WC) of the aboveground biomass and grain yield (GY)] in 30 recombinant F7 and F8 inbred lines (RILs) growing under full (FL) and limited (LM) irrigation regimes. The utility of different groups of spectral reflectance indices (SRIs) as an indirect assessment tool was tested based on heritability and genetic correlations. The performance of the SRIs and different models of partial least squares regression (PLSR) and stepwise multiple linear regression (SMLR) in estimating the destructive parameters was considered. Generally, all groups of SRIs, as well as different models of PLSR and SMLR, generated better estimations for destructive parameters under LM and combined FL+LM than under FL. Even though most of the SRIs exhibited a low association with destructive parameters under FL, they exhibited moderate to high genetic correlations and also had high heritability. The SRIs based on near-infrared (NIR)/visible (VIS) and NIR/NIR, especially those developed in this study, spectral band intervals extracted within VIS, red edge, and NIR spectral range, or individual effective wavelengths relevant to green, red, red edge, and middle NIR spectral region, were found to be more effective in estimating the destructive parameters under all conditions. Five models of SMLR and PLSR for each condition explained most of the variation in the three destructive parameters among genotypes. These models explained 42% to 46%, 19% to 30%, and 39% to 46% of the variation in DW, WC, and GY among genotypes under FL, 69% to 72%, 59% to 61%, and 77% to 81% under LM, and 71% to 75%, 61% to 71%, and 74% to 78% under FL+LM, respectively. Overall, these results confirmed that application of hyperspectral reflectance sensing in breeding programs is not only important for evaluating a sufficient number of genotypes in an expeditious and cost-effective manner but also could be exploited to develop indirect breeding traits that aid in accelerating the development of genotypes for application under adverse environmental conditions.Entities:
Keywords: partial least squares regression; phenomics; phenotyping; proximal sensing techniques; recombinant inbred lines; stepwise multiple linear regression; wavelength band selection
Year: 2019 PMID: 31850029 PMCID: PMC6892836 DOI: 10.3389/fpls.2019.01537
Source DB: PubMed Journal: Front Plant Sci ISSN: 1664-462X Impact factor: 5.753
Figure 2Coefficient of determinations (R2) for the linear relationships of different spectral reflectance indices with shoot dry weight per square meter (DW), water content of aboveground biomass (WC), and grain yield per hectare (GY) under full irrigation (FL), limited irrigation (LM) (n = 192), and the combined two treatments (FL+LM) (n = 384). R2 values ≥ 0.10 are significant at alpha = 0.05.
Figure 1Hierarchical clusters analysis of the 32 genotypes based on measured parameters using Euclidian distance matrix and unweighted pair-group method arithmetic average (UPGMA) under full irrigation (FL), limited irrigation (LM), and the combined two treatments (combined FL+LM).
Mean values ± standard deviations of shoot dry weight per square meter (DW), water content of aboveground biomass (WC), and grain yield per hectare (GY) of the three clusters group under full irrigation (FL), limited irrigation (LM) and the combined two treatments (FL+LM).
| Treatment | Cluster | Number of RILS | DW (kg m-2) | WC (%) | GY (ton ha-1) |
|---|---|---|---|---|---|
| 2.71 ± 0.11 | 79.0 ± 1.96 | 8.39 ± 0.65 | |||
| 2.10 ± 0.09 | 74.4 ± 2.22 | 6.46 ± 0.34 | |||
| 1.59 ± 0.11 | 70.7 ± 2.84 | 5.30 ± 0.42 | |||
| 1.58 ± 0.07 | 68.9 ± 2.43 | 4.62 ± 0.12 | |||
| 1.31 ± 0.10 | 64.2 ± 1.64 | 3.52 ± 0.41 | |||
| 0.95 ± 0.11 | 58.8 ± 1.97 | 2.50 ± 0.51 | |||
| 2.10 ± 0.13 | 73.5 ± 1.76 | 6.23 ± 0.42 | |||
| 1.69 ± 0.14 | 69.2 ± 1.62 | 5.06 ± 0.43 | |||
| 1.39 ± 0.10 | 65.9 ± 1.82 | 4.03 ± 0.37 |
Figure 3Genetic correlations between different spectral reflectance indices and measured parameters (shoot dry weight per square meter (DW), water content of aboveground biomass (WC), and grain yield per hectare (GY)) under full irrigation (FL), limited irrigation (LM), and the combined two treatments (FL+LM). R2 values ≥ 0.50 are significant at alpha = 0.05.
Figure 4Broad-sense heritability (%) for different spectral reflectance indices and three measured parameters (shoot dry weight per square meter (DW), water content of aboveground biomass (WC), and grain yield per hectare (GY)) under full irrigation (FL), limited irrigation (LM), and the combined two treatments (FL+LM).
Extraction of the important sensitive spectral band intervals based on the variable importance in projection (VIP) and loading weights of partial least square regression (PLSR) analysis over full wavelengths as well as the most influential wavelengths and their models using the stepwise multiple linear regression (SMLR) for the three measured parameters [shoot dry weight per square meter (DW), water content of aboveground biomass (WC), and grain yield per hectare (GY)] under full irrigation (FL), limited irrigation (LM), and the combined two treatments (FL+LM).
| Treatments | Par. | spectral band intervals | R2 | RMSE | influential wavelength | Equation | Model R2 | Model RMSE |
|---|---|---|---|---|---|---|---|---|
| 350–774 | 0.34* | 0.362 | 769 | DW = 2.24 + 0.82 (R769) – 8.8 (R1921) – 2.1 (R2443) | 0.19** | 0.396 | ||
| 1,891–2,030 | 0.18* | 0.456 | 1,921 | |||||
| 2,443–2,500 | 0.01 | 0.618 | 2,443 | |||||
| 359–733 | 0.06 | 5.183 | 733 | WC = 88.82 – 18.58 (R733) – 50.99 (R1899) | 0.12* | 3.83 | ||
| 1,899–1,978 | 0.01 | 10.57 | 1,899 | |||||
| 350–741 | 0.39* | 0.937 | 693 | GY = 9.38 – 14.74 (R693) – 8.69 (R1891) | 0.23** | 1.06 | ||
| 1,891–2,010 | 0.07 | 1.247 | 1,891 | |||||
| 350–733 | 0.63*** | 0.166 | 733 | DW = 1.09 – 5.56 (R733) + 4.99 (R751) | 0.69*** | 0.147 | ||
| 751–871 | 0.62*** | 0.167 | 751 | |||||
| 350–737 | 0.25* | 4.640 | 532 | WC = 63.44 – 74.6 (R532) + 41.7(R751) – 15.3 (R1066) | 0.53*** | 3.17 | ||
| 751–877 | 0.27* | 4.976 | 751 | |||||
| 1,026–1,098 | 0.001 | 6.985 | 1,066 | |||||
| 350–737 | 0.73*** | 0.468 | 737 | GY = 2.87 – 31.4 (R737) + 30.8 (R748) – 1.2 (R1061) | 0.77*** | 0.431 | ||
| 748–889 | 0.73*** | 0.467 | 748 | |||||
| 1,045–1,088 | 0.07 | 0.897 | 1,061 | |||||
| 350–737 | 0.69*** | 0.309 | 737 | DW = 1.35 –12.60 (R737) + 11.7 (R750) – 0.98 (R1896) | 0.59*** | 0.351 | ||
| 750–836 | 0.64*** | 0.329 | 750 | |||||
| 1,896–1,968 | 0.38* | 0.442 | 1,896 | |||||
| 350–734 | 0.23 | 5.189 | 557 | WC = 67.15 – 95.5 (R557) + 27.9(R812) | 0.65*** | 3.91 | ||
| 753–812 | 0.05 | 5.717 | 812 | |||||
| 350–738 | 0.74*** | 0.952 | 738 | GY = 3.63 – 46.8(R738) + 43.7 (R751) – 4.6 (R1947) | 0.65*** | 1.12 | ||
| 751–841 | 0.70*** | 1.032 | 751 | |||||
| 1,903–1,947 | 0.28* | 3.464 | 1,947 |
*, **, *** Significant at the 0.05, 0.01, and 0.001 probability levels, respectively.
Figure 5The variable importance in projection (VIP) and loading weights of PLSR analysis over full wavelengths to extract the sensitive spectral band intervals for each measured parameters [shoot dry weight per square meter (DW), water content of aboveground biomass (WC), and grain yield per hectare (GY)] under full irrigation (FL), limited irrigation (LM), and the combined two treatments (FL+LM).
Calibration and validation statistics of partial least square regression (PLSR) models based on entire full wavelengths (350–2500 nm) for estimating shoot dry weight per square meter (DW), water content of aboveground biomass (WC), and grain yield per hectare (GY) under full irrigation (FL), limited irrigation (LM) (n = 192), and the combined two treatments (FL+LM) (n = 384). Twenty-five percent of data sets were applied for validation, while the remaining data sets were included in training set.
| Treatments | Parameters | ONLVs | Calibration data set | Validation data set | ||||
|---|---|---|---|---|---|---|---|---|
| R² | RMSE. | RE (%) | R² | RMSE. | RE (%) | |||
| 6 | 0.44** | 0.327 | 15.35 | 0.45** | 0.333 | 15.63 | ||
| 3 | 0.19* | 3.639 | 4.89 | 0.20* | 3.658 | 4.78 | ||
| 6 | 0.43** | 0.908 | 13.64 | 0.44** | 0.902 | 13.55 | ||
| 5 | 0.71*** | 0.142 | 10.78 | 0.73*** | 0.137 | 10.42 | ||
| 5 | 0.61*** | 2.870 | 4.45 | 0.61*** | 2.840 | 4.40 | ||
| 6 | 0.79*** | 0.412 | 11.32 | 0.80*** | 0.401 | 11.01 | ||
| 8 | 0.71*** | 0.295 | 17.08 | 0.70*** | 0.302 | 17.48 | ||
| 6 | 0.70*** | 3.586 | 5.16 | 0.70*** | 3.621 | 5.21 | ||
| 9 | 0.78*** | 0.872 | 16.95 | 0.77*** | 0.874 | 16.98 | ||
*, **, *** Significant at the 0.05, 0.01, and 0.001 probability levels, respectively.
ONLVs, optimal number of latent variables.
RE, relative error.
SMLR Model summary for estimating the measured parameters based on different groups of SRIs.
| SRIs | Treat. | Par. | Model R2 | RMSE | Equation |
|---|---|---|---|---|---|
| SRI (480,440) | 0.14* | 0.384 | |||
| 0.13* | 3.81 | ||||
| 0.15* | 1.12 | ||||
| 0.61*** | 0.166 | ||||
| 0.51*** | 3.25 | ||||
| 0.60*** | 0.568 | ||||
| 0.54*** | 0.369 | ||||
| 0.59*** | 4.24 | ||||
| 0.56*** | 1.22 | ||||
| SRI (580,790) | 0.46** | 0.330 | |||
| 0.30** | 3.49 | ||||
| 0.46** | 0.903 | ||||
| 0.69*** | 0.150 | ||||
| 0.59*** | 3.02 | ||||
| 0.77*** | 0.441 | ||||
| 0.75*** | 0.278 | ||||
| 0.71*** | 3.60 | ||||
| 0.78*** | 0.869 | ||||
| SRI (760,710) | 0.42** | 0.338 | |||
| 0.26** | 3.55 | ||||
| 0.40** | 0.950 | ||||
| 0.72*** | 0.142 | ||||
| 0.60*** | 2.98 | ||||
| 0.80*** | 0.404 | ||||
| 0.71*** | 0.297 | ||||
| 0.70*** | 3.64 | ||||
| 0.76*** | 0.912 | ||||
| SRI (1650,622) | 0.38** | 0.346 | |||
| 0.23** | 3.59 | ||||
| 0.35** | 0.974 | ||||
| 0.62*** | 0.164 | ||||
| 0.52*** | 3.20 | ||||
| 0.69*** | 0.496 | ||||
| 0.71*** | 0.292 | ||||
| 0.66*** | 3.85 | ||||
| 0.74*** | 0.936 | ||||
| SRI (1500,1450) | 0.19** | 0.397 | |||
| 0.13* | 3.82 | ||||
| 0.13* | 1.13 | ||||
| 0.55*** | 0.178 | ||||
| 0.45** | 3.44 | ||||
| 0.60*** | 0.570 | ||||
| 0.61*** | 0.339 | ||||
| 0.64*** | 4.0 | ||||
| 0.66*** | 1.08 | ||||
| SRI (1100,351,1392) | 0.16* | 0.404 | |||
| 0.05* | 3.99 | ||||
| 0.11* | 1.14 | ||||
| 0.46** | 0.194 | ||||
| 0.35** | 3.73 | ||||
| 0.46** | 0.659 | ||||
| 0.54*** | 0.370 | ||||
| 0.52*** | 4.58 | ||||
| 0.57*** | 1.22 |
*, **, *** Significant at the 0.05, 0.01 and 0.001 probability levels, respectively.
FL, LM, and FL+LM, full irrigation, limited irrigation, and the combined two treatments.
DW, WC, and GY, shoot dry weight per square meter, water content of aboveground biomass, and grain yield per hectare.
Figure 6Relationship between estimated and observed measured parameters ((shoot dry weight per square meter (DW), water content of aboveground biomass (WC), and grain yield per hectare (GY)) under full irrigation (FL), limited irrigation (LM), and the combined two treatments (All) based on influential wavelengths or SRIs.