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[1] Leaf pigment content and composition provide important information about plant physiological status. Reflectance measurements offer a rapid, nondestructive technique to estimate pigment content. This paper describes a recently developed three-band conceptual model capable of remotely estimating total of chlorophylls, carotenoids and anthocyanins contents in leaves from many tree and crop species. We tuned the spectral regions used in the model in accord with pigment of interest and the optical characteristics of the leaves studied, and showed that the developed technique allowed accurate estimation of total chlorophylls, carotenoids and anthocyanins, explaining more than 91%, 70% and 93% of pigment variation, respectively. This new technique shows a great potential for noninvasive tracking of the physiological status of vegetation and the impact of environmental changes.

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[2] Pigment content and composition are related to the leaf physiological status. Chlorophylls (Chl) absorb solar light energy and provide mechanisms for its utilization in photosynthetic reactions. Carotenoids (Car) contribute to light-harvesting and also play a photo-protective role, preventing damage to the photosynthetic systems [e.g., Chappelle et al., 1992; Dawson et al., 1998; Gitelson et al., 2002, 2003; Merzlyak et al., 2003]. The red pigments, anthocyanins (Anth), protect leaves from excess light [Gitelson et al., 2002; Merzlyak and Chivkunova, 2000].

[3] Traditional methods of wet chemical pigment analysis are time consuming and expensive. They require destruction of the measured leaves and thus do not permit measurement of changes in pigments over time in a single leaf. In contrast, spectral reflectance measurements provide a noninvasive, rapid technique that can be used at different spatial scales. Despite development of good theoretical models relating Chl, water content, and structure with leaf reflectance [e.g., Jacquemoud and Baret, 1990; Dawson et al., 1998], needed information about leaf structure may not be available. To the best of our knowledge, there is no model that includes anthocyanin and carotenoid contents thus preventing prediction of content for these pigments.

[5] Recently, a conceptual three-band model has been developed and successfully used to relate reflectance with Chl content in leaves [Gitelson et al., 2003]. In this study we investigated the applicability of this model to noninvasive quantitative estimation of content for various pigments (total chlorophyll, carotenoid and anthocyanin) in the leaves of different tree and crop species.

2. Methods

[6] For calibration of the Chl and Car models, anthocyanin-free juvenile, mature and senescent leaves collected from 1992 to 2005 were used; Norway maple and horse chestnut leaves were from a park at Moscow State University (Russia), beech leaves from the University of Karlsruhe campus (Germany), maize, soybean and dogwood leaves were collected at Mead Nebraska (USA). For calibration of the Anth model, Anth-containing leaves from Norway maple and dogwood were used. The leaf total Chl, Car and Anth content was determined analytically from the same leaf samples used for reflectance measurement [see Gitelson et al., 2001, 2002, 2003]. Anth content was determined after extract acidification with concentrated HCl [see Gitelson et al., 2002]. Pigment content was expressed on a leaf area basis.

[7] Adaxial reflectance (R) spectra of leaves were taken in a spectral range between 400 and 800 nm with (a) a Hitachi 150–20 spectrophotometer (maple and chestnut), (b) a Shimadzu 2101 PC spectrophotometer (beech), and (c) a clip with a 2.3-mm diameter bifurcated fiber-optic attached to both an Ocean Optics USB2000 radiometer and to an Ocean Optics LS-1 light source (dogwood, soybean, and maize). Leaf reflectance spectra were recorded against BaSO_{4} as a standard. The reflectance spectrum was calculated as a ratio of leaf radiance to standard radiance at wavelength λ.

[8] Nine data sets containing 306 leaves (beech, chestnut, dogwood, maple, maize and soybean) were used for Chl model calibration (Table 1). Six data sets containing 234 leaves (beech, chestnut, and maple) were used for Car model calibration (Table 2). Three data sets containing 100 leaves (dogwood and maple) were used for Anth model calibration.

Table 1. Slopes (m) and Intercepts (n) of the Linear Relationships Between Green (Equation (3)) and Red Edge (Equation (4)) Models Versus Total Chl Content With Corresponding Root Mean Square Error of Chl Estimation (RMSE, in mg/m^{2}) Coefficient of Determination (r^{2}), Mean Total Chlorophyll Content (Chl_{mean}) and Number of Samples (N) For Each Species Studied^{a}

Species

N

Chl_{mean}

Green

RMSE

r^{2}

Red Edge

RMSE

r^{2}

m

n

m

n

a

For each species, the linear relationship was found to be the best fit function.

b

Anthocyanin-containing leaves; Chl was retrieved using red edge model (equation (4)).

Table 2. Slopes (m) and Intercepts (n) of the Linear Relationships Between Red Edge Model (Equation (6)) Versus Total Car Content With Corresponding Root Mean Square Error of Car Estimation (Car RMSE, in mg/m^{2}), Coefficient of Determination (r^{2}), Minimal (Car_{min}), Maximal, (Car_{max}) and Mean (Car_{mean}) Car Contents, Coefficient of Variation (CV = Car RMSE/Car_{mean}), and Number of Samples (N) for Each Species Studied^{a}

N

Car_{min}

Car_{max}

Car_{mean}

r^{2}

Car RMSE

CV, %

m

n

Chl RMSE

a

Chl RMSE is RMSE of Car estimation by Chl model (equation (4)). For each species, the linear relationship was found to be the best fit function.

Beech 1996

38

28

138

90

0.83

11.9

13

2.78

0.68

15.6

Beech 2000

28

18

80

50

0.91

4.0

8

2.88

−9.28

7.6

Chestnut 1996–97

20

29

94

52

0.71

7.7

15

1.81

−2.46

11.9

Chestnut 1999

22

52

166

96

0.70

17.2

18

1.52

−29.52

23.0

Maple 1992–1999

66

29

165

84

0.70

15.7

19

1.49

−16.35

23.8

Maple 2000

30

16

124

72

0.71

11.8

16

1.55

2.73

15.3

3. Results and Discussion

3.1. Model for Pigment Retrieval

[9] The infinite reflectance of a leaf, R_{∞}, in which further increase in thickness resulted in no noticeable differences in reflectance, was found to be closely related to the reciprocal of reflectance, R^{−1} [Gitelson et al., 2003]:

where a and b_{b} are the absorption and backscattering coefficients, respectively. a is a sum of absorption coefficients for the pigment of interest (a_{p}) and other pigments (a_{0}).

[10] To isolate a_{p}, the conceptual model [Gitelson et al., 2003] uses reflectances at three spectral bands. Reflectance in the first band R_{λ1} is maximally sensitive to absorption by the pigment of interest a_{p}. But reflectance is also affected by the absorption of other pigments a_{0} and by the variability in backscattering among samples b_{b}. To remove the effect of absorption by other pigments one needs to find a spectral band λ_{2} where absorption by the pigment of interest is much lower than at λ_{1}, a_{p}(λ_{2}) ≪ a_{p}(λ_{1}), and absorption by other pigments and the effect of backscattering are quite close to that at λ_{1} (i.e., a_{0}(λ_{2}) ∼ a_{0}(λ_{1}) and b_{b}(λ_{2}) ∼ b_{b}(λ_{1})). If R_{λ2}^{−1} is subtracted from R_{λ1}^{−1}, that gives (R_{λ1}^{−1}–R_{λ2}^{−1}) ∝ a_{p}(λ_{1})/b_{b.} To remove b_{b}, a third spectral band λ_{3} should be used where backscattering controls reflectance (i.e., R_{λ3} ∝ b_{b}). Multiplying the difference (R_{λ1}^{−1}–R_{λ2}^{−1}) by R_{λ3}, we have the model that may isolate a_{p}:

To find the optimal spectral bands λ_{1}, λ_{2}, and λ_{3} in the model, we used a stepwise technique based on linear regression of the model vs. content of the pigment of interest.

[11] Pigment content in leaves varied widely. In anthocyanin-free leaves (Anth <3 mg/m^{2}), Chl ranged between 1 and 860 mg/m^{2}, and Car between 14 and 166 mg/m^{2}. In Anth-containing leaves, Anth was between 5 and 102 mg/m^{2}, Chl ranged between 83 and 440 mg/m^{2} and Car between 30 and 190 mg/m^{2}.

3.2. Model Tuning for Chlorophyll Content Retrieval

[12] As the first step in model tuning we found the optimal position of λ_{2} using an initial λ_{1}^{0} = 670 nm (red Chl absorption maximum) and λ_{3}^{0} = 760 nm (a_{Chl}(λ_{3}) ∼ 0 and b_{b} controls reflectance). RMSE of Chl estimation by the model (R_{675}^{−1}–R_{λ2}^{−1}) × R_{800} had minimal values at λ_{2} > 760 nm for all species (Figure 1 for beech); we selected λ_{2}^{1} = 790 nm. In the second step we found the optimal position of λ_{3} in the model (R_{670}^{−1}–R_{790}^{−1}) × R_{λ3}. Minimal RMSE was in the NIR range where R_{λ3} relates closely to b_{b}. In the third step we found the optimal position of λ_{1} in the model (R_{λ1}^{−1}–R_{790}^{−1}) × R_{790}. RMSE had two distinct minima: in the green (around 550 nm) and in the red edge (690–725 nm) ranges (Figure 1). Therefore, two models can be used for Chl estimation in anthocyanin-free leaves if NIR is set beyond 760 nm:

For each species, the linear relationship between the Chl content and the models (equations (3) and (4)) was found to be the best fit function (Table 1).

[13] In Anth-containing leaves, the first and second steps of tuning gave the same results as for Anth-free leaves: λ_{2}^{1} = λ_{3}^{1} =790 nm (not shown). However, in the third step (Figure 2) minimal RMSE was in the red edge range only (690 to 725 nm). In the green range RMSE was maximal due to Anth absorption [Gitelson et al., 2001]. Thus, for Chl retrieval from Anth-containing leaves the equation (4) model should be used (Table 1, bottom lines: maple and dogwood).

3.3. Model Tuning for Carotenoids Content Retrieval

[14] Carotenoids content in crops and dogwood was related very closely (r^{2} > 0.97) with total Chl content, therefore Car content cannot be treated as an independent variable. However, in tree species (beech, chestnut and maple), it was possible to estimate Car content separately from Chl content despite the quite close correlation between Chl and Car (r^{2} was for beech: 0.78 in 1996 and 0.86 in 2000, for chestnut: 0.69 in 96–97 and 0.72 in 2000, for maple: 0.65 in 92–99 and 0.75 in 2000).

[15] The same procedure described above was used for model tuning. In the first step we found the optimal position of λ_{2} using an initial λ_{1}^{0} = 500 nm (Car absorption band) [Zur et al., 2000; Gitelson et al., 2002] and λ_{3}^{0} = 760 nm (a_{car}(λ_{3}) ∼ 0 and b_{b} controls reflectance). For all species, the RMSE using the (R_{500}^{−1}–R_{λ2}^{−1}) × R_{760} model showed minimal values at λ_{2}^{1} = 560–570 nm and around 700 nm (Figure 3 for beech). In these spectral bands a_{Car}(λ_{2}) ≪ a_{Chl}(λ_{1}) [Gitelson and Merzlyak, 1994a, 1994b] and a_{chl}(λ_{2}) ∼ a_{chl}(λ_{1}) [Chappelle et al., 1992; Gitelson and Merzlyak, 1994a, 1994b] and reciprocal reflectance is governed mainly by Chl content [Gitelson et al., 2003]. Thus, subtraction of either R_{560–570}^{−1} or R_{690–710}^{−1} from R^{−1}(λ_{1}) significantly decreased the RMSE of the Car estimation. For λ_{2}^{1}, 560–570 nm or 690–710 nm can be used in the second step of model tuning. The optimal position of λ_{3} in the (R_{500}^{−1}–R_{560}^{−1}) × R_{λ3} and (R_{500}^{−1}–R_{690–710}^{−1}) × R_{λ3} models was found in the NIR range beyond 760 nm where a_{car}(λ_{2}) ∼ a_{Chl}(λ_{1}) ∼ 0 and b_{b} controls reflectance (not shown). For the third step we selected λ_{3}^{1} = 790 nm and found the optimal position of λ_{1} in the (R_{λ1}^{−1}–R_{560–570}^{−1}) × R_{790} and (R_{λ1}^{−1}–R_{690–710}^{−1}) × R_{790} models at 510–520 nm (Figure 3). Thus, two models can be used for Car estimation in anthocyanin-free leaves with NIR set beyond 760 nm:

[16] For each species, the linear relationship between the Car content and the models (equations (5) and (6)) was found to be the best fit function (Table 2).

[17] Importantly, coefficients of the relationships relating models to Car remained almost the same for the independent data sets of each species (Table 2). Four data sets (maple and chestnut), taken in Russia under the same climatic conditions, had very close model coefficients. This suggests that the models equation (5) and (6) do not require parameterization when one works with the same species with the same origin, but might require parameterization for different species.

[18] As we mentioned above, Chl and Car were interrelated in the leaves studied. Thus it was important to compare the performance of the best Chl (equations (3) and (4)) and Car (equation (5) and (6)) models for Car retrieval. Car models were consistently better than Chl models in predicting Car (compare Car and Chl RMSE in Table 2). This shows that the subtraction of R^{−1}(λ_{2}), which is responsible for Chl absorption, allowed the model to be Car specific even in the case where Car and Chl were quite closely related.

3.4. Model Tuning for Anthocyanin Content Retrieval

[19] In the first step we found the optimal position of λ_{2} using an initial λ_{1}^{0} = 530 nm – close to maximum of leaf Anth absorption in acidic alcohols [Strack and Wray, 1989] and λ_{3}^{0} = 760 nm. RMSE with the (R_{530}^{−1}–R_{λ2}^{−1}) × R_{760} model had minimal values for both dogwood and maple at λ_{2}^{1} = 690–700 nm (Figure 4 for dogwood). In this spectral band reciprocal reflectance is governed mainly by Chl content [Gitelson et al., 2003]. The subtraction of R_{690–700}^{−1} from R^{−1}(λ_{1}), caused R^{−1}(λ_{1})–R^{−1}(λ_{2}) to be closely related to Anth content, however, the difference is also affected by scattering b_{b} that might vary among samples. The optimal position of λ_{3} in the (R_{530}^{−1}–R_{690–700}^{−1}) × R_{λ3} model was found in the NIR range beyond 760 nm where a_{Anth}(λ_{2}) ∼ a_{Chl}(λ_{1}) ∼ 0 and b_{b} controls reflectance (not shown). In the third step we found the optimal position of λ_{1} in the (R_{λ1}^{−1}–R_{690–710}^{−1}) × R_{790} model in a wide range around 550 nm. The model for Anth estimation, with NIR range beyond 760 nm, had the form:

[20] For both species studied, the linear relationship between the Anth content and the model (equation (7)) was found to be the best fit function. The equation (7) model yielded accurate assessment of Anth content, accounting for more than 93% of Anth variation. The coefficients of equation (7) were slightly different for dogwood and maple, thus, the model may require parameterization when applied to various species.

4. Conclusions

[21] For the first time one model, using reflectance in three spectral bands has been applied for non-destructive assessment of total chlorophyll, carotenoid and anthocyanin contents in plant leaves. Table 3 summarizes the spectral bands we recommend for each pigment content retrieval. In Anth-free leaves, both the green and the red edge bands can be used as λ_{1} for Chl estimation and as λ_{2} for Car estimation. Only four spectral bands are required for three pigments retrieval: 510–520 nm (carotenoids), 540–560 nm (anthocyanins), 690–710 nm (total chlorophyll) and 760–800 nm. The same conceptual model has been used for non-destructive pigment retrieval from reflectance spectra of fruit [Merzlyak et al., 2003, 2005], chlorophyll content in crops [Gitelson et al., 2005] as well as chlorophyll-a estimation in turbid productive waters [Dall'Olmo et al., 2003; Dall'Olmo and Gitelson, 2005] and in hypereutrophic waters [Zimba and Gitelson, 2006]. This study brings additional evidence that the conceptual model may present a unified approach to remote quantification of absorbing constituents in optically deep media.

Table 3. Spectral Bands for Retrieving Pigment Content From Leaf Reflectance Spectra^{a}

Pigment

λ_{1}

λ_{2}

λ_{3}

a

For chlorophyll content retrieval in Anth-free leaves (Anth < 3 mg/m^{2}), both the green and the red edge bands can be used as λ_{1}; in Anth-containing leaves (Anth-cont), only the red edge bands can be used as λ_{1}. For carotenoids estimation both the green and the red edge bands can be used as λ_{2}.

Chlorophylls, Anth-free

540–560

760–800

760–800

Chlorophylls, Anth-free

690–720

760–800

760–800

Chlorophylls, Anth-cont

690–720

760–800

Carotenoids

510–520

540–560

760–800

Carotenoids

510–520

690–710

760–800

Anthocyanins

540–560

690–710

760–800

Acknowledgments

[22] We thank Claus Buschmann, Veronica Ciganda, Olga Chivkunova, Mark Steel, Andres Vina and Yoav Zur for data collecting as well as Giorgio Dall'Olmo and Donald Rundquist for fruitful discussions. We acknowledge the support and the use of facilities and equipment provided by the Center for Advanced Land Management Information Technologies (CALMIT), University of Nebraska-Lincoln. A contribution of the University of Nebraska Agricultural Research Division, Lincoln, NE, Journal Series 15193. This research was also supported in part by funds provided through the Hatch Act and Russian Fund for Basic Research.