Tree Physiology 20, 49–56 © 2000 Heron Publishing—Victoria, Canada Light spectral composition in a tropical forest: measurements and model FRANCISCO DE CASTRO1,2 1 Department of Biology, University of Puerto Rico, P. O. Box 23360, UPR. Río Piedras, Puerto Rico 00931-3360, USA 2 Present address: Department of Fisheries and Wildlife, University of Minnesota, 200 Hodson Hall, 1980 Folwell Avenue, St. Paul, MN 55108, USA Received February 18, 1999 Summary I present a simple model that simulates vertical variations in the light spectrum within a forest canopy. The model considers only the vertical, downward transmission of light. The light in each canopy level was assumed to consist of non-intercepted radiation and radiation intercepted within the level and transmitted. The spectrum of non-intercepted light in each canopy level is the same as that of incident light above the canopy (input parameter), whereas the spectrum of transmitted light depends on leaf area index (LAI) and the mean transmission spectrum of leaves. The model was tested in a forest and provided adequate predictions of measured values. Stronger deviations were produced in the near infrared (NIR) waveband in lower canopy levels. Multiple regression between LAI, as the dependent variable, and spectral characteristics (Blue, Green, Red and NIR intensities) had an r 2 of 0.926. As a complement to other methods, I suggest light spectrum analysis as a non-destructive technique for estimating LAI in forest canopies. Keywords: canopy, irradiance, radiation, leaf area index, Puerto Rico, transmission. Introduction Forests exhibit much variation in light environment, not only in light quantity, but also in light quality (spectral characteristics). Both factors affect many important processes, such as photosynthesis, growth and morphogenesis of plants, communication among animals, microhabitat selection (Endler 1993), and seed germination (Metcalfe 1996, Lee et al. 1996). Many canopy light interception models have been developed, based on a variety of objectives and assumptions (e.g., Federer 1971, Charles-Edwards and Thorpe 1976, Jarvis and Leverenz 1983, Charles-Edwards et al. 1986, Cannell et al. 1987, Wang and Baldocchi 1989, Wang and Jarvis 1990, Yang et al. 1990, Gholz et al. 1991, Myneni 1991, Oker-Blom et al. 1991, Pukkala et al. 1991, West and Welles 1992, Bégué 1993, Ryel et al. 1993). However, in most models of radiation interception, only the quantitative, not the qualitative, aspect of light is taken into account. Only a limited range of the spectrum, the photosynthetic active radiation (PAR), is usually considered, because it is the primary variable affecting photosynthesis and plant growth. Some models also include the near infrared (NIR) waveband (Wang and Jarvis 1990). In many, if not all models, a parameter of primary importance is leaf area index (LAI). The importance of LAI has led to the development of several devices to estimate it that, in general, rely on the inversion of models of light transmittance through the canopy. There are also many models in the literature dealing with the detailed spectral characteristics of reflected radiation, as recorded by satellites (e.g., Kuusk 1994, 1995a, 1995b, 1996, Lewis 1994, Baret et al. 1995, Otterman et al. 1995). These models allow estimation of some important biophysical properties of the canopy over large areas, but they are not designed to predict the radiation transmitted through the canopy, and so they cannot predict the radiation environment at different heights from the top of the canopy to the forest floor. In this work, I present measurements of the light spectra of a 21-m vertical profile within the canopy of a tropical forest. The relationship between the spectral composition of light, LAI and optical properties of leaves is used to develop a model that simulates changes in the spectral composition at several heights in the canopy. The model considers only one dimension by assuming that the flux of radiation is directly downward. This is justified by the fact that, in a dense tropical forest, the gradient of light is strongly determined by the vertical axis. Although the model assumes that the flux of radiation is from top to bottom, this does not imply that the sun has to be at an elevation of 90°. Among the many factors that affect light quality as it traverses the canopy, filtering of light through foliage elements is the most important. Thus, it is assumed that the composition of light can be derived from the structure and optical characteristics of the canopy (Endler 1993), represented by LAI, leaf angles and the optical properties of leaves. The model parameters are the vertical profile of LAI and leaf angles, mean transmission spectrum of leaves, and the spectrum of incident radiation. The model calculates the spectrum of light for each of the heights at which LAI was measured. Materials and methods The study was conducted near El Verde Field Station (18°20′ N, 65°49′ W) in the north-western section of the Luquillo Experimental Forest (Puerto Rico). The area (a 16-ha perma- 50 DE CASTRO nent plot) supports tabonuco (Dacryodes excelsa Val.) forest (subtropical wet forest in the Holdridge system; Ewel and Whitmore 1973). In addition to tabonuco, the forest in the area is dominated by the palm Prestoea montana (R. Graham) Nichols, and the trees Manilkara bidentata (A. DC.) A. Cheval. and Sloanea berteriana (Choisy) (Odum and Pigeon 1970, Brown et al. 1983). Stocking density is approximately 800 trees ha −1 and includes 88 species. Because of human disturbance, none of the forest in the 16-ha plot can be considered primary forest. However, the southern part of the plot (about 6 ha) is similar to virgin stands of tabonuco forest (Odum 1970). A more detailed description of the plot is provided by Zimmerman et al. (1994). Measurements of LAI, mean leaf angle, and the spectrum of light between 0.35 and 1.15 µm were made at 2-m vertical intervals from a 25-m tower located near a corner of the 16-ha plot. calculated as the mean of the ten measurements made at that level. The top of the tower was above the canopy, so measurements at the highest level represent conditions in the open. Profiles of spectra were taken at midday on April 24 and 26 (one each day), when the sun was almost directly overhead at this latitude and time of year. I also took samples of leaves of all four of the species within reach of the tower at all levels. The transmission spectra (between 0.35 and 1.1 µm) of three randomly chosen leaves per species were measured with the spectroradiometer and an external integrating sphere (Li-Cor LI-1800-12). The leaves were maintained in high humidity and exposed to light until they were processed, always within a day of sampling. It was assumed that there were no significant differences in optical properties of the leaves along the vertical gradient (cf. Poorter et al. 1995). This assumption was justified by the need to keep both the model manageable and the number of parameters to a minimum. Leaf area index and leaf angles I measured LAI and mean leaf angles with an LAI-2000 canopy analyzer (Li-Cor Inc., Lincoln, NE), which estimates both variables simultaneously (LAI is presented as half of all-sided leaf area). The LAI measurements were made under conditions considered ideal for the LAI-2000 (LAI-2000 manual (1990)): i.e., in late afternoon, with a cloudless sky and the sun below 27°. These conditions ensured that direct light did not hit the sensor rings, which have a minimum elevation range of 27°. In addition, a view restriction cap of 15° was used to avoid the effect of excessive brightness of the sky zone in the direction of the sun. Although the Li-Cor LAI-2000 detects branches and twigs as well as leaves (Li-Cor 1990, Welles and Norman 1991), LAI estimates are probably affected more by clumping of the foliage than by the inclusion of non-foliar elements. Spectra and PPFD Spectral measurements (mean of three scans) were taken with a Li-Cor spectroradiometer equipped with a remote cosine receptor (LI-1800-11), which was held level approximately 1 m outside the tower, and was connected to the spectroradiometer with a fiber optic probe (LI-1800-2). The sensor was placed in shade except at the two uppermost canopy levels (where there was almost no shade). Shaded positions were chosen to maximize the effect of light filtering by leaves. The locations were evenly spaced within the 2-m range of the tower. The sensor was placed at the two extremes of the platform and at the center, always oriented in the same direction. It was impossible to measure the light spectrum over a wider area, because the tower was the only means of canopy access. At each canopy level, photosynthetic photon flux density (PPFD) was measured with a Li-Cor quantum sensor, connected to a data logger. The quantum sensor was attached to the sensor of the spectroradiometer, so both were located at the same point. Ten measurements of PPFD were made in the time that the spectroradiometer took to complete the three scans (approximately 1 min). The PPFD value for each level was Description of the model The model was applied in two steps. First the total amount of non-intercepted radiation reaching each canopy level was calculated, then the amount of radiation absorbed in each level was calculated as the difference between non-intercepted radiation in two consecutive levels. Second, once the total radiation in each level was known, its spectral composition was calculated according to the assumptions explained below. In this work, the term “ total incident radiation” means the total downward solar radiation flux density (Rt) between 0.35 and 1.1 µm, which were the limits of the waveband examined. The canopy was divided into several levels of equal thickness. Each canopy level was characterized by its LAI and mean leaf angle (α). It was assumed that the flux of light is vertical. The radiation that passes through any level of the canopy without being intercepted (Ru) can be expressed by a negative exponential function: Ru = Rte−(Lk), (1) where Rt is total incident radiation (direct plus diffuse), L is LAI in level H, and k is the extinction factor, which depends on the relative angles of leaves (α) to the sun. Because radiation flux was assumed to be vertical, the sun elevation was considered to be 90°, so k was always the cosine of mean leaf angle (α). The amount of radiation intercepted (Ri) within a canopy level H, is the difference between the amount of nonintercepted radiation at that level and the next (H + ∆H): Ri (H) = Ru(H+∆H)−Ru(H). (2) Part of the intercepted radiation is reflected, another part is absorbed and the rest is transmitted downward and passed to the next canopy level. The amount of radiation transmitted in each wavelength depends on the mean transmission coefficient of the leaves for that wavelength. So, light changes both quantitatively (total amount) and qualitatively (spectrum) as it TREE PHYSIOLOGY VOLUME 20, 2000 LIGHT SPECTRAL COMPOSITION IN A TROPICAL FOREST passes through the canopy. In the application of the model, the values of non-intercepted radiation (Ru) and intercepted radiation (Ri) were computed for each level, based on the values of LAI and leaf angles. The Ru and Ri values were then divided into the different wavelengths according to the following assumptions. (1) The proportion of radiation at each wavelength in non-intercepted radiation at a given level is the same as in the incident radiation above the canopy. (2) The proportion of radiation intercepted that is transmitted in each wavelength depends on the transmission coefficient of leaves in that wavelength. (3) Radiation intercepted within the level and transmitted (in each wavelength) is added to the corresponding wavelengths in the current level. (4) Second-order reflections are considered negligible. Non-intercepted radiation We can express total incident radiation (Rt ) between two wavelengths λ1 and λ2 as: λ2 Rt = ∫ R(λ)dλ . (3) λ1 Because spectroradiometers have a limited spectral resolution (1 nm in the case of the LI-1800), the measurement of Rt is not truly continuous, as expressed in the above formula, but is discrete, made at finite wavelength intervals (∆λ). Thus, Equation 3 can be expressed as: λ2 Rt = ∆λ∑ R(λ). (4) λ1 The proportion of radiation at wavelength λ with respect to the total radiation at a given height H, denoted c(λ, H), can be expressed as: c (λ,H ) = R(λ,H) Rt 51 The model was applied iteratively to every canopy level, producing a simulated spectrum between 0.35 and 1.1 µm for each level. The simulated spectra were then compared with measured spectra to test the model. From the simulated spectra it was possible to calculate PPFD for further comparisons with measured PPFD values. Results and discussion The profile and the accumulated profile of LAI at the tower are shown in Figure 1. The profile shows an approximately bimodal distribution, with a maximum accumulated LAI of 7 at ground level. It should be noted that we do not know the true LAI, only the estimate provided by the LAI-2000. Several studies have reported that the LAI-2000 may underestimate the true LAI by as much as 35–40% (Gower and Norman 1991) or 45% (Chason et al. 1991) because of foliage clumping, which is not considered in the underlying theory of the device. However, Chason et al. (1991) found that elimination of the three outer rings of the sensor in the calculations of LAI yielded an estimate that was not significantly different from the true value (4.17 ± 0.73 versus 4.89 ± 0.95), even when a random distribution of foliage was assumed. I compared the results obtained with different numbers of rings with those obtained with all five rings (Figure 2). The relationships were always quite good, with the slopes close to one, the intercepts close to zero and high r 2 values, which decreased as rings were eliminated in the calculations. It was concluded, therefore, that all of the estimates were similar in this particular location whatever the number of rings (but see de Castro and Fetcher 1998). When fewer than five rings were used in the calculation of LAI, the field of view of the device was also reduced: the outmost ring points to an elevation of 27° above the horizon, whereas the (5) . Thus, non-intercepted radiation in wavelength λ, at level H, Ru(λ, H), can be calculated as the product of the coefficient c(λ, H) for incident radiation, and total non-intercepted radiation at level H. Transmitted radiation Part of the radiation intercepted in each level is reflected, part is absorbed and part is transmitted. The transmitted proportion depends on the leaves’ transmission coefficient at each wavelength (τ). Following the same procedure as described for non-intercepted radiation, we can express the radiation transmitted within level H, at wavelength λ, Rt(λ, H) as: Rt(λ,H ) = Ri(H)c(λ,H)τ(λ). (6) So, the final expression of the model is: R(λ,H ) = Ru(H)c(λ,0) + Ri(H)c(λ,H)τ(λ). (7) Figure 1. Vertical profile of leaf area index (LAI, half of all-side leaf area) per canopy level (bars) and accumulated LAI (line) against height of measurement. TREE PHYSIOLOGY ON-LINE at http://www.heronpublishing.com 52 DE CASTRO Figure 2. Comparison of LAI estimates made with different numbers of sensor rings of the LAI-2000 (vertical axis), with that obtained with five rings (horizontal axis). innermost ring points vertically. On the other hand, the sensor of the spectroradiometer always receives radiation from all directions. For these reasons, I used the estimate of LAI obtained with all five rings in this work. Because the transmittance spectra of the leaves of species found around the tower were similar (Figure 3), the mean of the four species was used as the transmission coefficient in the calculations. The percentage of PPFD at ground level with respect to total PPFD at the top of the canopy was 0.53 and 1.35% on the two days of sampling, respectively. This value is similar to values found in the understory of other tropical forests (cf. Chazdon and Fetcher 1984) and is consistent with the heavy shading at the study site as a result of the relatively high LAI. The measured vertical variations in the spectrum of light are shown in Figures 4a and 4c. In the visible portion of the spectrum (0.4 to 0.7 µm), the radiant flux density decreased uniformly with decreasing height, but the form of the spectrum was mostly unchanged. In contrast, the proportion of the near infrared waveband (0.7 to 1.1 µm) relative to the total radiation increased with decreasing height. As a result, the radiation at the lower levels of the canopy was enriched in NIR wavelengths. The vertical variation in the ratio of red to far-red irradiance is shown in Figure 5. The red and far-red wavelengths are defined as centered on 0.66 and 0.73 µm, respectively, with a bandwidth of 10 nm (Smith 1994). At the top of the canopy, the R:FR ratio was 1.35, decreasing to 0.36 at ground level. These values are similar to those in other tropical forests (Lee et al. 1996). I also examined the relationship between LAI measured by the LAI-2000 and the spectral composition of solar radiation. First, the irradiance in the blue (0.4–0.5 µm), green (0.5–0.6 µm), red (0.6–0.7 µm), and NIR (0.7–1.1 µm) wavebands was calculated. Then I calculated the ratio of each waveband color Figure 3. Transmission spectra of leaves of the species around the tower. Values plotted are the means of three leaves per species. TREE PHYSIOLOGY VOLUME 20, 2000 LIGHT SPECTRAL COMPOSITION IN A TROPICAL FOREST 53 Figure 4. Spectral irradiance at several heights within the canopy. The graphs on the left-hand side (a, c) are observed values, and those on the righthand side (b, d) are simulated by the model. The two upper graphs (a, b) show the values of the upper part of the canopy (from 23 to 11 m). The two lower graphs (c, d) show the lower canopy levels (from 9 to 1 m). Note that the spectrum at 23 m in b, is not simulated, but measured, because it is an input parameter for the model. at each canopy level to its equivalent in incident radiation above the canopy. These ratios were used as independent variables in a multiple linear regression with LAI as the dependent variable (Table 1). The r 2 was 0.926, indicating the potential value of the spectral composition of light as a basis for predicting LAI. It should be emphasized that the aim of this procedure is not to use the model to predict LAI; this is not possible because the model uses LAI as an input parameter. The irradiances used as independent variables in the regression were those measured with the spectroradiometer, not those predicted by the model, whereas the dependent variable (LAI) was measured with the LAI-2000. To test the model, values of total irradiance and irradiance in different wavebands (blue, green, red and NIR), were calculated from both observed and predicted spectra, and then compared by linear regressions. The shape of the spectra can also be used as a subjective test of the adequacy of the model. In a further test, the actual PPFD measured with the quantum sensor was compared with predicted values of PPFD calculated from the simulated spectra with the Li-Cor software for the LI-1800. The predicted values of total irradiance and PPFD were in Table 1. Multiple linear regression between the spectral irradiance at different wavebands and leaf area index. The wavebands considered are: blue (0.4–0.5 µm), green (0.5–0.6 µm), red (0.6–0.7 µm) and NIR (0.7–1.1 µm). The multiple r 2 = 0.926, P < 0.0001. Note that the only positive coefficient is that of the green, indicating enrichment in green wavelengths as light passes through the canopy. Effect Coefficient Standard error Standard coefficient t-Value Constant Blue Green Red NIR 9.006 −644.038 876.628 −119.462 −122.122 1.787 548.164 888.325 265.955 78.582 0.0 −71.560 96.993 −13.188 −13.014 5.038 −1.175 0.987 −0.449 1.554 Analysis of Variance Figure 5. Vertical profile of the red:far-red ratio. The values shown are the ratio between irradiances at red and far-red wavelengths, defined as centered on 0.66 µm and 0.73 µm respectively, with a bandwidth of 10 nm. Source Sum of squares df Mean square F P Regression Residual 64.057 5.153 4 7 16.014 0.736 21.754 < 0.001 TREE PHYSIOLOGY ON-LINE at http://www.heronpublishing.com 54 DE CASTRO close agreement with measured values (Figure 6). The comparison of simulated irradiance in the different wavebands with the measured values also had high r 2 values (Figure 7). The form of the predicted spectra, on the other hand, showed an overestimation in the NIR region at the upper canopy levels, whereas it showed an underestimation at the lower canopy levels (Figure 4). Conclusions The model predictions were in relatively good agreement with measured values, especially in the visible part of the spectrum. The main differences were an overestimate of the amount of near-infrared radiation at the upper canopy levels, and an underestimate at the lower canopy levels. These discrepancies could be caused by several factors. First, the predicted spectra were based on the spectrum of incident light. This was measured only once, at the beginning of the sampling period, but it can change quite rapidly because of clouds, and thus, when the lower canopy levels were measured, the incident light may have had a different spectrum. This problem could be solved by using a second spectroradiometer to measure incident light at regular intervals. The spectrum of incident light also changes with the sun’s azimuth (McFarland and Munz 1975). Because the measurement process takes some time, this spectral change could affect the accuracy of the prediction. Second, Figure 6. Comparison of observed (points) and predicted (lines) values of total irradiance (above) and photosynthetic photon flux density (PPFD, below) in the vertical profile within the canopy. The measured values of total irradiance were obtained with a Li-Cor LI-1800 spectroradiometer. The measured values of PPFD were obtained with a quantum sensor. Figure 7. Regressions between observed (abscissa, independent variable) and predicted (ordinate, dependent variable) values for irradiance at different wavebands: blue (0.4–0.5 µm), green (0.5–0.6 µm), red (0.6–0.7 µm) and near infrared (NIR, 0.7–1.1 µm). and probably more importantly, the reflection of radiation was not included in the model. Because the reflection of foliage in the infrared is high, incorporating reflection would increase the predicted values in this range of the spectrum producing a better prediction. The good agreement between measured and simulated values suggests that the assumptions of the model, in particular the assumption that all the radiation is directly downward, are not seriously in error. Direct radiation comes mostly from the sun with varying angles, and diffuse radiation come from all the sky hemisphere, but the filtering effect of the canopy makes the downward gradient the most important. The omission of reflected radiation from the model is probably the cause of some of the observed discrepancies. The model presented here could be incorporated in more complex models of radiation interception, to enhance the detail of the predictions. The wavelength interval used in this work (2 nm) is probably too small for most purposes, and could be increased to simplify the calculations. It could be useful to use irregular wavelength intervals matching the main characteristics of the absorption spectra of leaves. The variation in light through the canopy, both the total amount and its spectral composition, is mostly caused by interception by leaves. This raises the possibility of using the spectral properties of measured transmitted radiation to estimate LAI. The multiple regression between LAI (dependent variable), as estimated by the LAI-2000, and the spectral characteristics measured with the spectroradiometer (blue, green, red and NIR values) had a high r 2 value, suggesting that the method could provide a non-destructive estimation of LAI in this type of forest. However, it will first be necessary to test this technique for predicting LAI from spectral characteristics against direct measurements of LAI. It should be emphasized that the LAI data used in this paper are not measurements, but the results of the inversion of a radiation model that is incor- TREE PHYSIOLOGY VOLUME 20, 2000 LIGHT SPECTRAL COMPOSITION IN A TROPICAL FOREST porated in the manufacturer’s software for the LAI-2000. Changes in spectral composition of the light at intermediate and large scales should be less affected by the spatial distribution of foliage than other methods for estimating LAI based on the inversion of radiation transmission models (Chason et al. 1991). It should be noted that the coefficients of the regression will probably change for different vegetation types because of differences in the transmission spectrum of the species and different characteristics of incident light. It is also possible that the same method will not work equally well in other types of forests. In the study site, a tropical rain forest, the canopy is relatively homogeneous and closed, and most of the radiation reaching a given level in the canopy is filtered through the foliage, which increases the effect of leaves on the spectral composition of the light. This might not be the case in a sparser forest, where a significant amount of radiation can reach the ground unfiltered by vegetation, which could weaken the relationship between LAI and light spectral composition. In the model tests, I found relatively good agreement between observed and predicted spectra, and the trends of decreasing total irradiance and PPFD down the canopy were correctly predicted by the model. The model can be applied to any range of wavelengths, provided that the total incident radiation matches the spectrum of incident light and the spectral characteristics of leaves in all the required wavebands are known. Acknowledgments Thanks to Adisel Montaña for her help in the field and valuable criticism of earlier versions of this manuscript. This work was supported by a NASA/EPSCoR grant to the University of Puerto Rico. References Baret, F., J.G.P.W. Clevers and M.D. Steven. 1995. The robustness of canopy gap fraction estimates from red and near-infrared reflectances—A comparison of approaches. Remote Sens. Environ. 54:141–151. Bégué, A. 1993. Leaf area index, intercepted photosynthetically radiation, and spectral vegetation indices: A sensitivity analysis for regular clumped canopies. Remote Sens. Environ. 46:45–69. Brown, S., A.E. Lugo, S. Silander and L. Liegel. 1983. Research history and opportunities in the Luquillo Experimental Forest. General Technical Report No. SO-44, USDA Forest Service, Southern Experimental Station, New Orleans. Cannell, M.G.R., R. Milne, L.J. Sheppard and M.H. Unsworth. 1987. Radiation interception and productivity of willow. J. Appl. Ecol. 24:261–278. Charles-Edwards, D. A. and M.R. Thorpe. 1976. Interception of diffuse and direct beam radiation by a hedgerow apple orchard. Ann. Bot. 40:603–613. Charles-Edwards, D.A., D. Doley and G.M. Rimmington. 1986. Modelling plant growth and development. Academic Press, Australia, 235 p. Chason, J.W., D.B. Baldocchi and M.A. Huston. 1991. A comparison of direct and indirect methods for estimating forest canopy leaf area. Agric. For. Meteorol. 57:107–128. Chazdon, R. and N. Fetcher. 1984. Photosynthetic light environments in a lowland tropical forest in Costa Rica. J. Ecol. 72:553–564. 55 de Castro, F. and N. Fetcher. 1998. Three dimensional model of the interception of light by a canopy. Agric. For. Meteorol. 90:215– 233. Endler, J.A. 1993. The color of light and its implications. Ecol. Monogr. 63:1–27. Ewel, J.J. and J.L. Whitmore. 1973. The ecological life zones of Puerto Rico and the U.S. Virgin Islands. US Forest Service Research Paper ITF-18. Institute of Tropical Forestry, Río Piedras, Puerto Rico, 72 p. Federer, C.A. 1971. Solar radiation absorption by leafless hardwood forests. Agric. Meteorol. 9:3–20. Gholz, H.L., S.A. Vogel, W.P. Cropper, Jr., K. McKelvey, K.C. Ewel, R.O. Teskey and P.J. Curran. 1991. Dynamics of canopy structure and light interception in Pinus elliottii stands, north Florida. Ecol. Monogr. 61:33–51. Gower, S.T. and J.M. Norman. 1991. Rapid estimation of leaf area index in conifer and broad leaf plantations. Ecology 72:1896–1900. Jarvis P.G. and J.W. Leverenz. 1983. Productivity of temperate deciduous and evergreen forests. In Encyclopedia of Plant Physiology, Vol. 12D. Eds. O.L. Lange, P.S. Nobel, C.B. Osmond and H. Ziegler. Springer-Verlag, Berlin, pp 233–280. Kuusk, A. 1994. A multispectral canopy reflectance model. Remote Sens. Environ. 51:342–350. Kuusk, A. 1995a. A markov-chain model of canopy reflectance. Agric. For. Meteorol. 76:221–236. Kuusk, A. 1995b. A fast invertible canopy reflectance model. Remote Sens. Environ 51:342–350. Kuusk, A. 1996. A computer-efficient plant canopy reflectance model. Comput. Geosci. 22:149–163. Lee, D.W., B. Krishnapillay, M. Marzalina, M. Haris and K.Y. Son. 1996. Irradiance and spectral quality affect Asian tropical rain forest tree seedling development. Ecology 77:568–580. Lewis, M.M. 1994. Species composition related to spectral classification in an Australian spiniflex hummock grassland. Int. J. Remote Sens. 15:3223–3239. Metcalfe, D.J. 1996. Germination of small-seeded tropical rainforest plants exposed to different spectral compositions. Can. J. Bot. 74:516–520. McFarland, W.N. and F.W. Munz. 1975. The photic environment in clear tropical seas during the day. Vision Res. 15:1053–1070. Myneni, R.B. 1991. Modeling radiative transfer and photosynthesis in three-dimensional vegetation canopies. Agric. For. Meteorol. 55:323–344. Odum, H.T., and R.F. Pigeon. 1970. A tropical rain forest. NTIS, Springfield, VA. Odum, H.T. 1970. The El Verde study area and the rain forest systems of Puerto Rico. In A Tropical Rain Forest. Eds. H.T. Odum and R.F. Pigeon. NTIS, Springfield, VA. Oker-Blom, P., J. Lappi and H. Smolander. 1991. Radiation regime and photosynthesis of coniferous stands. In Photon–Vegetation Interactions. Eds. R.B. Myneni, and J. Ross. Springer Verlag, Berlin, pp 469–499. Otterman, J., T. Brakke and J. Smith. 1995. Effects of leaf-transmittance versus leaf-reflectance on bidirectional scattering from canopy soil surface: an analytical study. Remote Sens. Environ. 51:49–60. Poorter, L., S.F. Oberbauer and D.B Clark. 1995. Leaf optical properties along a vertical gradient in a tropical rain forest canopy in Costa Rica. Am. J. Bot. 82:1257–1263. Pukkala, T., P. Becker, T. Kuuluvainen and P. Oker-Blom. 1991. Predicting spatial distribution of direct radiation below forest canopies. Agric. For. Meteorol. 55:295–307. TREE PHYSIOLOGY ON-LINE at http://www.heronpublishing.com 56 DE CASTRO Ryel, R.J., W. Beyschlag and M.M. Caldwell. 1993. Light field heterogeneity among tussock grasses: Theoretical considerations of light harvesting and seedling establishment in tussocks and uniform tiller distributions. Oecologia 98:241–246. Smith, H. 1994. Sensing the light environment: the functions of the phytochrome family. In Photomorphogenesis in Plants, 2nd Edn. Eds. R.E. Kendrick and G.H.N. Kronenberg. Kluwer Academic, Dordrecht, The Netherlands, 828 p. Wang, H. and D.D. Baldocchi. 1989. A numerical model for simulating the radiation regime within a deciduous forest canopy. Agric. For. Meteorol. 46:313–337. Wang, Y.P. and P.G. Jarvis. 1990. Description and validation of an array model MAESTRO. Agric. For. Meteorol. 51:257–280. Welles, J.M. and J.M. Norman. 1991. Instrument for indirect measurement of canopy architecture. Agron. J. 83:818–825. West, P.W. and K.F. Welles. 1992. Method of application of a model to predict the light environment of individual tree crowns and its use in a eucalypt forest. Ecol. Model. 60:199–231. Zimmerman, J.K., E.M. Everham, R.B. Waide, D.J. Lodge, C.M. Taylor and V.L. Brokaw. 1994. Responses of tree species to hurricane winds in subtropical wet forest in Puerto Rico: implications for tropical tree life histories. J. Ecol. 82:911–922. TREE PHYSIOLOGY VOLUME 20, 2000
© Copyright 2026 Paperzz