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Abstract and Applied Analysis
Volume 2013 (2013), Article ID 508315, 7 pages
Algorithms and Applications in Grass Growth Monitoring
1Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, A11 Datun Road, Chaoyang District, Beijing 100101, China
2College of Geography and Tourism, Chongqing Normal University, No. 12 Tianchen Road, Shapingba District, Chongqing 400047, China
3State Key Laboratory of Water Environment Simulation, School of Environment, Beijing Normal University, No. 19 Xinjiekouwai Street, Beijing 100875, China
Received 25 February 2013; Accepted 29 March 2013
Academic Editor: Craig Caulfield
Copyright © 2013 Jun Liu et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.
Monitoring vegetation phonology using satellite data has been an area of growing research interest in recent decades. Validation is an essential issue in land surface phenology study at large scale. In this paper, double logistic function-fitting algorithm was used to retrieve phenophases for grassland in North China from a consistently processed Moderate Resolution Spectrodiometer (MODIS) dataset. Then, the accuracy of the satellite-based estimates was assessed using field phenology observations. Results show that the method is valid to identify vegetation phenology with good success. The phenophases derived from satellite and observed on ground are generally similar. Greenup onset dates identified by Normalized Difference Vegetation Index (NDVI) and in situ observed dates showed general agreement. There is an excellent agreement between the dates of maturity onset determined by MODIS and the field observations. The satellite-derived length of vegetation growing season is generally consistent with the surface observation.
Vegetation phenology is the study of periodic plant life cycle events, such as bud burst, leaf out, flower bloom, and leaf fall, and how these are influenced by seasonal and interannual changes in environment . Because small fluctuations of climate can make a big difference in the timing of the vegetation phenological events, plant phenology is widely accepted as a robust indicator of the response of terrestrial ecosystems to climate change [2, 3]. Variations in the timing of vegetation phenophases are key components to identify and evaluate the effects of climatic change on terrestrial ecosystems [4, 5]. Plant phonological monitoring has been an area of growing research interest in recent decades.
Plant phenophases have been monitored by field observations for thousands of years [6, 7]. Long-term records of species-level phenophases are useful in monitoring local climatic changes [8, 9]. However, field phenological observations are difficult to extrapolate to large spatial scale and working intensive.
Satellite-based remotely sensed data provides the potential to scale from species-level observations to regional shifts of phenological patterns . More than 150 vegetation indices (VIs) have been produced from satellite data to describe the information of vegetation. Each index is designed to accentuate a particular vegetation property. For instance, Normalized Difference Vegetation Index (NDVI) derived from reflectance data collected by the Moderate Resolution Spectroradiometers (MODIS) on Terra and Aqua provides an indication of the canopy greenness of vegetation communities. NDVI has been proved to be valid for retrieving land surface phenology . A generalized VI temporal profile is theoretically smooth and continuous. However, due to the influences of the noise in the satellite data including the cloud cover, atmospheric effects, bidirectional effects, and snow cover, the time-series VI data are always with remarkable fluctuations .
A variety of methods are used to reduce noise in NDVI data and to reconstruct high-quality time-series VI data, for example, the asymmetric Gaussian function fitting, Savitzky-Golay filters, Fourier harmonic analysis, and piecewise logistic functions. After an empirically based comparison of different methods, Jennifer recommended the double logistic function-fitting algorithm due to robustness, scientific basis, and general applicability and some other desirable properties . Based on the smoothed temporal VI data, Zhang et al. identified the phenological transition dates by the derivative of the curvature of the function .
However, it is often ambiguous what the satellite-retrieved phenological estimates actually track. For instance, the greatest temporal increase in the NDVI is due to snow melt rather than “start of the season” (SOS) [14, 15]. As a result, it is necessary to compare the satellite-measured land surface phenology with data observed at ground level. However, to date, measures of land surface phenology usually compare poorly with in situ observed phenology . Therefore, researchers do not comprehensively understand how the myriad definitions and methods are related to ground-based phenology. A primary hurdle is the incompatibility of spatial scales at which two types of observations are commonly obtained, in addition to different characteristic of the data. Such limitations have greatly impeded progress in the further application of time-series VI data.
Here, the double logistic function-fitting algorithm was used to retrieve phenophases for grassland in North China using a consistently processed MODIS dataset. Then, assessment of phenological dates was conducted using field observation phenology.
2. Study Area
The study was conducted on Leymus chinensis grassland in Inner Mongolia, one of the most representative grassland regions of China. Because the phenophases of Leymus chinensis are easily detectable from both field observations and remotely sensed data, it is well suited for phenological study based on remote data. Chahar Right Back Banner, the study area, is located in latitude 41°27′N and longitude 113°11′E. The area is characterized by a north temperate continental monsoon climate with average annual precipitation of 325.7 mm, average annual temperature of 4.17°C, and mean annual aridity index of 22.99. Grassland (mainly Leymus chinensis) is the dominant vegetation (Figure 1).
3. Material and Methodology
3.1.1. MODIS Data
For this study, MOD13 A2 8-day NDVI and NDVI quality assurance products from Terra’s Moderate Resolution Imaging Spectroradiometer (MODIS) were used. The dataset covered one-year time series, from January 1, 2007 to December 31, 2007 and included 46 images. The MODIS data have a spatial resolution of 1 km at nadir, which is well suited to monitor seasonal vegetation dynamics at the scale of the landscape. These data were acquired from the US Geological Survey.
The NDVI is calculated from these individual measurements as follows: where VIS and NIR stand for the spectral reflectance measurements acquired in the visible (red) and near-infrared regions, respectively.
3.1.2. Field-Observed Data
Ground-observed grassland phenophases were obtained from Chen and Li . The observations of the different phases of Leymus chinensis are carried at Chahar Right Back Banner stations of Inner Mongolia. The observation criterion of the grassland has been developed by China Meteorological Administration.
The selected VI values were fitted with algorithm presented in Zhang et al. [13, 18] for reconstructing smoothing timeseries curves. This algorithm characterizes vegetation growth cycles using four transition dates derived from time series of MODIS VI data: (1) greenup, the date of onset of photosynthetic activity; (2) maturity, the date at which plant green leaf area is at maximum; (3) senescence, the date at which photosynthetic activity and green leaf area begin to rapidly decrease; (4) dormancy, the date at which physiological activity becomes near zero.
The annual change in satellite-derived VI data for a single growth or senescence cycle can be modeled using where is time in days, is the NDVI value at time , and are fitting parameters, is the maximum NDVI value, and is the initial background NDVI value. The fitting parameters and were determined using least-square fitting.
The rate of the change in the curvature of the fitted logistic models is used to determine the four key transition dates (Figure 2).
A series of preprocessing steps were performed to smooth MODIS NDVI data products using TIMESAT software to identify the single growth and senescence cycle. The objective is to eliminate the abnormal value, that is, cloud and snow. Then, the VI data could be fit to logistic functions described by (2).
Zhang et al.  define the onset as the date when the second derivative gets from positive to negative values. The onset of four transition dates corresponds to the times at which the second derivative gets from positive to negative values. These transitions dates indicate when one phenological phase transitions from one approximately linear stage to another. The curvature for (1) at time can be computed by where , is the angle of the unit tangent vector at time along a differentiable curve, and is the unit length of the curve. The rate of change of curvature can be computed by
The detailed flowchart of grassland growth monitoring process is illustrated in Figure 3. We first made a preprocess for the MOD13 A2 dataset taking MODIS Reprojection Tool (MRT) software as a platform. In order to eliminate the effect of cloud and snow, we smooth the dataset using TIMESAT software. For the corrected dataset, we simulated the phenophases for grassland through Arc Macro Language (AML) programming in accordance with the above algorithm.
4.1. The Effect of Data Smoothing
The final smoothed curve was produced from the double logistic model. Figure 4 shows the effect of data smoothing on the time series for a grassland pixel. The reconstructed NDVI time series is smoother and the noise resulting from the atmospheric conditions is considered as outliers and removed. The new smooth and continuous time series fit to natural rules of grassland growth.
4.2. Phenophases of Grassland
The phenological pattern of grassland of Inner Mogolia during a single growth cycle is realistically identified using the method described in Section 3. Figures 5(a) to 5(e) present ecologically and geographically coherent patterns that are consistent with known phenological behavior in this area.
Greenup onset begins at the early April (124 day-of-year) in the station. Note that south areas exhibit earlier greenup. In most regions, about 62 days are required from greenup to reach the mature phase, with relatively late mature in more northern regions. Senescence occurs at the beginning of August (247 day-of-year) without strong spatial trend. Dormancy onset begins at the end of October (318 day-of-year). The length of the growing season is about 190 days.
4.3. Comparison with Field Observation
Table 1 presents the field-observed dates versus phenological transition dates derived from MODIS NDVI. In situ phenology observations are collected from Chen and Li . Greenup onset dates identified by NDVI and in situ observed dates showed general agreement. There is an excellent agreement between the dates of maturity onset determined by MODIS and the field observations. However, values corresponding to the satellite onset estimate of senescence and dormancy date lag field-observed values by about 15–35 days. The satellite-derived length of vegetation growing season is generally consistent with the surface observation.
5. Conclusion and Discussion
This paper presents a valid methodology to identify grassland phenophases using remote sensing data. The double logistic model has been demonstrated as a flexible, repeatable, and realistic way to reconstruct time series. The phenophases derived from satellite and observed on ground are generally similar. However, values corresponding to the satellite onset estimate of senescence and dormancy date lag field-observed values by about 15–35 days. This may be explained by the field observation protocol adopted in describing phonological dates from maturity to senescence.
To improve accuracy, validation is an essential issue in land surface phenology study over large areas. This requires sufficient comparison between land surface phenology and in situ values, which is challenging because the location of field observation and MODIS pixels may not match .
Conflicts of Interests
The authors have declared that no conflict of interests exists.
This study was supported by the Key Project of National Natural Science Foundation of China (NSFC, no. 41030101) and the National Natural Science Foundation of China (NSFC, no. 41101115).
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