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Technical Comments
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| 1. |
A. K. Knapp and
M. D. Smith,
Science
291,
481
(2001)
|
| 2. | T. R. Karl, R. W. Knight, N. Plummer, Nature 377, 217 (1995) [CrossRef] [Web of Science] . |
| 3. |
D. S. Schimel,
et al.,
Science
287,
2004
(2000)
|
| 4. | C. B. Field, J. T. Randerson, C. M. Malmstrom, Remote Sens. Environ. 51, 74 (1995) [CrossRef]. |
| 5. | S. D. Prince and S. N. Goward, J. Biogeogr. 22, 815 (1995) [CrossRef]. |
| 6. | In (1), biomes were divided into forest, grassland, and desert. In our work, in addition to these three groups, the vegetation of the huge highland area of the Tibet-Qinghai Plateau was handled as a single group, termed alpine vegetation; cropland was also considered as a separate group, because it constitutes vegetation in a non-natural setting. |
| 7. | NDVI data for China were derived from the NOAA/NASA Pathfinder AVHRR land data set at 8 km spatial resolution and 10-day intervals from January 1982 to December 1999. Climatic data (monthly mean temperature and monthly precipitation) were compiled from the 1949 to 1999 temperature and precipitation data set of China at 0.1o × 0.1o resolution, produced by interpolating data of monthly mean temperature and monthly precipitation from 682 climatic stations (11). |
| 8. | C. S. Potter, et al., Global Biogeochem. Cycles 7, 811 (1993) [Web of Science]. |
| 9. | Solar radiation data used in the CASA model were derived from 1982 to 1999 Solar Radiation Dataset of China, produced from 98 solar radiation observation stations across the country. |
| 10. | H. N. Le Houerou, R. L. Bingham, W. Skerbek. J. Arid Environ. 15, 1 (1988). |
| 11. | J. Y. Fang, S. L. Piao, J. H. Ke, Z. Y. Tang, Technical Report, Center for Ecological Research and Education, Peking University, No. 01-03, 2001. |
| 12. | Supported by grant G2000046801 of the State Key Basic Research and Development Plan and grants 39425003 and 40024101 of the National Natural Science Foundation of China to J. Y. Fang. We thank L. Buse for editing an earlier draft. |
Response: We appreciate the NDVI and NPP analyses performed by Fang et al. Additional exploration of the relationships between climate variability and important ecosystem processes such as NPP is certainly needed, and we agree that the large spatial extent and sample size available from satellite and climate data sets provides a real opportunity to robustly test predictions about those relationships. This is one of the recognized strengths of satellite data sets.
However, we are concerned by a key assumption of their analysis--that NDVI data can be used to quantify NPP dynamics with equal accuracy and sensitivity across all biomes. It has been well established that NDVI can be related to chlorophyll content, leaf area, and standing crop biomass in most biomes (1, 2) and also NPP in some instances. Because standing crop biomass and NPP are positively related across broad spatial scales, it is common in the remote sensing literature for these very different ecosystem attributes to be treated as synonymous. It should be noted, however, that NDVI-based relationships typically are calibrated with standing crop biomass data, not NPP. Unfortunately, NDVI-NPP relationships are not robust under many conditions. In grazed grasslands, for example, where standing crop is low but NPP is high, NDVI can only accurately estimate standing crop (3, 4). Worldwide, it is likely that a majority of the grasslands remotely sensed are grazed.
We are unaware of any studies that have demonstrated that interannual variability in NDVI is sufficiently sensitive to detect differences in NPP equally well across the range of biomes included in the analysis of Fang et al. Indeed, the sensitivity of NDVI to interannual rainfall variation has been shown to be low in both very wet and very dry regions of Southern Africa (5). Thus, we believe that the conclusions reported by Fang et al. should be viewed with interest, but also with caution. The final relationship they present (their figure 1F), which is most relevant to our study (6), is primarily driven by a single point for the desert biome, and background soil reflectance in arid regions further complicates NDVI-NPP relationship in deserts (5). Furthermore, a similar analyses for both North America and Africa found either no relationship or only a weak relationship between climate variation and vegetation activity as determined by NDVI values (7). Although Fang et al. have used an extensive data set in their analysis, the strength of our study (6) is that it was based on direct measurements of NPP using techniques specifically developed for each biome. Clearly, the two approaches are complementary, but the inherent trade-offs between data quality and spatial extent must be considered when comparing these relationships.
Alan K. Knapp
Melinda D. Smith
Division of Biology
Kansas State University
Manhattan, KS
66506, USA
E-mail: aknapp{at}ksu.edu
| 1. | S. N. Goward, et al., Remote Sens. Environ. 47, 190 (1994) [CrossRef]. |
| 2. | L. L. Tieszen, et al., Ecol. Appl. 7, 59 (1997) . |
| 3. | M. I. Dyer, C. L. Turner, T. R. Seastedt, Ecol. Appl. 1, 443 (1991) . |
| 4. | C. L. Turner, et al., J. Geophys. Res. 97, 18855 (1992) . |
| 5. | Y. Richard and I. Poccard, Int. J. Remote Sens. 19, 2907 (1998) [CrossRef]. |
| 6. | A. K. Knapp and M. D. Smith, Science 291, 481 (2001) . |
| 7. | S. N. Goward and S. D. Prince, J. Biogeogr. 22, 549 (1995) [CrossRef]. |
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