Resumen
Changes in tropical-forest structure and aboveground biomass (AGB) contribute directly to atmospheric changes in CO 2 , which, in turn, bear on global climate. This paper demonstrates the capability of radar-interferometric phase-height time series at X-band (wavelength = 3 cm) to monitor changes in vertical structure and AGB, with sub-hectare and monthly spatial and temporal resolution, respectively. The phase-height observation is described, with a focus on how it is related to vegetation-density, radar-power vertical profiles, and mean canopy heights, which are, in turn, related to AGB. The study site covers 18 × 60 km in the Tapajós National Forest in the Brazilian Amazon. Phase-heights over Tapajós were measured by DLR?s TanDEM-X radar interferometer 32 times in a 3.2 year period from 2011?2014. Fieldwork was done on 78 secondary and primary forest plots. In the absence of disturbance, rates of change of phase-height for the 78 plots were estimated by fitting the phase-heights to time with a linear model. Phase-height time series for the disturbed plots were fit to the logistic function to track jumps in phase-height. The epochs of clearing for the disturbed plots were identified with ?1-month accuracy. The size of the phase-height change due to disturbance was estimated with ?2-m accuracy. The monthly time resolution will facilitate REDD+ monitoring. Phase-height rates of change were shown to correlate with LiDAR RH90 height rates taken over a subset of the TanDEM-X data?s time span (2012?2013). The average rate of change of phase-height across all 78 plots was 0.5 m-yr - 1 with a standard deviation of 0.6 m-yr - 1 . For 42 secondary forest plots, the average rate of change of phase-height was 0.8 m-yr - 1 with a standard deviation of 0.6 m-yr - 1 . For 36 primary forest plots, the average phase-height rate was 0.1 m-yr - 1 with a standard deviation of 0.5 m-yr - 1 . A method for converting phase-height rates to AGB-rates of change was developed using previously measured phase-heights and field-estimated AGB. For all 78 plots, the average AGB-rate was 1.7 Mg-ha - 1 -yr - 1 with a standard deviation of 4.0 Mg-ha - 1 -yr - 1 . The secondary-plot average AGB-rate was 2.1 Mg-ha - 1 -yr - 1 , with a standard deviation of 2.4 Mg-ha - 1 -yr - 1 . For primary plots, the AGB average rate was 1.1 Mg-ha - 1 -yr - 1 with a standard deviation of 5.2 Mg-ha - 1 -yr - 1 . Given the standard deviations and the number of plots in each category, rates in secondary forests and all forests were significantly different from zero; rates in primary forests were consistent with zero. AGB-rates were compared to change models for Tapajós and to LiDAR-based change measurements in other tropical forests. Strategies for improving AGB dynamical monitoring with X-band interferometry are discussed.