کد مقاله | کد نشریه | سال انتشار | مقاله انگلیسی | نسخه تمام متن |
---|---|---|---|---|
6459441 | 1421367 | 2017 | 10 صفحه PDF | دانلود رایگان |
- For 90% probability, 70Â years and 40Â years is needed for carbon and timber recovery.
- Timber stock recovery is driven by residual tree growth with little recruitment.
- Net increment of carbon in logged forests over 32 years was 0.64 Mg C haâ1 yrâ1.
- Bayesian approach allowed us to propagate uncertainty with biomass allometries.
- Carbon stored in managed forests will be less than old-growth forests.
The inclusion of managed tropical forests in climate change mitigation has made it important to find the sustainable sweet-spot for timber production, carbon retention, and the quick recovery of both. Here we focus on recovery of aboveground carbon and timber stocks over the first 32 years after selective logging with the CELOS Harvest System in Suriname. Our data are from twelve 1-ha permanent sample plots in which growth, survival, and recruitment of trees â¥15 cm diameter were monitored between 1978 and 2012. We evaluate plot-level changes in basal area, stem density, aboveground carbon, and timber stock in response to average timber harvests of 15, 23, and 46 m3 haâ1. We use a linear mixed-effects model in a Bayesian framework to quantify recovery time for aboveground carbon and timber stock, as well as annualized increments for both. Our statistical models accounted for the uncertainty associated with the height and biomass allometries used to estimate aboveground carbon and increased precision of annualized aboveground carbon increments by including data from forty-one plots located elsewhere on the Guiana Shield. The probabilities of aboveground carbon recovery to pre-logging levels 32 years after harvests of 15, 23 and 46 m3 haâ1 were 45%, 40%, and 24%, respectively. Net aboveground carbon increment for logged forests across all harvest intensities was 0.64 Mg C haâ1 yrâ1, more than twice the rate observed in unlogged forests (0.26 Mg C haâ1 yrâ1). The probabilities of timber stock recovery at the end of the 32-year period were highest after harvest intensities of 15 and 23 m3 haâ1 (with 80% probability) and lowest after the harvest of 46 m3 haâ1 (with 70% probability). Timber stock recovery across all harvest intensities was driven primarily by residual tree growth. Application of the legal cutting limit of 25 m3 haâ1 will require more than 70 and 40 years to recover aboveground carbon and timber stocks, respectively, with 90% probability. Based on the low recruitment rates of the twelve species harvested, the 25 year cutting cycle currently implemented in Suriname is too short for long-term timber stock sustainability. We highlight the value of propagating uncertainty from individual tree measurements to statistical predictions of carbon stock recovery. Ultimately, our study reveals the trade-offs that must be made between timber and carbon services as well as the opportunity to use carbon payments to enable longer cutting rotations to capture carbon from forest regrowth.
Journal: Forest Ecology and Management - Volume 391, 1 May 2017, Pages 246-255