OPEN Complex forest dynamics indicate SUBJECT AREAS: potential for slowing carbon FOREST ECOLOGY SUSTAINABILITY accumulation in the southeastern United FORESTRY States Received John W. Coulston1, David N. Wear2 & James M. Vose2 4 July 2014 Accepted 1United States Department of Agriculture Forest Service, 4700 Old Kingston Pike, Knoxville, TN 37919, 2United States Department 16 December 2014 of Agriculture Forest Service, PO Box 8008 North Carolina State University Raleigh, NC 27695. Published 23 January 2015 Over the past century forest regrowth in Europe and North America expanded forest carbon (C) sinks and offset C emissions but future C accumulation is uncertain. Policy makers need insights into forest C dynamics as they anticipate emissions futures and goals. We used land use and forest inventory data to Correspondence and estimate how forest C dynamics have changed in the southeastern United States and attribute changes to requests for materials land use, management, and disturbance causes. From 2007-2012, forests yielded a net sink of C because of net land use change (16.48 Tg C yr21) and net biomass accumulation (175.4 Tg C yr21). Forests disturbed should be addressed to by weather, insect/disease, and fire show dampened yet positive forest C changes (11.56, 11.4, 15.48 Tg C J.W.C. (jcoulston@fs. yr21, respectively). Forest cutting caused net decreases in C (276.7 Tg C yr21) but was offset by forest growth fed.us) (1143.77 Tg C yr21). Forest growth rates depend on age or stage of development and projected C stock changes indicate a gradual slowing of carbon accumulation with anticipated forest aging (a reduction of 9.5% over the next five years). Additionally, small shifts in land use transitions consistent with economic futures resulted in a 40.6% decrease in C accumulation. orests represent the largest sink of terrestrial carbon (C) and continued storage, forest growth, and removals for long life-span products may help reduce greenhouse gases in the future1. Over the past century, ‘‘forest transitions’’2 from a period of deforestation to reforestation and regrowth in Europe and North America, for F 3–5 example, have greatly expanded forest biomass and forest C sinks . In the U.S., the net C accumulation from land use, land use change, and forestry was equivalent to 15 percent of all emissions from the energy and transportation sectors in 20136. The potential for future C accumulation in forests is uncertain due in part to the combined effects of changes in forest growth rates, land use choices7, forest management, mortality-inducing events such as insect epidemics, other disturbances such as wildfires and hurricanes, and the direct and indirect effects of climate change8–10. Over broad spatial scales C accumulation rates are driven by multiple co-occurring vectors of change. Understanding the relative influence of these vectors of change on overall forest C dynamics represents a considerable challenge because they rarely occur in isolation and may have compounding effects. Several studies have examined C accumulation rates in relation to climate, atmospheric, disturbance, and land use histories using process/simulation models. Tian and colleagues11 simulated the effects of climate, land cover change, nitrogen deposition, atmospheric CO2 concentration, and tropospheric ozone on C sequestration and found that elevated CO2 was the largest contributor to C sequestration and land cover change was the largest contributor to C losses in the southeastern U.S. Pan and colleagues12 found that nitrogen deposition was the largest contributor to C accumulation in the mid-Atlantic U.S and that forest regrowth following disturbance had a greater capacity for C accumulation than did growth in old forests. Forest disturbance results in C emissions but then enhances net C uptake over the long run as forests revert to a more productive age-class but net effects depend on several factors including forest species, forest management, and environmental conditions13,14.In Canada, Kurz and colleagues15 suggest that managed forests may become a source of atmospheric C due to wide- spread insect outbreaks. At landscape and regional scales, the age-class distribution of the forest population in a region and forest aging strongly influence potential C accumulation. Forest aging, as used in this essay, addresses the temporal progres- sion of forests (growth, normal mortality levels) as modified by disturbance (mortality and removals). Both newly SCIENTIFIC REPORTS | 5 : 8002 | DOI: 10.1038/srep08002 1 www.nature.com/scientificreports established forests and old forests have limited capacity to sequester of agricultural land, with 2 701 km2 yr21 shifting from agricultural to carbon as compared to juvenile to middle-aged forests13. As forests forest land uses and 2 385 km2 yr21 shifting from agricultural to across the landscape age, C accumulation rates eventually decline. developed land uses (Table 1). Forest C increased 23.36 Tg yr21 as For example, Nabuurs and colleagues16 found strong indicators that a result of agriculture to forest transitions (Figure 2) but was partially forest C accumulation rates are declining in Europe. Disturbances offset by a forest C decrease of 13.13 Tg yr21 associated with forest to and land use transitions influences the overall forest age structure agriculture transitions. Forest to developed conversion (1 676 km2 across the landscape by either removing forests or resetting the forest yr21) resulted in a decrease in forest C of 20.73 Tg yr21. Shifts from to a younger age. The combined effects of forest aging, disturbance, forest use to non-forest use do not mean complete depletion of the C and land use change will determine the overall rate of C accumula- stock; rather a portion of the forest C (largely soil carbon) is trans- tion in the U.S.17 Quantifying concurrent influences of disturbances, ferred to the non-forest land use. land use change, growth, and forest cutting on forest C stock change Among disturbances that occurred between measurements, only requires a consistently measured and comprehensive data source and forest cutting reduced net forest C stock (276.7 Tg C yr21). Forests is fundamental to understanding C dynamics and improving projec- with weather, insect/disease, and fire disturbances showed net tions of forest C to support policy making. increases in forest C of 11.56, 11.4, and 15.48 Tg C yr21, respect- The present study uses recently remeasured forest inventory plots ively after accounting for salvage cutting following the initial disturb- for the entire southeastern U.S. to identify the relative influences of ance (Figure 2). Forest disturbances result in some tree mortality, but forest growth, land use changes that expand or reduce forest area, they did not lead to net reductions in total forest C stocks over the and various causes of forest mortality. Because the forest inventory remeasurement period due to the growth of residual trees, regenera- starts with a sampling of all land uses across a gridded landscape and tion to fill gaps, the stability of soil organic C, and changes in residual includes remeasurement of permanent plots, it provides estimates of dead material. The largest gain in forest C came from those areas all land use transitions among forest, agricultural, developed, and without a disturbance event reflecting forest growth (including C other land uses. The effects of weather (e.g. hurricanes, ice storms, increases in above ground, below ground, and forest floor pools) that and tornados), fire, and insect/disease outbreaks are isolated along resulted in a C accumulation of 143.77 Tg C yr21 (Figure 2). This with the effects of forest harvesting/management and land use exceeds losses from forest cutting by 87%. Rather than emitted to the changes. atmosphere, a large share of C losses from forest cutting is stored in The southeastern U.S. (Figure 1) provides an especially useful durable wood products20. laboratory for exploring forest dynamics: it has more forest land than The net gain of forest C represents the combined effects of dis- 96% of the countries reported by Food and Agriculture Organization turbance mortality, forest growth (above and below ground), forest 18 of the United Nations , produces .15% of global wood products floor accumulation, and the gradual decay of dead forest material. Of from largely (89%) private forests, contains intensively managed the 754 150 km2 of retained forest land use, 32 388 km2 yr21 (4.3% forests (18%, as indicated by forest planting activity), and is subject yr21) was disturbed. The extent of forest cutting was 21 968 km2 yr 21 19 to multiple extreme weather and biotic disturbances (e.g., hurri- (2.9% yr21). Insects and diseases, fire, and weather disturbances canes and wildfires). impacted 1 694 km2 yr 21 (0.2% yr21), 4 411 km2 yr 21 (0.6% yr21), and 4 297 km2 yr 21 (0.6% yr21), respectively. Disturbance and forest Results cutting occurred on 2.4 times as much area as experienced a land use From 2007–2012, total forest C increased by 81.95 Tg yr21 in the change. region. Land use changes resulted in forest area gains and a net The age structure of the forest is fundamental to understanding increase of 6.48 Tg yr21 while forest dynamics (growth, mortality, potential future C accumulation. When considering non-harvested cutting, forest floor accumulation) accounted for a net increase of areas, the C accumulation rate (Mg C ha21 yr21) for the region peaks 75.47 Tg yr21. Forest dominates land use (55% of period 2 inventory) at age classes 10–15 years and 15–20 years and then declines with age followed by agriculture (23%) and developed (12%) uses. (ages based on first period measurements, Figure 3a). C accumula- Approximately 95% of the area remained in the same land use tion rate drops by .50% by age class 35–40 and by .75% by age class between measurements.