Fast-growing forests such as tropical secondary forests can accumulate large amounts of carbon (C), and thereby play an important role in the atmospheric CO 2 balance. Because nitrogen (N) cycling is inextricably linked with C cycling, the question becomes: Where does the N come from to match high rates of C accumulation? In unique experimental 16-y-old plantations established in abandoned pasture in lowland Costa Rica, we used a mass-balance approach to quantify N accumulation in vegetation, identify sources of N, and evaluate differences among tree species in N cycling. The replicated design contained four broadleaved evergreen tree species growing under similar environmental conditions. Nitrogen uptake was rapid, reaching 409 (±30) kg·ha −1 ·y −1 , double the rate reported from a Puerto Rican forest and greater than four times that observed at Hubbard Brook Forest (New Hampshire, USA). Nitrogen amassed in vegetation was 874 (±176) kg·ha −1 , whereas net losses of soil N (0-100 cm) varied from 217 (±146) to 3,354 (±915) kg·ha −1 (P = 0.018) over 16 y. Soil C:N, δ 13 C values, and N budgets indicated that soil was the main source of biomass N. In Vochysia guatemalensis, however, N fixation contributed >60 kg·ha −1 ·y −1 . All species apparently promoted soil N turnover, such that the soil N mean residence time was 32-54 y, an order of magnitude lower than the global mean. High rates of N uptake were associated with substantial N losses in three of the species, in which an average of 1.6 g N was lost for every gram of N accumulated in biomass.carbon sequestration | forest regrowth | nitrogen cycle | soil organic nitrogen | species effects R ates of C accumulation can be rapid in secondary forests, to the extent that forest regrowth following harvest, abandonment of agricultural lands, and deforestation serves as an important sink for atmospheric CO 2 (1). The magnitude is on the order of 2.8 Pg C·y −1 (2), and thereby mitigates climate change. Moist tropical forests are especially productive: Tropical tree plantations capture 7-10 Mg C·ha −1 ·y −1 (3, 4). Abandoned agricultural and pasture land represents roughly half the landscape in the tropics (5); given its high C sequestration potential, if even half of these degraded ecosystems were reforested, it would substantially reduce rates at which CO 2 accumulates in the atmosphere. Tropical forests accounted for 55% of the 861 Pg C of the world's forest C stocks in 2007, a decrease from 58% in 1990 (6). From 1990 to 2007, deforestation of 284 Mha of intact tropical forests resulted in a loss of 58 Pg C while tropical forest regrowth on 110 Mha accrued 27 Pg C (6).Rapid C cycling is integrally linked to N cycling, because N-rich enzymes underlie photosynthesis and high N availability promotes plant productivity. The question becomes: Where does the N come from to match the observed high rates of C accumulation in biomass? Further, do tree species differ in this coupling of C and N cycling? From a conceptual framework, speciesspecific differences in the capture and ...