6533b82dfe1ef96bd12909d4

RESEARCH PRODUCT

Carbon stock increases up to old growth forest along a secondary succession in Mediterranean island ecosystems.

Riccardo ValentiniRiccardo ValentiniTommaso La MantiaEmilio BadalamentiLuca SapienzaJ. RühlGiovanna BattipagliaGiovanna SalaGiovanna SalaLuciano GristinaAgata Novara

subject

TopographySecondary succession010504 meteorology & atmospheric sciencesSettore AGR/05 - Assestamento Forestale E SelvicolturaEcological SuccessionMediterranean forests Carbon pools Soil carbon and nitrogen Holm oak Quercus ilex Sclerophyllous woody speciesEcological successionForests01 natural sciencesTreesSoilBiomassIslandsMultidisciplinarygeography.geographical_feature_categoryEcologyQRSoil chemistryEukaryota04 agricultural and veterinary sciencesPlantsOld-growth forestWoodTerrestrial EnvironmentsSettore AGR/02 - Agronomia E Coltivazioni ErbaceeMedicineEngineering and TechnologyEnvironmental MonitoringResearch ArticleCarbon SequestrationEnvironmental EngineeringForest EcologyEcological MetricsNitrogenScienceEcosystemsMediterranean IslandsOaksForest ecologyHumansEcosystemEcosystem0105 earth and related environmental sciencesgeographyLandformsEcology and Environmental SciencesOrganismsBiology and Life SciencesGeomorphologySoil carbonCarbonAgronomy040103 agronomy & agricultureLitterEarth Sciences0401 agriculture forestry and fisheriesEnvironmental science

description

The occurrence of old-growth forests is quite limited in Mediterranean islands, which have been subject to particularly pronounced human impacts. Little is known about the carbon stocks of such peculiar ecosystems compared with different stages of secondary succession. We investigated the carbon variation in aboveground woody biomass, in litter and soil, and the nitrogen variation in litter and soil, in a 100 years long secondary succession in Mediterranean ecosystems. A vineyard, three stages of plant succession (high maquis, maquis-forest, and forest-maquis), and an old growth forest were compared. Soil samples at two soil depths (0-15 and 15-30 cm), and two litter types, relatively undecomposed and partly decomposed, were collected. Carbon stock in aboveground woody biomass increased from 6 Mg ha-1 in the vineyard to 105 Mg ha-1 in old growth forest. Along the secondary succession, soil carbon considerably increased from about 33 Mg ha-1 in the vineyard to about 69 Mg ha-1 in old growth forest. Soil nitrogen has more than doubled, ranging from 4.1 Mg ha-1 in the vineyard to 8.8 Mg ha-1 in old growth forest. Both soil parameters were found to be affected by successional stage and soil depth but not by their interaction. While the C/N ratio in the soil remained relatively constant during the succession, the C/N ratio of the litter strongly decreased, probably following the progressive increase in the holm oak contribution. While carbon content in litter decreased along the succession, nitrogen content slightly increased. Overall, carbon stock in aboveground woody biomass, litter and soil increased from about 48 Mg ha-1 in the vineyard to about 198 Mg ha-1 in old growth forest. The results of this study indicate that, even in Mediterranean environments, considerable amounts of carbon may be stored through secondary succession processes up to old growth forest. The occurrence of old-growth forests is quite limited in Mediterranean islands, which have been subject to particularly pronounced human impacts. Little is known about the carbon stocks of such peculiar ecosystems compared with different stages of secondary succession. We investigated the carbon variation in aboveground woody biomass, in litter and soil, and the nitrogen variation in litter and soil, in a 100 years long secondary succession in Mediterranean ecosystems. A vineyard, three stages of plant succession (high maquis, maquis-forest, and forest-maquis), and an old growth forest were compared. Soil samples at two soil depths (0-15 and 15-30 cm), and two litter types, relatively undecomposed and partly decomposed, were collected. Carbon stock in aboveground woody biomass increased from 6 Mg ha(-1) in the vineyard to 105 Mg ha(-1) in old growth forest. Along the secondary succession, soil carbon considerably increased from about 33 Mg ha(-1) in the vineyard to about 69 Mg ha(-1) in old growth forest. Soil nitrogen has more than doubled, ranging from 4.1 Mg ha(-1) in the vineyard to 8.8 Mg ha(-1) in old growth forest. Both soil parameters were found to be affected by successional stage and soil depth but not by their interaction. While the C/N ratio in the soil remained relatively constant during the succession, the C/N ratio of the litter strongly decreased, probably following the progressive increase in the holm oak contribution. While carbon content in litter decreased along the succession, nitrogen content slightly increased. Overall, carbon stock in aboveground woody biomass, litter and soil increased from about 48 Mg ha(-1) in the vineyard to about 198 Mg ha(-1) in old growth forest. The results of this study indicate that, even in Mediterranean environments, considerable amounts of carbon may be stored through secondary succession processes up to old growth forest.

10.1371/journal.pone.0220194https://pubmed.ncbi.nlm.nih.gov/31339941