Premium
Fine root dynamics in a loblolly pine forest are influenced by free‐air‐CO 2 ‐enrichment: a six‐year‐minirhizotron study
Author(s) -
PRITCHARD SETH G.,
STRAND ALLAN E.,
McCORMACK M. LUKE,
DAVIS MICHEAL A.,
FINZI ADRIEN C.,
JACKSON ROBERT B.,
MATAMALA ROSER,
ROGERS HUGO H.,
OREN RAM
Publication year - 2008
Publication title -
global change biology
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 4.146
H-Index - 255
eISSN - 1365-2486
pISSN - 1354-1013
DOI - 10.1111/j.1365-2486.2007.01523.x
Subject(s) - biomass (ecology) , environmental science , canopy , cycling , seasonality , standing crop , zoology , agronomy , loblolly pine , soil carbon , soil water , pinus <genus> , biology , horticulture , botany , ecology , forestry , soil science , geography
Efforts to characterize carbon (C) cycling among atmosphere, forest canopy, and soil C pools are hindered by poorly quantified fine root dynamics. We characterized the influence of free‐air‐CO 2 ‐enrichment (ambient +200 ppm) on fine roots for a period of 6 years (Autumn 1998 through Autumn 2004) in an 18‐year‐old loblolly pine ( Pinus taeda ) plantation near Durham, NC, USA using minirhizotrons. Root production and mortality were synchronous processes that peaked most years during spring and early summer. Seasonality of fine root production and mortality was not influenced by atmospheric CO 2 availability. Averaged over all 6 years of the study, CO 2 enrichment increased average fine root standing crop (+23%), annual root length production (+25%), and annual root length mortality (+36%). Larger increase in mortality compared with production with CO 2 enrichment is explained by shorter average fine root lifespans in elevated plots (500 days) compared with controls (574 days). The effects of CO 2 ‐enrichment on fine root proliferation tended to shift from shallow (0–15 cm) to deeper soil depths (15–30) with increasing duration of the study. Diameters of fine roots were initially increased by CO 2 ‐enrichment but this effect diminished over time. Averaged over 6 years, annual fine root NPP was estimated to be 163 g dw m −2 yr −1 in CO 2 ‐enriched plots and 130 g dw m −2 yr −1 in control plots ( P = 0.13) corresponding to an average annual additional input of fine root biomass to soil of 33 g m −2 yr −1 in CO 2 ‐enriched plots. A lack of consistent CO 2 × year effects suggest that the positive effects of CO 2 enrichment on fine root growth persisted 6 years following minirhizotron tube installation (8 years following initiation of the CO 2 fumigation). Although CO 2 ‐enrichment contributed to extra flow of C into soil in this experiment, the magnitude of the effect was small suggesting only modest potential for fine root processes to directly contribute to soil C storage in south‐eastern pine forests.