Temporal changes in spatial patterns of soil moisture following disturbance: an experimental approach

被引:51
作者
Guo, D
Mou, P
Jones, RH
Mitchell, RJ
机构
[1] Univ N Carolina, Dept Biol, Greensboro, NC 27402 USA
[2] Virginia Polytech Inst & State Univ, Dept Forestry, Blacksburg, VA 24061 USA
[3] Virginia Polytech Inst & State Univ, Dept Biol, Blacksburg, VA 24061 USA
[4] Jones Ecol Res Ctr, Newton, GA 31770 USA
关键词
girdling; geostatistics; Pinus elliottii; scale; whole-tree harvesting;
D O I
10.1046/j.1365-2745.2001.00667.x
中图分类号
Q94 [植物学];
学科分类号
071001 ;
摘要
1 We quantified changes in spatial heterogeneity of soil moisture over 2.5 years in a Pinus elliottii Engelm. forest, following disturbance and succession. We harvested or girdled upper canopy trees and measured three components of heterogeneity - global (non-spatial) variability, spatial dependence and temporal persistence - in replicate plots, using sample points arrayed at a fine scale (0.5-6 m) nested within a coarser scale (5-60 m). 2 Global variability increased after disturbance and then declined, eventually returning to the level recorded in an undisturbed plot. Harvesting resulted in greater, more rapid and more prolonged changes in global variability than girdling. 3 Geostatistical parameters for measuring spatial dependence were largely unaffected by disturbance. Spatial dependence was, however, quite variable across replicate plots and was stronger at the finer sampling scale. 4 Spearman rank correlations showed that the spatial pattern of soil moisture had greater long-term persistence in the undisturbed and girdled plots than in the harvested plots. 5 Some elements of spatial heterogeneity appear to vary over time in a predictable manner. Detection of temporal trends may be improved if multiple components of heterogeneity are quantified, more than one scale of observation is used, replicate plots are employed and sole reliance on geostatistics is avoided.
引用
收藏
页码:338 / 347
页数:10
相关论文
共 71 条
[1]   ECOLOGICAL NEIGHBORHOODS - SCALING ENVIRONMENTAL PATTERNS [J].
ADDICOTT, JF ;
AHO, JM ;
ANTOLIN, MF ;
PADILLA, DK ;
RICHARDSON, JS ;
SOLUK, DA .
OIKOS, 1987, 49 (03) :340-346
[2]  
[Anonymous], 1994, EXPLOITATION ENV HET
[3]  
[Anonymous], 1977, J ENVIRON QUAL
[4]   INFLUENCE OF MICROTOPOGRAPHY AND CANOPY SPECIES ON SPATIAL PATTERNS OF FOREST UNDERSTORY PLANTS [J].
BEATTY, SW .
ECOLOGY, 1984, 65 (05) :1406-1419
[5]   Environmental heterogeneity and species diversity of forest sedges [J].
Bell, G ;
Lechowicz, MJ ;
Waterway, MJ .
JOURNAL OF ECOLOGY, 2000, 88 (01) :67-87
[6]   THE SPATIAL STRUCTURE OF THE PHYSICAL-ENVIRONMENT [J].
BELL, G ;
LECHOWICZ, MJ ;
APPENZELLER, A ;
CHANDLER, M ;
DEBLOIS, E ;
JACKSON, L ;
MACKENZIE, B ;
PREZIOSI, R ;
SCHALLENBERG, M ;
TINKER, N .
OECOLOGIA, 1993, 96 (01) :114-121
[7]   Spatial dependence of soil enzyme activities along a slope [J].
Bergstrom, DW ;
Monreal, CM ;
Millette, JA ;
King, DJ .
SOIL SCIENCE SOCIETY OF AMERICA JOURNAL, 1998, 62 (05) :1302-1308
[8]   Optimal spatial sampling design for the estimation of the variogram based on a least squares approach [J].
Bogaert, P ;
Russo, D .
WATER RESOURCES RESEARCH, 1999, 35 (04) :1275-1289
[9]  
Breshears DD, 1997, ECOL APPL, V7, P1201, DOI 10.1890/1051-0761(1997)007[1201:OIHISR]2.0.CO
[10]  
2