Scale-dependent biases in species counts in a grassland

被引:87
作者
Klimes, L
Dancák, M
Hájek, M
Jongepierová, I
Kucera, T
机构
[1] Inst Bot, Sect Plant Ecol, CZ-37982 Trebon, Czech Republic
[2] Palacky Univ, Dept Bot, Unit Gen & Systemat Bot & Geobot, Olomouc 77236, Czech Republic
[3] Masaryk Univ, Dept Systemat Bot & Geobot, Fac Sci, Brno 61137, Czech Republic
[4] Adm Protected Landscape Area Bile Karpaty, Veseli Moravou 69801, Czech Republic
关键词
sampling error; species richness estimate; species-rich meadow;
D O I
10.2307/3236910
中图分类号
Q94 [植物学];
学科分类号
071001 ;
摘要
Numbers of plant species were recorded in species-rich meadows in the Bile Karpaty Mts., SE Czech Republic. with the aim to evaluate the sampling error made by well-trained observers. Five observers recorded vascular plants in seven plots ranging from 9.8 cm(2) to 4 m(2) independently and were not time-limited. in larger plots a discrepancy of 10-20% was found between individual estimates, in smaller plots discrepancy increased to 33%. on average. The gain in observed species richness by combining records of individual observers (in comparison with the mean numbers estimated by single observers) decreased from the smallest plot (27-82% for two to five observers) to the largest one (13-25%). However, after misidentified and suspicious records were eliminated. the gain was much lower and became seale-independent two observers added 12% species, on average, and the increase by combining species lists made by three or more observers was negligible (3% more on average). It is concluded that most discrepancies between individual observers were caused by misidentification of rare seedlings and young plants. We suggest that in species-rich meadows plants should be recorded by at least three observers together and that they should consult all problematic plant specimens together in the field. to minimize errors.
引用
收藏
页码:699 / 704
页数:6
相关论文
共 14 条
[1]  
Boulinier T, 1998, ECOLOGY, V79, P1018, DOI 10.1890/0012-9658(1998)079[1018:ESRTIO]2.0.CO
[2]  
2
[3]  
Hawksworth D.L., 1996, BIODIVERSITY MEASURE
[4]  
JONGEPIEROVA I., 1994, PRIRODA, V1, P185
[5]   Estimating the effectiveness of further sampling in species inventories [J].
Keating, KA ;
Quinn, JF ;
Ivie, MA ;
Ivie, LL .
ECOLOGICAL APPLICATIONS, 1998, 8 (04) :1239-1249
[6]   SEASONAL AND OBSERVER DIFFERENCES IN VASCULAR PLANT RECORDS FROM BRITISH WOODLANDS [J].
KIRBY, KJ ;
BINES, T ;
BURN, A ;
MACKINTOSH, J ;
PITKIN, P ;
SMITH, I .
JOURNAL OF ECOLOGY, 1986, 74 (01) :123-131
[7]   Small-scale plant mobility in a species-rich grassland [J].
Klimes, L .
JOURNAL OF VEGETATION SCIENCE, 1999, 10 (02) :209-218
[8]   VARIABILITY IN SPECIES RICHNESS AND GUILD STRUCTURE IN 2 SPECIES-RICH GRASSLANDS [J].
KLIMES, L ;
JONGEPIER, JW ;
JONGEPIEROVA, I .
FOLIA GEOBOTANICA & PHYTOTAXONOMICA, 1995, 30 (02) :243-253
[9]   HOW RELIABLE ARE OUR VEGETATION ANALYSES [J].
LEPS, J ;
HADINCOVA, V .
JOURNAL OF VEGETATION SCIENCE, 1992, 3 (01) :119-124
[10]   EXPERIMENTAL ESTIMATES OF CENSUS EFFICIENCY AND PSEUDOTURNOVER ON ISLANDS - ERROR TREND AND BETWEEN-OBSERVER VARIATION WHEN RECORDING VASCULAR PLANTS [J].
NILSSON, IN ;
NILSSON, SG .
JOURNAL OF ECOLOGY, 1985, 73 (01) :65-70