Definition of sampling units begets conclusions in ecology: The case of habitats for plant communities
Permanent lenke
https://hdl.handle.net/10037/8657Dato
2015-03-05Type
Journal articleTidsskriftartikkel
Peer reviewed
Forfatter
Mörsdorf, Martin Alfons; Ravolainen, Virve; Støvern, Einar; Yoccoz, Nigel Gilles; Jonsdottir, Ingibjørg; Bråthen, Kari AnneSammendrag
In ecology, expert knowledge on habitat characteristics is often used to define sampling
units such as study sites. Ecologists are especially prone to such approaches
when prior sampling frames are not accessible. Here we ask to what extent can
different approaches to the definition of sampling units influence the conclusions
that are drawn from an ecological study? We do this by comparing a formal versus
a subjective definition of sampling units within a study design which is based on
well-articulated objectives and proper methodology. Both approaches are applied to
tundra plant communities in mesic and snowbed habitats. For the formal approach,
sampling units were first defined for each habitat in concave terrain of suitable slope
using GIS. In the field, these units were only accepted as the targeted habitats if
additional criteria for vegetation cover were fulfilled. For the subjective approach,
sampling units were defined visually in the field, based on typical plant communities
of mesic and snowbed habitats. For each approach, we collected information about
plant community characteristics within a total of 11 mesic and seven snowbed units
distributed between two herding districts of contrasting reindeer density. Results
from the two approaches differed significantly in several plant community characteristics
in both mesic and snowbed habitats. Furthermore, differences between the
two approaches were not consistent because their magnitude and direction differed
both between the two habitats and the two reindeer herding districts. Consequently,
we could draw different conclusions on how plant diversity and relative abundance
of functional groups are differentiated between the two habitats depending on the
approach used. We therefore challenge ecologists to formalize the expert knowledge
applied to define sampling units through a set of well-articulated rules, rather than
applying it subjectively. We see this as instrumental for progress in ecology as only
rules based on expert knowledge are transparent and lead to results reproducible by
other ecologists.