Abstract
When assessing changes in populations of species, it is essential that the methods used to collect data have some level of precision and preferably also good accuracy. One commonly used method to collect pollinators is colour pan traps, but this method has been suggested to be biased by the abundance of surrounding flowers. The present study evaluated the relationship between pan trap catches and the frequency of flowers on small (25 m2) and large (2–6 ha) spatial scales. If pan traps work well, one should assume a positive relationship, that is, more insects caught when they have more food. However, in contrast, we found that catches in pan traps were often negatively affected by flower frequency. Among the six taxa evaluated, the negative bias was largest in Vespoidea and Lepturinae, while there was no bias in solitary Apoidea (Cetoniidae, Syrphidae and social Apoidea were intermediate). Furthermore, red flowers seemed to contribute most to the negative bias. There was also a tendency that the negative bias differed within the flight season and that it was higher when considering the large spatial scale compared to the small one. To conclude, pan trap catches may suffer from a negative bias due to surrounding flower frequency and color. The occurrence and magnitude of the negative bias were context and taxon dependent, and therefore difficult to adjust for. Thus, pan traps seem less suited to evaluate differences between sites and the effect of restoration, when gradients in flower density are large. Instead, it seems better suited to monitor population changes within sites, and when gradients are small.
Highlights
Pollinating insects are important for many plant species and provide an essential ecosystem service to man (Aizen et al, 2009; Gallai et al, 2008)
Red was the color most affected by negative bias while white and blue seemed unaffected (Figure 6)
One expects the catch to reflect the size of targeted insect populations
Summary
Pollinating insects are important for many plant species and provide an essential ecosystem service to man (Aizen et al, 2009; Gallai et al, 2008). To assess populations of pollinators and to monitor changes in response to habitat deterioration, as well as to conservation efforts, it is essential that the methods used to collect data on pollinator fauna have some degree of precision Accuracy in data is important (i.e., to what extent it represents the populations sampled), but possibly an unrealistic goal when sampling an insect assemblage (Cooper et al, 2012; Sutherland & Parrella, 2011; Walther & Moore, 2005). A sampling scheme is unlikely to collect more than a single, targeted species with high accuracy. In many cases it seems feasible to accept a consistent bias as long as relevant trends can be inferred
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