From: Relationship between agricultural pesticides and the diet of riparian spiders in the field
Variable | Unit and explanation | Loading on SPCA axes | Value | |
---|---|---|---|---|
Mean | SD | |||
Toxicity | Maximum of log sum toxic unit for the most sensitive freshwater invertebrate | Excluded from SPCA | − 0.56 | 0.52 |
pHb | First axis; 0.33 | 8.19 | 0.18 | |
Oxygenb | [%] dissolved oxygen in the stream | First axis; 0.45 | 75.99 | 8.95 |
Field distance index | Weighted distance of streams to agriculturally used fields for right and left site of the stream, at sampling site | First axis; − 0.13 | 0.64 | 0.25 |
Corridor land use meadows | [%] land cover with meadows within a 200 m distance to the stream | First axis; − 0.14 | 52.5 | 25.78 |
Catchment size | [km2] size of catchment area | First axis; 0.30 | 76.03 | 67.16 |
Catchment land use type 1 | [%] land cover with arable land and permanent crops in the catchmentc | First axis; − 0.31 | 30.34 | 13.92 |
Maximal width stream | [m] widest part of the stream at sampling site | First axis; 0.39 | 3.57 | 1.35 |
Minimal width stream | [m] narrowest part of the stream at sampling site | First axis; 0.42 | 2.28 | 1.23 |
Riffles | [%] | First axis; 0.36 | 41.92 | 28.03 |
Sulphatea | [mg/L] | Second axis; 0.36 | 64.54 | 33.38 |
Riparian cover shrubs | [%] riparian land covered with shrubs within 5 m to stream along a 20 m transect | Second axis; 0.62 | 16.15 | 15.93 |
Riparian cover meadows | [%] riparian land covered with meadows within 5 m to stream along a 20 m transect | Second axis; − 0.59 | 25.38 | 25.02 |
Catchment land use type 2 | [%] pastures and heterogenous agricultural areas in the catchmentc | Second axis; − 0.37 | 39.07 | 7.54 |