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Open Access 23.07.2024 | Correction

Correction: Human disturbance and habitat structure drive eurasian otter habitat selection in heavily anthropized river basins

verfasst von: Arnau Tolrà, Jordi Ruiz-Olmo, Joan Lluís Riera

Erschienen in: Biodiversity and Conservation | Ausgabe 10/2024

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The online version of the original article can be found at https://​doi.​org/​10.​1007/​s10531-024-02826-9.

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Correction: Biodiversity and Conservation (2024) 33:1683–1710
In this article, the Tables 1 and 2 have been published with incorrect formatting. In Table 1, the variables in the first column are not mentioned in a single line and in Table 2, the subheadings in the first row are not clearly aligned with the second row.
The original article has been corrected.
The correct version of tables are given below.
Table 1
Variables recorded in the sampling transects and used to explain the Eurasian otter habitat selection, including their unit, code and range
Environmental variables (unit)
Code
Range
Altitude (m)
ALT
0 to 788 m
Distance to sea (km)
DSEA
0 to 58.79 km
Water temperature (ºC)
TEMP
10.4 to 19.6 °C
Water conductivity (µS/cm)
COND
32 to 542 µS/cm
Average channel depth (cm)
DEPTH
10 to 85 cm
Average channel width (m)
WIDTH
2 to 40 m
Flow velocity (1–5)
VELOC
Predominate slow waters to predominate fast waters
Large woody debris (1–10)
DEBWOOD
Absence of large woody debris within riverbed to > 10 of large woody debris within riverbed
Tributaries and wetlands (1–10)
TRIBU
Absence of tributary streams and wetlands within 1 km around the transect to > 1 important tributary stream and a wetland within the transect
River form (1–10)
FORM
Linear riverbed form to > 2 meandering curves and abundance of moderate curves
Islets and arms (1–10)
ISLARM
Absence of islets and arms to > 10 medium-sized arms (length 8–35 m) and > 5 large-sized arms (length > 35 m)
Pools (1–10)
POOL
Absence of > 1 m depth pools within the riverbed to > 10 pools within the riverbed
Riverbank refuges (1–10)
REFU
Heavily altered riverbanks without refuges to riverbanks with an abundant refuge (shrubs, large woody debris, roots, rock systems, etc.)
Distance to urban centres (m)
DURB
20 to 3620 m
Human population (1–10)
POPU
0 to 200,000 inhabitants within 2 km perimeter
Human accessibility (1–10)
ACCSHUM
Absence of roads, paths and riverbed accesses to roads or paths on both riverbanks with two regular riverbed accesses
Distance to roads (m)
DROAD
1 to 4270 m
Tree cover (%)
VEGARB
0 to 100%
Helophytic cover (%)
VEGHELO
0 to 30%
Exotic vegetation (%)
VEGEXO
0 to 100%
Water permanence (1–10)
STAB
Minimum 15 days completely dry to permanent flow with a minimum depth of 60 cm
Aquatic vegetation (1–15)
VEGAQU
Absent surface and bottom aquatic vegetation to abundant surface and bottom aquatic vegetation
Table 2
Comparison and statistical differences of habitat variables on otter breeding and non-breeding sites and otter presence and absence sites. Values represents means and standard errors. P-values are the result from two-sample Wilcoxon test between otter breeding and non-breeding sites and otter presence and absence sites
 
Otter reproduction
Otter occurrence
Wilcoxon test (p)
Breeding
No breeding
Presence
Absence
Breeding
Presence
Distance to sea (km)
24.56 ± 2.93
25.85 ± 1.66
25.16 ± 0.71
27.51 ± 1.17
ns
ns
Altitude (m)
119.25 ± 43.12
156.75 ± 23.23
118.47 ± 6.32
238.41 ± 21.41
ns
p < 0.001
Channel depth (cm)
42.06 ± 7.57
28.42 ± 2.33
34.32 ± 1.36
31.68 ± 1.70
p < 0.01
p < 0.001
Channel width (m)
10.06 ± 2.43
7.65 ± 0.97
8.83 ± 0.46
7.85 ± 0.76
ns
p < 0.001
Human accessibility (index)
3.25 ± 0.45
5.28 ± 0.29
4.78 ± 0.13
5.87 ± 0.16
p < 0.05
p < 0.001
Distance to urban centres (m)
1563.75 ± 227.234
935.02 ± 129.30
861.31 ± 49.75
959.68 ± 91.50
p < 0.05
ns
Human population (index)
1.25 ± 0.23
2.73 ± 0.18
2.57 ± 0.08
2.68 ± 0.13
p < 0.01
ns
Distance to roads (m)
192.62 ± 99.35
190.53 ± 76.07
121.59 ± 16.11
125.54 ± 23.65
ns
ns
Tributaries and wetlands (index)
6.50 ± 0.96
4 ± 0.36
5.36 ± 0.21
3.15 ± 0.20
p < 0.05
p < 0.001
Large woody debris (index)
8.38 ± 0.50
4.53 ± 0.24
5.57 ± 0.14
3.84 ± 0.14
p < 0.001
p < 0.001
River form (index)
6.63 ± 0.62
3.47 ± 0.26
4.59 ± 0.16
2.49 ± 0.09
p < 0.001
p < 0.001
Islands and arms (index)
6.88 ± 0.76
3.77 ± 0.28
4.74 ± 0.16
2.95 ± 0.13
p < 0.01
p < 0.001
Pools (index)
9.13 ± 0.12
6.32 ± 0.21
7.02 ± 0.11
6.61 ± 0.14
p < 0.001
p < 0.05
Riverbank refuges (index)
5.88 ± 0.12
3.12 ± 0.16
3.79 ± 0.10
3.06 ± 0.09
p < 0.001
p < 0.001
Water permanence (index)
7.75 ± 0.41
5.46 ± 0.36
6.24 ± 0.18
5.97 ± 0.22
p < 0.05
ns
Tree cover (%)
6.50 ± 0.33
5.50 ± 0.43
5.30 ± 0.18
5.75 ± 0.28
ns
ns
Helophyte cover (%)
5.87 ± 0.61
4.38 ± 0.30
5.14 ± 0.15
4.44 ± 0.19
ns
p < 0.01
Exotic vegetation (%)
4.50 ± 0.50
6.10 ± 0.29
5.71 ± 0.13
5.64 ± 0.21
p < 0.05
ns
Water temperature (ºc)
16.59 ± 0.44
16.13 ± 0.31
16.36 ± 0.13
15.76 ± 0.24
ns
ns
Water conductivity (µS/cm)
525.50 ± 96.64
557.23 ± 44.48
577.99 ± 21.21
597.55 ± 29.50
ns
ns
Flow velocity (index)
2.37 ± 0.32
2.95 ± 0.14
2.62 ± 0.06
3.23 ± 0.09
ns
p < 0.001
Aquatic vegetation (index)
10.88 ± 0.77
8.37 ± 0.42
9.43 ± 0.19
8.44 ± 0.30
p < 0.05
p < 0.05
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Titel
Correction: Human disturbance and habitat structure drive eurasian otter habitat selection in heavily anthropized river basins
verfasst von
Arnau Tolrà
Jordi Ruiz-Olmo
Joan Lluís Riera
Publikationsdatum
23.07.2024
Verlag
Springer Netherlands
Erschienen in
Biodiversity and Conservation / Ausgabe 10/2024
Print ISSN: 0960-3115
Elektronische ISSN: 1572-9710
DOI
https://doi.org/10.1007/s10531-024-02891-0