Christiansen, Bernd (2006): Fish size distribution of different fish species at epibenthic sledge sample M60/1_758 [dataset]. PANGAEA, https://doi.org/10.1594/PANGAEA.358449, In: Christiansen, Bernd; Arístegui Ruiz, Javier; Bett, Brian J; Kiriakoulakis, Kostas; Martins, Ana; Menezes, Gui M; White, Martin (2015): Compilation of scientific results of the OASIS project [dataset publication series]. PANGAEA, https://doi.org/10.1594/PANGAEA.842709
Always quote citation above when using data! You can download the citation in several formats below.
Related to:
Christiansen, Bernd (2004): Meteor-Cruise M60/1, Short Cruise Report, 11.11.2003-6.12.2003, OASIS. Universität Hamburg, Institut für Hydrobiologie und Fischereiwissenschaft, Germany, 8 pp, https://www.ldf.uni-hamburg.de/meteor/wochenberichte/wochenberichte-meteor/m60/m60-1-scr.pdf
Project(s):
Funding:
Fifth Framework Programme (FP5), grant/award no. EVK3-CT-2002-00073: Oceanic Seamounts: an Integrated Study
Coverage:
Latitude: 33.012639 * Longitude: -14.355000
Date/Time Start: 2003-12-04T17:33:00 * Date/Time End: 2003-12-04T17:33:00
Minimum Elevation: -186.0 m * Maximum Elevation: -186.0 m
Event(s):
M60/1_758 (758) * Latitude: 33.012639 * Longitude: -14.355000 * Date/Time: 2003-12-04T17:33:00 * Elevation: -186.0 m * Location: Northeast Atlantic * Campaign: M60/1 * Basis: Meteor (1986) * Method/Device: Epibenthic sledge (EBS)
Comment:
preserved material (formaldehyde)
Parameter(s):
| # | Name | Short Name | Unit | Principal Investigator | Method/Device | Comment |
|---|---|---|---|---|---|---|
| 1 | Species | Species | Christiansen, Bernd | |||
| 2 | Sample ID | Sample ID | Christiansen, Bernd | |||
| 3 | Length | l | mm | Christiansen, Bernd | total length | |
| 4 | Length, standard | I std | mm | Christiansen, Bernd | ||
| 5 | Mass, brutto | Brutto | g | Christiansen, Bernd | wet weight |
License:
Creative Commons Attribution 3.0 Unported (CC-BY-3.0)
Size:
305 data points
Data
| 1 Species | 2 Sample ID | 3 l [mm] | 4 I std [mm] | 5 Brutto [g] |
|---|---|---|---|---|
| Anthias anthias | EBS/2-1 | 165 | 115 | 35.900 |
| Anthias anthias | EBS/2-2 | 90 | 65 | 6.470 |
| Anthias anthias | EBS/2-3 | 80 | 55 | 3.800 |
| Anthias anthias | EBS/2-4 | 85 | 60 | 5.340 |
| Arnoglossus rueppeli | EBS/2-1 | 140 | 120 | 13.000 |
| Arnoglossus rueppeli | EBS/2-2 | 120 | 100 | 7.830 |
| Arnoglossus rueppeli | EBS/2-3 | 115 | 100 | 8.110 |
| Arnoglossus rueppeli | EBS/2-4 | 110 | 90 | 6.880 |
| Arnoglossus rueppeli | EBS/2-5 | 105 | 90 | 6.150 |
| Arnoglossus rueppeli | EBS/2-6 | 80 | 75 | 2.550 |
| Arnoglossus rueppeli | EBS/2-7 | 105 | 90 | 7.090 |
| Arnoglossus rueppeli | EBS/2-8 | 60 | 50 | 1.110 |
| Arnoglossus rueppeli | EBS/2-9 | 50 | 45 | 0.600 |
| Arnoglossus rueppeli | EBS/2-10 | 65 | 55 | 1.480 |
| Arnoglossus rueppeli | EBS/2-11 | 50 | 45 | 0.650 |
| Arnoglossus rueppeli | EBS/2-12 | 50 | 45 | 0.740 |
| Callanthias ruber | EBS/2-1 | 130 | 85 | 12.620 |
| Callanthias ruber | EBS/2-2 | 105 | 80 | 8.250 |
| Callanthias ruber | EBS/2-3 | 95 | 70 | 6.800 |
| Callanthias ruber | EBS/2-4 | 85 | 65 | 5.570 |
| Callanthias ruber | EBS/2-5 | 100 | 70 | 6.000 |
| Callanthias ruber | EBS/2-6 | 90 | 60 | 5.100 |
| Callanthias ruber | EBS/2-7 | 100 | 65 | 6.030 |
| Callanthias ruber | EBS/2-8 | 80 | 60 | 4.410 |
| Callanthias ruber | EBS/2-9 | 70 | 55 | 3.430 |
| Callanthias ruber | EBS/2-10 | 65 | 50 | 2.350 |
| Callanthias ruber | EBS/2-11 | 55 | 45 | 1.800 |
| Callanthias ruber | EBS/2-12 | 45 | 35 | 1.070 |
| Macroramphosus spp. | EBS/2-1 | 110 | 98 | 7.479 |
| Macroramphosus spp. | EBS/2-2 | 115 | 103 | 8.321 |
| Macroramphosus spp. | EBS/2-3 | 115 | 105 | 11.077 |
| Macroramphosus spp. | EBS/2-4 | 115 | 102 | 8.861 |
| Macroramphosus spp. | EBS/2-5 | 120 | 108 | 11.346 |
| Macroramphosus spp. | EBS/2-6 | 125 | 110 | 15.057 |
| Macroramphosus spp. | EBS/2-7 | 117 | 105 | 11.495 |
| Macroramphosus spp. | EBS/2-8 | 115 | 105 | 11.196 |
| Macroramphosus spp. | EBS/2-9 | 116 | 105 | 10.256 |
| Macroramphosus spp. | EBS/2-10 | 110 | 98 | 8.361 |
| Macroramphosus spp. | EBS/2-11 | 87 | 100 | 5.903 |
| Macroramphosus spp. | EBS/2-12 | 125 | 110 | 10.166 |
| Macroramphosus spp. | EBS/2-13 | 100 | 87 | 5.828 |
| Macroramphosus spp. | EBS/2-14 | 97 | 81 | 4.802 |
| Macroramphosus spp. | EBS/2-15 | 92 | 82 | 3.841 |
| Macroramphosus spp. | EBS/2-16 | 95 | 85 | 5.647 |
| Macroramphosus spp. | EBS/2-17 | 120 | 110 | 9.311 |
| Macroramphosus spp. | EBS/2-18 | 95 | 85 | 5.125 |
| Macroramphosus spp. | EBS/2-19 | 120 | 108 | 8.996 |
| Macroramphosus spp. | EBS/2-20 | 100 | 90 | 5.716 |
| Macroramphosus spp. | EBS/2-21 | 120 | 110 | 9.553 |
| Macroramphosus spp. | EBS/2-22 | 120 | 110 | 9.267 |
| Macroramphosus spp. | EBS/2-23 | 110 | 100 | 9.024 |
| Macroramphosus spp. | EBS/2-24 | 120 | 107 | 9.205 |
| Macroramphosus spp. | EBS/2-25 | 110 | 95 | 8.702 |
| Macroramphosus spp. | EBS/2-26 | 100 | 88 | 6.193 |
| Macroramphosus spp. | EBS/2-27 | 100 | 88 | 5.953 |
| Macroramphosus spp. | EBS/2-28 | 100 | 90 | 5.556 |
| Macroramphosus spp. | EBS/2-29 | 100 | 90 | 6.413 |
| Macroramphosus spp. | EBS/2-30 | 90 | 80 | 4.319 |
| Macroramphosus spp. | EBS/2-31 | 115 | 105 | 8.903 |
| Macroramphosus spp. | EBS/2-32 | 95 | 84 | 5.423 |
| Macroramphosus spp. | EBS/2-33 | 100 | 89 | 6.512 |