| Literature DB >> 19066625 |
Janet Mann1, Brooke L Sargeant, Jana J Watson-Capps, Quincy A Gibson, Michael R Heithaus, Richard C Connor, Eric Patterson.
Abstract
Tool use is rare in wild animals, but of widespread interest because of its relationship to animal cognition, social learning and culture. Despite such attention, quantifying the costs and benefits of tool use has been difficult, largely because if tool use occurs, all population members typically exhibit the behavior. In Shark Bay, Australia, only a subset of the bottlenose dolphin population uses marine sponges as tools, providing an opportunity to assess both proximate and ultimate costs and benefits and document patterns of transmission. We compared sponge-carrying (sponger) females to non-sponge-carrying (non-sponger) females and show that spongers were more solitary, spent more time in deep water channel habitats, dived for longer durations, and devoted more time to foraging than non-spongers; and, even with these potential proximate costs, calving success of sponger females was not significantly different from non-spongers. We also show a clear female-bias in the ontogeny of sponging. With a solitary lifestyle, specialization, and high foraging demands, spongers used tools more than any non-human animal. We suggest that the ecological, social, and developmental mechanisms involved likely (1) help explain the high intrapopulation variation in female behaviour, (2) indicate tradeoffs (e.g., time allocation) between ecological and social factors and, (3) constrain the spread of this innovation to primarily vertical transmission.Entities:
Mesh:
Year: 2008 PMID: 19066625 PMCID: PMC2587914 DOI: 10.1371/journal.pone.0003868
Source DB: PubMed Journal: PLoS One ISSN: 1932-6203 Impact factor: 3.240
Figure 1Photograph of Sponger.
Courtesy of Ewa Krzyszczyk.
Foraging patterns for sponging and TDPD females.
| Variable | Sponge-Carrier Mean±SE | TDPD Mean±SE | Z- or t Score | p-value |
| % of time spent foraging | 47.2±4.77 | 35.84±5.24 | −1.59 | 0.110 |
| Duration of foraging bouts (min) | 8.50±1.02 | 9.59±1.26 | −0.75 | 0.446 |
| Mean dive duration (min) | 1.58±0.07 | 1.64±0.11 | −1.00 | 0.316 |
| % of tail-out dives during foraging | 83.47±3.43 | 65.44±5.17 | −2.71 |
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| % time in predominant foraging method | 45.08±4.91 | 26.77±5.08 | −2.57 |
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| % of foraging time devoted to primary foraging type | 96.00±2.05 | 35.84±4.91 | −2.41 |
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| % of bouts devoted to primary foraging type | 93.89±2.65 | 78.09±5.97 | −2.19 |
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| % time in deep water when not foraging | 93.40±2.44 | 57.38±7.78 | −3.84 |
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The last five variables in the table show the degree of specialization exhibited by sponger relative to TDPD females.
Figure 2Habitat use of 132 adult female bottlenose dolphins in Shark Bay in 286 km2 study area.
Image shows sightings of spongers (white circles, N = 16 spongers, 900 sightings, 52.9±12.6 per sponger) with non-spongers (red circles, N = 116 non-spongers, 9,742 sightings, 84.7±11.3 per female) in our main study area using only one sighting per day per female. In both maps, spongers are placed on top of the other females. Three zones are represented: channels (hatched lines), deep water (cross-hatched) and shallow moderate depth (open). Spongers were sighted 84.1±2.8% of the time in channels. Non-spongers were sighted 17.0±2.2% of the time in channels. If the primary area (>50% of sightings) is used to define adult female density by zone, then 32 females use channels as their primary area (female density = 0.34 females per km2), including all spongers and 16 non-spongers; 48 females use deep water as their primary area (0.60 females per km2) and 44 females use shallow-moderate depths as their primary area (0.40 females per km2). Seven females could not be assigned to a primary area. The map shows where spongers were sighted, but sponge foraging only occurred in channel habitats and, on rare occasion, in the deep (>7 m) northwest portion of the study area.