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Earthworms in the diet of herring (Larus argentatus) breeding on an off-shore island Pennycott, Tom W.; Grant, David; Nager, Ruedi G.

Published in: Study

DOI: 10.1080/00063657.2020.1743232

Published: 06/08/2020

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Citation for published version (APA): Pennycott, T. W., Grant, D., & Nager, R. G. (2020). in the diet of herring gulls (Larus argentatus) breeding on an off-shore island. Bird Study, 67(1), 131-134. https://doi.org/10.1080/00063657.2020.1743232

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Download date: 02 Oct 2021 “This is an Accepted Manuscript of an article published by Taylor & Francis Group in Bird Study on 06/04/2020, available online: https://doi.org/10.1080/00063657.2020.1743232.” 1 Earthworms in the diet of Herring Gulls (Larus argentatus) breeding on an off-shore

2 island

3 Tom W. Pennycott, Browncarrick Drive, Ayr, KA7 4JA, Scotland.

4 David Grant, University of the West of Scotland, Ayr Campus, Ayr, KA8 0SX, Scotland.

5 Ruedi G. Nager, Graham Kerr Building, IBAHCM, University of Glasgow, G12 8QQ,

6 Scotland.

7 Short title: Earthworms and Herring Gulls

8 Key words (in addition to those in title): regurgitated pellets; terrestrial vegetation; chaetae,

9 rainfall

10 Email of correspondence author: [email protected]

11

12 Summary

13 Pellets of indigestible material regurgitated by Herring Gulls breeding on Lady Isle, Firth of

14 Clyde, Scotland, were collected in 2018 and 2019 and examined for chaetae.

15 Nearly two-thirds (65.6%) of the 314 pellets came from gulls that had consumed one or more

16 earthworms. Significantly fewer pellets (57.6%) contained chaetae in 2018, a relatively dry

17 May to July, than in 2019 (72.0%) when rainfall was close to the long-term average for May

18 to July. There were significant associations between the presence of large quantities of

19 terrestrial vegetation in the pellet and the detection of large numbers of earthworm chaetae

20 and/or fragments of terrestrial arthropods, suggesting that recent consumption of these food

21 items is likely when pellets contain large quantities of vegetation.

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22 Earthworms in the diet of Herring Gulls (Larus argentatus) breeding on an off-shore

23 island

24

25 The Herring population in the UK is currently in decline and has been since the 1970s,

26 warranting its red-listed status (Eaton et al. 2015). The exact reasons for this population

27 decline are unknown but changes in food resources could be one possible explanation

28 (Mitchell et al. 2004). Any advances in the understanding of the diet of this are

29 therefore to be regarded as positive.

30 Information about the diet of Herring Gulls in southwest Scotland and nearby Northern

31 Ireland, based on analysis of regurgitated pellets, has been provided by Melville (1974),

32 Nogales et al. (1995) and O’Hanlon et al. (2017). However, the methodology used in these

33 studies did not include examination for the remains of earthworms (Class ,

34 Family ). Earthworms were recognised as a source of food for gulls as long ago

35 as the 1920s and 1930s (Portielje 1928, O’Mahony 1935) and are potentially highly nutritious

36 (Edwards 1985). Most parts of an earthworm are easily digested after being eaten by a bird

37 or mammal, but the chaetae (bristle-like structures found in their hundreds on the outer

38 surface of earthworms) are not digested and are passed out in the faeces or regurgitated in

39 pellets where they can be detected using appropriate methodology (Coulson & Coulson

40 2008).

41 Within southwest Scotland, the Clyde Basin is an important area for breeding Herring Gulls,

42 and Lady Isle (55.53°N, 4.73°W), a very small (4.4 hectares) unpopulated island within the

43 Clyde Basin 5.6 km off the Ayrshire coast, hosts a large and, in the Scottish context,

44 significant Herring Gull colony, with approximately 4-5% of the total Scottish Herring Gull

45 breeding population (Grant et al. 2013). Lady Isle also has smaller numbers of breeding

46 Lesser Black-backed Gulls L. fuscus and Great Black-backed Gulls L. marinus (Grant et al.

47 2013).

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48 Determining whether Herring Gulls on Lady Isle consume earthworms is important in studies

49 looking at resource use by gulls in this area of Scotland, to establish baseline data for the

50 occurrence of this food item in their diet and to complement previous studies in this region by

51 Nogales et al. (1995) and O’Hanlon et al. (2017). In addition, many previous researchers

52 (Harris 1965; Vernon 1970; Melville 1974; Nogales et al. 1995; Coulson & Coulson 2008;

53 Lindborg et al. 2012; O’Hanlon et al. 2017) have reported the presence of large quantities of

54 terrestrial vegetation in pellets produced by different species of gulls. In most of these

55 studies no attempts were made to look for earthworm chaetae and the significance of the

56 vegetation was unclear. Coulson & Coulson (2008) did, however, propose that such

57 terrestrial vegetation was accidentally consumed when gulls were foraging for earthworms

58 and insects. Here, using an enhanced method of pellet analysis, we explored the importance

59 of earthworms in the diet of Herring Gulls breeding in a coastal colony, and tested a possible

60 association between the presence of large quantities of terrestrial vegetation and the

61 detection of large numbers of earthworm chaetae in Herring Gull pellets.

62 On Lady Isle, Herring Gulls nest predominantly on the periphery of the island whereas

63 Lesser and Great Black-backed Gulls occupy slightly higher ground with more vegetation in

64 the interior (Grant et al. 2013). During the 2018 and 2019 breeding seasons, we collected

65 pellets from rocks, nests or the vicinity of nests in areas on Lady Isle in which Herring Gulls

66 breed (139 in May – July 2018, 175 in May – July 2019) and stored them in a deep freeze

67 prior to testing. Each pellet was defrosted and left for at least two hours in a 100 ml container

68 filled with water. The pellets were teased apart within the water, agitated vigorously for two

69 minutes with glass beads, and the contents passed through a disposable coarse sieve

70 (mesh size 1-2 mm) into a collecting container. Larger items remained in the sieve and small

71 items such as earthworm chaetae passed through the sieve into the washings. A 45 ml

72 container with a conical base was filled with some of the washings and allowed to stand for

73 at least 20 minutes to permit sedimentation of any earthworm chaetae present. Using a

74 disposable transfer pipette, six drops (approximately 300 µl) of sediment were transferred to

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75 a glass slide, glass coverslips added, and the slides examined using a binocular microscope

76 with transmitted light at a magnification of x100 (x10 eyepiece and x10 objective lens). If the

77 sediment was very thick, three drops of sediment were mixed with three drops of water on

78 the slide. The number of earthworm chaetae detected in 300 µl of sediment was recorded as

79 0, 1-50 or over 50. This threshold was chosen pragmatically after a pilot study in 2017 used

80 this methodology to determine chaetae numbers in 36 gull pellets, in which small numbers

81 (1-50) possibly reflected an earthworm meal in the recent past and larger numbers (>50 in

82 300 µl of sediment) suggested more recent consumption of one or more earthworms.

83 The contents of the sieve were dried and examined grossly and with a binocular dissecting

84 microscope (magnification range 7-45) and the main component(s) identified, quantified and

85 recorded, including the presence of large quantities (comprising more than 40% of the pellet)

86 of coarse terrestrial vegetation such as leaves, stems and roots.

87 When viewed under transmitted light at x100 magnification, earthworm chaetae were clearly

88 visible as long, narrow, yellowish, glassy translucent structures with faint transverse

89 striations. Most had an elongate sigmoid shape, with up-turning and down-turning of

90 dissimilar opposite ends and with a slightly thickened band approximately one third along

91 their length (Figure 1). Statistical comparisons were calculated by Pearson’s chi-squared test

92 with Yates’ correction, using an on-line statistical calculator

93 (https://www.socscistatistics.com/tests/chisquare/).

94 We collected and analysed a total of 314 pellets. The commonest items making up at least

95 25% of the bulk of a pellet were anthropogenic debris such as waste food, plastic, paper,

96 aluminium foil and glass (32.2% of pellets), cereal husks and/or kernels (30.6%) and marine

97 items such as fragments of fish, crabs and langoustines (10.2%). Evidence of earthworm

98 consumption was found in 206 out of 314 (65.6%) pellets: 98 pellets (31.2%) contained large

99 numbers (>50 in 300 µl of sediment) of chaetae, and smaller numbers (1-50 chaetae in 300

100 µl of sediment) were found in a further 108 pellets (34.4%). Earlier studies on the diet of

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101 Herring Gulls in the Firth of Clyde did not use methods that would readily detect earthworm

102 chaetae in pellets (Nogales et al. 1995, O’Hanlon et al. 2017), but using different

103 methodology we found earthworm chaetae in two-thirds of pellets. This is probably an

104 overestimate of the frequency of earthworms in the diet as chaetae could be detected in the

105 faeces of Choughs Pyrrhocorax pyrrhocorax for at least twelve faecal evacuations after

106 consumption of an earthworm (Meyer et al. 1994), and the detection of small numbers of

107 chaetae probably reflected carry-over of chaetae from an earlier meal. Thus, the frequency

108 of pellets with larger numbers of chaetae (31.2%) better reflects the contribution of

109 earthworms to the diet of Herring Gulls, although our threshold of >50 chaetae in 300 µl of

110 sediment was chosen pragmatically and may require further study. Coulson & Coulson

111 (2008) found a high frequency of pellets containing earthworm chaetae (55.2%) in Lesser

112 Black-backed Gulls breeding in an inland urban colony in southwest Scotland, and Sibly &

113 McCleery (1983) found that earthworms were one of the four most important food sources

114 for a coastal colony of Herring Gulls close to an agricultural landscape in northwest England.

115 This variation in the presence of earthworms in diet samples may be due to differences in

116 accessibility to areas rich in earthworms and/or methodological differences between studies.

117 The findings from the current study on Lady Isle demonstrate that the prevalence of pellets

118 containing chaetae is much greater than previous research into the diet of Herring Gulls in

119 Scotland and Northern Ireland had suggested and supports the conclusion of Coulson &

120 Coulson (2008) that the methodology employed is key to determining the presence or

121 absence of earthworm chaetae in gull pellets.

122 Within-year comparison of pellets was not considered valid because some pellets containing

123 tightly wrapped terrestrial vegetation can remain relatively intact for over six weeks (T.

124 Pennycott, unpubl. data), and thus pellets collected in the chick-rearing phase could have

125 been produced during the egg incubation stage. Instead, between-year comparisons were

126 carried out. Significantly fewer pellets contained chaetae in 2018 (80 out of 139 pellets,

127 57.6%) than in 2019 (126 out of 175 pellets, 72.0%) (Pearson’s chi-squared test with Yates’

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128 correction, ꭕ2=6.54, n=314, P<0.05). Similarly, fewer pellets contained large numbers of

129 chaetae in 2018 (22 out of 139 pellets, 15.8%) than in 2019 (76 out of 175 pellets, 43.4%)

130 (Pearson’s chi-squared test with Yates’ correction, ꭕ2=26.22, n=314, P<0.01). These

131 differences possibly reflect the effects of weather conditions on earthworm numbers and

132 accessibility, with earthworms becoming more available after wet conditions (Vernon 1972,

133 Kruuk 1978). Total rainfall recorded at Prestwick (approximately 6.5 km from Lady Isle) for

134 May-July 2018 was 135 mm (the driest May-July recorded at Prestwick between 2010 and

135 2019), whereas total rainfall for May-July 2019 was 215 mm, close to the ten-year Prestwick

136 May-July mean of 212 mm (Scottish Environment Protection Agency

137 https://apps.sepa.org.uk/rainfall/data/index/344764 Accessed 26/08/19). Thus, the wetter

138 weather in 2019 could explain the higher proportion of pellets with earthworm chaetae in that

139 year.

140 In 89 pellets (28.3%), coarse terrestrial vegetation comprised at least 40% of the bulk of the

141 pellet (Figure 2). There was a highly significant association between the presence of much

142 coarse terrestrial vegetation and large numbers (>50 in 300 µl of sediment) of earthworm

143 chaetae in gull pellets (Pearson’s chi-squared test with Yates’ correction, ꭕ2=234.99, n=314,

144 P<0.01). Of the 89 pellets in which coarse vegetation made up at least 40% of the bulk of

145 the pellet, 85 (95.5%) had large numbers of earthworm chaetae. Conversely, of the

146 remaining 225 pellets with moderate, little or no coarse terrestrial vegetation, only 13 (5.8%)

147 contained large numbers of earthworm chaetae. Fragments of terrestrial arthropods (mostly

148 of the Order Coleoptera and earwigs of the Order Dermaptera) were found in 73

149 pellets (23.2%), although never comprising 25% of the bulk of any pellet, and there was a

150 highly significant association between the presence of much coarse terrestrial vegetation

151 and the detection of fragments of terrestrial arthropods (Pearson’s chi-squared test with

152 Yates’ correction, ꭕ2=58.54, n=314, P<0.01). These findings support earlier suggestions that

153 terrestrial vegetation had been accidentally picked up with food items (Harris 1965; Vernon

154 1970; Coulson & Coulson 2008). Based on the strong association between terrestrial

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155 vegetation and large numbers of earthworm chaetae, we recommend that, in future studies,

156 pellets with large quantities of coarse terrestrial vegetation be examined for the presence of

157 earthworm chaetae using appropriate methodology.

158 To enhance the detection of earthworm chaetae, we adopted a simple and inexpensive

159 methodology that could be used after minimal training. The technique also detected other

160 structures such as the microscopic remains of food items and the eggs of parasitic

161 helminths, including syngamid roundworms, hairworms and flukes. The trade-off for

162 simplicity was reduced sensitivity. It is highly unlikely that all the earthworm chaetae were

163 initially recovered from each pellet, and subsequent dilution factors further reduced the

164 sensitivity. However, the level of sensitivity was considered acceptable as earthworms

165 typically have eight chaetae for each of their 100-150 segments (Edwards & Bohlen 1996)

166 and thus a single earthworm can have many hundreds of chaetae. Similar or adapted

167 methodology could, therefore, be used in future studies looking at the composition of gull

168 pellets and diets.

169 Coulson & Coulson (2008) found that earthworms frequently contributed to the diet of Lesser

170 Black-backed Gulls breeding in an inland colony in southwest Scotland and recommended

171 that further studies be carried out in other large gulls. Our study has shown that the same is

172 true for Herring Gulls breeding in a coastal colony in southwest Scotland, although they also

173 consumed marine food and other terrestrial items such as cereal and refuse. This may

174 suggest that earthworms can constitute an important part of the Herring Gull’s diet even

175 when other commonly used food resources are available. It adds to our understanding of the

176 diet of Herring Gulls and provides a baseline against which findings from future studies may

177 be compared, should changes in agricultural land use, refuse management or local fishery

178 activity influence resource use by breeding Herring Gulls.

179

180 Acknowledgements

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181 SAC Consulting Veterinary Services, Auchincruive, Ayr, kindly provided access to the

182 Olympus binocular microscope. Roselle Smith, Klaudyna Maniszewska and James Scarlett

183 from Glasgow University assisted in the collection of some of the pellets. We are also

184 grateful to the anonymous reviewer whose comments greatly improved the text.

185

186

187 References

188 Coulson, J.C. & Coulson, B.A. 2008. Lesser black-backed gulls Larus fuscus nesting in an

189 inland urban colony: the importance of earthworms (Lumbricidae) in their diet. Bird Study 55:

190 297-303.

191

192 Eaton, M., Aebischer, N., Brown, A., Hearn, R., Lock, L., Musgrove, A., Noble, D.,

193 Stroud, D. & Gregory R. 2015. of Conservation Concern 4: the population status of

194 birds in the UK, Channel Islands and Isle of Man. British Birds 108: 708–746

195

196 Edwards, C.A. 1985. Production of feed protein from waste by earthworms.

197 Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences

198 310: 299-307

199

200 Edwards C.A. & Bohlen P.J. 1996. and Ecology of Earthworms. Chapman & Hall,

201 London.

202

203 Grant, D., Robertson, D., Nager, R. & McCracken, D. 2013. The status of breeding gulls

204 on Lady Isle, Ayrshire. 2012. Scottish Birds 33: 298-307.

205

206 Harris, M.P. 1970. The food of some Larus gulls. Ibis 107: 43-53

8

207

208 Kruuk, H. 1978. Foraging and spatial organization of the European , Meles

209 meles L. Behavioural Ecology and Sociobiology 4, 75–89.

210

211 Lindborg, V.A., Ledbetter, J.F., Walat, J.M. & Moffett, C. 2012. Plastic consumption and

212 diet of Glaucous-winged Gulls (Larus glaucescens). Marine Pollution Bulletin 64: 2351-2356.

213

214 Melville, D. 1974. Analysis of herring gull pellets collected in Co. Antrim. Seabird Report

215 1972-1974, pp40-46

216

217 Meyer R.M., Buckland P.C. & Monaghan P. 1994. The diet of the chough Pyrrhocorax

218 pyrrhocorax as indicated by analysis of digested prey remains. Avocetta 18: 95-106.

219

220 Mitchell, P.I., Newton, S.F., Ratcliffe, N. & Dunn, T.E. 2004. Seabird populations of Britain

221 and Ireland. T. & AD Poyser, London

222

223 Nogales, M., Zonfrillo, B. & Monaghan, P. 1995. Diets of adult and chick Herring Gulls

224 Larus argentatus argenteus on Ailsa Craig, south-west Scotland. Seabird 17: 56-63.

225

226 O’Hanlon, N.J., McGill, R.A.R. & Nager, R.G. 2017. Increased use of intertidal resources

227 benefits breeding success in a generalist gull species. Marine Ecology Progress Series 574:

228 193-210.

229

230 O'Mahony, E. 1935. Herring Gull eating earthworms. The Irish Naturalists' Journal 5: 309.

231

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232 Portielje, A.F.J. 1928. Zur Ethologie bzw. Psychologie der Silbermowe, Larus a. argentatus.

233 Pontopp. Ardea 17: 112-149

234

235 Sibly, R.M. & McCleery, R.H. 1983. Increase in weight of herring gulls while feeding.

236 Journal of Animal Ecology 52: 35-50.

237

238 Vernon, J.D.R. 1970. Food of the Common Gull on in autumn and winter. Bird

239 Study 17: 36-38

240

241 Vernon, J.D.R. 1972. Feeding habitats and food of the Black-headed and Common Gulls.

242 Part 2 – Food. Bird Study 19: 173-186

243

244

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245 Figure legends

246

247 Figure 1. Earthworm chaeta from gull pellet from Lady Isle. Bar=100 µm.

248

249

250 Figure 2. Much coarse terrestrial vegetation in pellet containing large numbers of earthworm

251 chaetae.

252

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