The composition of the aphid fauna (Insecta, Hemiptera) of the Royal Botanic Gardens, Kew.

At least a dozen species of aphids (Insecta, Hemiptera) of non-native origin have expanded their range in Europe, however the importance of botanic gardens in this phenomenon has not been studied previously in detail. As a case study, investigations on the species composition and host range of Aphidomorpha in the Royal Botanic Gardens, Kew, London, United Kingdom, were conducted over a period of twelve days, in June 2017. The inventory study was carried out in the collection of living plants, both in the gardens and the glasshouses and nurseries. In total, 94 taxa of Aphidomorpha are identified (one phylloxerid, one adelgid and 92 species of aphids). 20 species are regarded as alien to the European aphid fauna and among them nine are believed to be the first published records for Kew. 20 species are regarded as serious pests, capable of virus transmission. The list of host plants includes 155 taxa from 89 genera and 49 families. Ericolophium holsti (Takahashi), species of Asiatic origin associated with Rhododendron spp., was found for the first time in the field in the UK. Changes in the species composition of the aphid fauna in reference to the Eastop's studies in 1960s were discussed.

Introduction

Aphids, and closely related phylloxerids and adelgids (Insecta: Hemiptera: Aphidomorpha), are one of the most important groups of pests on cultivated and ornamental plants in the temperate regions. Possible effects include weakening and distortion of host plants, decreased growth rates, secretion of large amounts of honeydew and the transfer of plant viruses[1,2]. The fight against these insects is difficult due to their biology – holocyclic or, in some species, anholocyclic (i.e. without sexual phase) mode of reproduction and extremely high female fecundity (e.g. the peach-potato aphid Myzus persicae (Sulzer)[3] or the soybean aphid Aphis glycines Matsumura[4]). Another important feature is the host alternation: the presence of various generations in one season, including winged morphs responsible for dispersal and locating secondary (or new) hosts[2]. Intraspecific variation (e.g. in expression of sexuality in the bird cherry-oat aphid Rhopalosiphum padi L.[5]), the way in which foraging affects the physiology of the plants infested (including the influence of virus-induced changes[6]) and the observed lack of susceptibility to some insecticides[7], are additional factors, which have enabled aphids to exploit their food-plants. The species of non-native origin play a special role, especially in new areas, and under favourable conditions can become invasive[8,9] or can attack native[10] or endemic plants[11]. As many as 102 alien aphid species have been reported in Europe[12]. However, this number is continuously changing due to the increasing globalization of trade in plants and plant material, together with climate change[13,14]. Consequently, it leads to an increase in the introduction and spread of new and damaging plant pests and pathogens, causing serious losses in plant production[15-19]. On the other hand, the distribution of these insects is limited by the presence of the host plants, i.e. the alien aphids are absent where the host plant does not occur. Some alien aphids were introduced with the exotic host[20,21], thus, these (at least in some cases), are restricted to artificial habitats such as botanic gardens, greenhouses, parks and gardens in city areas. Among them, botanic gardens are classified as the oldest form of urban greenery, covering all aspects of plant conservation policy, practice and education and characterized by high plant diversity[22]. At the same time, botanic gardens are a small but significant part of the invasive plant problem[23-26]. However, their role in the spread of an organism as closely associated with the host plant as Aphidomorha, has not been sufficiently studied.

Created in 1759, the Royal Botanic Gardens, Kew (Kew), across its 132 hectares, grows one of the largest and most diverse living plant collections in the world. This is London’s largest UNESCO World Heritage Site, designated in 2003, with more than 100,000 living plants. These represent numerous and diverse plant families with extensive collections of trees, herbaceous, alpine and economic plants from most parts of the world, located in distinctive areas and glasshouses, and as such is an excellent target for collecting Aphidomorpha. The first list of aphids, collected by Laing in Kew, was published in 1920[27]. Later, in 1962 and 1965, further contributions to the aphid fauna of Kew were published by Eastop[28,29]. The first list brings the total number of aphids known from Kew to 91 taxa, the second one comprised 77 taxa. In total, over four years of collecting (1958, 1960, 1961 and 1962), 142 taxa of aphids were listed. Some of them were marked as introduced or even as a first record for Europe. With a few minor exceptions[30-32], further intensive studies on the aphid fauna of Kew have not been carried out.

The aim of the paper is to ascertain the number of Aphidomorpha species infesting plants in Kew and see how the aphid fauna has changed since Eastop’s research 60 years ago. Moreover, it will allow identification of non-native species and whether the number of introductions of aliens has changed. It will also determine the number of economically important species of aphids.

Results

The composition of the Aphidomorpha fauna of the Royal Botanic Gardens, Kew

A total of 221 aphid samples were collected during the twelve days in Kew. In total, 94 taxa of Aphidomorpha were identified. Adelgidae and Phylloxeridae were represented by a single species each, whereas there were 92 taxa from Aphididae (species and subspecies) belonging to nine subfamilies: Eriosomatinae, Anoeciinae, Mindarinae, Drepanosiphinae, Phyllaphidinae, Calaphidinae, Chaitophorinae, Aphidinae and Lachninae. Aphidinae, the most numerous subfamily, was represented by 20 genera and 44 species. The richest genus represented in the collection was Aphis Linnaeus (11 species). The subfamily Calaphidinae (21 species) was most frequently represented by species belonging to the tribe Panaphidini (14 species). The fewest species in Aphididae were from the subfamilies Anoeciinae, Mindarinae, Drepanosiphinae and Phyllaphidinae.

In only seven locations surveyed (Aquatic Garden, Duke’s Garden, Lake, Mediterranean Garden, Pond, Rhododendron Dell, Redwood Grove) the number of species was the same as the number of samples collected. In other locations, the number of samples was slightly higher than the number of species, the highest in the Populus collection (5 species and 14 samples). The two richest locations for aphid species and samples were the Arboretum Nursery (15 species and 17 samples) and the Plant Family Beds (12 species and 16 samples). In other locations, from 1 to 10 species (Fig. 1) and 1 to 14 samples were found. In these locations, all samples were collected in outdoor conditions, except for a few samples collected in a greenhouses in Arboretum Nursery or Tropical Nursery. In contrast, in indoor conditions in the Palm House, Water Lily House, Princess of Wales Conservatory or Davies Alpine House no samples were collected.

Figure 1

Collecting area and the number of collected species. The abbreviations denote as follow: (1) AColl. – Acer spp. collection; (2) ARBN – Arboretum Nursery; (3) BColl. – Betula spp. collection; (4) PColl. – Populus spp. collection; (5) QColl. – Quercus spp. collection; (6) AG – Aquatic Garden; (7) BG – Bamboo Garden; (8) DG – Duke’s Garden; (9) JG – Japanese Garden; (10) L – Lake; (11) MG – Mediterranean Garden; (12) NO – near Orangery; (13) P – Pond; (14) PFB – Plant Family Beds; (15) Pi – Pinetum; (16) RD – Rhododendron Dell; (17) RG – Rock Garden; (18) RK – Royals Kitchen; (19) ReG – Redwood Grove; (20) RoG – Rose Garden; (21) SVP – Student Vegetables Plot; (22) TRON – Tropical Nursery.

Alien aphid species

20 species were regarded as alien to the European aphid fauna and among them nine are believed to be the first published records for Kew: Aphis (Aphis) gossypii Glover, 1877, A. (A.) spiraecola Patch, 1914, A. (Toxoptera) aurantii Boyer de Fonscolombe, 1841, Chaetosiphon (Pentatrichopus) fragaefolii (Cockerell, 1901), Ericolophium holsti (Takahashi, 1935), Illinoia (Illinoia) liriodendri (Monell, 1879), Illinoia (Masonaphis) lambersi (MacGillivray, 1960), Macrosiphum (Macrosiphum) albifrons Essig, 1911, Neotoxoptera formosana (Takahashi, 1921).

Pest species

20 species were regarded as serious pests, capable of virus transmission: Aphis (Aphis) fabae Scopoli, 1763, A. (A.) gossypii, A. (A.) pomi De Geer, 1773, A. (A.) spiraecola, A. (Bursaphis) grossulariae Kaltenbach, 1843, A. (Toxoptera) aurantii, Hyalopterus pruni (Geoffroy, 1762), Rhopalosiphum nymphaeae (Linnaeus, 1761), Acyrthosiphon (Acyrthosiphon) pisum Harris, 1776, Brachycaudus (Prunaphis) cardui (Linnaeus, 1758), Cavariella aegopodii (Scopoli, 1763), Chaetosiphon (Pentatrichopus) fragaefolii, Cryptomyzus (Cryptomyzus) ribis (Linnaeus, 1758), Dysaphis (Dysaphis) tulipae (Boyer de Fonscolombe, 1841), Macrosiphum (Macrosiphum) euphorbiae (Thomas, 1878), M. (M.) rosae (Linnaeus, 1758), Megoura viciae Buckton, 1876, Myzus (Myzus) cerasi (Fabricius, 1775), M. (M.) ornatus Laing, 1932, M. (Nectarosiphon) persicae (Sulzer, 1776).

Although the garden staff use mostly natural methods to control such serious pests (i.e. the biocontrols of different mixes of parasitoid wasps like Aphidius colemani Viereck, 1912, A. ervi Haliday, 1834, A. matricariae Haliday, 1834 Aphelinus abdominalis (Dalman, 1820), Praon volucre (Haliday, 1833), Ephedrus cerasicola Starý, 1962 and the predatory fly Aphidoletes aphidimyza (Rondani, 1847) or lace wing Chrysoperla carnea (Stephens, 1836) (P. Rees pers. comm.), without spreading aggressive insecticides, most infected host plants did not have visible damage. The exception were some plants in the Student Vegetables Plot e.g. Prunus sp., Solanum lycopersicon, Solanum tuberosum and in the Arboretum Nursery e.g. Acer palmatum ‘BiHoo’, Ribes orientalis, where feeding aphids promoted curled and distorted leaves as well as chlorosis or honeydew deposits. In the collection of living plants grown out in the Gardens feeding Phylloxera glabra (von Heyden, 1837) had caused necrotic spots on the leaves of Quercus dentata in the Quercus collection.

Host-plants associations

The list of host plants includes 155 taxa from 89 genera and 49 families and is summarised in Table 1. The most frequently infested plant species belong to Fagaceae (20 species, 25 samples), Betulaceae and Sapindaceae (13 species and 15 samples each). The most frequently infested genera were Quercus (10 species, 21 samples) and Acer (6 species, 15 samples). The highest diversity of aphid species was observed on Quercus and consisted of 10 species. Aphis (A.) fabae and Macrosiphum (M.) euphorbiae were the most frequent aphid species found with the widest host range. Whereas A. (A.) fabae was found on colonized about 30 host plants, M. (M.) euphorbiae was only associated with ten hosts. The remaining species were associated with one to four host plants (Table 1).

Table 1

Host plant index and associated Aphidomorpha species collected in the Royal Botanic Gardens, Kew.

No.	Host plant taxon	Aphidomorpha taxon
1	Abies pinsapo Boiss.	Mindarus abietinus
2	Acer campestre L.	Periphyllus hirticornis, Periphyllus lyropictus
3	Acer griseum (Franch.) Pax	Periphyllus acericola
4	Acer negundo L.	Periphyllus testudinaceus
5	Acer oblongum Wall. ex DC.	Drepanosiphum platanoidis
6	Acer oliverianum Pax	Periphyllus testudinaceus
7	Acer palmatum Thunb.	Periphyllus californiensis
8	Acer palmatum Thunb. ‘Bi Hoo’	Periphyllus californiensis, Periphyllus testudinaceus
9	Acer palmatum Thunb. ‘Senkaki’	Periphyllus testudinaceus,
10	Acer pseudoplatanus L.	Drepanosiphum platanoidis
11	Acer heldreichii subsp. trautvetteri (Medw.) A.E. Murray	Drepanosiphum platanoidis, Periphyllus acericola
12	Achillea millefolium L. ‘Pink Grapefruit’	Brachycaudus (Prunaphis) cardui, Macrosiphoniella (Macrosiphoniella) absinthii
13	Achillea sp.	Aphis (Aphis) fabae, Macrosiphoniella (Macrosiphoniella) millefolii
14	Acorus calamus L.’Variegatus’	Rhopalosiphum nymphaeae
15	Aesculus × hybrida DC.	Periphyllus testudinaceus
16	Aesculus turbinata Blume	Aphis (Aphis) fabae
17	Ageratina ligustrina (DC.) R.M. King & H. Rob.	Aphis (Aphis) fabae
18	Allium nutans L.	Neotoxoptera formosana
19	Alnus glutinosa (L.) Gaertn.	Pterocallis (Pterocallis) maculata
20	Alnus rubra Bong.	Pterocallis (Pterocallis) alni
21	Aquilegia vulgaris L.	Macrosiphum (Macrosiphum) euphorbiae
22	Arctium lappa L.	Aphis (Aphis) fabae
23	Artemisia absinthium L.	Macrosiphoniella (Macrosiphoniella) absinthii
24	Bambusa sp.	Takecallis arundinariae
25	Betula utilis subsp. albosinensis (Burkill) Ashburner & McAll.	Symydobius oblongus
26	Betula dauurica Pall.	Calaphis flava
27	Betula ermanii Cham.	Calaphis flava
28	Betula grossa Siebold & Zucc.	Callipterinella calliptera
29	Betula pubescens var. litwinowii (Doluch.) Ashburner & McAll.	Symydobius oblongus
30	Betula pendula Roth	Euceraphis betulae
31	Betula pendula subsp. mandshurica (Regel) Ashburner & McAll.	Clethrobius comes
32	Betula pendula subsp. szechuanica (C.K. Schneid.) Ashburner & McAll.	Euceraphis betulae
33	Betula utilis D. Don	Symydobius oblongus
34	Betula utilis D. Don var. prattii Burkill	Betulaphis quadrituberculata, Calaphis flava, Monaphis antennata
35	Bremeria landia var. holosericea (Sm.) A.P. Davis & Razafim.	Aphis (Aphis) spiraecola
36	Camellia japonica L.	Aphis (Toxoptera) aurantii
37	Carpinus cordata Blume var. chinensis Franch.	Myzocallis (Myzocallis) carpini
38	Castanea sativa Mill.	Myzocallis (Agrioaphis) castanicola,
39	Cedrus atlantica (Endl.) Manetti ex Carrière	Cinara (Cinara) cedri
40	Cedrus libani A. Rich.	Cinara (Cinara) cedri
41	Celastrus orbiculatus Thunb.	Aphis (Aphis) fabae
42	Cistus laurifolius L.	Aphis (Aphis) fabae
43	Clianthus puniceus (G. Don) Sol. ex Lindl.	Acyrthosiphon (Acyrthosiphon) malvae
44	Cornus mas L.	Macrosiphum (Macrosiphum) euphorbiae
45	Cornus sp.	Anoecia corni
46	Corylus avellana L.	Myzocallis (Myzocallis) coryli, Corylobium avellanae
47	Crataegus pentagyna Waldst. & Kit. ex Willd.	Aphis (Aphis) pomi
48	Crossandra pungens Lindau	Myzus (Nectarosiphon) persicae
49	Cynara cardunculus L.	Aphis (Aphis) fabae
50	Digitalis purpurea L.	Aphis (Aphis) fabae
51	Echium amoenum Fisch. & C.A. Mey.	Aphis (Aphis) fabae
52	Erythranthe naiandina (J.M. Watson & C. Bohlen) G.L. Nesom	Aphis (Aphis) fabae
53	Eschscholzia californica Cham.	Aphis (Aphis) fabae
54	Euphorbia characias L.	Macrosiphum (Macrosiphum) euphorbiellum
55	Fagus sylvatica L.	Phyllaphis fagi
56	Fagus sylvatica ‘Tricolor’	Phyllaphis fagi
57	Fatsia japonica (Thunb) Decne. & Planch.	Aphis (Aphis) fabae
58	Foeniculum vulgare Mill.	Cavariella aegopodii
59	Fragaria × ananassa (Duchesne ex Weston) Duchesne ex Rozier	Chaetosiphon (Pentatrichopus) fragaefolii
60	Hedera sp.	Aphis (Aphis) fabae
61	Hedlundia minima (Ley) Sennikov & Kurtto	Aphis (Aphis) pomi
62	Ilex sp.	Aphis (Aphis) ilicis
63	Iris pallida Lam.	Macrosiphum (Macrosiphum) euphorbiae
64	Iris sp.	Aphis (Aphis) newtoni, Rhopalosiphum nymphaeae, Dysaphis (Dysaphis) tulipae, Macrosiphum (Macrosiphum) euphorbiae
65	Juglans regia L.	Chromaphis juglandicola, Panaphis juglandis
66	Koelreuteria bipinnata Franch.	Aphis (Aphis) fabae
67	Lathyrus montanus Bernh.	Megoura viciae
68	Lathyrus sp.	Acyrthosiphon (Acyrthosiphon) pisum
69	Leptodermis pilosa Diels	Aphis (Aphis) gossypii
70	Leucanthemum × superbum (Bergmans ex J.W.Ingram) D.H. Kent	Aphis (Aphis) fabae, Brachycaudus (Prunaphis) cardui
71	Liriodendron tulipifera L.	Illinoia (Illinoia) liriodendri
72	Lonicera implexa Aiton.	Hyadaphis passerinii
73	Lupinus ehrenbergii Schltdl. var. ehrenbergii	Macrosiphum (Macrosiphum) albifrons
74	Lupinus ‘My Castle’	Macrosiphum (Macrosiphum) albifrons
75	Lupinus ‘The Governor’	Macrosiphum (Macrosiphum) albifrons
76	Lychnis coronaria (L.) Desr.	Brachycaudus (Acaudus) lychnidis
77	Malus domestica (Sukow) Borkh.	Dysaphis (Pomaphis) plantaginea
78	Malus tschonoskii (Maxim.) C.K. Schneid.	Aphis (Aphis) pomi
79	Matricaria chamomilla L.	Brachycaudus (Prunaphis) cardui
80	Monarda fistulosa L. var menthifolia (Graham) Fernald	Aphis (Aphis) fabae
81	Musa sp.	Aphis (Aphis) fabae
82	Nelumbo nucifera Gaertn.	Macrosiphum (Macrosiphum) euphorbiae
83	Oenothera magellanica Phil.	Aphis (Bursaphis) grossulariae
84	Oxylobium lineare Benth.	Aphis (Aphis) gossypii
85	Paulownia fargesii Franch.	Macrosiphum (Macrosiphum) euphorbiae
86	Phragmites australis (Cav.) Trin. ex Steud.	Hyalopterus pruni
87	Phyllostachys aurea (André) Rivière & C. Rivière	Takecallis arundinariae
88	Picea sp.	Adelges laricis, Cinara (Cinara) piceae
89	Pieris japonica (Thunb.) D. Don ex G. Don	Aphis (Aphis) fabae
90	Pinus nigra J.F. Arnold	Cinara (Cinara) pini, Cinara (Schizolachnus) pineti
91	Pinus patula Schiede ex Schltdl. & Cham.	Cinara (Cinara) pini
92	Pinus sylvestris L.	Cinara (Cinara) pinea
93	Pinus sylvestris L. ‘Beuvronensis’	Cinara (Cinara) pilosa
94	Polyspora sp.	Aphis (Aphis) fabae
95	Populus balsamifera L.	Pemphigus spyrothecae, Pterocomma populeum
96	Populus × canadensis Moench	Chaitophorus leucomelas, Pterocomma populeum
97	Populus × canescens (Ait.) Sm.	Chaitophorus populeti
98	Populus incrassata Dode	Pterocomma populeum
99	Populus grandidentata Michx.	Chaitophorus leucomelas, Pterocomma populeum
100	Populus nigra L.	Chaitophorus leucomelas, Pterocomma populeum
101	Populus nigra L. subsp. betulifolia (Pursh) W. Wettst. ex Buttler & Hand	Thecabius affinis, Chaitophorus leucomelas, Pterocomma populeum
102	Primula sec. Proliferae	Myzus (Myzus) ornatus
103	Primula sp.	Myzus (Myzus) ornatus
104	Prunus serrulata Lindl. ‘Amanogawa’	Myzus (Myzus) cerasi
105	Prunus × yedoensis Matsum.	Myzus (Nectarosiphon) persicae
106	Pseudosasa japonica (Siebold & Zucc. ex Steud.) Makino ex Nakai	Takecallis arundicolens
107	Pyrus sp.	Melanaphis pyraria
108	Rosa ‘Jacques Cartier’	Macrosiphum (Macrosiphum) rosae
109	Rosa ‘Tuscany’	Macrosiphum (Macrosiphum) rosae
110	Rosa sp.	Macrosiphum (Macrosiphum) rosae, Maculolachnus submacula
111	Quercus cornelius-mulleri Nixon & K. P. Steele	Lachnus pallipes
112	Quercus chenii Nakai	Thelaxes dryophila
113	Quercus dentata Thunb.	Phylloxera glabra
114	Quercus faginea Lam.	Lachnus roboris
115	Quercus falcata Michx.	Lachnus roboris
116	Quercus germana Schltdl. & Cham.	Thelaxes dryophila
117	Quercus × hispanica Lam. ‘Lucombeana'	Tuberculatus (Tuberculoides) annulatus
118	Quercus ilex L.	Thelaxes suberi
119	Quercus mongolica Fisch. ex Ledeb.	Myzocallis (Agrioaphis) castanicola
120	Quercus nigra L.	Lachnus roboris
121	Quercus palustris Munchh.	Lachnus pallipes
122	Quercus pontica K. Koch	Lachnus roboris
123	Quercus robur L.	Myzocallis (Agrioaphis) castanicola, Myzocallis (Myzocallis) boerneri, Tuberculatus (Tuberculatus) querceus, Tuberculatus (Tuberculoides) annulatus
124	Quercus rugosa Née	Thelaxes suberi
125	Quercus × sargentii ‘Thomas’ Rehder	Lachnus roboris
126	Quercus sp.	Lachnus roboris
127	Rheum palmatum L.	Aphis (Aphis) fabae
128	Rheum rhabarbarum L.	Aphis (Aphis) fabae
129	Rhododendron ‘Golden Sunset’	Illinoia (Masonaphis) lambersi
130	Rhododendron sp.	Aphis (Aphis) spiraecola, Ericolophium holsti
131	Ribes nigrum L.	Cryptomyzus (Cryptomyzus) ribis
132	Ribes orientale Desf.	Cryptomyzus (Cryptomyzus) korschelti
133	Ribes sp.	Aphis (Bursaphis) grossulariae
134	Rudbeckia sp.	Aphis (Aphis) fabae
135	Salix aegyptiaca L.	Aphis (Aphis) farinosa
136	Salix × fragilis L.	Chaitophorus salijaponicus niger
137	Salix lasiolepis Benth.	Chaitophorus horii beuthani, Pterocomma pilosum
138	Salix myrsinifolia Salisb.	Chaitophorus vitellinae
139	Salix prolixa Andersson	Aphis (Aphis) farinosa
140	Sasa palmata (Burb.) E.G. Camus	Takecallis arundinariae, Takecallis taiwanus
141	Saurauia napaulensis DC.	Myzus (Myzus) ornatus
142	Sedum telephium L.	Aphis (Aphis) sedi, Macrosiphum (Macrosiphum) hellebori
143	Sequoia sempervirens (D. Don) Endl.	Illinoia (Illinoia) morrisoni
144	Silybum marianum (L.) Gaertn.	Aphis (Aphis) fabae
144	Skimia sp.	Macrosiphum (Macrosiphum) euphorbiae
146	Solanum lycopersicum L.	Macrosiphum (Macrosiphum) euphorbiae
147	Solanum tuberosum L.	Aphis (Aphis) fabae
148	Tilia tomentosa Moench	Eucallipterus tiliae
149	Verbascum densiflorum Bertol.	Aphis (Aphis) verbasci
150	Viburnum farreri Stearn	Aphis (Aphis) fabae
151	Viburnum sp.	Aphis (Aphis) fabae
152	Vicia faba L.	Aphis (Aphis) fabae
153	Wahlenbergia angustifolia (Roxb.) A. DC.	Macrosiphum (Macrosiphum) euphorbiae
154	Yucca glauca Nutt.	Aphis (Aphis) fabae
155	Yucca sp.	Aphis (Aphis) fabae, Macrosiphum (Macrosiphum) euphorbiae

The list of all collected species is presented in Table 2 and the Supplementary Material. In the Supplementary Material Aphidomorpha species were listed in systematic category alphabetically and sampling data for each aphid species include: locality, host plant, date and the unique sample number.

Table 2

Aphidomorpha collected during Eastop’s (1962, 1965) and the present (2017) study in the Royal Botanic Gardens, Kew.

No.	Taxon	Eastop		2017
		1962	1965
	ADELGIDAE: ADELGINAE
1	Adelges laricis Vallot, 1836			+
	PHYLLOXERIDAE: PHYLLOXERINAE
2	Phylloxera glabra (von Heyden, 1837)			+
	APHIDIDAE: ERIOSOMATINAE
3	Eriosoma patchiae patchiae (Bӧrner & Blunck, 1916)	+	+
4	Eriosoma patchiae lanuginosum (Hartig, 1839)		+
5	Pemphigus bursarius (Linnaeus, 1758)*	+
6	Pemphigus spyrothecae Passerini, 1856	+		+
7	Thecabius affinis (Kaltenbach, 1843)*		+	+
	APHIDIDAE: ANOECIINAE
8	Anoecia corni (Fabricius, 1775)*	+		+
	APHIDIDAE:THELAXINAE
9	Glyphina betulae (Linnaeus, 1758)		+
10	Thelaxes dryophila (Schrank, 1801)*	+	+	+
11	Thelaxes suberi (Del Guercio, 1911)		+	+
	APHIDIDAE: MINDARINAE
12	Mindarus abietinus Koch, 1857	+		+
	APHIDIDAE: DREPANOSIPHINAE
13	Drepanosiphum platanoidis (Schrank, 1801)*	+		+
	APHIDIDAE:PHYLLAPHIDINAE
14	Phyllaphis fagi Linnaeus, 1767*	+		+
	APHIDIDAE:CALAPHIDINAE: Calaphidini
15	Betulaphis quadrituberculata (Kaltenbach, 1843)		+	+
16	Calaphis flava Mordvilko, 1928*	+	+	+
17	Callipterinella calliptera (Hartig, 1841)			+
18	Callipterinella minutissima (Stroyan, 1953)		+
19	Clethrobius comes (Walker, 1848)			+
20	Euceraphis betulae (Koch, 1855)			+
21	Euceraphis punctipennis (Zetterstedt, 1828)*	+	+
22	Monaphis antennata (Kaltenbach, 1843)		+	+
23	Symydobius oblongus (Von Heyden, 1837)			+
	APHIDIDAE:CALAPHIDINAE: Panaphidini
24	! Chromaphis juglandicola (Kaltenbach, 1843)*		+	+
25	Eucallipterus tiliae (Linnaeus, 1758)*	+		+
26	Myzocallis (Agrioaphis) castanicola Baker, 1917*	+		+
27	Myzocallis (Myzocallis) boerneri Stroyan, 1957	+		+
28	Myzocallis (Myzocallis) carpini (Koch, 1855)		+	+
29	Myzocallis (Myzocallis) coryli (Goeze, 1778)*		+	+
30	Myzocallis (Myzocallis) schreiberi Hille Ris Lambers & Stroyan, 1959		+
31	! Panaphis juglandis (Goeze, 1778)*		+	+
32	Pterocallis (Pterocallis) alni (De Geer, 1773)			+
33	Pterocallis (Pterocallis) maculata (von Heyden, 1837)			+
34	! Takecallis arundicolens (Clarke, 1903)		+	+
35	! Takecallis arundinariae (Essig, 1917)		+	+
36	! Takecallis taiwanus (Takahashi, 1926)		+	+
37	Tuberculatus (Tuberculatus) querceus (Kaltenbach, 1843)*	+		+
38	Tuberculatus (Tuberculoides) annulatus (Hartig, 1841)	+		+
	APHIDIDAE:SALTUSAPHIDINAE
39	Subsaltusaphis sp.		+
	APHIDIDAE:CHAITOPHORINAE: Chaitophorini
40	Chaitophorus capreae (Mosley, 1841)*	+	+
41	Chaitophorus horii beuthani (Bӧrner, 1950)			+
42	Chaitophorus leucomelas Koch, 1854*	+		+
43	Chaitophorus populeti (Panzer, 1804)			+
44	Chaitophorus salijaponicus niger Mordvilko, 1929	+		+
45	Chaitophorus vitellinae (Schrank, 1801)			+
46	Periphyllus acericola (Walker, 1848)			+
47	! Periphyllus californiensis (Shinji, 1917)	+		+
48	Periphyllus hirticornis (Walker, 1848)		+	+
49	Periphyllus lyropictus (Kessler, 1886)			+
50	Periphyllus testudinaceus (Fernie, 1852)*	+	+	+
	APHIDIDAE:CHAITOPHORINAE: Siphini
51	Caricosipha paniculatae Bӧrner, 1939		+
	APHIDIDAE:APHIDINAE: Aphidini
52	Aphis (Aphis) comosa (Bӧrner, 1950)		+
53	Aphis (Aphis) craccae Linnaeus, 1758	+
54	Aphis (Aphis) cytisorum sarothamni Franssen, 1928		+
55	Aphis (Aphis) fabae Scopoli, 1763*	+	+	+
56	Aphis (Aphis) fabae solanella Theobald, 1914	+
57	Aphis (Aphis) farinosa Gmelin, 1790			+
58	Aphis (Aphis) genistae Scopoli, 1763	+
59	! Aphis (Aphis) gossypii Glover, 1877			+
60	Aphis (Aphis) ilicis Kaltenbach, 1843	+		+
61	Aphis (Aphis) nasturtii Kaltenbach, 1843	+
62	Aphis (Aphis) newtoni Theobald, 1927			+
63	Aphis (Aphis) pomi De Geer, 1773			+
64	Aphis (Aphis) praeterita Walker, 1849	+
65	Aphis (Aphis) salicariae Koch, 1855	+
66	Aphis (Aphis) sedi Kaltenbach, 1843			+
67	! Aphis (Aphis) spiraecola Patch, 1914			+
68	Aphis (Aphis) verbasci Schrank, 1801			+
69	Aphis (Bursaphis) epilobiaria Theobald, 1927	+
70	Aphis (Bursaphis) epilobii Kaltenbach, 1843*	+
71	Aphis (Bursaphis) grossulariae Kaltenbach, 1843			+
72	! Aphis (Toxoptera) aurantii Boyer de Fonscolombe, 1841			+
73	Hyalopterus pruni (Geoffroy, 1762)		+	+
74	Melanaphis luzulella (Hille Ris Lambers, 1947)	+
75	Rhopalosiphum nymphaeae (Linnaeus, 1761)		+	+
76	Rhopalosiphum oxyacanthae (Schrank, 1801)*	+	+
77	Rhopalosiphum padi (Linnaeus, 1758)	+	+
78	Schizaphis (Paraschizaphis) scirpi (Passerini, 1874)		+
	APHIDIDAE:APHIDINAE: Macrosiphini
79	Acyrthosiphon (Acyrthosiphon) loti (Theobald, 1913)	+
80	Acyrthosiphon (Acyrthosiphon) malvae (Mosley, 1841)*	+	+	+
81	Acyrthosiphon (Acyrthosiphon) pisum Harris, 1776*	+	+	+
82	Aulacorthum solani (Kaltenbach, 1843)*	+	+
83	Brachycaudus (Acaudus) lychnidis (Linnaeus, 1758)*		+	+
84	Brachycaudus (Brachycaudus) helichrysi (Kaltenbach, 1843)*	+
85	Brachycaudus (Prunaphis) cardui (Linnaeus, 1758)			+
86	Brachycolus cucubali (Passerini, 1863)	+
87	Brevicoryne brassicae (Linnaeus, 1758)*	+
88	Capitophorus hippophaes (Walker, 1852)	+	+
89	Capitophorus inulae (Passerini, 1860)	+
90	Capitophorus pakansus Hottes & Frison, 1931	+
91	Cavariella aegopodii (Scopoli, 1763)*	+	+	+
92	Cavariella archangelicae (Scopoli, 1763)		+
93	Cavariella pastinacae (Linnaeus, 1758)		+
94	Cavariella theobaldi (Gillete & Bragg, 1918)	+	+
95	Ceruraphis eriophori (Walker, 1848)		+
96	! Chaetosiphon (Pentatrichopus) fragaefolii (Cockerell, 1901)			+
97	Coloradoa achilleae Hille Ris Lambers, 1939		+
98	Coloradoa tanacetina (Walker, 1850)	+
99	Corylobium avellanae (Schrank, 1801)*		+	+
100	Cryptaphis poae (Hardy, 1850)		+
101	Cryptomyzus (Cryptomyzus) korschelti Bӧrner, 1938			+
102	Cryptomyzus (Cryptomyzus) ribis (Linnaeus, 1758)			+
103	Delphiniobium junackianum (Karsch, 1887)	+	+
104	Diuraphis (Holcaphis) holci (Hille Ris Lambers, 1956)		+
105	Dysaphis (Dysaphis) apifolia (Theobald, 1923)	+
106	Dysaphis (Dysaphis) tulipae (Boyer de Fonscolombe, 1841)			+
107	Dysaphis (Pomaphis) pyri (Boyer de Fonscolombe, 1841)*	+	+
108	Dysaphis (Pomaphis) plantaginea (Passerini, 1860)			+
109	Elatobium abietinum (Walker, 1849)*		+
110	! Ericolophium holsti (Takahashi, 1935)			+
111	Hyadaphis passerinii (Del Guercio, 1911)			+
112	Hyalopteroides humilis (Walker, 1852)		+
113	Hyperomyzus (Hyperomyzus) lactucae (Linnaeus, 1758)	+
114	Hyperomyzus (Hyperomyzus) lampsanae (Bӧrner, 1932)	+
115	Hyperomyzus (Neonasonovia) picridis (Bӧrner & Blunck, 1916)		+
116	! Illinoia (Illinoia) andromedae (MacGillivray, 1953)	+
117	! Illinoia (Illinoia) goldmayrae (Knowlton, 1938)	+	+
118	! Illinoia (Illinoia) liriodendri (Monell, 1879)			+
119	! Illinoia (Illinoia) morrisoni (Swain, 1918)	+		+
120	! Illinoia (Masonaphis) lambersi (MacGillivray, 1960)			+
121	Linosiphon galiophagum (Wimshurst, 1923)		+
122	Liosomaphis berberidis (Kaltenbach, 1843)*	+
123	Lipaphis (Lipaphis) erysimi (Kaltenbach, 1843)	+
124	Longicaudus trirhodus (Walker, 1849)	+
125	Macrosiphoniella (Macrosiphoniella) abrotani (Walker, 1852)	+
126	Macrosiphoniella (Macrosiphoniella) absinthii (Linnaeus, 1758)	+	+	+
127	Macrosiphoniella (Macrosiphoniella) artemisiae (Boyer de Fonscolombe, 1841)		+
128	Macrosiphoniella (Macrosiphoniella) millefolii (De Geer, 1773)*	+		+
129	! Macrosiphoniella (Macrosiphoniella) sanborni (Gillette, 1908)	+
130	Macrosiphoniella (Macrosiphoniella) sejuncta (Walker, 1848)		+
131	Macrosiphoniella (Macrosiphoniella) tapuskae (Hottes & Frison, 1931)		+
132	Macrosiphoniella (Phalangomyzus) oblonga (Mordvilko, 1901)	+	+
133	! Macrosiphum (Macrosiphum) albifrons Essig, 1911			+
134	Macrosiphum (Macrosiphum) cholodkovskyi (Mordvilko, 1909)	+
135	Macrosiphum (Macrosiphum) daphnidis Bӧrner, 1950	+
136	! Macrosiphum (Macrosiphum) euphorbiae (Thomas, 1878)*	+	+	+
137	Macrosiphum (Macrosiphum) euphorbiellum Theobald, 1917			+
138	Macrosiphum (Macrosiphum) funestum (Macchiati, 1885)		+
139	Macrosiphum (Macrosiphum) hellebori Theobald &Walton, 1923	+		+
140	Macrosiphum (Macrosiphum) rosae (Linnaeus, 1758)*	+		+
141	Macrosiphum (Macrosiphum) stellariae Theobald, 1913		+
142	Megoura viciae Buckton, 1876		+	+
143	Melanaphis pyraria (Passerini, 1861)			+
144	Metopeurum fuscoviride Stroyan, 1950	+
145	Metopolophium (Metopolophium) dirhodum (Walker, 1849)*	+
146	Myzaphis rosarum (Kaltenbach, 1843)		+
147	Myzus (Myzus) cerasi (Fabricius, 1775)			+
148	Myzus (Myzus) lythri (Schrank, 1801)	+
149	! Myzus (Myzus) ornatus Laing, 1932	+	+	+
150	! Myzus (Nectarosiphon) persicae (Sulzer, 1776)*	+		+
151	! Myzus (Sciamyzus) ascalonicus Doncaster, 1946	+	+
152	! Myzus (Sciamyzus) cymbalariae Stroyan, 1954	+
153	Nasonovia (Nasonovia) ribisnigri (Mosley, 1841)*	+
154	! Neomyzus circumflexus (Buckton, 1876)*	+
155	! Neotoxoptera formosana (Takahashi, 1921)			+
156	Ovatomyzus stachyos Hille Ris Lambers, 1947		+
157	Ovatus (Ovatus) crataegarius (Walker, 1850)	+
158	Ovatus (Ovatus) insitus (Walker, 1849)	+
159	Pterocomma pilosum Buckton, 1879	+		+
160	Pterocomma populeum (Kaltenbach, 1843)	+	+	+
161	Pterocomma rufipes (Hartig, 1841)		+
162	Sitobion (Sitobion) avenae (Fabricius, 1775)*	+	+
163	Sitobion (Sitobion) fragariae (Walker, 1848)*		+
164	! Sitobion (Sitobion) luteum (Buckton, 1876)	+
165	Tubaphis ranunculina (Walker, 1852)		+
166	Uroleucon (Uroleucon) achilleae (Koch, 1855)*	+
167	Uroleucon (Uroleucon) cichorii (Koch, 1855)	+
168	Vesiculaphis theobaldi Takahashi, 1930		+
169	! Wahlgreniella arbuti (Davidson, 1910)		+
	LACHNINAE: Eulachnini
170	! Cinara (Cinara) cedri Mimeur, 1936			+
171	Cinara (Cinara) cuneomaculata (Del Guercio, 1909)		+
172	Cinara (Cinara) pectinatae (Nӧrdlinger, 1880)	+
173	Cinara (Cinara) piceae (Panzer, 1800)			+
174	Cinara (Cinara) pilicornis (Hartig, 1841)*	+	+
175	Cinara (Cinara) pilosa (Zetterstedt, 1940)			+
176	Cinara (Cinara) pinea (Mordvilko, 1895)*		+	+
177	Cinara (Cinara) pini (Linnaeus, 1758)			+
178	Cinara (Cupressobium) juniperi (De Geer, 1773)*	+
179	Cinara (Schizolachnus) pineti (Fabricius, 1781)	+		+
180	Eulachnus agilis (Kaltenbach, 1843)*	+
181	Eulachnus brevipilosus Bӧrner, 1940		+
182	Eulachnus rileyi (Williams, 1911)	+
	LACHNINAE: Lachnini
183	Lachnus pallipes (Hartig, 1841)			+
184	Lachnus roboris (Linnaeus, 1758)			+
185	Maculolachnus submacula (Walker, 1848)			+
	LACHNINAE: Tuberolachnini
186	Tuberolachnus salignus (Gmelin, 1790)	+

An exclamation mark [!] beside the name denotes alien species; a star mark * indicates species listed by Laing (1920).

Discussion

According to Botanic Gardens Conservation International (BGCI), the Royal Botanic Gardens, Kew includes globally significant ex situ plant collections, covering approximately a third of known plant diversity, world-class seed banks, glasshouses and tissue culture infrastructures. It remains an open question, whether the Aphidomorpha present in Kew should be treated as an element of its biodiversity or an element threatening this diversity.

Aphids are strictly associated with their host plants. The presence of the host plant determines the presence of aphids, so it can be expected that with the constant species composition of plants in Kew, species composition of aphids will also be constant over time.

Comparing both Eastops aphid lists[28,29], it can be seen that in the following years the species composition of the aphids varied significantly, in terms of quantity. In 1962, 91 species were found, while in 1965 77 taxa. In both lists we find only 25 common species. In 1962, greater variation was also demonstrated in the level of subfamilies and genera and the number of alien and pest species. Macrosiphini was dominant in both lists (Table 3). Comparing the whole aphid fauna collected by Eastop[28,29], and during the present study, it is worth underlining, that in four years of collection, Eastop identified 142 taxa. In comparison, collecting aphids within twelve days allowed for identification of 95 species. The first conclusion is that the Kew aphid fauna is still rich and in a relatively short time a large number of aphid samples can be collected. However, comparing Eastop’s lists of species and results of the current study only 50 taxa are found in common (28 species in 1962 and 27 species in 1965). In the 1960’s Eastop collected 90 taxa that were not recorded during the present study. At the same time, current research has provided information on 45 species not listed by Eastop (Tables 2 and 3). Most of these species are in general widespread and common, some of them were collected by Eastop in Kew district but outside the Garden[28,29] and are not included in the Table 2. The differences in the number of collected taxa results rather from the time spent collecting aphids (four years versus twelve days), than other conditions. The research was conducted in June, convenient due to the biology of aphids (both monoecious or heteroecious species) for collecting these insects. An exception may be species that in the early summer do not appear, like Tuberolachnus salignus (Gmelin, 1790), or which finish their life cycle earlier, such as aphids of the genus Glyphina[33], both of them listed by Eastop[28,29]. The exception may also apply to species for various reasons considered rare in the Britain aphidofauna[33,34], such as Callipterinella calliptera (Hartig, 1841), Clethrobius comes (Walker, 1848), Monaphis antennata (Kaltenbach, 1843), Pterocallis (Pterocallis) maculata (von Heyden, 1837) or Lachnus pallipes (Hartig, 1841), found during this study. As Macrosiphini are dominant among species that were not common on both lists, the number of economically important species of aphids, capable of virus transmission, is twice as high in Eastop’s study, as in the current survey. However, the number of species of foreign origin found during present study is twice as high compared to Eastop’s lists. This is obvious, because at least five of these species have been found in Europe in recent decades (e.g. Illinoia (M.) lambersi in 1971, Macrosiphum (M.) albifrons in 1981 or Illinoia (I.) liriodendri in 1998)[12]. It is also worth emphasizing, that among 155 listed host plants, 23 are regarded as threatened according to the IUCN. Most of them have a very limited distribution and a restricted habitat in their native range. For example, Wahlenbergia angustifolia is endemic to the island of St Helena, listed as Vulnerable[35], whereas Abies pinsapo, distributed in small areas of Spain and Morocco, is listed as Endangered[36]. Our research proves, that far away from their natural range, in favourable conditions, they can be also colonized by aphids. In the case of endemic or native plant species, in their natural range, this threat can be important[37]. In addition to sampling aphids from threatened species of host plants, they were also collected from one of Kew Gardens’ Heritage trees, Quercus × hispanica ‘Lucombeana’, which is believed to have been planted at Kew in 1773.

Table 3

The most important quantitative data resulting from the Eastops’ lists (1962, 1965) and current research (2017).

	Eastop 1962	Eastop 1965	2017 (present study)
Total number of taxa	91	77	94
Total number of taxa	142
Total number of taxa	186
Common number of taxa	50
Taxonomic comparison
Adelginae	0	0	1
Phylloxerinae	0	0	1
Eriosomatinae	3	3	2
Anoeciinae	1	0	1
Thelaxinae	1	3	2
Mindarinae	1	0	1
Drepanosiphinae	1	0	1
Phyllaphidinae	1	0	1
Calaphidinae	7	13	21
Saltusaphidinae	0	1	0
Chaitophorinae	5	4	10
Aphidinae/Aphidini	13	8	13
Aphidinae/Macrosiphini	51	41	31
Lachninae	7	4	9
Alien species
	12	10	20
Common number of taxa	4
Pest species
	25	17	20
Common number of taxa	9

In total, 191 species of aphids have been listed from Kew[28-32,38], including the present study, which is almost 1/3 of species presented in the check-list of aphids in Britain[39]. Kew includes globally significant ex situ collections, covering approximately a third of known plant diversity. Therefore, it is not surprising, that due to the diversity of host plants from different parts of the world, the variety of aphids associated with them is so large and it will probably grow.

Aphid species are not evenly distributed within Europe. The number of alien species present in a country is significantly and positively correlated with the number of native species recorded in that country, and, to a lesser extent, with the number of local taxonomists. Great Britain, with 65 alien aphid species, is on the top of European countries with identified numbers of those species. Among them, 36 were a first European record and at least five of them were first detected in Kew. Most of those species (18) came from North America, ten from Temperate Asia, two from Africa or tropical/subtropical areas of the world, respectively, two from Asia (generally) and two are cryptogenic[12]. The first record of alien species in the British aphidofauna (and Europe as a whole) concerned Eriosoma lanigerum (Hausmann, 1802) recorded in 1787[40]. The newest record is the presence of Ericolophium holsti, trapped in 2011[13]. The detection of species over the years has also been interesting. In 18th and 19th centuries there were three species, in 20th century 30 species (with the greatest number between 1950–1980 when 14 alien species were recorded, ten from North America) and in 21st century three species have been found[12,13].

The aphid fauna of Kew includes a significant number of non-native aphid species. In 1962 and 1965 Eastop listed 18 alien species (on subsequent lists twelve and ten species, respectively). Among them Illinoia (I.) andromedae (MacGillivray, 1953) and Illinoia (I.) goldamaryae (Knowlton, 1938) (both from North America), were known as a first record for Europe. Unfortunately, during our study, the presence of those species in Kew was not confirmed. The third known species, recorded by Eastop[28] as new for Europe - Illinoia (I.) morrisoni (Swain, 1918), associated with Sequoia sempervirens, was collected during the present study from the young shoots of its host plant in the Redwood Grove, in the same location as 60 years ago. In Britain, since Eastop’s original find, this species has been found three times – in Scotland (2001, suction-trap), South Wales (2007 from the host-plant) and Kent (2014, from the host-plant)[33]. However, now is treated as common and widely distributed in Britain[33]. In Europe, this species was recorded from France[41], Italy[42] and Portugal[43].

Our inventory study brings data on ten additional non-native species of aphids detected in Kew (Table 2), at least half of these are known to be expanding their range. The clear movement of the alien aphid species is visible in the example of Neotoxoptera formosana (the onion aphid). The onion aphid, a pest of wild and cultivated (especially commercial) Allium has been recorded on the following hosts: Allium ascalonicum, A. cepa, A. chinense, A. fistulosum, A. porrum, A. sativum, A. schoenoprasum, A. tuberosum, and others[44]. In Europe this Asian species, is known from France (first record in 1984[45]), Finland (first record in 1994 on onions imported from the Netherlands), Italy (first record in 2000 on chives, A. schoenoprasum grown under glasshouse conditions[46], Germany (first record in 2006 on stored onions in Konstanz (Bruehl, pers. comm.) and in 2007 in two fields of chives[47]) and the Netherlands (first record in 1994 and in 2008 on chives from a garden centre[48]). In the UK, this pest was found in September 1999, on a stock of Welsh onions (A. fistulosum) growing in a plastic tub in the Model Vegetable Garden at RHS Wisley, Surrey. The following year, in May, the species was again detected at RHS Wisley. N. formosana does not usually occur in the UK, although winged form was trapped in 40 ft aerial suction traps at Kirton, Lincolnshire in May 2002 and from Silwood Park in October 2005[44]. Later, the species was detected in Fife, Scotland in 2008 and on an onion purchased at a supermarket in Inverness, Scotland in August 2013[33]. It has a narrow host range. However, now is widespread and well established in Britain[49] and it represents a potential risk to the UK Allium industry, which since 1995/96 has averaged approximately 13,000 ha with a value of just under £100 million. It can transmit viruses that cause plant damage and stunting although it is not a very efficient vector[44,47]. During the present study, the species was collected from the shoot of Allium nutans in the Rock Gardens of Kew. It proved that N. formosana can establish in Britain not only on Allium crops but also on common, wild Allium spp. and could survive in a cool maritime climate such as the UK.

To a lesser extent, we can now witness the expanding range of another non-native species. Ericolophium holsti is an alien species, first recorded in 2011 as new to Europe, which has only been recorded in the UK in the Rothamsted Insect Survey’s suction-traps. A single winged specimen was trapped in 2011 at Ascot, Berkshire, subsequently in 2012 three were caught at Rothamsted, Harpenden 60 km away[13]. In 2014 four specimens were caught, one each at Warwick, Harpenden, Hertfordshire; Boston, Lincolnshire; and Starcross, (near Exeter), Devon. This species of Asiatic origin, associated with Rhododendron spp., was not found in the field in Britain[50]. During this study, for the first time, the species was collected from the shoots of cultivated Rhododendron spp. in the Rhododendron Dell of Kew. The species was observed on three individuals of the host-plant – mostly winged morphs, however on one plant a colony of winged, wingless and nymphs was observed. This is the first record of E. holsti found in the field in the UK on its host. It is worth noting, that the new location in Kew (field study) is the closest to its original place of collection in Ascot, a distance of about 35 km (suction-trap). As a novel alien species detected in Europe, it is difficult to predict the impact of E. holsti on its host-plants. There was a similar situation for Cinara curvipes (Patch, 1912), which was first recorded in 1999 in Kew[32] and soon spread to other parts of the UK[51]. Its spread into continental Europe was also very quick, as the species was detected in 2001 in Germany and Serbia; in 2007 in Switzerland, Czech Republic, Slovakia and Slovenia; in 2013 in Hungary; in 2014 in Austria; and in 2015 in Poland. C. curvipes is able to infest native European coniferous trees and in some countries, has pest status[52,53].

Thus, in Kew 30 species non-native for Europe have been listed so far[28,29,31,32], including the present study, which is half of all known non-native species detected in the UK. The combination of factors like a large and diverse collections of plants, the majority of which are exotic in Kew, the short distance to airports (Heathrow airport <11 km), seaports (the Port of London ~16 km) and human population density (London), promotes both the settlement and the spread of species of foreign origin, but firstly the introduction[54]. In particular, potential hotspots of invasions such as airports, should be monitored as a priority to prevent new invasions from these species[55,56] (e.g. at Heathrow, one of the world’s busiest airports close to Kew, various plants, including threatened ones, have been confiscated[57]). As Aphidomorpha are small insects, easily transported by air or with plant material, the number of introductions of aliens will probably increase, this is also linked to the continued expansion of the worldwide air transportation network[58]. Moreover, aphids are able to adapt to climate change faster than many other insect groups studied because of their low developmental threshold temperature and high intrinsic rate of increase[39]. Botanic gardens are not substitutes for study in natural areas but should be viewed as complementary. The plants are well identified thus making the identification of insects, even from exotic plants, easier. In particular, in the case of Aphidomorpha, which are mostly strictly associated with their host plants. The key factor is the prevention of an introduction of a non-native species. If prevention fails, then early detection and rapid response to remove the species becomes very important. It is easier to fight invasiveness if the discovery of the non-native species is made early[59]. With simple tools (short-term faunistic inventory of important insects) we achieved effective results. According to this, botanic gardens shouldn’t be the gateway for alien species, but instead the gateway to information on alien and invasive ones. Therefore, the database of such species (even in form of simple list) will help identify the scale and spatial pattern of invasive alien and pest species and can be used as a framework for considering indicators for early warning as well as a model for other studies.

Material and Methods

Collecting area

The Royal Botanic Gardens, Kew (Kew) are situated in the London Borough (district) of Richmond upon Thames, in southwest Greater London, United Kingdom, 51° 28′ 0.12″ N 0° 16′ 59.88″ W. Surveys reported here were carried out mostly in the collection of living plants grown unprotected outside in the Gardens, as well as a limited number in controlled conditions within glasshouses and nurseries on site. The abbreviations denote as follow: AColl. – Acer spp. collection; ARBN – Arboretum Nursery; BColl. – Betula spp. collection; PColl. – Populus spp. collection; QColl. – Quercus spp. collection; AG – Aquatic Garden; BG – Bamboo Garden; DG – Duke’s Garden; JG – Japanese Garden; L – Lake; MG – Mediterranean Garden; NO – near Orangery; P – Pond; PFB – Plant Family Beds; Pi – Pinetum; RD – Rhododendron Dell; RG – Rock Garden; RK – Royal Kitchen; ReG – Redwood Grove; RoG – Rose Garden; SVP – Student Vegetables Plot; TRON – Tropical Nursery. In the case of unlocalized records, the exact situation of the host plant was not specially noted. The source of map (Fig. 1) of collecting areas was the Gardens Development Unit, the Royal Botanic Gardens, Kew. The Fig. 1 was prepared using Corel Draw 17.1.0.572, 2014 Corel Corporation.

Sampling procedure

The investigation was conducted over a period of twelve days, from 5th to 16th June 2017. The aphids were collected directly from the host plants with a fine hair brush and placed into Eppendorf tubes containing 70% and 98% ethanol. Location, sampling date and host plant name were recorded on the labels placed onto the tubes.

Species identification

Adult wingless (apt. viv.) or winged (al. viv.) females (or aestivating larvae in the case of the genus Periphyllus van der Hoeven) were slide mounted using the method of Kanturski and Wieczorek[60] and identified to species level. The slides were examined using a Nikon Ni-U light microscope. Names and classification follow Nieto Nafría and Favret[61], with the exception of the taxonomic position of all the former Pterocommatinae, which have been placed in the tribe Macrosiphini. Samples were identified by K. Wieczorek based on morphological diagnostic features using standard literature-based keys[49,62-71]. Only small amount of samples were not identified as the immature generations (larvae or nymphs) were collected. These samples were not included into the list of species. The lists of alien Aphididae in Europe[12] were used to identify the alien species. An exclamation mark [!] beside the name denotes those species. Aliens are treated as species with native ranges outside Europe. Pest status was given according to Blackman and Eastop[1]. The aphid material is deposited in the collection of the Department of Zoology, University of Silesia, Katowice, Poland (DZUS) and will be subsequently digitalized. Voucher specimens for collected samples in 98% ethanol are deposited in the Lab-based Collections Royal Botanic Gardens, Kew, London, UK. The sources for the botanical nomenclature was the International Plant Names Index[72].

Supplementary Information.