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The Phytophagous Insect Fauna of Tanacetum Vulgare L. (Asteraceae) in Central Europe

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The Phytophagous Insect Fauna of Tanacetum Vulgare L. (Asteraceae) in Central Europe Beitr. Ent. Berlin ISSN 0005-805X 48 (1998) 1 S. 219-235 31.03.1998 The phytophagous insect fauna of Tanacetum vulgare L. (Asteraceae) in Central Europe With 4 tables G r eg o r Sc h m it z Summary A comprehensive description of the Central European phytophagous complex of Tanacetum vulgare L., 1753 (Asteraceae) is presented, based on personal observations, data from the literature and information from specialists. The phytophagous complex consists of 143 species, of which 13.3% are monophagous and 44.8% are restricted to Asteraceae. Larval development was recorded for 135 species. Roughly two- thirds of the species feed on the plant tissue while the rest are sap-suckers. Thirty-five percent of the species are endophytic. Twenty-five species are for the first time reported to live on T. vulgare, including a new species ofMelanagromyza (Dipt., Agroray zidae). The identity of a Liriomyza species (Agromyzidae) and a Lasioptera species (Cecidomyiidae) remained unresolved. The agricultural pest insects, for which T. vulgare represents a source of food, are listed. In order to find a suitable agent against T. vulgare, which has become a serious, alien pasture weed in some regions of North America, a preliminary selection of herbivores is given, which could be subjected to pre-release studies. Zusammenfassung Der mitteleuropäische Phytophagenkomplex von Tanacetum vulgareh., 1753 (Asteraceae) wird ausgehend von eigenen Beobachtungen, Literaturhinweisen und Angaben von Spezialisten dargestellt. Dem Komplex gehören 143 Arten an, von denen 13.3% monophag und 44.8% auf Asteraceae beschränkt sind. 135 Arten entwickeln sich als Larven an der Pflanze. Etwa zwei Drittel der Arten befressen Pflanzengewebe, während sich der Rest auf saugende Weise ernährt. Endophytisch leben 35% der Arten. Für 25 Arten wurde T. vulgare erstmals als Wirtspflanze festgestellt, darunter eine bisher unbeschriebene Melanagro- myza-Art (Dipt., Agromyzidae). Auch die Identität einer Liriomyza-Art (Agromyzidae) und einer Lasio­ ptera-hri (Cecidomyiidae) blieb ungeklärt. Es wird dargestellt, welche in der Landwirtschaft schädlichen Insekten sich von T. vulgare ernähren. Um brauchbare Gegenspieler gegen die in Nordamerika eingeführte und als lästiges Weideunkraut bedeutsame Pflanze zu finden, wird eine Auswahl von Phytophagen diskutiert, die für eingehendere biologische Prüfungen in Frage kommen. Keywords Tanacetum vulgare L., 1753 - herbivores - phytophagous insect fauna - biological weed control - Central Europe - Melanagromyza - guilds - spatial distribution - host specificity - feeding mode. DOI: 10.21248/contrib.entomol.48.1.219-235 Powered by TCPDF (www.tcpdf.org) 220 SCHMITZ, G.: The phytophagous insect fauna of Tanacetum vulgare L. 1. Introduction In Central Europe, tansy Tanacetum vulgare L. 1753 (Asteraceae) inhabits naturally disturbed areas along riverbanks and various anthropogenic sites, such as field ridges, wastelands, fallow lands and ruderal meadows (Wagenttz, 1987). As a characteristic species of the Artemisietea vulgaris Lohm., Prsg. et Tx. in Tx. 50, this perennial herb is an important member of the ruderal vegetation (Oberdörfer, 1979). The Eurasian plant was introduced in North America, Australia, New Zealand (for map see H ulten, 1968) and Reunion (WALTER & STRAKA, 1970) during the course of colonization. As described previously by Klausnjtzer (1966, 1968a), T. vulgare hosts a diverse entomo- fauna. However, no broadening studies of the phytophagous complex of the plant have since been conducted. Only isolated studies on the biology of the host-specific species of the complex are available. For example, biological data were collected for the following species: Uroleucon tanaceti (L.) (Horn., Aphididae) by HOLTFRETER (1977), Rhopalomyia tanaceticola K arsch (Dip., Cecidomyiidae) by Klausnitzer (1967a) and Haus (1991), Isophrictis striatella Denis & Sch iff. (Lep., Gelechiidae) by H aus (1991), and Depressaria emeritella S ir. (Oecophoridae) by Klausnitzer (1967b). This work provides an updated description of the phytophagous complex of T. vulgare. This information appears to be of interest for the following reasons: 1. A survey of the phytophagous insects of T. vulgare enables us to expand on current knowledge of the structure of the phytophagous complexes of herbaceous plants. The data seem to be of importance for comparing the utilization of a plant by insects in different distribution areas (c.f. Lawton 1984), and thus for more accurately assessing the status of the plant in local flora. In the case of T. vulgare, it is not completely certain whether the plant is indigenous or archeophytic in Central Europe (Lohmeyer & Sukopp, 1992). 2. An analysis of the complex would yield essential information for understanding the ecological effects of the plant in (Central European) farmlands. Klausnitzer (1968b), and later N entw ig (1992) and F rei & Man h art (1992), already showed that the plant hosts aphid species which are beneficial in biological control because they represent important alternative hosts for beneficial insects. The role of monophagous aphid species in this context is well documented. On the other hand, it must be considered that the plant is also an important host for agricultural pest species. Thus, this study presents and discusses a list of pest insects found on T. vulgare. 3. During the last ten years T. vulgare has become a serious pasture weed in some regions of North America where biocontrol programs are being considered. This development began with the cultivation of T. vulgare in colonial gardens on the east coast of North America for medicinal use. It migrated from there into the wild and then spread westward through the temperate zones (M m cH , 1992). Today T. vulgare is found from Nova Scotia and Ontario across Minnesota to Oregon and Nevada, and south roughly to North Carolina, Missouri and California (Britton & Brown, 1970; M m cH , personal communication, 1996). The species continues to spread in Alberta (Alberta Environmental Centre, 1993), particularly in the southern region of the former boreal mixedwoods (M cC lay, 1989; Stron g & Leeggat, 1981). In addition to roadsides, fallow lands, fence rows and riverbanks, the neophyte also colonizes pastures and meadows in some areas, where it has become an economic factor due to its rejection by livestock (West. Soc. Weed Sei., 1991; cf. Duke, 1985). T. vulgare has become one of the ten most serious pasture weeds in Washington and DOI: 10.21248/contrib.entomol.48.1.219-235 Powered by TCPDF (www.tcpdf.org) Beitr. Ent. 48 (1998) 1 221 Idaho (MmcH & Kyser, 1987). Experiments with chemical control methods have met with only partial success up to now, due to the ability of rhizomes to regenerate (Lass et al., 1987; M iller & Callihan, 1992). Biological control using herbivores appears to be increasingly indicated today (ScHROEDER, personal communication, 1995, STRONG & L eeggat, 1981). A description of the Central European complex of phytophagous insects on T. vulgare may permit a preliminary selection of species as candidates for use in bio­ logical control, which could then be subjected to pre-release studies. 2. Materials and methods Criteria for the inclusion of a species: The list of phytophagous insects and the following analyses pertain to Central Europe. Central Europe refers to the region from Denmark south­ ward to the main ridge of the Alps inclusive, and from eastern France (east of the Rhône) and the Benelux countries westward to central Poland and the border of the Czech Republic and Slovakia. Furthermore, this study is limited to arthropods, particularly those which feed on the living tissue or sap of T. vulgare. Species which appeared on T. vulgare at random are excluded. Proof of reproduction on the plant was not a mandatory requirement. Data from the literature are included if T. vulgare (or ”Chrysanthemum vulgare”) was cited as the host plant. In order to avoid errors, particularly those due to the consideration of out-dated host records, the lists were submitted to specialists for review (see acknowledgments). Field studies: Data were gathered in field studies conducted between 1992 and 1994 within the framework of a study of the impact of urbanization on the phytophagous insect complexes of Artemisia vulgaris L. and T. vulgare (Schm itz, 1995b, 1996, 1997). In this context, the presence of phytophagous insects was investigated on natural gravel sites around the Ahr river mouth (Rhineland Palatinate, Germany) as "primary habitats" and on ruderal sites in and around the city of Bonn (North Rhine-Westphalia) as anthropogenic sites. The above-ground sections of the plants were searched manually four times in each vegetation period (1992: 37 individual pat­ ches, 1993: 99 individual plants on 5 large sites). Flower-bud sections (1992: 10 buds from each of the 37 patches, 1993: 20 buds from each of 84 individual plants on 5 large sites) and root­ stocks (1992: 25 individual patches, 1993: 39 individual plants on 5 large sites) were investiga­ ted once each year. Stem inhabitants were collected using eclectors (SCHMITZ, 1995a) : (1992: 738 stems from the preceding year from 13 sites, 1993: 973 stems from the preceding year from 25 sites, 1994: 993 stems from the preceding year from 68 individual plants on 5 large sites). Larval morphology was used as the basis for identifying the leaf miners. The "Micro- lepidoptera" were collected in random samples by rearing them from the plants. The Traminae collected from the roots and several of the Miridae and Curculionidae
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